Environmental Protection Act
Loi sur la protection de l’environnement

R.R.O. 1990, REGULATION 347

GENERAL — WASTE MANAGEMENT

Consolidation Period: From December 17, 2014 to the e-Laws currency date.

Last amendment: O. Reg. 302/14.

This Regulation is made in English only.

SKIP TABLE OF CONTENTS

CONTENTS

   

Sections

 

Definitions

1

 

Designation and Exemption of Wastes

2-3

 

Waste Disposal Sites and Waste Management Systems

4-10

 

Standards for Waste Disposal Sites

11-16.1

 

Management of Asbestos Waste

17

 

Waste Generation Facilities

17.1-17.2

 

Generator Registration

18

 

Manifests — Generator Requirements

19

 

Manifests — Carrier Requirements

20-22

 

Manifests — Transport within Ontario

23

 

Manifests — Transport out of Ontario

24

 

Manifests — Transport into Ontario

25

 

Manifests — Transport through Ontario

26

 

Refusals

27

 

On-Site Thermal Treatment Equipment

28

 

Woodwaste Combustor Sites

28.1

 

Waste-Derived Fuel Sites

28.3-28.6

 

Existing Hospital Incinerators

29

 

Field Operations

29.1-29.5

 

Stationary Refrigerant Waste

30-35

 

Mobile Refrigerant Waste

36-42

 

Selected Waste Depots

42.1-42.17-60

 

Pesticide Container Depots

61-73

 

Land Disposal of Hazardous Waste

74-85

Schedule 1

Hazardous industrial waste

 

Schedule 1.1

Exempt hazardous industrial wastes

 

Schedule 2

Part a — acute hazardous waste chemical

 

Schedule 2

Part b — hazardous waste chemical

 

Schedule 2.1

Exempt acute hazardous waste chemicals

 

Schedule 2.2

Exempt hazardous waste chemicals

 

Schedule 3

Severely toxic contaminants

 

Schedule 4

Leachate quality criteria

 

Schedule 5

Land disposal treatment requirements for characteristic wastes

 

Schedule 6

Universal treatment standards (uts) for characteristic wastes

 

Schedule 7

Treatment methods and standards

 

Schedule 8

Alternative treatment for hazardous debris

 

Schedule 9

Test method for the determination of “liquid waste” (slump test)*

 

Schedule 10

 

Schedule 11

 

Schedule 12

 

Schedule 13

 

Definitions

1.  (1)  In this Regulation,

“access road” means a road that leads from a public road to a waste disposal site;

“acute hazardous waste chemical” means,

(a) a commercial waste chemical listed as an acute hazardous waste chemical in Part A of Schedule 2, other than a waste described in Schedule 2.1,

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless,

(i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 2.1, or

(ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of the acute hazardous waste chemical from which it was derived;

“agricultural waste” means waste generated by a farm operation activity, but does not include,

(a) domestic waste that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary waste,

(b) waste from a sewage works to which section 53 of the Ontario Water Resources Act applies,

Note: On January 1, 2015, clause (b) is revoked and the following substituted: (See: O. Reg. 302/14, ss. 1 (1), 4)

(b) waste from a sewage works within the meaning of the Ontario Water Resources Act, if one of the criteria set out in subsection (1.0.1) is met;

(c) a dead farm animal within the meaning of Ontario Regulation 106/09 (Disposal of Dead Farm Animals) made under the Nutrient Management Act, 2002 or a regulated dead animal within the meaning of Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001,

(d) inedible material within the meaning of Ontario Regulation 31/05 (Meat) made under the Food Safety and Quality Act, 2001, or

(e) any material that is condemned or derived from a carcass at a registered establishment within the meaning of the Meat Inspection Act (Canada);

“anaerobic digestion” means the decomposition of organic matter by bacteria in an oxygen-limiting environment;

“anaerobic digestion materials” means materials that are intended for treatment in a mixed anaerobic digestion facility, whether the materials are generated at the agricultural operation or received at the agricultural operation from an outside source;

“anaerobic digestion output” means any solid or liquid material that results from the treatment of anaerobic digestion materials in a mixed anaerobic digestion facility;

“aqueous waste” means waste that is aqueous and contains less than 1 per cent total organic carbon by weight and less than 1 per cent total suspended solids by weight;

“asbestos waste” means solid or liquid waste that results from the removal of asbestos-containing construction or insulation materials or the manufacture of asbestos-containing products and contains asbestos in more than a trivial amount or proportion;

“biodiesel” means a fuel or fuel component that is comprised of mono-alkyl esters of long-chain fatty acids that are derived from plant oils or animal fats, if the fuel or fuel component,

(a) conforms to the detailed requirements shown in Table 1 of ASTM International Standard D6751, entitled “Standard Specification for Biodiesel Fuel Blend Stock (B100) for Middle Distillate Fuels”, as amended from time to time, when tested by the test methods indicated in that Standard, or

(b) is in accordance with the limits specified in Table 1 of European Standard EN 14214, entitled “Automotive Fuels – Fatty acid methyl esters (FAME) for diesel engines – Requirements and test methods”, as amended from time to time, when tested by the test methods indicated in that Standard;

“carrier” means the operator of a waste transportation system;

“cell”, in respect of a landfilling site, means a deposit of waste that has been sealed by cover material so that no waste deposited in the cell is exposed to the atmosphere;

“characteristic waste” means hazardous waste that is,

(a) corrosive waste,

(b) ignitable waste,

(c) leachate toxic waste, or

(d) reactive waste;

“commercial waste” includes asbestos waste;

“commercial waste chemical” means a waste that is or contains a commercial chemical product or manufacturing chemical intermediate of a specified generic name and includes,

(a) an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name,

(b) residues or contaminated material from the clean-up of a spill of a commercial chemical product or manufacturing chemical intermediate of the specified generic name or of an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name, or

(c) an empty container or the liner from an empty container that contained a commercial chemical product or manufacturing chemical intermediate of the specified generic name, or an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name, or residues or contaminated materials from the clean-up of a spill of any of them, unless the empty container or the liner from the empty container has been triple rinsed,

but, except as specified in clause (a), (b) or (c), does not include a waste stream or waste material contaminated with material of the specified generic name;

“common mercury waste” means,

(a) electrical switches, thermostats or fluorescent lamps that contain mercury and that are damaged, worn out or discarded,

(b) thermometers, barometers or other measuring devices that contain mercury and that are damaged, worn out or discarded,

(c) discarded material that contains mercury from dental procedures carried out by a member of the Royal College of Dental Surgeons of Ontario;

“common mercury waste recovery facility” means a site at which common mercury waste is received for recovery of mercury and at which no disposal of common mercury waste or of mercury takes place;

“composting” means the treatment of waste by aerobic decomposition of organic matter by bacterial action for the production of stabilized humus;

“composting facility” means a facility,

(a) where composting is carried out, and

(b) in respect of which an environmental compliance approval has been issued under Part II.1 of the Act;

“composting material” has the same meaning as in Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001;

“corrosive waste” means,

(a) a waste that is aqueous and has a pH less than or equal to two or greater than or equal to 12.5 as determined by a pH meter,

(b) a waste that is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 millimetres per year at a test temperature of 55 Celsius using test NACE TM-01-69 or an equivalent test approved by the Director, or

(c) a waste that is a solid and, when prepared in a mixture or solution with distilled water that is 50 per cent waste by weight, has a pH less than or equal to two or greater than or equal to 12.5 as determined by a pH meter, other than,

(i) solid incinerator ash or fly-ash from a woodwaste combustor site, or

(ii) solid wastes generated by a manufacturer of pulp, paper, recycled paper, corrugated cardboard or other paper products;

“cover material” means soil or other material approved for use in sealing cells in landfilling;

“cured compost” has the same meaning as in Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001;

“derelict motor vehicle” means a motor vehicle that,

(a) is inoperable, and

(b) has no market value as a means of transportation, or, has a market value as a means of transportation that is less than the cost of repairs required to put it into operable condition;

“disposal facility” has the same meaning as in Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001;

“domestic waste” includes asbestos waste;

“dump” means a waste disposal site where waste is deposited without cover material being applied at regular intervals;

“dust suppressant” means a waste used for dust suppression in accordance with an environmental compliance approval in respect of a dust suppression waste management system;

“dust suppression site” means a waste disposal site where dust suppressant is deposited;

“electroplating” includes common and precious metal electroplating, anodizing, chemical etching and milling, and includes cleaning and stripping associated with common and precious metal electroplating, anodizing, chemical etching and milling, but does not include chromating, phosphating, immersion plating, colouring or other chemical conversion coating, electroless plating or printed circuit board manufacturing;

“empty container” means a container from which all wastes and other materials have been removed using the removal practices such as pumping or pouring commonly used for the specific materials and that contains less than 2.5 centimetres of material on the bottom of the container;

“engineered facility” means, in respect of a landfilling site, anything affixed to or made part of land that is intended to be a functional element or feature of the landfilling site for more than five years and that is created or put in place by human activity;

“existing hospital incinerator” means an incinerator put into operation before the 31st day of December, 1985 owned by a hospital within the meaning of the Public Hospitals Act at which pathological waste but no hauled liquid industrial waste or other hazardous waste is incinerated;

“farm operation” means an agricultural, aquacultural or horticultural operation, other than a race track or a zoo, that is engaged in any or all of the following:

1. Growing, producing or raising farm animals.

2. The production of agricultural crops, including greenhouse crops, maple syrup, mushrooms, nursery stock, tobacco, trees and turf grass.

3. The processing, by the operator of the farm operation, of anything mentioned in paragraphs 1 and 2, where the processing is primarily in relation to products produced from the agricultural, aquacultural or horticultural operation.

4. The use of transport vehicles by the operator of the farm operation, to transport anything mentioned in paragraphs 1 and 2, where the use of transport vehicles is primarily in relation to products produced from the agricultural, aquacultural or horticultural operation;

“farm operation activity” means an activity mentioned in paragraphs 1 to 4 of the definition of “farm operation”;

“field operations” means operations that,

(a) take place at a location that is not,

(i) the primary place of business of the person who undertakes the operations,

(ii) a warehouse, factory or production plant of the person who undertakes the operations, or

(iii) a local waste transfer facility,

(b) involve mobile health care, take place at a location that is owned or controlled by the person who undertakes the operations or take place in accordance with the written agreement of the person who owns or controls the location where the operations take place,

(c) are not primarily waste management operations, and

(d) primarily involve,

(i) construction, demolition or renovation,

(ii) mining,

(iii) servicing, maintaining or monitoring,

(iv) the operation of a utility, including communication networks, electric power lines or pipelines,

(v) the operation of highways, including a facility dedicated to the maintenance and upkeep of a section of highway,

(vi) environmental, geophysical or agricultural field testing,

(vii) mobile health care,

(viii) the supply of medical equipment or medication directly to the home of a human being to whom mobile health care is provided,

(ix) the operation of a specimen collection centre,

(x) the transportation in a vehicle of specimens and waste generated by the collection of specimens from a specimen collection centre, if,

(A) the specimens and waste result from the operation of the specimen collection centre,

(B) the sole purpose for which the vehicle is being operated is to transport the specimens and waste, and

(C) the specimens and waste are transported to a laboratory associated with the operation of the specimen collection centre,

(xi) spill clean-up or emergency response activities, if the person engaging in those activities is,

(A) the owner of the spilled material,

(B) a person who had control of the spilled material,

(C) a municipality,

(D) a person or member of a class of persons designated for the purposes of clause 100 (1) (c) of the Act,

(E) a person who has jurisdiction and control over a highway,

(F) a person who holds an environmental compliance approval issued in respect of an activity mentioned in subsection 27 (1) of the Act authorizing spill clean-up or emergency response activities,

(G) the Ministry,

(H) a police force, or

(I) a fire department,

(xii) housekeeping, maintenance and collection and removal of litter, rubbish, abandoned or discarded material and debris on or near a highway by a person who has jurisdiction and control over the highway,

(xiii) housekeeping, maintenance and collection and removal of littered, abandoned or discarded needles and syringes on or near parks, beaches or other public property by a person responsible for the maintenance of the property, or

(xiv) activities associated with operating trade shows, exhibitions or other temporary events;

“fly-ash” means particulate matter removed from combustion flue gases;

“food processing and preparation operations” include food packing, food preserving, wine making, cheese making and restaurants;

“generator” means the operator of a waste generation facility;

Note: On January 1, 2015, subsection (1) is amended by adding the following definition: (See: O. Reg. 302/14, ss. 1 (2), 4)

“GNF” means GNF within the meaning of Ontario Regulation 300/14 made under the Nutrient Management Act, 2002 that is generated at a greenhouse operation that is registered under that regulation;

“grinding” means the treatment of waste by uniformly reducing the waste to particles of controlled maximum size;

“hauled liquid and hazardous waste collection system” means a waste management system or any part thereof for the collection, handling, transportation, storage or processing of hauled liquid industrial waste or hazardous waste but does not include the disposal thereof;

“hauled liquid industrial waste” means liquid industrial waste transported in a tank or other container for treatment or disposal;

“hauled sewage” means,

(a) domestic waste that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary or sink waste or laundry waste, and

(b) other waste that is suitable for storage, treatment or disposal in a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992, if the waste is not fully disposed of at the site where it is produced, other than,

(i) waste that is,

(A) from a sewage works that is subject to an environmental compliance approval, and

(B) conveyed, by a sewer that is subject to an environmental compliance approval, away from the site where it is produced, or

(ii) waste in a vehicle sewage holding tank;

Note: On January 1, 2015, clause (b) is amended by striking out “or” at the end of subclause (b) (i), by adding “or” at the end of subclause (b) (ii) and by adding the following subclause: (See: O. Reg. 302/14, ss. 1 (3), 4)

(iii) GNF;

“hazardous industrial waste” means,

(a) a waste listed as a hazardous industrial waste in Schedule 1, other than a waste described in Schedule 1.1,

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless,

(i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 1.1, or

(ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of the hazardous industrial waste from which it was derived;

“hazardous waste” means a waste that is a,

(a) hazardous industrial waste,

(b) acute hazardous waste chemical,

(c) hazardous waste chemical,

(d) severely toxic waste,

(e) ignitable waste,

(f) corrosive waste,

(g) reactive waste,

(h) radioactive waste, except radioisotope wastes disposed of in a landfilling site in accordance with the written instructions of the Canadian Nuclear Safety Commission,

(i) pathological waste,

(j) leachate toxic waste, or

(k) PCB waste,

but does not include,

(l) hauled sewage,

(m) waste from the operation of a sewage works subject to the Ontario Water Resources Act where the works,

(i) is owned by a municipality,

(ii) is owned by the Crown or the Ontario Clean Water Agency, subject to an agreement with a municipality under the Ontario Water Resources Act, or

(iii) receives only waste similar in character to the domestic sewage from a household,

(n) domestic waste,

(o) incinerator ash resulting from the incineration of waste that is neither hazardous waste nor liquid industrial waste,

(p) waste that is a hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste and that is produced in any month in an amount less than five kilograms or otherwise accumulated in an amount less than five kilograms,

(q) waste that is an acute hazardous waste chemical and that is produced in any month in an amount less than one kilogram or otherwise accumulated in an amount less than one kilogram,

(r) an empty container or the liner from an empty container that contained hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste,

(s) an empty container of less than twenty litres capacity or one or more liners weighing, in total, less than ten kilograms from empty containers, that contained acute hazardous waste chemical,

(t) the residues or contaminated materials from the clean-up of a spill of less than five kilograms of waste that is a hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste, or

(u) the residues or contaminated materials from the clean-up of a spill of less than one kilogram of waste that is an acute hazardous waste chemical;

“hazardous waste chemical” means,

(a) a commercial waste chemical listed as a hazardous waste chemical in Part B of Schedule 2, other than a waste described in Schedule 2.2,

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless,

(i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 2.2, or

(ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of the hazardous waste chemical from which it was derived;

“highway” has the same meaning as in the Highway Traffic Act;

“hospital incinerator” means an incinerator owned by a hospital within the meaning of the Public Hospitals Act;

“ignitable waste” means a waste that,

(a) is a liquid, other than an aqueous solution containing less than 24 per cent alcohol by volume and has a flash point less than 61 Celsius, as determined by the Tag Closed Cup Tester (ASTM D-56-79), the Setaflash Closed Cup Tester (ASTM D-3243-77 or ASTM D-3278-78), the Pensky-Martens Closed Cup Tester (ASTM D-93-79), or as determined by an equivalent test method approved by the Director,

(b) is a solid and is capable, under standard temperature and pressure, of causing fire through friction, absorption of moisture or spontaneous chemical changes and, when ignited, burns so vigorously and persistently that it creates a danger,

(c) is a Class 2.1 Flammable Gas within the meaning of paragraph 2.14(a) of the Transportation of Dangerous Goods regulations made under the Transportation of Dangerous Goods Act (Canada),

(d) is a Class 5.1 Oxidizing Substance within the meaning of paragraph 2.24(a) of the Transportation of Dangerous Goods regulations made under the Transportation of Dangerous Goods Act (Canada), or

(e) is a Class 5.2 Organic Peroxide within the meaning of paragraph 2.24(b) of the Transportation of Dangerous Goods regulations made under the Transportation of Dangerous Goods Act (Canada);

“incinerator ash” means the ash residue, other than fly-ash, resulting from incineration where the waste is reduced to ashes containing by weight less than 10 per cent of combustible materials;

“incinerator waste” means the residue from incineration, other than incinerator ash and fly-ash;

“individual collection system” means the collection of a householder’s own domestic wastes by a householder and the transportation of such wastes to a waste disposal site by the householder;

“industrial waste” means waste, other than municipal waste, from,

(a) an enterprise or activity involving warehousing, storage or industrial, manufacturing or commercial processes or operations,

(b) research or an experimental enterprise or activity,

(c) an enterprise or activity to which clause (a) would apply if the enterprise or activity were carried on for profit,

(d) clinics that provide medical diagnosis or treatment,

(e) schools, laboratories or hospitals, or

(f) a facility or vehicle owned or operated by a municipality;

“inert fill” means earth or rock fill or waste of a similar nature that contains no putrescible materials or soluble or decomposable chemical substances;

“intact manifest” means a paper manifest as provided by the Ministry, with all six parts intact;

“intact waste battery” means an electric battery that is intact but is damaged, spent, worn out or discarded;

“in-vehicle sewage” means waste produced in a vehicle that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary or sink waste, laundry waste or similar waste that would normally be carried away by a sewer if it were not produced in a vehicle;

“laboratory” has the same meaning as in the Laboratory and Specimen Collection Centre Licensing Act;

“land disposal” means, with respect to a waste, the deposit or disposal of the waste upon, into, in or through land, including,

(a) the deposit of the waste at a dump,

(b) the landfilling of the waste,

(c) the discharge of the waste into a geological formation by means of a well, and

(d) the landfarming of the waste, in the case of a petroleum refining waste,

and “land disposed” has a corresponding meaning;

“landfarming” means the biodegradation of petroleum refining wastes by naturally occurring soil bacteria by means of controlled application of the wastes to land followed by periodic tilling;

“landfilling” means the disposal of waste by deposit, under controlled conditions, on land or on land covered by water, and includes compaction of the waste into a cell and covering the waste with cover materials at regular intervals;

“leachate toxic waste” means a waste producing leachate containing any of the contaminants listed in Schedule 4 at a concentration equal to or in excess of the concentration specified for that contaminant in Schedule 4 using the Toxicity Characteristic Leaching Procedure;

“liquid industrial waste” means waste that is both liquid waste and industrial waste but does not include,

(a) hazardous waste,

(a.1) hauled sewage,

Note: On January 1, 2015, the definition of “liquid industrial waste” is amended by adding the following clause: (See: O. Reg. 302/14, ss. 1 (4), 4)

(a.2) GNF,

(b) waste from the operation of a sewage works described in clause (m) of the definition of “hazardous waste”,

(c) waste from the operation of a water works subject to the Ontario Water Resources Act or the Safe Drinking Water Act, 2002,

(d) waste that is produced in any month in an amount less than twenty-five litres or otherwise accumulated in an amount less than twenty-five litres,

(e) waste directly discharged by a generator from a waste generation facility into,

(i) a sewage works, other than a storm sewer, that is subject to the Ontario Water Resources Act or was established before April 3, 1957, or

(ii) a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992,

(f) waste that results directly from food processing and preparation operations,

(g) drilling fluids and produced waters associated with the exploration, development or production of crude oil or natural gas,

(h) processed organic waste, or

(i) asbestos waste;

“liquid waste” means waste that has a slump of more than 150 millimetres using the Test Method for the Determination of Liquid Waste (slump test) set out in Schedule 9;

“listed waste” means hazardous waste that is,

(a) an acute hazardous waste chemical,

(b) hazardous industrial waste,

(c) a hazardous waste chemical, or

(d) severely toxic waste;

“local waste transfer facility” means a site,

(a) at which waste from field operations is received, bulked, temporarily stored and transferred,

(b) that is owned or controlled by the person who undertakes the field operations referred to in clause (a) or by a person on whose behalf those field operations are undertaken,

(c) at which no waste is received other than waste from field operations, and

(d) that is used primarily for functions other than waste management;

“lubricating oil” means petroleum-derived or synthetic crankcase oil, engine oil, hydraulic fluid, transmission fluid, gear oil, heat transfer fluid, or other oil or fluid used for lubricating machinery or equipment;

“manifest” means a numbered document called a manifest that was obtained from the Ministry and includes a paper or electronic manifest;

“Manual” means the publication entitled “Registration Guidance Manual for Generators of Liquid Industrial and Hazardous Waste”, published by the Ministry of Environment and Energy and dated April 1995, as amended from time to time;

“marine craft waste disposal system” means a waste disposal system operated by a person or a municipality for the receiving of waste from marine craft for deposit in holding tanks;

“Ministry website” means the website at www.ene.gov.on.ca;

“mixed anaerobic digestion” means anaerobic digestion of both on-farm anaerobic digestion materials and off-farm anaerobic digestion materials in the same facility;

“mixed anaerobic digestion facility” means an anaerobic digestion facility that treats both on-farm anaerobic digestion materials and off-farm anaerobic digestion materials on a farm unit on which an agricultural operation is carried out;

“mobile health care” means human or animal health care that takes place at,

(a) the home of a human being or animal to whom the health care is provided, or

(b) a location at which emergency services or ambulance services are provided to a human being or animal,

but does not include health care that is provided at,

(c) a hospital as defined in the Public Hospitals Act or a private hospital as defined in the Private Hospitals Act,

(d) an institution as defined in the Mental Hospitals Act,

(e) a nursing home as defined in the Nursing Homes Act,

(f) a home as defined in the Homes for the Aged and Rest Homes Act,

(g) a home for special care as defined in the Homes for Special Care Act,

(h) the professional office of a member of the Royal College of Dental Surgeons of Ontario,

(i) the professional office of a member of the College of Physicians and Surgeons of Ontario,

(j) the professional office of a member of the College of Nurses of Ontario, or

(k) the professional office of a member of the College of Veterinarians of Ontario;

“mobile refrigerant waste” means refrigerant removed from the air-conditioning, heat pump, refrigeration or freezer unit of anything used for the purposes of transportation;

“mobile refrigerant waste collector” means a mobile refrigerant waste management system that collects mobile refrigerant waste it has removed from equipment in which refrigerant is used;

“mobile refrigerant waste recycler” means a mobile refrigerant waste management system that receives mobile refrigerant waste from other mobile refrigerant waste management systems and recycles it;

“municipal waste” means,

(a) any waste, whether or not it is owned, controlled or managed by a municipality, except,

(i) hazardous waste,

(ii) liquid industrial waste, or

(iii) gaseous waste, and

(b) solid fuel, whether or not it is waste, that is derived in whole or in part from the waste included in clause (a);

“non-aqueous waste” means waste that is not aqueous waste;

“non-hazardous solid industrial waste” means industrial waste that is not liquid industrial waste and is not hazardous waste and includes asbestos waste;

“off-farm anaerobic digestion materials” means anaerobic digestion materials that are not generated at an agricultural operation and that are received at an agricultural operation from an outside source;

“on-farm anaerobic digestion materials” means anaerobic digestion materials that are generated at an agricultural operation;

“on-site garbage grinder” means a grinder,

(a) used for the treatment of waste that is subsequently discharged as sewage, and

(b) located in a building or structure used principally for functions other than waste management;

“on-site incinerator” means an incinerator located at a site used principally for functions other than waste management in which only waste generated on that site is incinerated;

“on-site road” means a road for the movement of vehicles and equipment within a waste disposal site;

“on-site thermal treatment equipment” means thermal treatment equipment located at a site used principally for functions other than waste management in which only waste generated on that site is subject to thermal treatment, and includes an on-site incinerator;

“organic soil conditioning” means the incorporation of processed organic waste in the soil to improve its characteristics for crop or ground cover growth;

“packing and baling” means the treatment of waste by its compression into blocks or bales and binding or sheathing the blocks with wire, metal, plastic or other material;

“pathological waste” means,

(a) any part of the human body, including tissues and bodily fluids, but excluding fluids, extracted teeth, hair, nail clippings and the like, that are not infectious,

(b) any part of the carcass of an animal infected with a communicable disease or suspected by a licensed veterinary practitioner to be infected with a communicable disease,

(c) non-anatomical waste infected with communicable disease,

(d) a mixture of a waste referred to in clause (a), (b) or (c) and any other waste or material, or

(e) a waste derived from a waste referred to in clause (a), (b) or (c), unless the waste that is derived from the waste referred to in clause (a), (b) or (c) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of pathological waste referred to in clause (a), (b) or (c);

“PCB” has the same meaning as in Regulation 362 of the Revised Regulations of Ontario, 1990 (Waste Management — PCBs) made under the Act;

“PCB waste” has the same meaning as in Regulation 362 of the Revised Regulations of Ontario, 1990 (Waste Management — PCBs) made under the Act;

“processed organic waste” means waste that is predominantly organic in composition and has been treated by aerobic or anaerobic digestion, or other means of stabilization, and includes sewage residue from sewage works that are subject to the provisions of the Ontario Water Resources Act;

“radioactive waste” includes,

(a) a mixture of radioactive waste and any other waste or material, and

(b) a waste derived from radioactive waste, unless the waste that is derived from the radioactive waste is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of radioactive waste;

“reactive waste” means a waste that,

(a) is normally unstable and readily undergoes violent change without detonating,

(b) reacts violently with water,

(c) forms potentially explosive mixtures with water,

(d) when mixed with water, generates toxic gases, vapours or fumes in a quantity sufficient to present danger to human health or the environment,

(e) is a cyanide or sulphide bearing waste which, when exposed to pH conditions between two and 12.5, can generate toxic gases, vapours or fumes in a quantity sufficient to present danger to human health or the environment,

(f) is capable of detonation or explosive reaction if it is subjected to a strong initiating source or if heated under confinement,

(g) is readily capable of detonation or explosive decomposition or reaction at standard temperature and pressure,

(h) is a Class 1 Explosive within the meaning of section 2.9 of the Transportation of Dangerous Goods regulations made under the Transportation of Dangerous Goods Act (Canada);

“receiver” means the operator of any facility to which waste is transferred by a carrier;

“regulated mixed anaerobic digestion facility” means a mixed anaerobic digestion facility that,

(a) is regulated under Part IX.1 of Ontario Regulation 267/03 (General) made under the Nutrient Management Act, 2002, and

(b) is not subject to an environmental compliance approval issued in respect of an activity mentioned in subsection 27 (1) of the Act;

“scavenging” means the uncontrolled removal of reusable material from waste at a waste disposal site;

“severely toxic waste” means,

(a) a waste that contains a contaminant listed as a severely toxic contaminant in Schedule 3 at a concentration greater than one part per million,

(b) a mixture of a waste referred to in clause (a) and any other waste or material, or

(c) a waste derived from a waste referred to in clause (a), unless the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of severely toxic waste referred to in clause (a);

“site” means one property and includes nearby properties owned or leased by the same person where passage from one property to another involves crossing, but not travelling along, a public highway;

“soil mixture” includes a mixture of soil and liquids, sludges or solids, where,

(a) the mixture cannot be separated by simple mechanical removal processes; and

(b) based on visual inspection, the volume of the mixture is made up primarily of soil or other finely divided material that is similar to soil;

“specimen collection centre” has the same meaning as in the Laboratory and Specimen Collection Centre Licensing Act;

“stationary refrigerant waste” means refrigerant that is not mobile refrigerant waste and that is removed from an air-conditioning unit, heat pump, refrigeration or freezer unit;

“stationary refrigerant waste collector” means a stationary refrigerant waste management system that collects stationary refrigerant waste it has removed from equipment in which refrigerant is used;

“stationary refrigerant waste recycler” means a stationary refrigerant waste management system that receives stationary refrigerant waste from other stationary refrigerant waste management systems and recycles it;

“subject waste” means,

(a) liquid industrial waste,

(b) hazardous waste, and

(b.1) waste that was characteristic waste but that has been treated so that it is no longer characteristic waste, if the waste may not be disposed of by land disposal under subsection 79 (1),

but does not include waste described in subsection (3);

“thermal treatment” includes incineration, gasification, pyrolysis or plasma arc treatment;

“thermal treatment site” means a waste disposal site where thermal treatment is used;

“total waste disposal volume” means, for a landfilling site, the maximum volume of waste, including the volume of any daily or intermediate cover, to be deposited at the site in the space extending from the base of the waste fill zone or the top of any engineered facilities located on the base of the site to the bottom of the final cover;

“Toxicity Characteristic Leaching Procedure” means the Toxicity Characteristic Leaching Procedure, Method 1311, that appears in United States Environmental Protection Agency Publication SW-846 entitled “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, as amended from time to time, or a test method that the Director has approved in writing as equivalent;

“transfer” means physical transfer of possession;

“transfer station” means a waste disposal site used for the purpose of transferring waste from one vehicle to another for transportation to another waste disposal site;

“treatment code” means a code listed as a treatment code in Schedule 7;

“vehicle” includes a rail car;

“vehicle sewage holding tank” means a device permanently mounted in or on a vehicle to receive in-vehicle sewage produced in the vehicle;

“waste battery recovery facility” means a site at which intact waste batteries are received for recovery of battery components and at which no disposal of intact waste batteries or of recovered battery components takes place;

“waste biomass” means organic matter that is derived from a plant or animal, that is available on a renewable basis and that is,

(a) waste from harvesting or processing agricultural products or forestry products,

(b) waste resulting from the rendering of animals or animal by-products,

(c) solid or liquid material that results from the treatment of wastewater generated by a manufacturer of pulp, paper, recycled paper or paper products, including corrugated cardboard,

(d) waste from food processing and preparation operations, or

(e) woodwaste;

“waste electrical and electronic equipment” has the same meaning as in Ontario Regulation 393/04 (Waste Electrical and Electronic Equipment) made under the Waste Diversion Act, 2002;

“waste fill zone” means the three-dimensional zone in which waste is disposed of by landfilling;

“waste generation facility” means those facilities, equipment and operations that are involved in the production, collection, handling or storage of waste at a site;

“waste transportation system” means those facilities, equipment and operations that are involved in transporting waste beyond the boundaries of a site or from site to site;

“waste-derived fuel” means waste that,

(a) is hazardous waste, liquid industrial waste, waste described in clause (p), (q), (r), (s), (t) or (u) of the definition of “hazardous waste” or waste described in clause (d) of the definition of “liquid industrial waste”,

(b) contains not more than 5 milligrams per kilogram arsenic, not more than 2 milligrams per kilogram cadmium, not more than 10 milligrams per kilogram chromium, not more than 50 milligrams per kilogram lead, not more than 2 milligrams per kilogram PCBs (as defined in Regulation 362 of the Revised Regulations of Ontario, 1990) and not more than 1,500 milligrams per kilogram total halogens,

(c) has a flash point of at least 38 Celsius as determined by the Tag Closed Cup Tester (ASTM D-56-79), the Setaflash Closed Cup Tester (ASTM D-3243-77 or ASTM D-3278-78), the Pensky-Martens Closed Cup Tester (ASTM D-93-79) or an equivalent test method approved by the Director,

(d) has a quality as fuel not worse than commercially available low grade fuel, and

(e) is located at or destined for a waste-derived fuel site, where it will be wholly utilized as a fuel or fuel supplement in a combustion unit;

“waste-derived fuel site” means a waste disposal site where waste-derived fuel is wholly utilized as a fuel or fuel supplement in a combustion unit used principally for functions other than waste management and the site may include blending or bulking facilities but may not include facilities for treatment or processing of waste-derived fuel generated off the site;

“woodwaste” means waste,

(a) that is wood or a wood product, including tree trunks, tree branches, leaves and brush,

(b) that is not contaminated with chromated copper arsenate, ammoniacal copper arsenate, pentachlorophenol or creosote, and

(c) from which easily removable hardware, fittings and attachments, unless they are predominantly wood or cellulose, have been removed,

but does not include,

(d) an upholstered article, or

(e) an article to which a rigid surface treatment is affixed or adhered, unless the rigid surface treatment is predominantly wood or cellulose;

“woodwaste combustor site” means a waste disposal site where woodwaste is subject to thermal treatment or wholly utilized as a fuel or fuel supplement in a combustion unit. R.R.O. 1990, Reg. 347, s. 1; O. Reg. 240/92, s. 1; O. Reg. 501/92, s. 1; O. Reg. 555/92, s. 1; O. Reg. 105/94, s. 1; O. Reg. 190/94, s. 1; O. Reg. 512/95, s. 1; O. Reg. 157/98, s. 1; O. Reg. 460/99, s. 1; O. Reg. 558/00, s. 1 (1-11); O. Reg. 501/01, s. 1; O. Reg. 323/02, s. 1; O. Reg. 461/05, s. 1; O. Reg. 102/07, s. 1 (1-6); O. Reg. 280/07, s. 1; O. Reg. 292/07, s. 1; O. Reg. 395/07, s. 1; O. Reg. 217/08, s. 1 (1); O. Reg. 110/09, s. 1; O. Reg. 336/09, s. 1; O. Reg. 337/09, s. 1; O. Reg. 234/11, s. 1 (1-13); O. Reg. 283/12, s. 1; O. Reg. 334/13, s. 1.

Note: On January 1, 2015, section 1 is amended by adding the following subsection: (See: O. Reg. 302/14, ss. 1 (5), 4)

(1.0.1)  For the purposes of clause (b) of the definition of “agricultural waste” in subsection (1), one of the following criteria must be met for waste from a sewage works to be excluded from the definition of “agricultural waste”:

1. Section 53 of the Ontario Water Resources Act applies to the sewage works.

2. The sewage works is for the management of GNF and the following criteria are met:

i. Section 53 of the Ontario Water Resources Act does not apply to the sewage works under clause 53 (6) (a) of that Act or section 3.3 of Ontario Regulation 525/98 (Approval Exemptions) made under that Act.

ii. Ontario Regulation 300/14 (Greenhouse Nutrient Feedwater) made under the Nutrient Management Act, 2002 does not apply to the management of the GNF under subsection 1 (3) of that regulation. O. Reg. 302/14, s. 1 (5).

(1.1)  For the purpose of better understanding the definition of “engineered facility” in subsection (1), the following things are examples of common engineered facilities, if they are intended to be functional elements or features of a landfilling site for more than five years:

1. Berms.

2. Drainage ditches.

3. Liners.

4. Covers.

5. Pumps.

6. Facilities to detect, monitor, control, collect, redirect or treat leachate, surface water or ground water.

7. Facilities to detect, monitor, control, collect, redirect, treat, utilize or vent landfill gas. O. Reg. 217/08, s. 1 (2).

(2)  For the purpose of this Regulation, a waste is derived from a hazardous waste if it is produced from the hazardous waste by blending, stabilization, processing, treatment or disposal. O. Reg. 558/00, s. 1 (12).

(3)  The definition of “subject waste” in subsection (1) does not include the following wastes:

1. Waste from the servicing of motor vehicles at a retail motor vehicle service station or service facility that has a written agreement for the collection and other management of such waste with the owner or operator of a waste management system in respect of which an environmental compliance approval has been issued authorizing the collection and other management of such waste.

2. Intact waste batteries destined for a waste battery recovery facility.

3. Common mercury waste destined for a common mercury waste recovery facility.

4. Waste electrical and electronic equipment that is intact and is destined for a site at which it is to be processed for the recovery of materials.

5. Printed circuit boards that are waste, are intact and are destined for a site at which they are to be processed for the recovery of materials.

6. Waste from,

i. a nursing home under the Nursing Homes Act,

ii. a home under the Homes for the Aged and Rest Homes Act,

iii. a home for special care under the Homes for Special Care Act,

iv. the professional office of a member of the Royal College of Dental Surgeons of Ontario, or

v. the professional office of a member of the College of Physicians and Surgeons of Ontario. O. Reg. 102/07, s. 1 (7); O. Reg. 234/11, s. 1 (14).

Designation and Exemption of Wastes

2.  (1)  The following are designated as wastes:

1. Dust suppressant.

2. Inert fill.

3. Processed organic waste.

4. Material that consists solely of waste from one or more of the categories set out in Schedule 1, 2 or 3 of Ontario Regulation 101/94 and that either,

i. has been separated from other kinds of waste at the source of the material, or

ii. comes from a waste disposal site.

5. Rock fill or mill tailings from a mine.

6. Waste-derived fuel.

7. Hazardous waste.

8. Hauled liquid industrial waste.

9. Used tires that have not been refurbished for road use.

10. Stationary refrigerant waste.

11. Mobile refrigerant waste.

12. Woodwaste.

13. Municipal waste.

14. Residue from an industrial, manufacturing or commercial process or operation, if the residue leaves the site where the process or operation is carried on.

15. Hauled sewage.

16. Used lubricating oil. O. Reg. 555/92, s. 2; O. Reg. 105/94, s. 2 (1); O. Reg. 128/98, s. 1; O. Reg. 157/98, s. 2; O. Reg. 280/07, s. 2.

Note: On January 1, 2015, subsection (1) is amended by adding the following paragraph: (See: O. Reg. 302/14, ss. 2, 4)

17. GNF.

(2)  The following materials from the time they leave a construction site or a demolition site are designated wastes:

1. Brick.

2. Corrugated cardboard.

3. Concrete.

4. Drywall.

5. Steel.

6. Wood. O. Reg. 105/94, s. 2 (2).

(3)  A designation set out in subsection (2) does not apply to material leaving a construction site or demolition site that is being delivered,

(a) to the vendor of the material for resale as construction material;

(b) to permanent premises of the person undertaking the construction or the person on whose behalf the construction is undertaken, for use as construction material by or for the person; or

(c) to permanent premises of the person undertaking the demolition or the person on whose behalf the demolition is undertaken, for use as construction material by or for the person. O. Reg. 105/94, s. 2 (2).

3.  (1)  The following wastes are exempted from Part V of the Act and this Regulation:

1. Agricultural wastes.

2. Inedible material within the meaning of Ontario Regulation 31/05 (Meat) made under the Food Safety and Quality Act, 2001.

2.1 Any material that is condemned or derived from a carcass at a registered establishment within the meaning of the Meat Inspection Act (Canada).

3. Dead farm animals within the meaning of Ontario Regulation 106/09 (Disposal of Dead Farm Animals) made under the Nutrient Management Act, 2002 or regulated dead animals within the meaning of Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001.

4. Revoked: O. Reg. 157/98, s. 3.

5. Inert fill.

6. Rock fill or mill tailings from a mine.

7. Material set out in subsection (2). R.R.O. 1990, Reg. 347, s. 3; O. Reg. 105/94, s. 3 (1); O. Reg. 157/98, s. 3; O. Reg. 110/09, s. 2 (1).

(2)  The material referred to in paragraph 7 of subsection (1) is any of the following:

1. Municipal waste, hazardous waste or liquid industrial waste, other than used or shredded or chipped tires, if,

i. the waste is transferred by a generator for direct transportation to a site to be wholly used at the site in an ongoing agricultural, commercial, manufacturing or industrial process or operation that,

A. is used principally for functions other than waste management, and

B. does not involve combustion or land application of the waste, or

ii. the waste is not processed organic waste from a composting facility and is transferred by a generator for direct transportation to a site,

A. to be promptly packaged for retail sale to meet a realistic market demand, or

B. to be offered for retail sale to meet a realistic market demand.

2. Municipal waste, consisting solely of waste from a single category of waste set out in Schedule 1, 2 or 3 of Ontario Regulation 101/94, transferred by a generator and destined for,

i. a waste disposal site that, but for the exemption in section 5 of Ontario Regulation 101/94, would be a municipal waste recycling site to which Part IV of that regulation applies and that is located at a manufacturing establishment that uses all the output, other than residues, of the site, or

ii. a site for use at the site in an ongoing agricultural, commercial, manufacturing or industrial process or operation used principally for functions other than waste management if the process or operation does not involve combustion or land application of the waste.

3. Residue remaining after metal is recovered from wire and cable and transferred by a generator for direct transportation to a site at which it will be processed for recovery of metal and plastic using a process that does not involve combustion of the residue or any part of the residue.

4. Chipped wood, other than chipped painted wood, chipped treated wood or chipped laminated wood, intended for use as ground cover.

5. Waste wood, other than painted wood, treated wood or laminated wood, transferred by a generator and destined for a site at which it is to be chipped for eventual use as ground cover.

6. Pickle liquor transferred by a generator for direct transportation to a site at which it is to be wholly utilized as a treatment chemical in,

i. a sewage works that is subject to the Ontario Water Resources Act,

i.1 a sewage works outside Ontario, if the utilization of pickle liquor for this purpose is acceptable to the environmental regulatory authority in the jurisdiction where the sewage works is located, or

ii. a wastewater treatment facility that discharges into a sanitary sewer.

7. Solid photographic waste that contains silver, including spent chemical recovery cartridges that contain silver, transferred by a generator and destined for a site at which it is to be processed for recovery of silver.

8. Waste paint or waste coatings transferred by a generator and destined for a site at which the waste is to be used in an ongoing manufacturing process for the production of paint or coatings, if the process does not involve combustion of the waste and the paint or coatings that are produced are not used as fuel.

9. Emission control dust from the primary production of steel in electric furnaces, if the dust is transferred by a generator for direct transportation to a site at which it is to be used as a feedstock in an ongoing high temperature metal recovery process in a rotary kiln, flame reactor, electric furnace, plasma arc furnace, slag reactor, industrial furnace or combination of a rotary hearth furnace and electric furnace.

10. Spent activated carbon transferred by a generator for direct transportation to a site at which it is to be used in a process to reactivate activated carbon.

11. Metal bearing waste, other than lead acid batteries or aqueous waste, that is transferred by a generator for direct transportation to a smelter at which the waste is to be used as a feedstock in an ongoing operation for the recovery of metal, including waste that, for the purpose of being used as a feedstock, is processed through size reduction, blending, calcining, roasting, sintering, drying, pelletizing, cleaning, leaching or separation of solids from liquids, but not including waste that, for the purpose of being used as a feedstock, is processed in any other manner.

12. Printed circuit boards that are waste and that are transferred by a generator and destined for a smelter at which they are to be used as a feedstock in an ongoing operation for the recovery of metal.

13. Waste that is to be processed and used at the same site where it is generated, if,

i. neither the processing nor the use of the waste involves combustion or land application of the waste, and

ii. the waste is not PCB waste, soil or a soil mixture.

14. Waste biomass transferred by a generator and destined for a site at which it is to be used as a feedstock in the production of ethanol or biodiesel, whether or not it is processed before it is used as a feedstock and whether or not it is processed before it is received at the site at which it is to be used as a feedstock.

15. Crumb rubber recovered from used, chipped or shredded tires and destined for use as a feedstock in the production of rubber products other than fuel products.

16. Waste glass that is to be used as aggregate in pipe bedding or in the subsurface of roads or parking areas.

17. Waste asphalt pavement transferred by a generator for direct transportation to,

i. a site at which it is to be used as construction aggregate, or

ii. a site at which waste asphalt pavement is processed for use as construction aggregate and at which no disposal of waste or processed waste takes place.

18. Waste asphalt pavement transferred by a generator for direct transportation to a site at which waste asphalt pavement is stored for use as construction aggregate, if,

i. the waste asphalt pavement is stored at least 30 metres away from the nearest watercourse, lake or pond, or there are engineered works in place to prevent the waste from having any adverse effect on any watercourse, lake or pond, and

ii. the waste asphalt pavement is stored at,

A. a construction area for not more than 120 days,

B. a permanent place of business for a person who is in the business of construction,

C. a pit or quarry for which a permit or licence has been issued under the Aggregate Resources Act,

D. a road works yard owned by a municipality or the Crown in right of Ontario, or

E. a place that is at least 100 metres from the nearest dwelling.

19. Waste asphalt shingles transferred by a generator and destined for a site at which they will be used as aggregate or surface layer in the construction of walkways for pedestrian use, roads or parking areas, if, before being used for that purpose, the shingles are processed at a site at which the only processing that occurs is sorting, size reduction and the removal of other wastes from the shingles.

20. Organic waste from food processing and preparation operations or operations for the sale or distribution of food, if,

i. the waste is transferred by a generator and destined for a site at which the waste will be used in an ongoing agricultural, commercial, manufacturing or industrial process or operation, whether or not it is processed before it is used in the process or operation and whether or not it is processed before it is received at the site at which it will be used in the process or operation, and

ii. the agricultural, commercial, manufacturing or industrial process or operation does not involve combustion or land application of the waste.

21. Anaerobic digestion output that is intended for application on agricultural land as nutrient,

i. if it was generated by a regulated mixed anaerobic digestion facility, or

ii. if the anaerobic digestion materials did not contain sewage biosolids or human body waste and at least 50 per cent, by volume, of the total amount of anaerobic digestion materials were on-farm anaerobic digestion materials.

22. Manure, paunch manure or used animal bedding transferred by a generator for direct transportation to a farm operation at which it is to be used to improve the growing of crops, whether or not it is processed at the operation before it is used to improve the growing of crops.

23. Solid waste plant material that is,

i. generated from crops that have not been processed, or that have been processed without any use of chemicals, other than food grade chemicals used only to clean the crops or the surrounding processing area and equipment, and

ii. transferred by a generator for direct transportation to a farm operation at which it is to be used to improve the growing of crops, whether or not it is processed at the operation before it is used to improve the growing of crops.

24. Composting material or cured compost if it is transferred by a disposal facility that is operating under a licence issued under the Food Safety and Quality Act, 2001.

25. Processed organic waste from a composting facility, if the waste meets the requirements for Category AA or Category A compost in Part II of the document published by the Ministry entitled “Ontario Compost Quality Standards”, as amended from time to time, originally dated July 25, 2012 and available through the Ministry’s website on the Internet and through the Ministry’s Public Information Centre.

26. Processed organic waste from a composting facility, if,

i. the waste meets the requirements for Category AA compost relating to standards for metals in compost, quality of feedstock and pathogens in Part II of the document published by the Ministry entitled “Ontario Compost Quality Standards”, as amended from time to time, originally dated July 25, 2012 and available through the Ministry’s website on the Internet and through the Ministry’s Public Information Centre,

ii. the environmental compliance approval issued under Part II.1 of the Act in respect of the composting facility,

A. was issued before January 1, 2013, and

B. contains terms or conditions that address matters relating to the quality of the waste, other than matters relating to standards for metals in compost, quality of feedstock and pathogens, and

iii. the holder of environmental compliance approval has complied with the terms and conditions mentioned in sub-subparagraph ii B. O. Reg. 105/94, s. 3 (2); O. Reg. 128/98, s. 2 (1); O. Reg. 461/05, s. 2; O. Reg. 102/07, s. 2 (1); O. Reg. 395/07, s. 2 (1); O. Reg. 110/09, s. 2 (2); O. Reg. 336/09, s. 2; O. Reg. 283/12, s. 2 (1, 2).

Note: On July 1, 2015, paragraph 26 is revoked. (See: O. Reg. 283/12, ss. 2 (3), 3 (2))

(3)  Despite subsection (1), material that is referred to in subparagraph 1 i or paragraph 6, 9, 10 or 11 of subsection (2) is exempt from Part V of the Act and this Regulation only if the carrier has in his or her possession while transporting the material a document from the owner or operator of the site to which the material is being transported that,

(a) indicates that the owner or operator of the site to which the material is being transported agrees to accept the material;

(b) specifies the use that will be made of the material; and

(c) if the paragraph of subsection (2) that refers to the material refers to an ongoing process or operation, stipulates that the process or operation is ongoing at the time the material is being transported. O. Reg. 102/07, s. 2 (2).

(3.0.1)  Despite subsection (1), material that is referred to in paragraph 2, 2.1 or 3 of subsection (1) or paragraph 24 of subsection (2) is exempt from Part V of the Act and this Regulation unless it is transferred to a waste disposal site that is operating under an environmental compliance approval. O. Reg. 110/09, s. 2 (3); O. Reg. 234/11, s. 2.

(3.0.2)  Despite subsection (1), material that is referred to in paragraph 1, 2, 2.1 or 3 of subsection (1) or paragraph 22, 23 or 24 of subsection (2) is not exempt from section 29 of the Act. O. Reg. 110/09, s. 2 (3).

(3.1)  Despite subsection (1), material that is referred to in paragraph 7 or 8 of subsection (2) is exempt from Part V of the Act and this Regulation only if,

(a) every carrier has in his or her possession while transporting the material a document from the owner or operator of the site to which the material is destined that,

(i) indicates that the owner or operator of the site to which the material is destined agrees to accept the material,

(ii) specifies the use that will be made of the material, and

(iii) if the material is referred to in paragraph 8 of subsection (2), stipulates that the manufacturing process referred to in that paragraph is ongoing at the time the material is being transported; and

(b) the owner or operator of every site to which the material is delivered and at which the material is collected, handled, stored or transferred before reaching the site to which the material is destined has in his or her possession while collecting, handling, storing or transferring the material a document from the owner or operator of the site to which the material is destined that,

(i) indicates that the owner or operator of the site to which the material is destined agrees to accept the material,

(ii) specifies the use that will be made of the material, and

(iii) if the material is referred to in paragraph 8 of subsection (2), stipulates that the manufacturing process referred to in that paragraph is ongoing at the time the material is being collected, handled, stored or transferred. O. Reg. 102/07, s. 2 (2).

(3.2)  If a waste referred to in paragraph 13 of subsection (2) is one of the following types of waste, any residue from the processing of the waste shall be deemed, for the purposes of this Regulation, to be a waste derived from a waste referred to in clause (a) of the definition of that type of waste in subsection 1 (1):

1. Acute hazardous waste chemical.

2. Hazardous industrial waste.

3. Hazardous waste chemical.

4. Severely toxic waste. O. Reg. 102/07, s. 2 (2).

(3.3)  Paragraph 20 of subsection (2) does not apply to organic waste from food processing and preparation operations or operations for the sale or distribution of food, if the waste is transferred by a generator and destined for a site at which the waste will be subject to anaerobic digestion, composting or any other process or operation that results in the production of material intended for land application. O. Reg. 395/07, s. 2 (2).

(4)  In subsection (2),

“ground cover” means,

(a) mulch,

(b) landscaping material, or

(c) surfacing material for,

(i) trails or walkways for pedestrian use,

(ii) trails or paths for use by livestock or other animals,

(iii) pens or enclosures for livestock or other animals,

(iv) playgrounds,

(v) parking areas, or

(vi) private roads. O. Reg. 128/98, s. 2 (2).

Waste Disposal Sites and Waste Management Systems

4.  Revoked: O. Reg. 105/94, s. 4.

5.  (1)  The following waste disposal sites are exempt from Part V of the Act and this Regulation:

1. On-site incinerators at the site of a veterinary hospital.

2. On-site garbage grinders.

3. Derelict motor vehicle sites.

4. Incinerators at the site of a crematorium within the meaning of the Cemeteries Act.

5. Regulated mixed anaerobic digestion facilities. R.R.O. 1990, Reg. 347, s. 5 (1); O. Reg. 395/07, s. 3.

(2)  Subsection 27 (1) of the Act does not apply in respect of a dust suppression site if,

(a) the site has been designated in an environmental compliance approval in respect of establishing and operating a dust suppression waste management system; and

(b) the site is established and operated in accordance with the approval. O. Reg. 234/11, s. 3.

(3)  Revoked: O. Reg. 555/92, s. 4.

(4)  No person shall use waste oil as a dust suppressant. R.R.O. 1990, Reg. 347, s. 5 (4).

5.0.1  (1)  In this section,

“municipal waste pilot project site” means a waste disposal site, other than a landfilling site or dump, where municipal waste is processed or disposed of primarily to,

(a) assist in the design of technology for processing or disposing of municipal waste,

(b) assess the merits of a technology for processing or disposing of municipal waste, or

(c) demonstrate the merits of a technology for processing or disposing of municipal waste. O. Reg. 234/11, s. 4.

(2)  Subject to subsection (3), this section applies to,

(a) an application for an environmental compliance approval for the use, operation, establishment, alteration, extension or enlargement of a municipal waste pilot project site; and

(b) an application to amend a term or condition described in subsection (5). O. Reg. 234/11, s. 4.

(3)  Subsection (2) applies to an application if,

(a) the applicant gives the Director a written notice that,

(i) specifically mentions this section, and

(ii) requests that this section apply; and

(b) the Director is satisfied that not more than 75 tonnes of municipal waste will be processed or disposed of at the site on any day. O. Reg. 234/11, s. 4.

(4)  If an environmental compliance approval is issued on an application described in subsection (2),

(a) the operator of the municipal waste pilot project site shall promptly notify the Director in writing of the date that municipal waste is first received at the site in accordance with the environmental compliance approval; and

(b) the operator of the municipal waste pilot project site shall ensure that not more than 75 tonnes of municipal waste are processed or disposed of at the site on any day. O. Reg. 234/11, s. 4.

(5)  An environmental compliance approval that is issued on an application described in clause (2) (a) must contain a term or condition that prohibits the operation of the municipal waste pilot project site after the third anniversary of the date that municipal waste is first received at the site, or after such earlier date as is specified in the environmental compliance approval. O. Reg. 234/11, s. 4.

(6)  Subject to subsections (8) and (9), the Director may, on application, alter the term or condition referred to in subsection (5) if the Director is satisfied that the amendment is necessary to,

(a) assist in the design of technology for processing or disposing of municipal waste;

(b) assess the merits of a technology for processing or disposing of municipal waste; or

(c) demonstrate the merits of a technology for processing or disposing of municipal waste. O. Reg. 234/11, s. 4.

(7)  The Director is not required to consider an application to alter the term or condition referred to in subsection (5) if,

(a) the application is seeking the first alteration of the term or condition; and

(b) the application is made less than half way through the period between the date that municipal waste is first received at the site and the date after which the term or condition prohibits the operation of the municipal waste pilot project site. O. Reg. 234/11, s. 4.

(8)  An alteration of a term or condition under subsection (6) shall not extend the period during which the municipal waste pilot project site may be operated for more than 12 months. O. Reg. 234/11, s. 4.

(9)  An alteration of a term or condition under subsection (6) shall not extend the period during which the municipal waste pilot project site may be operated beyond the fifth anniversary of the date that municipal waste is first received at the site. O. Reg. 234/11, s. 4.

5.0.2  A waste disposal site is exempt from Part V of the Act and from this Regulation if,

(a) it is a NASM plan area, as defined in Ontario Regulation 267/03 (General) made under the Nutrient Management Act, 2002; and

(b) it satisfies the requirements of section 8.3 of that regulation. O. Reg. 336/09, s. 3.

5.1  Revoked: O. Reg. 234/11, s. 5.

5.2  (1)  In this section,

“service area”, with respect to a landfilling site, means the geographical area from which the site is permitted, under an environmental compliance approval, to receive municipal waste. O. Reg. 234/11, s. 6.

(2)  A municipality that owns or operates a landfilling site is exempt from section 27 of the Act with respect to increasing the service area of the site if the additional area from which the site will receive municipal waste is,

(a) within the boundaries of the local municipality in which the site is located or, if the upper tier municipality in which the local municipality is located is exercising the power to provide landfilling sites for the local municipality, within the boundaries of that upper tier municipality;

(b) within the boundaries of the municipality that owns or operates the site;

(c) within the boundaries of an area that is not organized as a municipality and that abuts the municipality that owns or operates the site; or

(d) within the boundaries of a separated municipality that abuts the municipality that owns or operates the site. O. Reg. 234/11, s. 6.

(3)  A municipality that owns or operates a landfilling site that has been filled is exempt from section 27 of the Act with respect to increasing the service area of another landfilling site that it owns and operates if,

(a) the municipality relied on an exemption under this section to expand the service area of the filled site or to increase the rate at which municipal waste was received at the filled site; and

(b) the additional area from which the other landfilling site will receive municipal waste is part or all of the area from which the filled site received municipal waste. O. Reg. 234/11, s. 6.

(4)  A person, other than a municipality, who owns or operates a landfilling site is exempt from section 27 of the Act with respect to increasing the service area of the site if,

(a) the additional area from which the site will receive municipal waste is within the boundaries of a municipality from which it already receives municipal waste;

(b) the municipality referred to in clause (a) is a local municipality or an upper tier municipality that is exercising the power to provide landfilling sites for the local municipality; and

(c) the site has an environmental compliance approval that includes terms or conditions establishing a periodic quantity limit for deliveries of waste to the landfilling site. O. Reg. 234/11, s. 6.

(5)  An increase in the service area to which subsection (2), (3) or (4) applies is exempt from being the subject matter of a hearing under subsection 20.15 (1) of the Act. O. Reg. 234/11, s. 6.

(6)  An increase in the service area of a landfilling site that is owned or operated by a person other than a municipality is exempt from being the subject matter of a hearing under subsection 20.15 (1) of the Act if,

(a) the additional area from which the site will receive municipal waste is within the boundaries of a municipality from which it already receives municipal waste;

(b) the municipality referred to in clause (a) is a local municipality or an upper tier municipality that is exercising the power to provide landfilling sites for the local municipality;

(c) the site has an environmental compliance approval;

(d) the Director imposes a term or condition establishing a periodic quantity limit for deliveries of waste to the site; and

(e) the periodic quantity limit is equivalent to an estimate based on existing terms or conditions defining a service area for the site or on historic deliveries to the site. O. Reg. 234/11, s. 6.

(7)  An increase in the rate at which municipal waste may be received at a landfilling site owned or operated by a municipality from areas within its service area is exempt from being the subject matter of a hearing under subsection 20.15 (1) of the Act. O. Reg. 234/11, s. 6.

6.  (1)  For the purposes of subsection (3),

(a) each tire weighing less than twelve kilograms is one tire unit;

(b) each tire weighing twelve kilograms or more is the number of tire units that results from dividing twelve into the number of kilograms that the tire weighs; and

(c) each twelve kilograms of chipped or shredded tires is a tire unit. R.R.O. 1990, Reg. 347, s. 6 (1).

(2)  Steel that has been separated from other components of tires in the process of chipping or shredding tires shall not be counted for the purposes of clause (1) (c). R.R.O. 1990, Reg. 347, s. 6 (2).

(3)  Section 27 of the Act does not apply in respect of a used tire site if,

(a) the total number of tire units at the site is less than 5,000;

(b) the total volume of the piles of tire units at the site is less than 300 cubic metres; and

(c) used, chipped or shredded tires are not subject to thermal treatment or buried at the site. O. Reg. 183/92, s. 1; O. Reg. 555/92, s. 5 (1); O. Reg. 102/07, s. 5.

(4)  Despite subsection (3), the only persons exempted from section 40 of the Act for depositing waste at a used tire site described in subsection (3) are persons belonging to one of the following classes:

1. The owner of the land on which the site is located.

2. A person acting with the written permission of the owner of the land on which the site is located.

3. The operator of a motor vehicle service station acting in the ordinary course of the service station business, in the case of a site that is accessory to the station.

4. A person acting with the permission of the operator of a motor vehicle service station and in the ordinary course of the service station business, in the case of a site that is accessory to the station. O. Reg. 183/92, s. 1; O. Reg. 555/92, s. 5 (2).

(5)  Revoked: O. Reg. 183/92, s. 1.

7.  Section 27 of the Act does not apply to vehicle sewage holding tanks. O. Reg. 157/98, s. 4.

8.  (1)  The following waste management systems are exempt from Part V of the Act and this Regulation:

1. Individual collection systems.

2. Marine craft waste disposal systems. R.R.O. 1990, Reg. 347, s. 8 (1).

(2)  Revoked: O. Reg. 461/05, s. 4.

(3)  Section 27 of the Act does not apply in respect of trucks for hauling used tires. R.R.O. 1990, Reg. 347, s. 8 (3).

(3.1)  Subject to subsection (3.2), sections 27, 40 and 41 of the Act do not apply in respect of trucks for hauling off-farm anaerobic digestion materials listed in Schedule 1 or 2 of Ontario Regulation 267/03 (General) made under the Nutrient Management Act, 2002 to a waste disposal site that, pursuant to paragraph 5 of subsection 5 (1), is exempt from Part V of the Act and this Regulation. O. Reg. 395/07, s. 4.

(3.2)  Trucks for hauling off-farm anaerobic digestion materials to a waste disposal site referred to in subsection (3.1) are exempt from sections 27, 40 and 41 of the Act only if every carrier has in his or her possession while transporting the materials a document from the owner or operator of the waste disposal site that indicates that the owner or operator of the site agrees to accept the materials. O. Reg. 395/07, s. 4.

(4)  Sections 27, 40 and 41 of the Act do not apply in respect of a waste management system or waste disposal site, if the only management of waste done by the system or at the site is the collection, handling, transportation, storage or transfer of,

(a) waste that consists of,

(i) waste electrical and electronic equipment that is intact, or

(ii) printed circuit boards,

and that is transferred by a generator and is destined for a site at which the waste is to be processed for the recovery of materials;

(b) intact waste batteries that are transferred by a generator and are destined for a waste battery recovery facility; or

(c) common mercury waste that is transferred by a generator and is destined for a common mercury waste recovery facility. O. Reg. 102/07, s. 6; O. Reg. 337/09, s. 3.

(5)  Despite clauses (4) (b) and (c), a waste management system or waste disposal site for the collection, handling, transportation, storage or transfer of waste referred to in those clauses is exempt from sections 27, 40 and 41 of the Act only if,

(a) every carrier has in his or her possession while transporting the waste a document from the owner or operator of the waste battery recovery facility or common mercury waste recovery facility that indicates that the owner or operator of the facility agrees to accept the waste; and

(b) the owner or operator of every site at which the waste is collected, handled, stored or transferred before reaching the waste battery recovery facility or common mercury waste recovery facility has in his or her possession while collecting, handling, storing or transferring the material a document from the owner or operator of the waste battery recovery facility or common mercury waste recovery facility that indicates that the owner or operator of the facility agrees to accept the waste. O. Reg. 102/07, s. 6.

(6)  Sections 27, 40 and 41 of the Act do not apply in respect of a waste disposal site if,

(a) the only management of waste done at the waste disposal site is the collection, handling, storage, transfer or processing of woodwaste;

(b) none of the woodwaste is stored at the waste disposal site for more than 18 months;

(c) the woodwaste is transferred by a generator and is destined for one or more woodwaste combustor sites;

(d) the owner or operator of the waste disposal site has in his or her possession, while collecting, handling, storing, transferring or processing woodwaste, a document from the owner or operator of each woodwaste combustor site to which the woodwaste is destined that indicates that,

(i) the owner or operator of the woodwaste combustor site agrees to accept the woodwaste, and

(ii) the woodwaste will be used at the woodwaste combustor site principally for functions other than waste disposal; and

(e) no more woodwaste is stored at the waste disposal site than is reasonably capable of being subject to thermal treatment or wholly utilized as a fuel or fuel supplement during a period of six months at the woodwaste combustor sites to which the woodwaste is destined. O. Reg. 102/07, s. 6.

(7)  Sections 27, 40 and 41 of the Act do not apply in respect of a waste management system if,

(a) the only management of waste done by the waste management system is the collection, handling, transportation, storage, transfer or processing of woodwaste;

(b) none of the woodwaste is stored at waste disposal sites that are part of the waste management system for more than 18 months;

(c) the woodwaste is transferred by a generator and is destined for one or more woodwaste combustor sites;

(d) the owner or operator of every waste disposal site that is part of the waste management system has in his or her possession, while collecting, handling, storing, transferring or processing woodwaste, a document from the owner or operator of each woodwaste combustor site to which the woodwaste is destined that indicates that,

(i) the owner or operator of the woodwaste combustor site agrees to accept the woodwaste, and

(ii) the woodwaste will be used at the woodwaste combustor site principally for functions other than waste disposal; and

(e) no more woodwaste is stored at waste disposal sites that are part of the waste management system than is reasonably capable of being subject to thermal treatment or wholly utilized as a fuel or fuel supplement during a period of six months at the woodwaste combustor sites to which the woodwaste is destined. O. Reg. 102/07, s. 6.

(8)  If, pursuant to subsection (6) or (7), sections 27, 40 and 41 of the Act do not apply in respect of a waste disposal site or waste management system, the owner and the operator of the waste disposal site or waste management system shall ensure that all woodwaste that is transported from the waste disposal site or by the waste management system is transported to,

(a) a woodwaste combustor site that uses the woodwaste principally for functions other than waste disposal; or

(b) a waste disposal site or waste management system that, pursuant to subsection (6) or (7), is also exempt from sections 27, 40 and 41 of the Act. O. Reg. 102/07, s. 6.

(9)  Sections 27, 40 and 41 of the Act do not apply in respect of a waste disposal site if,

(a) the only management of waste done at the waste disposal site is the collection, handling, storage, transfer or processing of woodwaste; and

(b) the site is operated by the holder of a land use permit issued under the Public Lands Act that authorizes the collection, handling, storage transfer or processing of woodwaste at the site. O. Reg. 102/07, s. 6.

9.  The standards, procedures and requirements set out in this Regulation do not apply to the extent that terms and conditions in an environmental compliance approval issued in respect of an activity mentioned in subsection 27 (1) of the Act impose different standards, procedures or requirements. R.R.O. 1990, Reg. 347, s. 9; O. Reg. 234/11, s. 7.

10.  No person shall use, operate or establish a waste management system or waste disposal site or any part of either of them except in accordance with the applicable prescribed standards. R.R.O. 1990, Reg. 347, s. 10.

Standards for Waste Disposal Sites

11.  The following are prescribed as standards for the location, maintenance and operation of a landfilling site:

1. Access roads and on-site roads shall be provided so that vehicles hauling waste to and on the site may travel readily on any day under all normal weather conditions.

2. Access to the site shall be limited to such times as an attendant is on duty and the site shall be restricted to use by persons authorized to deposit waste in the fill area.

3. Drainage passing over or through the site shall not adversely affect adjoining property and natural drainage shall not be obstructed.

4. Drainage that may cause pollution shall not, without adequate treatment, be discharged into watercourses.

5. Waste shall be placed sufficiently above or isolated from the maximum water table at the site in such manner that impairment of groundwater in aquifers is prevented and sufficiently distant from sources of potable water supplies so as to prevent contamination of the water, unless adequate provision is made for the collection and treatment of leachate.

6. Where necessary to isolate a landfilling site and effectively prevent the egress of contaminants, adequate measures to prevent water pollution shall be taken by the construction of berms and dykes of low permeability.

7. Where there is a possibility of water pollution resulting from the operation of a landfilling site, samples shall be taken and tests made by the owner of the site to measure the extent of egress of contaminants and, if necessary, measures shall be taken for the collection and treatment of contaminants and for the prevention of water pollution.

8. The site shall be located a reasonable distance from any cemetery.

9. Adequate and proper equipment shall be provided for the compaction of waste into cells and the covering of the cells with cover material.

10. Where climatic conditions may prevent the use of the site at all times, provisions shall be made for another waste disposal site which can be used during such periods.

11. Where required for accurate determination of input of all wastes by weight, scales shall be provided at the site or shall be readily available for use.

12. All waste disposal operations at the site shall be adequately and continually supervised.

13. Waste shall be deposited in an orderly manner in the fill area, compacted adequately and covered by cover material by a proper landfilling operation.

14. Procedures shall be established for the control of rodents or other animals and insects at the site.

15. Procedures shall be established, signs posted, and safeguards maintained for the prevention of accidents at the site.

16. The waste disposal area shall be enclosed to prevent entry by unauthorized persons and access to the property shall be by roadway closed by a gate capable of being locked.

17. A green belt or neutral zone shall be provided around the site and the site shall be adequately screened from public view.

18. Whenever any part of a fill area has reached its limit of fill, a final cover of cover material shall be placed on the completed fill and such cover shall be inspected at regular intervals over the next ensuing period of two years and where necessary action shall be taken to maintain the integrity and continuity of the cover materials.

19. Scavenging shall not be permitted. R.R.O. 1990, Reg. 347, s. 11.

11.1  (0.1)  In this section,

“Section 39 Director” means a Director appointed under section 5 of the Act for the purposes of section 39 of the Act as that section read immediately before it was repealed. O. Reg. 234/11, s. 8.

(1)  The owner and the operator of a landfilling site described in subsection (2) shall ensure that on or before June 30, 2009 a written report is submitted to the Section 39 Director respecting,

(a) the design, operation, maintenance and monitoring of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure; and

(b) if any of the facilities referred to in clause (a) already exist, the improvements, if any, that can be made to those facilities to increase the amount of landfill gas generated by the site that can be collected, and burned or used, and the date by which the improvements can be made and implemented. O. Reg. 217/08, s. 2; O. Reg. 337/09, s. 4.

(2)  This section applies to a landfilling site that meets the following criteria:

1. The site accepts only municipal waste for disposal.

2. On or after June 30, 2009, the site will landfill waste under a certificate of approval or provisional certificate of approval issued under Part V of the Act.

3. On or after June 30, 2009, the site will have a total waste disposal volume of more than 1.5 million cubic metres.

4. A written report has not been required to be prepared with respect to the site under subsection 15 (1) of Ontario Regulation 232/98 (Landfilling Sites) made under the Act. O. Reg. 217/08, s. 2.

(3)  This section does not apply to a landfilling site associated with forest products operations, such as the operations of a lumber mill, sawmill, pulp mill or similar facility, if the waste deposited at the site is produced by the forest products operations and is predominantly solid, non-hazardous process waste, such as woodwaste, effluent treatment solids, hog fired boiler ash, recycling process rejects, lime mud, grits or dregs. O. Reg. 217/08, s. 2.

(4)  This section does not apply to a landfilling site if the only waste landfilled at the site is coal ash. O. Reg. 217/08, s. 2.

(5)  This section does not apply to a landfilling site if a written report is submitted to the Section 39 Director before June 30, 2009 showing that the nature and quantity of landfill gas generated by the site is not likely to be of significant concern to the Director, based on the following factors:

1. The characteristics of the site.

2. The type of waste to be deposited.

3. The rate at which waste is deposited at the site. O. Reg. 217/08, s. 2.

(6)  This section does not apply to a landfilling site that meets the following criteria:

1. The site operates under a certificate of approval or provisional certificate of approval issued under Part V of the Act.

2. The certificate of approval or provisional certificate of approval permits the use of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation but does not require that some or all of those facilities be used.

3. The site has in operation facilities that are not required by the certificate of approval or provisional certificate of approval for the collection, and for the burning or use, of landfill gas generated by the site during site operation.

4. The owner or the operator of the site gives the Section 39 Director a written notice that,

i. specifically mentions this subsection, and

ii. requests that this section not apply. O. Reg. 217/08, s. 2.

11.2  (0.1)  In this section,

“Section 39 Director” means a Director appointed under section 5 of the Act for the purposes of section 39 of the Act as that section read immediately before it was repealed. O. Reg. 234/11, s. 9 (1).

(1)  If section 11.1 does not apply to a landfilling site because the criteria listed in subsection 11.1 (6) are met, the owner and the operator of the site shall ensure that, on or before June 30, 2009, a written report is submitted to the Section 39 Director,

(a) identifying the areas of the site where facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation are in operation and for which there is no requirement under the certificate of approval or provisional certificate of approval under which the site operates;

(b) describing the design and operation of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure in the areas of the site that are identified in clause (a);

(c) respecting the design, operation, maintenance and monitoring of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure in the areas of the site that are not identified in clause (a); and

(d) if any of the facilities referred to in clause (c) already exist, respecting the improvements, if any, that can be made to those facilities to increase the amount of landfill gas generated by the site that can be collected, and burned or used, and the date by which the improvements can be made and implemented. O. Reg. 217/08, s. 2; O. Reg. 337/09, s. 5.

(2)  The owner and the operator of a landfilling site for which a written report was required to be submitted under subsection (1) shall ensure that, on or before June 30, 2016, a written report is submitted to the Director respecting,

(a) the design, operation, maintenance and monitoring of the facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure; and

(b) if any of the facilities referred to in clause (a) already exist, the improvements, if any, that can be made to those facilities to increase the amount of landfill gas generated by the site that can be collected, and burned or used, and the date by which the improvements can be made and implemented. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 9 (2).

11.3  (1)  Subject to subsection (2), the owner and the operator of a landfilling site to which section 11.1 or 11.2 applies shall ensure that the following facilities and improvements to the facilities are in operation for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure:

1. If section 11.1 applies, the facilities referred to in clause 11.1 (1) (a) and any improvements identified under clause 11.1 (1) (b).

2. If section 11.2 applies, the facilities referred to in clause 11.2 (1) (c) and any improvements identified under clause 11.2 (1) (d). O. Reg. 217/08, s. 2.

(2)  If, after a report was submitted under subsection 11.1 (1) or 11.2 (1), facilities other than facilities referred to in subsection (1) have been required as a condition in an environmental compliance approval, the owner and the operator shall ensure that the facilities required by the Director are in operation for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure. O. Reg. 234/11, s. 10.

(3)  This section applies to a portion of a waste fill zone in a landfilling site to which section 11.1 applies or in an area of a landfilling site to which section 11.2 applies that is not identified in clause 11.2 (1) (a) if, at any time on or after December 31, 2010,

(a) the portion of the zone has reached its maximum capacity; or

(b) no further waste has been deposited in the portion of the zone during the preceding six months. O. Reg. 217/08, s. 2.

11.4  (0.1)  In this section,

“Section 39 Director” means a Director appointed under section 5 of the Act for the purposes of section 39 of the Act as that section read immediately before it was repealed. O. Reg. 234/11, s. 11 (1).

(1)  The owner and the operator of a landfilling site described in subsection (4) shall ensure that for 2009 and every subsequent year, an annual report is submitted to the Director on or before June 1 of the following year. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 11 (2).

(2)  The report required under subsection (1) shall be in writing and shall include the following with respect to the facilities for the collection, and for the burning or use, of landfill gas generated by the landfilling site during site operation and following site closure:

1. A statement of the total landfill gas volume collected by the facilities at the site during the year.

2. A statement of the percentage of the volume described in paragraph 1 that was methane gas.

3. A statement of the reduction in methane emissions from the landfilling site associated with the burning or use of landfill gas during the year, expressed in units of tonnes of carbon dioxide equivalent and based on a global warming potential of 21 for methane gas.

4. A description of how sound scientific or engineering principles have been used to support the statements required by paragraphs 1, 2 and 3.

5. All calculations and information that support the statements required by paragraphs 1, 2 and 3. O. Reg. 217/08, s. 2.

(3)  The report required for 2009 under subsection (1) shall include the information described in subsection (2) only for the period that begins on June 30, 2009 and ends on December 31, 2009. O. Reg. 217/08, s. 2.

(4)  This section applies to a landfilling site that meets the following criteria:

1. The site accepts only municipal waste for disposal.

2. On or after June 30, 2009, the site landfills waste and is subject to an environmental compliance approval.

3. On or after June 30, 2009, the site has a total waste disposal volume of more than 1.5 million cubic metres. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 11 (3).

(5)  This section does not apply to a landfilling site associated with forest products operations, such as the operations of a lumber mill, sawmill, pulp mill or similar facility, if the waste deposited at the site is produced by the forest products operations and is predominantly solid, non-hazardous process waste, such as woodwaste, effluent treatment solids, hog fired boiler ash, recycling process rejects, lime mud, grits or dregs. O. Reg. 217/08, s. 2.

(6)  This section does not apply to a landfilling site if the only waste landfilled at the site is coal ash. O. Reg. 217/08, s. 2.

(7)  This section does not apply to a landfilling site for which a written report has been submitted to the Section 39 Director under subsection 11.1 (5). O. Reg. 217/08, s. 2.

(8)  This section ceases to apply to a landfilling site if the Director amends an environmental compliance approval to which the site is subject to state that the nature and quantity of landfill gas generated by the site is not of significant concern to the Director. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 11 (4).

11.5  (1)  On request of the Director, the owner or the operator who is required to submit a report under section 11.1, 11.2 or 11.4 shall provide further information with respect to the subject matter of the report. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 12 (1).

(2)  The information requested under subsection (1) shall be provided to the Director by a date set by the Director at the time of the request. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 12 (2).

12.  The following are prescribed as standards for the location, maintenance and operation of a thermal treatment site:

1. The location of the thermal treatment site shall be selected so as to reduce the effects of nuisances such as dust, noise and traffic.

2. Fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste shall be kept separate from incinerator ash and disposed of or otherwise dealt with separately from incinerator ash.

3. Fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste shall only be disposed of at,

i. Revoked: O. Reg. 337/09, s. 6.

ii. a landfilling site authorized to accept fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste by the terms of,

A. an environmental compliance approval issued after the 1st day of January, 1990, or

B. an amendment to an environmental compliance approval made after the 1st day of January, 1990.

4. The thermal treatment equipment shall be located,

i. so that it is accessible for the transportation of wastes thereto without nuisance,

ii. taking into account meteorological considerations to minimize environmental effects, and

iii. so that the services and utilities required for the operation of the thermal treatment equipment are available, including facilities for the disposal of residue and of quenching and scrubbing water.

5. The design and capacity of the thermal treatment equipment shall be of a type and size adequate to efficiently process the quantities of waste that may be expected, so that a minimum volume of residue is obtained, the putrescible materials remaining as residue are reduced to a minimum and a minimum of air pollution results.

6. The following equipment shall be provided as necessary for particular applications:

i. Scales for the accurate determination of the input of all wastes by weight.

ii. A storage pit or other storage facilities.

iii. A crane or other means of removing waste from the pit or other storage facilities.

iv. Means of controlling dusts and odours.

v. Such instruments as may be necessary for the efficient operation of the thermal treatment equipment.

7. The thermal treatment site shall include an unloading area properly enclosed and of sufficient size for the intended operation.

8. Access roads shall be provided for vehicles hauling waste to the thermal treatment site.

9. On-site fire protection shall be provided and, where possible, arrangements shall be made with a fire department or municipality for adequate fire fighting services in case of an emergency.

10. Scavenging shall not be permitted. R.R.O. 1990, Reg. 347, s. 12; O. Reg. 102/07, s. 7; O. Reg. 337/09, s. 6; O. Reg. 234/11, s. 13.

12.1  Revoked: O. Reg. 512/95, s. 2.

13.  The following are prescribed as standards for the location, maintenance and operation of a dump:

1. The fill area shall not be subject to flooding and shall be so located that no direct drainage leads to a watercourse.

2. The site shall be at least one-quarter of a mile from the nearest dwelling.

3. The site shall be at least two hundred yards from the nearest public road.

4. The site shall be at least 100 feet from any watercourse, lake or pond.

5. The site shall not be on land covered by water.

6. Signs shall be posted stating requirements for the operation of the dump, including measures for the control of vermin and insect infestation.

7. The site shall be so located and operated as to reduce to a minimum the hazards resulting from fire.

8. The operator of a dump shall apply such cover material at such intervals as is necessary to prevent harm or material discomfort to any person.

9. Scavenging shall not be permitted. R.R.O. 1990, Reg. 347, s. 13.

14.  (1)  No dump shall be established, altered, enlarged or extended in Ontario. O. Reg. 337/09, s. 7 (1).

(2), (3)  Revoked: O. Reg. 337/09, s. 7 (2).

14.0.1  If hazardous waste is being handled, stored, treated or disposed of at a waste disposal site or transferred to a waste disposal site, no person shall cause or permit the hazardous waste to be mixed, blended, bulked or in any other way intermingled with any other waste or material, unless the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the waste disposal site. O. Reg. 461/05, s. 5; O. Reg. 234/11, s. 14.

14.1  The following are prescribed as standards for the location, maintenance and operation of waste disposal sites for hauled sewage:

1. A person shall not apply hauled sewage in any manner that permits it to enter a watercourse or drainage ditch.

2. A person shall not apply hauled sewage in any manner that results in runoff leaving the site.

3. If the operator of a proposed site is not the owner of the land on which the site is to be located, the operator must, before applying for approval to engage at the site in an activity mentioned in subsection 27 (1) of the Act, obtain written authorization from the owner for the proposed use of the site. O. Reg. 157/98, s. 5; O. Reg. 234/11, s. 15.

14.2  (1)  Subject to subsection (3), no person shall cause or permit waste from a portable toilet to be applied to land or otherwise deposited at a site except,

(a) at a waste disposal site that is subject to an environmental compliance approval permitting the temporary storage of hauled sewage and from which the hauled sewage is not subsequently removed and disposed of except in accordance with this section;

(b) at a waste disposal site that is subject to an environmental compliance approval permitting the disposal of hauled sewage for drying and requiring the dried residue to be periodically removed and disposed of at a waste disposal site approved to accept the dried residue;

(c) at a landfilling site that is subject to an environmental compliance approval for the final disposal of hauled sewage;

(d) at a sewage works that is subject to an environmental compliance approval permitting the receipt of sanitary sewage or hauled sewage; or

(e) at a site that is subject to an environmental compliance approval permitting the processing of waste and which processes waste in a manner that ensures that the waste meets all of the following requirements after it has been processed:

(i) the concentration of Escherichia coli (E. coli) in the waste is not more than 2x106 colony forming units per gram of total solids (dry weight),

(ii) the concentration in the waste of each metal listed in the Table to this section is not more than the maximum concentration set out for that metal in the Table,

(iii) the pH value of the waste is not less than 6.0,

(iv) the waste has been passed through a screen and contains no more than 0.5 per cent dry weight of plastic objects and no more than 2 per cent dry weight of other non-biodegradable objects, including, but not limited to, glass and metal objects. O. Reg. 326/03, s. 1; O. Reg. 234/11, s. 16 (1-5).

(2)  Subsection (1) applies despite anything contained in a certificate of approval or a provisional certificate of approval that was issued before this section comes into force. O. Reg. 326/03, s. 1.

(3)  No person shall cause or permit waste from a portable toilet to be disposed of at an organic soil conditioning site unless,

(a) the organic soil conditioning site is subject to an environmental compliance approval permitting the spreading or application of treated waste from a portable toilet;

(b) the waste has been treated so that the concentration of Escherichia coli (E. coli) is not more than 2x106 colony forming units per gram of total solids (dry weight);

(c) the concentration in the waste of each metal listed in the Table to this section is not more than the maximum concentration set out for that metal in the Table;

(d) the pH value of the treated waste is not less than 6.0; and

(e) the waste has been passed through a screen and contains no more than 0.5 per cent dry weight of plastic objects and no more than 2 per cent dry weight of other non-biodegradable objects, including, but not limited to, glass and metal objects. O. Reg. 326/03, s. 1; O. Reg. 234/11, s. 16 (6).

TABLE

Item

Metal

Maximum Permissible Concentration (In mg/kg Of Solids, Dry Weight)

1.

Arsenic

170

2.

Cadmium

34

3.

Cobalt

340

4.

Chromium-

2,800

5.

Copper

1,700

6.

Mercury

11

7.

Molybdenum

94

8.

Nickel

420

9.

Lead

1,100

10.

Selenium

34

11.

Zinc

4,200

O. Reg. 326/03, s. 1.

15.  The following are prescribed as standards for the location, maintenance and operation of an organic soil conditioning site:

1. The site shall be so located that it is an adequate distance from any watercourse, as determined by the land slope, to prevent direct surface drainage to the watercourse.

2. The site shall be at least 300 feet from the nearest individual dwelling.

3. The site shall be at least 1,500 feet from any area of residential development.

4. The site shall be so located that the maximum level of the ground water table at the site is at a sufficient distance below the surface to prevent the impairment of ground water in aquifers as determined by the permeability of the soil.

5. The site shall be at least 300 feet from any water wells.

6. No processed organic waste shall be applied to the site during any period in which conditions are such that surface runoff is likely to occur taking into account land slope, soil permeability and the climatic conditions of the area.

7. The site shall be established only on land that is, or is intended to be, used for pasture, fallow or the growing of forage crops,

i. during the current growing season, or

ii. where application of the processed organic waste is made sometime after the current growing season, to the end of the subsequent growing season.

8. Berms and dykes of low permeability shall be constructed on the site where necessary to isolate the site and effectively prevent the egress of contaminants. R.R.O. 1990, Reg. 347, s. 15.

16.  (1)  The following are prescribed as standards for the operation of a waste management system:

1. All waste collection vehicles and waste carriers shall be so constructed as to enable waste to be transferred safely and without nuisance from storage containers to the vehicle.

2. Bodies of waste collection vehicles and waste carriers shall be so constructed as to withstand abrasion and corrosion from the waste.

3. Bodies of waste collection vehicles and waste carriers shall be leakproof and covered where necessary to prevent the emission of offensive odours, the falling or blowing of waste material from the vehicles or the release of dust or other air-borne materials that may cause air pollution.

4. Valves that are part of a waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall have a locking mechanism and shall be locked when the vehicle contains the waste and the driver of the vehicle is not in attendance.

5. Whenever liquid industrial waste or hazardous waste is being transferred to or from a waste transportation vehicle, the driver of the vehicle must be present unless the generator or receiver is present.

5.1 If hazardous waste is being transferred to or from a waste transportation vehicle or is being transported in a waste transportation vehicle, no person shall cause or permit the hazardous waste to be mixed, blended, bulked or in any other way intermingled with any other waste or material, unless,

i. the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the receiving facility named in the manifest that is related to the waste transportation vehicle’s load, and the carrier has, accompanying the load, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste, or

ii. the mixing, blending, bulking or other intermingling is done in accordance with an environmental compliance approval issued in respect of a waste transportation system that the waste transportation vehicle is part of.

6. A waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall be clearly marked with the name and number appearing on the environmental compliance approval that authorizes the transportation.

7. Where a waste transportation vehicle is used for transporting liquid industrial waste or hazardous waste, a copy of the environmental compliance approval that authorizes that transportation shall be kept in the vehicle.

8. A waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall be constructed, maintained, operated and marked or placarded in accordance with the applicable requirements of the Transportation of Dangerous Goods Act (Canada).

9. The driver of a waste transportation vehicle used for the transportation of municipal waste, liquid industrial waste or hazardous waste shall be trained in,

i. the operation of the vehicle and waste management equipment,

ii. relevant waste management legislation, regulations and guidelines,

iii. major environmental concerns pertaining to the waste to be handled,

iv. occupational health and safety concerns pertaining to the waste to be handled, and

v. emergency management procedures for the wastes to be handled.

10. A waste transportation vehicle used for transporting municipal waste shall be clearly marked with the name and number appearing on the environmental compliance approval that authorizes the transportation.

11. Where a waste transportation vehicle is used for transporting municipal waste, a copy of the environmental compliance approval that authorizes that transportation shall be kept in the vehicle.

12. If the waste management system is used for hauled sewage, the operator of the system shall ensure that every tank used for the transportation of hauled sewage has inscribed in plain view the words “Sewage Waste” in letters that are at least 15 centimetres in height, unless the tank bears a company designation in letters of at least that height that clearly indicates the nature of the contents.

13. If the waste management system is used for hauled sewage, the operator of the system shall ensure that any part of the system that comes into contact with hauled sewage is not used for the collection, handling, treatment, transportation, storage or processing of any material other than hauled sewage or a material approved in writing by the Director.

14. A person shall not discharge or permit the discharge of hauled sewage from a tank that is part of a waste management system to the ground except in accordance with terms and conditions contained in an environmental compliance approval or order. R.R.O. 1990, Reg. 347, s. 16; O. Reg. 105/94, s. 7 (1); O. Reg. 157/98, s. 6 (1); O. Reg. 461/05, s. 6; O. Reg. 234/11, s. 17 (1-4); O. Reg. 348/12, s. 1.

Note: On January 1, 2015, subsection (1) is amended by adding the following paragraph: (See: O. Reg. 302/14, ss. 3, 4)

15. No person shall discharge or permit the discharge of GNF at a waste disposal site for hauled sewage.

(2)  Paragraphs 10 and 11 of subsection (1) do not apply,

(a) if the vehicle is owned and operated by or operated exclusively for a municipality or the Crown; or

(b) if the vehicle is operating as part of a waste management system in respect of which no environmental compliance approval is required. O. Reg. 105/94, s. 7 (2); O. Reg. 234/11, s. 17 (5).

(3)  Paragraph 13 of subsection (1) does not apply if,

(a) the part of the waste management system that came into contact with hauled sewage is not used for the collection, handling, treatment, transportation, storage or processing of hazardous waste, hauled liquid industrial waste or liquids for human or animal consumption;

(b) the part of the system that came into contact with hauled sewage is used for the collection, handling, treatment, transportation, storage or processing of other liquid material and the owner or operator of the system obtains every approval required for that purpose; and

(c) the part of the system that came into contact with hauled sewage is cleaned, to the satisfaction of any person to whom the other liquid material will be transferred, before that part of the system is used for the collection, handling, treatment, transportation, storage or processing of the other liquid material. O. Reg. 157/98, s. 6 (2).

(4)  If, pursuant to subsection (3), a part of a waste management system that came into contact with hauled sewage is used for the collection, handling, treatment, transportation, storage or processing of other liquid material, a person shall not use that part of the system again for hauled sewage unless it, and any other part of the system that was contaminated during the collection, handling, treatment, transportation, storage or processing of the other liquid material, has been cleaned to the satisfaction of the Director. O. Reg. 157/98, s. 6 (2).

(5)  The operator of a waste management system for hauled sewage shall,

(a) keep daily records of the premises from which hauled sewage is collected and the amounts of sewage collected from those premises;

(b) keep daily records of the disposal site or disposal sites at which hauled sewage is discharged or disposed of and the amounts of hauled sewage discharged or disposed of at those sites; and

(c) keep the daily records required by clauses (a) and (b) available for review by the Director, as the Director may require, for a period of at least two years after the calendar year to which the records relate. O. Reg. 157/98, s. 6 (2).

16.1  The following are prescribed as standards for the operation and maintenance of vehicle sewage holding tanks:

1. A person shall not discharge or permit the discharge of effluent from a vehicle sewage holding tank to the surface of the ground or into ground water, surface water, a piped water supply, a well water supply, a watercourse or a drainage ditch.

2. A person shall not discharge or permit the discharge of effluent from a vehicle sewage holding tank except from a place on or part of the tank, or from a piping system connected to the tank, that is designed to discharge effluent.

3. The owner and the operator of a vehicle sewage holding tank shall ensure that insects and animals are prevented from gaining access to sewage in the tank.

4. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank does not discharge micro organisms of intestinal origin into the natural environment in a manner that may be hazardous to human health.

5. The owner and the operator of a vehicle sewage holding tank shall ensure that no gas is discharged into a building or structure from the tank or a piping system connected to the tank except in a manner for which the tank or piping system was designed.

6. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank does not receive any waste other than in-vehicle sewage produced in the vehicle.

7. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank and any piping system connected to the tank are maintained in good operating condition. O. Reg. 157/98, s. 7.

Management of Asbestos Waste

17.  No person shall manage asbestos waste except in accordance with the following:

1. No person shall cause or permit asbestos waste to leave the location at which it is generated except for the purpose of transporting it, in accordance with paragraph 2, to a waste disposal site, the operator of which has agreed to accept it and has been advised as to its anticipated time of arrival.

2. Asbestos waste transported to a waste disposal site shall,

i. be in a rigid, impermeable, sealed container of sufficient strength to accommodate the weight and nature of the waste, or

ii. where the asbestos waste is being transported in bulk, be transported by means of a waste management system that is subject to an environmental compliance approval that specifically authorizes the transportation of asbestos waste in bulk.

3. Where a container referred to in subparagraph i of paragraph 2 is a cardboard box, the waste must be sealed in a six-mil polyethylene bag placed within the box.

4. Every container referred to in subparagraph i of paragraph 2 must be free from punctures, tears or leaks.

5. The external surfaces of every container referred to in subparagraph i of paragraph 2 and of every vehicle or vessel used for the transport of asbestos waste must be free from asbestos waste.

6. Both sides of every vehicle used for the transportation of asbestos waste and every container referred to in subparagraph i of paragraph 2 must display thereon in large, easily legible letters that contrast in colour with the background the word “CAUTION” in letters not less than ten centimetres in height and the words:

CONTAINS ASBESTOS FIBRES

Avoid Creating Dust and Spillage

Asbestos May be Harmful To Your Health

Wear Approved Protective Equipment.

7. Asbestos waste being transported from the location at which it is generated,

i. shall be transported,

A. by a driver trained in the management of asbestos waste,

B. as directly as may be practicable, to the waste disposal site at which disposal of the asbestos waste is intended to take place,

ii. shall not be transferred to a transfer station or other waste disposal site where disposal of the asbestos waste will not take place, but it may be transported to a waste disposal site that is subject to an environmental compliance approval that specifically authorizes acceptance and processing of asbestos waste,

iii. shall not be transported with any other cargo in the same vehicle,

iv. shall not be transported in a compaction type waste haulage vehicle,

v. where it is being transported in cardboard boxes, shall be in an enclosed vehicle,

vi. shall be properly secured and covered with a suitable tarpaulin or net if it is transported in a vehicle that is not enclosed, and

vii. shall be transported only in vehicles equipped with emergency spill cleanup equipment including a shovel, a broom, wetting agent, protective clothing, a supply of six-mil polyethylene bags, bag closures and personal respiratory equipment.

8. During the transportation or unloading thereof, any asbestos waste that is loose or in a container that is punctured, broken or leaking shall be packaged, immediately on discovery, in a six-mil polyethylene bag.

9. Where containers of asbestos waste are being unloaded, the unloading shall be carried out so that no loose asbestos or punctured, broken or leaking containers of asbestos waste are landfilled.

10. Asbestos waste may be deposited only at locations in a landfilling site that have been adapted for the purpose of receiving asbestos waste or are otherwise suitable for that purpose.

11. Asbestos waste may be deposited at a landfilling site only while the depositing is being supervised by the operator of the site or a person designated by the operator for the purpose and the person supervising is not also operating machinery or the truck involved.

12. Where asbestos waste is deposited, as set out in paragraph 10, at least 125 centimetres of garbage or cover material must be placed forthwith over the deposited asbestos waste in such a manner that direct contact with compaction equipment or other equipment operating on the site is avoided.

13. Every person handling asbestos waste or containers of asbestos waste, supervising the unloading of asbestos waste in bulk or cleaning asbestos waste residues from containers, vehicles or equipment shall wear protective clothing and personal respiratory equipment while so doing.

14. Protective clothing that has been or is suspected of having been in contact with asbestos waste shall be changed at the site of the exposure and either properly disposed of as asbestos waste or washed at the end of the working day.

15. Disposable protective clothing shall not be reused.

16. Every person directly or indirectly involved in the transportation, handling or management of asbestos waste shall take all precautions necessary to prevent asbestos waste from becoming airborne. R.R.O. 1990, Reg. 347, s. 17; O. Reg. 234/11, s. 18.

Waste Generation Facilities

17.1  (1)  Sections 27, 40 and 41 of the Act do not apply to a waste generation facility in respect of the activities set out in subsection (2), to the extent that those activities relate to,

(a) waste that was produced at the waste generation facility, other than PCB waste; or

(b) waste that came legally to the waste generation facility but was not produced at the facility, other than PCB waste, soil or a soil mixture. O. Reg. 461/05, s. 7.

(2)  The following activities are the activities referred to in subsection (1):

1. The production, collection, handling or temporary storage of municipal waste.

2. The production, collection, handling or temporary storage of subject waste.

3. The processing of waste, if the processing does not involve,

i. the combustion or land application of municipal waste, hazardous waste or liquid industrial waste,

ii. the mixing, blending, bulking or other intermingling of waste or other material with characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, or

iii. the processing of soil.

4. The processing of municipal waste with on-site thermal treatment equipment that, pursuant to subsection 28 (1) of this Regulation, is exempt from the operation of section 27 of the Act.

5. The processing of characteristic waste or listed waste, if the processing involves the mixing, blending, bulking or other intermingling of waste or other material with the characteristic waste or listed waste, and,

i. the processing will, by itself or in conjunction with other processing, permit the land disposal of the characteristic waste or listed waste under section 75, 76, 77, 78 or 79, or

ii. the mixed, blended, bulked or otherwise intermingled waste is to be transported to a receiving facility, the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the receiving facility, and the operator of the waste generation facility has, at the waste generation facility, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste.

6. The processing of waste so that it becomes exempt from Part V of the Act and this Regulation under paragraph 7 of subsection 3 (1).

7. The introduction of waste into, and the processing of waste in preparation for the introduction of the waste into,

i. a sewage works that is subject to the Ontario Water Resources Act or that was established before August 3, 1957, or

ii. a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992.

8. The packaging or offering of waste for retail sale to meet a realistic market demand, and the processing of waste, if the processing is for the purpose of packaging or offering the waste for retail sale to meet a realistic demand.

9. The transfer to a waste transportation vehicle of,

i. municipal waste, or

ii. subject waste, other than characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed.

10. The transfer to a waste transportation vehicle of characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, if the transfer does not involve the mixing, blending, bulking or other intermingling of the characteristic waste or listed waste with any other waste or material.

11. The transfer to a waste transportation vehicle of characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, if the transfer involves the mixing, blending, bulking or other intermingling of the characteristic waste or listed waste with any other waste or material and,

i. the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the receiving facility named in the manifest that is related to the waste transportation vehicle’s load, and the carrier has, accompanying the load, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste, or

ii. the mixing, blending, bulking or other intermingling is done in accordance with an environmental compliance approval issued in respect of a waste transportation system that the waste transportation vehicle is part of. O. Reg. 461/05, s. 7; O. Reg. 102/07, s. 8; O. Reg. 234/11, s. 19; O. Reg. 334/13, s. 2.

(3)  Subsection (1) does not apply to a waste generation facility if waste management is the principal function of the waste generation facility. O. Reg. 461/05, s. 7.

17.2  If a waste generation facility to which subsection 17.1 (1) applies stores subject waste, the operator and the owner of the facility shall ensure that it is operated in accordance with the following rules:

1. Subject waste must be stored, handled and maintained so as to prevent,

i. leaks or spills of the waste, or

ii. damage to or deterioration of the container in which the waste is stored.

2. Subject waste must not be stored for a period exceeding 24 months unless,

i. an application for approval under Part II.1 of the Act respecting the storage of subject waste by the waste generation facility has been made and has not yet been determined, or

ii. an application for a certificate of approval respecting the storage of subject waste by the waste generation facility was made before Part II.1 of the Act came into force and has not yet been determined.

3. The first time that subject waste is stored at the waste generation facility for more than 90 days, a notice must be given to the Director, within five business days after the 90th day of storage, that,

i. describes, as accurately as possible, the nature, amount and location of subject waste stored, or expected to be stored in the future, at the waste generation facility for more than 90 days, and

ii. indicates how frequently subject waste is expected to be stored in the future at the waste generation facility for more than 90 days.

4. If notice is given under paragraph 3, written notice must be given to the Director of,

i. any change in the information referred to in paragraph 3, within five business days after the change, or

ii. the closure of the waste generation facility, within five business days after the closure.

5. If subject waste is stored at the waste generation facility for more than 90 days, a record must be made of the following information within five business days after the 90th day of storage:

i. The name and waste number of the waste.

ii. The quantity of the waste.

iii. The manner in which the waste is stored.

iv. The reasons for storing the waste.

v. The anticipated time and manner of disposal of the waste.

6. A record made under paragraph 5 must be updated as often as necessary to ensure that it contains information that is current to within five business days.

7. A record made or updated under paragraph 5 or 6 must be retained at the location where subject waste is stored, or

i. the record must be maintained at the head office of the operator or owner of the facility, and

ii. an electronic copy of the record must be retained at the location where subject waste is stored.

8. A record made or updated under paragraph 5 or 6 must be retained until the date that the subject waste is no longer stored, and for at least two years after that date. O. Reg. 461/05, s. 7; O. Reg. 337/09, s. 8; O. Reg. 234/11, s. 20.

Generator Registration

18.  (1)  Every generator who operates a waste generation facility that is involved in the production, collection, handling or storage of subject waste shall,

(a) before transferring any subject waste from that waste generation facility or within three months after producing, collecting or storing subject waste at that facility, submit an initial Generator Registration Report to the Director in respect of the facility; and

(b) on or before February 15 in every year after the year in which an initial report is submitted under clause (a), submit an annual Generator Registration Report to the Director in respect of each waste generation facility operated by the generator. O. Reg. 337/09, s. 9 (1).

(1.1)  Subsection (1) applies to waste produced, collected, handled or stored at the waste generation facility that is subject waste and that is characteristic waste or listed waste, even if the waste ceases to be hazardous waste while it is at the facility. O. Reg. 461/05, s. 8 (1).

(2)  Every report referred to in subsection (1) or (6) shall be in the form or format provided or approved by the Ministry, shall comply with the Manual and shall contain the data, analysis and other information necessary to enable the Director to satisfy himself or herself of the following:

1. The quality, quantity and nature of the waste.

2. The required treatment for the waste and the planned treatment for the waste.

3. The intended manner and location of the disposal of the waste or, if the waste is not to be disposed, the use to which the waste will be put.

4. Compliance with all applicable legal requirements. O. Reg. 461/05, s. 8 (2).

(3)  Upon receipt of an initial or annual Generator Registration Report and the required fee, the Director shall post on the Ministry website a generator registration document for the waste generation facility that is the subject of the Generator Registration Report setting out the date of the posting, the name of the generator, a generator registration number and the applicable waste numbers accepted by the Director. O. Reg. 501/01, s. 2 (1).

(4)  A generator registration document posted under subsection (3) is valid until the earlier of the posting of a revised or subsequent generator registration document in respect of the same waste generation facility and February 15 of the year after the year in which the document was posted. O. Reg. 501/01, s. 2 (1).

(5)  Revoked: O. Reg. 461/05, s. 8 (3).

(6)  If there is any change from the information submitted in an initial Generator Registration Report, the most recent annual Generator Registration Report or any previous supplementary Generator Registration Reports, the generator shall submit a supplementary Generator Registration Report to the Director within 15 days after the change. O. Reg. 461/05, s. 8 (4).

(6.1)  A generator who submits an initial, annual or supplementary Generator Registration Report to the Director shall make a record of all data, analysis and other information used in the preparation of the report, and shall keep the record, for at least three years, at the waste generation facility, or

(a) shall keep the record, for at least three years, at the head office of the generator; and

(b) shall keep an electronic copy of the record, for at least three years, at the waste generation facility. O. Reg. 337/09, s. 9 (2).

(7)  Upon receipt of a supplementary Generator Registration Report that relates to a valid generator registration document, the Director shall post on the Ministry website a revised generator registration document. O. Reg. 501/01, s. 2 (1).

(7.1)  No generator shall transfer a particular subject waste from a waste generation facility to a waste transportation system unless a valid generator registration document for that waste generation facility with a waste number for that particular subject waste is posted on the Ministry website. O. Reg. 501/01, s. 2 (1).

(7.2)  In all transfers of subject waste under this Regulation, every generator shall use the generator registration number issued in respect of the waste generation facility from which the subject waste is being transferred and the applicable waste numbers set out in the Manual. O. Reg. 501/01, s. 2 (1).

(8)  Every generator shall keep a record of the subject waste disposed of at the waste generation facility including the name, waste number, quantity and disposition of the waste. R.R.O. 1990, Reg. 347, s. 18 (8).

(9)  A record referred to in subsection (8) may be disposed of after two years. R.R.O. 1990, Reg. 347, s. 18 (9).

(10)  Revoked: O. Reg. 461/05, s. 8 (5).

(11)  A generator who transfers subject waste to a waste transportation system shall, within four weeks after the transfer, confirm that the waste was delivered to the intended receiving facility or to another receiving facility approved to accept the waste, and, if the generator does not confirm the delivery within that period, the generator shall, within six weeks after the transfer, notify the Director in writing that the delivery has not been confirmed. O. Reg. 337/09, s. 9 (3); O. Reg. 234/11, s. 21 (1).

(12)  In unusual circumstances, such as a spill, a process aberration or upset, or the circumstances described in subsection 22 (2), where a generator discovers that a generator registration number or a waste number is needed to comply with this Regulation in the disposal of subject waste, the Director may assign a generator registration number or accept a waste number identified by the generator. R.R.O. 1990, Reg. 347, s. 18 (12); O. Reg. 234/11, s. 21 (2).

(13)  Where a generator registration number is assigned under subsection (12), subsection (7.1) does not apply and subsections (1) and (2) shall be complied with within ninety days. O. Reg. 501/01, s. 2 (2).

(14)  Where a waste number is accepted under subsection (12), subsection (7.1) does not apply. O. Reg. 501/01, s. 2 (2).

(14.1)  Subsection (11) does not apply if an electronic manifest is used. O. Reg. 501/01, s. 2 (2).

(15)  Revoked: O. Reg. 337/09, s. 9 (4).

Manifests — Generator Requirements

19.  (1)  No generator shall permit subject waste to pass from the generator’s control or to leave the waste generation facility except,

(a) by transfer of the subject waste to a waste transportation system that is subject to an environmental compliance approval and where the generator has completed a manifest in respect of the waste in accordance with the Manual and this Regulation; or

(b) by direct discharge to a sewage works, other than a storm sewer, that is subject to the Ontario Water Resources Act or was established before August 3, 1957, or into a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992. R.R.O. 1990, Reg. 347, s. 19 (1); O. Reg. 460/99, s. 3; O. Reg. 501/01, s. 3; O. Reg. 337/09, s. 10; O. Reg. 234/11, s. 22; O. Reg. 334/13, s. 3.

(2)  No generator shall transfer subject waste to a waste transportation system unless the subject waste is so packaged or marked that it meets the transport requirements of the Transportation of Dangerous Goods Act (Canada). R.R.O. 1990, Reg. 347, s. 19 (2).

Manifests — Carrier Requirements

20.  (1)  Every carrier shall report to the Director the number of every intact manifest supplied to the carrier that is lost, spoiled or used other than in accordance with this Regulation, within 15 days after the carrier becomes aware of the loss, spoilage or use. O. Reg. 337/09, s. 11.

(2)  Every carrier shall return to the Director every intact manifest or partial manifest supplied to the carrier that is not used for the purposes of this Regulation because it has been spoiled or completed erroneously or for any other reason, within three days after the carrier has decided not to use the manifest. O. Reg. 501/01, s. 4.

20.1  (1)  No carrier shall have possession of subject waste in Ontario unless the waste was accepted from a generator and waste generation facility for which a valid generator registration document for that waste generation facility with a waste number for that particular subject waste is posted on the Ministry website. O. Reg. 501/01, s. 5.

(2)  Subsection (1) does not apply in respect of subject waste,

(a) accepted from a generator to whom section 18 does not apply; or

(b) accepted from outside Ontario for the purpose of being transported for transfer to a receiving facility outside Ontario. O. Reg. 501/01, s. 5.

21.  (1)  No carrier shall have possession of subject waste unless the carrier has, accompanying the waste, a manifest in respect of the waste, completed by the generator in accordance with the Manual and this Regulation, except during a transfer while the manifest is being completed by a generator or receiver. R.R.O. 1990, Reg. 347, s. 21 (1); O. Reg. 460/99, s. 4.

(2)  For purposes of subsection (1), a manifest is not completed by a generator in accordance with this Regulation if it contains an obvious error. R.R.O. 1990, Reg. 347, s. 21 (2).

(3)  A printed copy of an electronic manifest with sections A and B completed shall be sufficient for the purposes of subsection (1). O. Reg. 501/01, s. 6.

22.  (1)  No carrier shall permit subject waste to pass from the carrier’s control except in accordance with this Regulation. R.R.O. 1990, Reg. 347, s. 22 (1).

(2)  A carrier, with the specific approval of the Director, may transfer subject waste in Ontario to another vehicle in the same waste transportation system or to a waste transportation system that is subject to an environmental compliance approval or to a receiving facility to alleviate a dangerous situation. O. Reg. 234/11, s. 23.

(3)  Where a truckload or less of subject waste has been transferred by a generator to a waste transportation system, the carrier shall, on the day the waste is transferred, transport the waste to the receiving facility named in the manifest related to that load unless the carrier is permitted to do otherwise by subsection (2) or section 27. R.R.O. 1990, Reg. 347, s. 22 (3); O. Reg. 337/09, s. 12.

Manifests — Transport within Ontario

23.  (1)  This section applies where a generator transfers subject waste in Ontario to a waste transportation system for transport to a receiving facility in Ontario and, for the purpose of this section, “generator” includes a carrier to whom subsection 22 (2) applies. R.R.O. 1990, Reg. 347, s. 23 (1).

(2)  Where subject waste is transferred to a waste transportation system by a generator and a paper manifest is used,

(a) for each truckload or part of a truckload that is transferred, the carrier shall,

(i) complete section B (Carrier) of an intact manifest in accordance with the Manual, and

(ii) at the time of the transfer, give the manifest to the generator; and

(b) for each truckload or part of a truckload that is transferred, the generator shall,

(i) at the time of the transfer, obtain from the carrier the intact manifest, with section B completed, complete section A (Generator) of the manifest in accordance with the Manual, remove Copy 1 (White) and Copy 2 (Green) of the manifest, and return the remaining four copies to the carrier,

(ii) return Copy 1 (White) of the manifest to the Director within three working days after the transfer, and

(iii) retain Copy 2 (Green) of the manifest, for at least two years, at the waste generation facility, or

(A) retain Copy 2 (Green) of the manifest, for at least two years, at the head office of the generator, and

(B) retain an electronic copy of the manifest, for at least two years, at the waste generation facility. O. Reg. 337/09, s. 13 (1).

(2.1)  Where subject waste is transferred to a waste transportation system by a generator and an electronic manifest is used, for each truckload or part thereof transferred, at the time of the transfer,

(a) the generator shall give the carrier electronic access to the manifest;

(b) the carrier shall electronically complete section B (Carrier) of the manifest; and

(c) the generator shall,

(i) electronically complete section A (Generator) of the manifest in accordance with the Manual,

(ii) give the receiver electronic access to the manifest,

(iii) electronically submit the manifest, with sections A and B completed, to the Director, and

(iv) if requested by the carrier, print a paper copy of the manifest, as submitted under subclause (iii), and give it to the carrier. O. Reg. 501/01, s. 7 (2).

(3)  A carrier may transfer subject waste,

(a) with the specific approval of the Director, to another vehicle of the same waste transportation system, to a waste transportation system that is subject to an environmental compliance approval or to a specified receiving facility as mentioned in clause (b), (c) or (d) to alleviate a dangerous situation;

(b) to a waste disposal site that is subject to an environmental compliance approval that authorizes acceptance of the waste;

(c) with the consent of the owner of the sewage works, to a sewage works in respect of which an environmental compliance approval has been issued and that is not in contravention of the approval; or

(d) to a waste-derived fuel site having a combustion unit that is subject to an environmental compliance approval issued in respect of an activity mentioned in section 9 of the Act that authorizes acceptance and combustion of the waste. R.R.O. 1990, Reg. 347, s. 23 (3); O. Reg. 234/11, s. 24 (1-4).

(4)  Every carrier transferring waste under subsection (3) shall, at the time of the transfer, give the receiver the remaining four parts of the paper manifest, or the number of the electronic manifest, completed for that load of waste. O. Reg. 501/01, s. 7 (3).

(5)  Where a transfer of subject waste takes place under subsection (3) and a paper manifest is used, the receiver shall,

(a) at the time of the transfer, obtain from the carrier the remaining four copies of the manifest referred to in subclause (2) (b) (i), with sections A and B completed, complete section C (Receiver) of the remaining four copies of the manifest in accordance with the Manual, remove Copy 4 (Pink), and return Copy 4 (Pink) to the carrier;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the transfer;

(c) retain Copy 5 (Blue) of the manifest, for at least two years, at the receiving facility named in the manifest, or

(i) retain Copy 5 (Blue) of the manifest, for at least two years, at the head office of the receiver, and

(ii) retain an electronic copy of the manifest, for at least two years, at the receiving facility named in the manifest; and

(d) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the transfer. O. Reg. 337/09, s. 13 (2).

(5.1)  Where a transfer of subject waste takes place under subsection (3) and an electronic manifest is used, the receiver shall obtain from the carrier the number of the manifest completed for that load, shall electronically access the manifest and shall, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director. O. Reg. 501/01, s. 7 (5).

(6)  Every carrier transferring waste under subsection (3) shall, prior to leaving the site of the transfer, obtain from the receiver of the waste Copy 4 (Pink) of the manifest referred to under clause (5) (a) and shall retain it for a period of two years. R.R.O. 1990, Reg. 347, s. 23 (6); O. Reg. 337/09, s. 13 (3).

(7)  Where a paper manifest is used, every carrier who is the operator of a waste transportation system that is subject to an environmental compliance approval to operate as a dust suppression waste management system may deposit for the purpose of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval and, where that is done, shall,

(a) at the time of completion of the deposit, complete section C (Receiver) of the remaining four parts of the applicable manifest received under subclause (2) (b) (i);

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the deposit;

(c) retain Copy 4 (Pink) of the manifest for two years; and

(d) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the deposit. R.R.O. 1990, Reg. 347, s. 23 (7); O. Reg. 501/01, s. 7 (6); O. Reg. 337/09, s. 13 (4); O. Reg. 234/11, s. 24 (5).

(8)  Where an electronic manifest is used, every carrier described in subsection (7) may deposit for the purpose of dust suppression, in accordance with the approval described in subsection (7), dust suppressant at a dust suppression site designated in the approval and, where that is done, shall, as quickly as is reasonably possible following completion of the deposit,

(a) electronically access the manifest completed for that load;

(b) electronically complete section C (Receiver) of the manifest; and

(c) electronically submit the manifest, with sections A, B and C completed, to the Director. O. Reg. 501/01, s. 7 (7).

Manifests — Transport out of Ontario

24.  (1)  This section applies where a generator transfers subject waste in Ontario to a waste transportation system for transport to a receiving facility outside Ontario. R.R.O. 1990, Reg. 347, s. 24 (1).

(2)  Where subject waste is transferred for transport to a receiving facility in a Canadian jurisdiction, a manifest issued under the Transportation of Dangerous Goods Act (Canada) or an equivalent manifest issued by a Canadian jurisdiction may be used for purposes of compliance with this Regulation. R.R.O. 1990, Reg. 347, s. 24 (2).

(3)  Where subject waste is transferred for transport to a receiving facility in a Canadian jurisdiction and the laws of that jurisdiction require submission to authorities in that jurisdiction of the equivalent of Copy 1 or 3 of a manifest, submission to the Director of a photocopy of the copy submitted or of a copy retained may be substituted for the requirement to submit Copy 1 or 3 of a manifest. R.R.O. 1990, Reg. 347, s. 24 (3).

(4)  Where subject waste is transferred to a waste transportation system by a generator and a paper manifest is used,

(a) for each truckload or portion thereof transferred, the carrier shall complete section B (Carrier) of an intact manifest and give the manifest, at the time of the transfer, to the generator; and

(b) for each truckload or portion thereof transferred, the generator shall obtain from the carrier the intact manifest, with section B completed, and shall,

(i) at the time of the transfer, complete section A (Generator) in accordance with the Manual,

(ii) remove Copy 1 (White) and return it to the Director within three working days after the transfer,

(iii) remove Copy 2 (Green) and retain it, for at least two years, at the waste generation facility, or

(A) remove Copy 2 (Green) and retain it, for at least two years, at the generator’s head office, and

(B) retain an electronic copy of the manifest, for at least two years, at the waste generation facility, and

(iv) return the remaining four copies of the manifest to the carrier at the time of the transfer. R.R.O. 1990, Reg. 347, s. 24 (4); O. Reg. 460/99, s. 6; O. Reg. 501/01, s. 8 (1); O. Reg. 337/09, s. 14.

(4.1)  Where subject waste is transferred to a waste transportation system by a generator and an electronic manifest is used, for each truckload or part thereof transferred, at the time of the transfer,

(a) the generator shall give the carrier electronic access to the manifest;

(b) the carrier shall electronically complete section B (Carrier) of the manifest; and

(c) the generator shall,

(i) electronically complete section A (Generator) of the manifest in accordance with the Manual,

(ii) give the receiver electronic access to the manifest,

(iii) electronically submit the manifest, with sections A and B completed, to the Director, and

(iv) if requested by the carrier, print a paper copy of the electronic manifest, as submitted under subclause (iii), and give it to the carrier. O. Reg. 501/01, s. 8 (2).

(5)  No carrier shall transport subject waste out of Ontario destined for a receiving facility outside Ontario unless the carrier has reason to believe the intended receiver is willing to complete section C (Receiver) of the applicable manifest completed for that load of waste and, in the case of an electronic manifest, electronically submit the completed manifest to the Director. R.R.O. 1990, Reg. 347, s. 24 (5); O. Reg. 501/01, s. 8 (3).

(6)  Where a paper manifest is used, every carrier transferring subject waste to a receiving facility outside Ontario shall, at the time of the transfer, give the receiver the remaining four parts of the manifest for completion of section C (Receiver). O. Reg. 501/01, s. 8 (4).

(7)  Where a paper manifest is used, every carrier who transfers waste under subsection (6) shall,

(a) return Copy 3 (Yellow) of the manifest to the Director within three working days after the transfer;

(b) retain Copy 4 (Pink) of the manifest for two years; and

(c) remove Copy 6 (Brown) of the manifest and return it to the generator indicated on the manifest within three working days after the transfer. R.R.O. 1990, Reg. 347, s. 24 (7); O. Reg. 501/01, s. 8 (5).

(8)  Every manifest referred to in subsection (7) shall have section C (Receiver) completed by the receiver. R.R.O. 1990, Reg. 347, s. 24 (8).

(9)  Where an electronic manifest is used, every carrier who transfers subject waste under subsection (6) shall, at the time of the transfer, give the receiver the number of the electronic manifest completed for that load of waste and request that the receiver electronically access the manifest and, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director. O. Reg. 501/01, s. 8 (6).

(10)  Every carrier shall notify the Director forthwith of the number of the electronic manifest, the name of the receiver, if it is not the same as that set out in section A of the manifest, and the date of the transfer to the receiver, where the carrier is aware that the receiver has not complied with a request made under subsection (9). O. Reg. 501/01, s. 8 (6).

Manifests — Transport into Ontario

25.  (1)  This section applies where subject waste is transferred outside Ontario to a waste transportation system for transport to a receiving facility in Ontario. R.R.O. 1990, Reg. 347, s. 25 (1).

(2)  Where subject waste is transferred in Canada for transport to a receiving facility in Ontario, a manifest under the Canadian Environmental Protection Act, 1999 (Canada) or any equivalent manifest issued by a Canadian jurisdiction may be used for purposes of compliance with this Regulation. R.R.O. 1990, Reg. 347, s. 25 (2); O. Reg. 337/09, s. 15 (1).

(3)  Where a paper manifest is used, no carrier shall bring subject waste into Ontario for purposes of transport to a receiving facility in Ontario unless,

(a) Revoked: O. Reg. 501/01, s. 9 (2).

(b) for each truckload or portion thereof to be transferred, the carrier completed section B (Carrier) of an intact manifest and gave it, at the time of the transfer, to the generator for completion of section A (Generator) and return to the carrier; and

(c) the applicable manifest with section B (Carrier) completed by the carrier and section A (Generator) completed by the generator accompanies the waste. R.R.O. 1990, Reg. 347, s. 25 (3); O. Reg. 501/01, s. 9 (1, 2).

(3.1)  Where an electronic manifest is used, no carrier shall bring subject waste into Ontario for purposes of transport to a receiving facility in Ontario unless, for each truckload or portion thereof to be transferred, at the time of the transfer from the generator,

(a) the carrier electronically completed section B (Carrier) of the manifest; and

(b) the generator electronically completed section A (Generator) of the manifest and electronically submitted the manifest, with sections A and B completed, to the Director. O. Reg. 501/01, s. 9 (3).

(4)  Where a paper manifest is used, every carrier who brings subject waste into Ontario for transfer to a receiving facility in Ontario shall forward to the Director, within three working days after the out of province transfer, Copy 1 (White) of the manifest showing the generator registration number and the applicable waste number. O. Reg. 501/01, s. 9 (4).

(5)  A carrier may transfer subject waste,

(a) to a waste disposal site that is subject to an environmental compliance approval that authorizes acceptance of the waste;

(b) with the consent of the owner of the sewage works, to a sewage works in respect of which an environmental compliance approval has been issued, and that is not in contravention of the approval; or

(c) to a waste-derived fuel site having a combustion unit that is subject to an environmental compliance approval in respect of activities mentioned in section 9 of the Act that authorizes acceptance and combustion of the waste. R.R.O. 1990, Reg. 347, s. 25 (5); O. Reg. 234/11, s. 25 (1-3).

(6)  Every carrier transferring waste under subsection (5) shall, at the time of the transfer, give the receiver the remaining four parts of the paper manifest completed in respect of the waste or number of the electronic manifest completed in respect of the waste, as the case may be. O. Reg. 501/01, s. 9 (5).

(7)  Where a transfer of subject waste takes place under subsection (5) and a paper manifest is used, the receiver shall obtain from the carrier the remaining four parts of the manifest completed in respect of that load of waste and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest in accordance with the Manual;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the transfer;

(c) remove Copy 4 (Pink) of the manifest and return it to the carrier at the time of the transfer;

(d) retain Copy 5 (Blue) of the manifest, for at least two years, at the receiving facility named in the manifest, or

(i) retain Copy 5 (Blue) of the manifest, for at least two years, at the receiver’s head office, and

(ii) retain an electronic copy of the manifest, for at least two years, at the receiving facility named in the manifest; and

(e) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the transfer. R.R.O. 1990, Reg. 347, s. 25 (7); O. Reg. 501/01, s. 9 (6); O. Reg. 337/09, s. 15 (2, 3).

(7.1)  Where a transfer of subject waste takes place under subsection (5) and an electronic manifest is used, the receiver shall obtain from the carrier the number of the manifest completed for that load, shall electronically access the manifest and shall, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director. O. Reg. 501/01, s. 9 (7).

(8)  Where a paper manifest is used, every carrier who has transferred waste under subsection (5) shall, prior to leaving the site of the transfer, obtain from the receiver Copy 4 (Pink) of the manifest and shall retain it for two years. O. Reg. 501/01, s. 9 (8).

(9)  Where a paper manifest is used, every carrier who is the operator of a waste transportation system that is subject to an environmental compliance approval to operate as a dust suppression waste management system may deposit for the purpose of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval and, where that is done, shall,

(a) at the time of completion of the deposit, complete section C (Receiver) of the remaining four parts of the manifest accompanying the waste;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the deposit;

(c) retain Copy 4 (Pink) of the manifest for two years; and

(d) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the deposit. R.R.O. 1990, Reg. 347, s. 25 (9); O. Reg. 501/01, s. 9 (9); O. Reg. 234/11, s. 25 (4).

(10)  Where an electronic manifest is used, every carrier described in subsection (9) may deposit for the purpose of dust suppression, in accordance with the approval described in subsection (9), dust suppressant at a dust suppression site designated in the approval and, where that is done, shall, as quickly as is reasonably possible following completion of the deposit,

(a) electronically access the manifest completed for that load;

(b) electronically complete section C (Receiver) of the manifest; and

(c) electronically submit the manifest, with sections A, B and C completed, to the Director. O. Reg. 501/01, s. 9 (10).

Manifests — Transport through Ontario

26.  (1)  No carrier shall transport through Ontario subject waste from outside Ontario for transfer to a receiving facility outside Ontario unless the generator has with the waste, for each truckload or portion thereof, a manifest, or a paper copy of an electronic manifest, completed in accordance with the requirements of the jurisdiction issuing the manifest. O. Reg. 501/01, s. 10.

(2)  Where this section applies, a manifest issued under the Canadian Environmental Protection Act, 1999 (Canada) or an equivalent manifest issued by a Canadian jurisdiction or a Uniform Hazardous Waste Manifest as prescribed by the United States Environmental Protection Agency may be used for purposes of compliance with this Regulation. R.R.O. 1990, Reg. 347, s. 26 (2); O. Reg. 337/09, s. 16.

Refusals

27.  (0.1)  A receiver shall decide whether to accept or refuse to accept a transfer of subject waste within 24 hours after the waste arrives at the receiving facility. O. Reg. 337/09, s. 17.

(1)  A receiver who refuses to accept a transfer of subject waste shall prepare a refusal report in a form or format provided or approved by the Ministry and return it to the Director within three working days after the refusal. O. Reg. 501/01, s. 11 (1).

(2)  Where a carrier intends to transfer subject waste to a receiving facility and the waste is refused by the intended receiver, the carrier, before attempting to make a different transfer, shall consult and obtain the instructions of the generator, unless written instructions have been provided by the generator in advance and may transfer the waste to a receiving facility indicated in the instructions. R.R.O. 1990, Reg. 347, s. 27 (2).

(3)  If waste is refused by the intended receiver at the receiving facility and if the carrier cannot conveniently make a different transfer in accordance with this Regulation, the carrier may transfer the unadulterated waste to the waste generation facility set out in section A (Generator) of the applicable manifest and the carrier shall, at the time of the transfer, give the generator four parts of the paper manifest or the number of the electronic manifest, as the case may be, that was completed in respect of the waste. O. Reg. 501/01, s. 11 (2).

(4)  Every generator shall accept a transfer of unadulterated subject waste in the circumstances described in subsection (3). R.R.O. 1990, Reg. 347, s. 27 (4).

(5)  Where a transfer of subject waste occurs under subsection (3) and a paper manifest is used, the generator shall obtain from the carrier the remaining four parts of the applicable manifest completed by the generator in accordance with this Regulation and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(b) return Copy 3 (Yellow) to the Director within three working days after the transfer;

(c) return Copy 4 (Pink) to the carrier at the time of the transfer; and

(d) retain Copy 6 (Brown) for two years. R.R.O. 1990, Reg. 347, s. 27 (5); O. Reg. 501/01, s. 11 (3).

(5.1)  Where a transfer of subject waste occurs under subsection (3) and an electronic manifest is used, the generator shall obtain from the carrier the number of the electronic manifest completed for that load, shall electronically access the manifest and shall, at the time of the transfer,

(a) electronically complete section C (Receiver) of the manifest; and

(b) electronically submit the manifest, with sections A, B and C completed, to the Director. O. Reg. 501/01, s. 11 (4).

(6)  Where a paper manifest is used, every carrier who has transferred waste under subsection (3) shall, prior to leaving the site of the transfer, obtain from the receiver Copy 4 (Pink) of the manifest and shall retain it for two years. O. Reg. 501/01, s. 11 (5).

(7)  A waste generation facility is exempt from the requirement of a waste disposal site certificate of approval under section 27 of the Act in respect of an acceptance of waste under this section. R.R.O. 1990, Reg. 347, s. 27 (7).

On-Site Thermal Treatment Equipment

28.  (1)  On-site thermal treatment equipment is exempt from the operation of section 27 of the Act unless the equipment is used to subject hazardous waste or liquid industrial waste to thermal treatment. O. Reg. 102/07, s. 9.

(2)  Revoked: O. Reg. 234/11, s. 26.

(3)  This section does not apply to on-site thermal treatment equipment at a woodwaste combustor site or waste-derived fuel site. O. Reg. 102/07, s. 9.

Woodwaste Combustor Sites

28.1  (1)  Sections 27, 40 and 41 of the Act do not apply to a woodwaste combustor site for residential heating in respect of woodwaste if not more than fifty cubic metres of woodwaste is stored at the woodwaste combustor site at any time. O. Reg. 337/09, s. 18 (1).

(2)  Sections 27, 40 and 41 of the Act do not apply to a woodwaste combustor site in respect of woodwaste if,

(a) none of the woodwaste stored at the woodwaste combustor site is stored there for more than 18 months; and

(b) no more woodwaste is stored at the woodwaste combustor site than is reasonably capable of being subject to thermal treatment or wholly utilized as a fuel or fuel supplement during a period of six months at the site. O. Reg. 102/07, s. 10; O. Reg. 337/09, s. 18 (2).

(2.1)  Subsection (2) does not apply on any day on which more than 100 tonnes of woodwaste are subject to thermal treatment at the site, if the sole purpose of subjecting the woodwaste to thermal treatment is to dispose of it. O. Reg. 102/07, s. 10.

(2.2)  Subsection (2) does not apply to a woodwaste combustor site at which woodwaste is subject to thermal treatment, if the principal function of the site is waste disposal. O. Reg. 102/07, s. 10.

(2.3)  Sections 27, 40 and 41 of the Act do not apply to a woodwaste combustor site in respect of woodwaste if,

(a) woodwaste is subject to thermal treatment at the woodwaste combustor site and the principal function of the site is waste disposal;

(b) not more than 100 tonnes of woodwaste is subject to thermal treatment at the woodwaste combustor site on any day;

(c) not more than 500 cubic metres of woodwaste is stored at the woodwaste combustor site at any time; and

(d) none of the woodwaste stored at the woodwaste combustor site is stored there for more than six months. O. Reg. 102/07, s. 10; O. Reg. 337/09, s. 18 (3).

(3)  A woodwaste combustor site is exempt from section 27 of the Act in respect of its use and operation if,

(a) the woodwaste combustor site was first put into operation before the 26th day of September, 1992; and

(b) immediately before the 26th day of September, 1992, no certificate of approval or provisional certificate of approval under Part V of the Environmental Protection Act was required for the use or operation of the woodwaste combustor site. O. Reg. 555/92, s. 8.

(4)  A woodwaste combustor site that is exempt under subsection (3) ceases to be exempt if the use or operation of the woodwaste combustor site changes substantially. O. Reg. 555/92, s. 8.

(5)  A woodwaste combustor site that is exempt under subsection (3) ceases to be exempt at the end of the twelve-month period immediately following the 26th day of September, 1992, if the woodwaste combustor site is in operation on fewer than thirty days during that twelve-month period. O. Reg. 555/92, s. 8.

28.2  Revoked: O. Reg. 234/11, s. 27.

Waste-Derived Fuel Sites

28.3  (1)  A waste-derived fuel site is exempt from section 27 of the Act if,

(a) the only waste-derived fuel utilized at the waste-derived fuel site is waste-derived fuel that is generated at the waste-derived fuel site and has never left the site; and

(b) not more than ten tonnes of waste-derived fuel is utilized at the waste-derived fuel site on any day. O. Reg. 555/92, s. 8.

(2)  A waste-derived fuel site is exempt from section 27 of the Act in respect of its use and operation if,

(a) the waste-derived fuel site was first put into operation before the 26th day of September, 1992; and

(b) immediately before the 26th day of September, 1992, no certificate of approval or provisional certificate of approval under Part V of the Environmental Protection Act was required for the use or operation of the waste-derived fuel site. O. Reg. 555/92, s. 8.

(3)  A waste-derived fuel site that is exempt under subsection (2) ceases to be exempt if the use or operation of the waste-derived fuel site changes substantially. O. Reg. 555/92, s. 8.

(3.1)  A waste-derived fuel site described in subsection 28.6 (1) that is exempt under subsection (2) ceases to be exempt if,

(a) the site is altered by the replacement of the combustion unit;

(b) the site is altered by an increase in the capacity of the combustion unit or the incorporation of an additional combustion unit; or

(c) the site is enlarged or extended. O. Reg. 280/07, s. 3.

(4)  A waste-derived fuel site that is exempt under subsection (2) ceases to be exempt at the end of the twelve-month period immediately following the 26th day of September, 1992, if the waste-derived fuel site is in operation on fewer than thirty days during that twelve-month period. O. Reg. 555/92, s. 8.

28.4  Revoked: O. Reg. 234/11, s. 27.

28.5  (1)  At a waste-derived fuel site, no person shall mix waste that is not waste-derived fuel with any other waste or material, if the material resulting from the mixing is waste-derived fuel. O. Reg. 555/92, s. 8.

(2)  Subsection (1) does not apply to prohibit the mixing of two or more wastes that are generated at the waste-derived fuel site and have never left the site. O. Reg. 555/92, s. 8.

28.6  (1)  No person shall use, operate, establish, alter, enlarge or extend a waste-derived fuel site, or cause or permit the use, operation, establishment, alteration, enlargement or extension of a waste-derived fuel site, if the site includes a combustion unit that is used principally for heating the interior of a building or other enclosed space for the comfort of occupants or for the provision of a suitable temperature for materials, including plant or animal life, in the building or enclosed space. O. Reg. 280/07, s. 4.

(2)  Subsection (1) does not apply to a waste-derived fuel site that is located in the Territorial District of Algoma, Cochrane, Kenora, Manitoulin, Nipissing, Parry Sound, Rainy River, Sudbury, Thunder Bay or Timiskaming. O. Reg. 280/07, s. 4.

(3)  Before June 1, 2009, subsection (1) does not apply to a waste-derived fuel site that is in operation on the day this section comes into force, if, on the day this section comes into force,

(a) the combustion unit is operating under a certificate of approval that authorizes acceptance and combustion of waste and that was issued under section 9 of the Act before January 11, 2007;

(b) the site is used in agriculture; or

(c) pursuant to subsection 28.3 (2), the site is exempt from section 27 of the Act in respect of its use and operation. O. Reg. 280/07, s. 4.

(4)  Subsection (3) ceases to apply to a waste-derived fuel site if,

(a) the site is altered by the replacement of the combustion unit;

(b) the site is altered by an increase in the capacity of the combustion unit or the incorporation of an additional combustion unit; or

(c) the site is enlarged or extended. O. Reg. 280/07, s. 4.

Existing Hospital Incinerators

29.  (1)  Revoked: R.R.O. 1990, Reg. 347, s. 29 (3); See O. Reg. 323/02, s. 2.

(2)  Revoked: R.R.O. 1990, Reg. 347, s. 29 (3); See O. Reg. 323/02, s. 2.

(3)  Spent: O. Reg. 323/02, s. 2.

(4)  All existing hospital incinerators that operated under the authority of subsection (1) or (2) and all hospital incinerators operating under a certificate of approval issued before December 6, 2002 must cease operations on or before December 6, 2003. O. Reg. 323/02, s. 2.

(5)  All certificates of approval for hospital incinerators issued before this subsection came into force are revoked on December 6, 2003. O. Reg. 323/02, s. 2.

Field Operations

29.1  Section 18 does not apply to a generator in respect of subject waste from field operations if the subject waste is destined for a local waste transfer facility. O. Reg. 337/09, s. 19.

29.2  Sections 19 to 26 do not apply to generators, carriers or receivers of subject waste from field operations if the subject waste is destined for a local waste transfer facility. O. Reg. 337/09, s. 19.

29.3  Sections 27, 40 and 41 of the Act do not apply to a local waste transfer facility if,

(a) no hazardous waste or liquid industrial waste, other than waste from field operations, is received or stored at the facility; and

(b) there is available, at or near the facility, fire-fighting equipment and spill clean-up and containment equipment that is appropriate to the quantities and types of waste at or expected to be at the facility. O. Reg. 337/09, s. 19.

29.4  Sections 27, 40 and 41 of the Act do not apply in respect of a local waste transfer facility if,

(a) access to the facility is controlled by gates, fencing, attendants or other security measures;

(b) subject to clause (c), any hazardous waste or liquid industrial waste at the facility is stored on an impermeable pad that,

(i) is or can be covered to keep out precipitation, and

(ii) has curbs, berms, catch basins or other features that are sufficient to prevent hazardous waste or liquid industrial waste from escaping into the natural environment;

(c) any syringes or other sharps, and any related waste, at the facility are stored indoors in puncture resistant containers that prevent exposure or spilling of the contents;

(d) the locations where hazardous waste, liquid industrial waste and waste described in clause (c) are stored at the facility are readily accessible for inspection, containment of spills and spills clean-up;

(e) there is available, at or near the facility, fire-fighting equipment and spill clean-up and containment equipment that is appropriate to the quantities and types of waste at or expected to be at the facility;

(f) a written record is kept each time hazardous waste or liquid industrial waste is received and stored at the facility or is transferred from the facility, and the record specifies the nature and quantity of the waste and is retained at the facility for at least two years after the record is made; and

(g) written notice that identifies the facility and sets out the facility’s location and the quantities and types of wastes that are at or are anticipated to be at the facility is given to the Director,

(i) one month before the facility is established, or

(ii) within fifteen days after this section comes into force, in the case of a facility that is in operation when this section comes into force. O. Reg. 337/09, s. 19; O. Reg. 234/11, s. 28.

29.5  Sections 27, 40 and 41 of the Act and section 16 of this Regulation do not apply in respect of a waste management system if,

(a) the system is owned or operated by a person who undertakes field operations or a person on whose behalf field operations are undertaken; and

(b) the operations of the system are limited to the collection and handling of waste from the field operations referred to in clause (a) and the transportation of the waste to,

(i) a local waste transfer facility, or

(ii) a waste disposal site that is authorized to receive the waste, if the waste is not subject waste. O. Reg. 337/09, s. 19.

Stationary Refrigerant Waste

30.  (1)  A stationary refrigerant waste collector that collects stationary refrigerant waste shall,

(a) recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers; or

(b) transport it to,

(i) a wholesale dealer in refrigerants,

(ii) a stationary refrigerant waste recycler, or

(iii) a stationary refrigerant waste disposal site that is subject to an environmental compliance approval to handle stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 30 (1); O. Reg. 190/94, s. 2 (1); O. Reg. 234/11, s. 29 (1).

(2)  A wholesale dealer in refrigerants that receives stationary refrigerant waste shall transport it to,

(a) a stationary refrigerant waste recycler; or

(b) a stationary refrigerant waste disposal site that is subject to an environmental compliance approval to handle stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 30 (2); O. Reg. 234/11, s. 29 (2).

(3)  A stationary refrigerant waste recycler that receives stationary refrigerant waste shall recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers. R.R.O. 1990, Reg. 347, s. 30 (3); O. Reg. 190/94, s. 2 (2).

31.  (1)  A stationary refrigerant waste collector shall keep a written record each time that stationary refrigerant waste is,

(a) removed and collected, at the stationary refrigerant waste collector’s ordinary place of business, from equipment in which refrigerant is used;

(b) received at the stationary refrigerant waste collector’s ordinary place of business, after being removed and collected at another location from equipment in which refrigerant is used; or

(c) transported from or recycled at the stationary refrigerant waste collector’s ordinary place of business. R.R.O. 1990, Reg. 347, s. 31 (1).

(2)  A wholesale dealer in refrigerants shall keep a written record each time that it receives or transports stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 31 (2).

(3)  A stationary refrigerant waste recycler shall keep a written record each time that it receives or recycles stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 31 (3).

(4)  A record made under this section shall show,

(a) the date the stationary refrigerant waste was collected, received, transported or recycled;

(b) the source of the stationary refrigerant waste;

(c) the quantity collected, received, transported or recycled;

(d) the type of stationary refrigerant waste; and

(e) what was done with the stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 31 (4).

(5)  A record made under this section may be disposed of after two years. R.R.O. 1990, Reg. 347, s. 31 (5).

(6)  Revoked: O. Reg. 190/94, s. 3.

32.  (1)  A stationary refrigerant waste disposal site that is the ordinary place of business of a stationary refrigerant waste collector or that is operated by a wholesale dealer in refrigerants is exempt from section 27 of the Act if,

(a) access to stationary refrigerant waste is controlled by gates, fencing, attendants or other security measures;

(b) containers in which stationary refrigerant waste is stored are clearly marked as to contents;

(c) stationary refrigerant waste is stored in a location and manner that prevents damage or deterioration;

(d) stored stationary refrigerant waste is readily accessible for inspection by a provincial officer;

(e) there is available, at or near the site, firefighting equipment and spill clean-up and containment equipment appropriate to the quantities and types of stationary refrigerant waste on or likely to be on the site; and

(f) written notice is given to the Director within ninety days after the establishment of the site, specifying the location of the site and the quantities and types of stationary refrigerant waste on or likely to be on the site. R.R.O. 1990, Reg. 347, s. 32 (1).

(2)  A stationary refrigerant waste disposal site is exempt from section 27 of the Act if,

(a) stationary refrigerant waste is removed and collected on the site from equipment in which refrigerant is used; and

(b) the site is not the ordinary place of business of the stationary refrigerant waste collector. R.R.O. 1990, Reg. 347, s. 32 (2).

33.  A stationary refrigerant waste management system is exempt from section 27 of the Act if all stationary refrigerant waste disposal sites used in the system are,

(a) exempt from section 27 of the Act; or

(b) established and operated in accordance with an environmental compliance approval. R.R.O. 1990, Reg. 347, s. 33; O. Reg. 234/11, s. 30.

34.  Section 18 does not apply in respect of subject waste that is stationary refrigerant waste unless,

(a) a stationary refrigerant waste collector transports stationary refrigerant waste directly from the waste generation facility to,

(i) a stationary refrigerant waste recycler, or

(ii) a stationary refrigerant waste disposal site that is subject to an environmental compliance approval to handle stationary refrigerant waste; or

(b) the waste generation facility is operated by a wholesale dealer in refrigerants. R.R.O. 1990, Reg. 347, s. 34; O. Reg. 234/11, s. 31.

35.  Section 19 and sections 21 to 27 do not apply in respect of subject waste that is stationary refrigerant waste being managed in accordance with section 30. O. Reg. 461/05, s. 9.

Mobile Refrigerant Waste

36.  (1)  On and after the 1st day of July, 1991, no person shall discharge or permit the discharge of mobile refrigerant waste into the natural environment. R.R.O. 1990, Reg. 347, s. 36 (1).

(2)  On and after the 1st day of July, 1991, a person who removes mobile refrigerant waste from equipment in which refrigerant is used shall collect the mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 36 (2).

37.  (1)  A mobile refrigerant waste collector that collects mobile refrigerant waste shall,

(a) recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers; or

(b) transport it to,

(i) a mobile refrigerant waste recycler, or

(ii) a mobile refrigerant waste disposal site that is subject to an environmental compliance approval to handle mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 37 (1); O. Reg. 190/94, s. 4 (1); O. Reg. 234/11, s. 32.

(2)  A mobile refrigerant waste recycler that receives mobile refrigerant waste shall recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers. R.R.O. 1990, Reg. 347, s. 37 (2); O. Reg. 190/94, s. 4 (2).

38.  (1)  A mobile refrigerant waste collector shall keep a written record each time that mobile refrigerant waste is,

(a) removed and collected, at the mobile refrigerant waste collector’s ordinary place of business, from equipment in which refrigerant is used;

(b) received at the mobile refrigerant waste collector’s ordinary place of business, after being removed and collected at another location from equipment in which refrigerant is used; or

(c) transported from or recycled at the mobile refrigerant waste collector’s ordinary place of business. R.R.O. 1990, Reg. 347, s. 38 (1).

(2)  A mobile refrigerant waste recycler shall keep a written record each time that it receives or recycles mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 38 (2).

(3)  A record made under this section shall show,

(a) the date the mobile refrigerant waste was collected, transported, received or recycled;

(b) the source of the mobile refrigerant waste;

(c) the quantity collected, transported, received or recycled;

(d) the type of mobile refrigerant waste; and

(e) what was done with the mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 38 (3).

(4)  A record made under this section may be disposed of after two years. R.R.O. 1990, Reg. 347, s. 38 (4).

(5)  Revoked: O. Reg. 190/94, s. 5.

39.  (1)  A mobile refrigerant waste disposal site that is the ordinary place of business of a mobile refrigerant waste collector is exempt from section 27 of the Act if equipment is kept at the site for collecting mobile refrigerant waste removed from equipment in which refrigerant is used. R.R.O. 1990, Reg. 347, s. 39 (1).

(2)  A mobile refrigerant waste disposal site is exempt from section 27 of the Act if,

(a) mobile refrigerant waste is removed and collected on the site from equipment in which refrigerant is used; and

(b) the site is not the ordinary place of business of the mobile refrigerant waste collector. R.R.O. 1990, Reg. 347, s. 39 (2).

40.  A mobile refrigerant waste management system is exempt from section 27 of the Act if all mobile refrigerant waste disposal sites used in the system are,

(a) exempt from section 27 of the Act; or

(b) established and operated in accordance with an environmental compliance approval. R.R.O. 1990, Reg. 347, s. 40; O. Reg. 234/11, s. 33.

41.  Section 18 does not apply in respect of subject waste that is mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 41.

42.  Section 19 and sections 21 to 27 do not apply in respect of subject waste that is mobile refrigerant waste being managed in accordance with section 37. O. Reg. 461/05, s. 10.

Selected Waste Depots

42.1-42.17  Revoked: O. Reg. 298/94, s. 1.

43.  In sections 44 to 59,

“lubricant” means crankcase oil, gear oil, transmission fluid and hydraulic fluid;

“selected waste depot” means a depot where selected waste is accepted, handled and stored. O. Reg. 298/94, s. 1.

44.  (1)  For the purposes of this section and sections 45 to 59, the products listed in Column A are selected products and the wastes listed in Column B are selected wastes:

Column A

Column B

    1. anti-freeze

    1. waste anti-freeze

    2. lubricant

    2. waste lubricant

    3. oil filters

    3. waste oil filters

O. Reg. 298/94, s. 1.

(2)  For the purposes of sections 45 to 59, the types of selected product are those listed in Column A of subsection (1) and the types of selected waste are those listed in Column B of subsection (1). O. Reg. 298/94, s. 1.

45.  (1)  Sections 47 to 59 apply in relation to selected waste depots that have the following characteristics:

1. The depot is at a location at which a business sells goods or services motor vehicles as one of its primary functions.

2. The depot is managed by a person who owns or has the charge, management or control of the business.

3. The depot is set up to accept, handle and store only selected waste of a type that results from a type of selected product regularly sold at the business. O. Reg. 298/94, s. 1.

(2)  For the purposes of sections 47 to 59, a business and a depot are associated if they have the relationship to each other set out in paragraphs 1, 2 and 3 of subsection (1). O. Reg. 298/94, s. 1.

46.  (1)  Sections 27, 40 and 41 of the Act do not apply in relation to a selected waste depot that has the characteristics set out in subsection 45 (1). O. Reg. 298/94, s. 1.

(2)  Sections 18, 19 and 21 to 27 of this Regulation do not apply to require reports or manifests in respect of selected waste stored at or removed from a selected waste depot that has the characteristics set out in subsection 45 (1). O. Reg. 298/94, s. 1.

(3)  Sections 27 and 41 of the Act and section 16 of this Regulation do not apply to the transportation of selected waste by the generator of the waste to a selected waste depot that has the characteristics set out in subsection 45 (1), unless the generator of the waste is required to submit a report under section 18 of this Regulation in respect of the waste. O. Reg. 298/94, s. 1.

47.  (1)  Each operator and owner of a selected waste depot shall ensure that no selected waste is accepted at the depot until 15 days after written notice of intent to operate the depot is given to the Chief Fire Official appointed under subsection 1.1.8 of Ontario Regulation 388/97 (Fire Code) made under the Fire Protection and Prevention Act, 1997 and to the Director responsible for the region in which the depot is located. O. Reg. 298/94, s. 1; O. Reg. 461/05, s. 11; O. Reg. 234/11, s. 34 (1).

(2)  The notice of intent to operate a selected waste depot shall include the following information:

1. The address of the depot and the location of the depot at the address.

2. The name under which the business associated with the depot carries on business.

3. The types of selected waste to be accepted at the depot.

4. The size, type and number of storage containers to be used at the depot. O. Reg. 298/94, s. 1.

(3)  Each operator and owner of a selected waste depot shall notify the Chief Fire Official and the Director responsible for the region in which the depot is located of any change in respect of the information submitted under this section, no later than 15 days before the change occurs. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 34 (2).

48.  Each operator and owner of a selected waste depot shall ensure, by means of gates, fencing, locks, guards or otherwise, that only people authorized by an operator or owner have access to selected waste at the depot. O. Reg. 298/94, s. 1.

49.  Each operator and owner of a selected waste depot shall ensure that notice of the days and hours during which selected waste will be accepted at the depot is clearly posted at the depot and shall ensure that selected waste is accepted at the depot only during those days and hours. O. Reg. 298/94, s. 1.

50.  Each operator and owner of a selected waste depot shall ensure that any selected waste accepted at the depot is deposited forthwith into storage containers at the depot. O. Reg. 298/94, s. 1.

51.  (1)  Each operator and owner of a selected waste depot shall ensure that each person who accepts, handles, stores or deposits selected waste at the depot is knowledgeable about,

(a) legislation, regulations and Ministry guidelines relevant to the operation of the depot;

(b) environmental issues related to the selected waste to be handled at the depot;

(c) occupational health and safety issues related to the selected waste to be handled at the depot;

(d) the use and operation of any equipment likely to be used in the safe operation of the depot;

(e) procedures for dealing with emergencies, including fire and explosion, that might arise at the depot in connection with the selected waste to be handled there; and

(f) procedures for dealing with spills of selected waste at the depot, including clean-up, disposal and reporting procedures. O. Reg. 298/94, s. 1.

(2)  Each operator and owner of a selected waste depot shall ensure that each person who accepts, handles, stores or deposits selected waste at the depot is,

(a) an employee of the business associated with the depot;

(b) an owner of the business associated with the depot or a person who has the charge, management or control of the business associated with the depot; or

(c) an employee of a person mentioned in clause (b). O. Reg. 298/94, s. 1.

52.  (1)  Each operator and owner of a selected waste depot shall take all reasonable steps to ensure that,

(a) selected waste is only accepted at the depot if it is of a type that results from the type of selected product regularly sold at the business associated with the depot;

(b) no more than five waste oil filters, no more than 25 litres of waste antifreeze and no more than 25 litres of waste lubricant are accepted at the depot from any one person on any one day; and

(c) selected waste is not accepted at the depot if it is brought to the depot by or on behalf of a generator required to submit a report under subsection 18 (1) in respect of the waste. O. Reg. 298/94, s. 1.

(2)  The taking of all reasonable steps for the purposes of subsection (1) includes ensuring that each person who accepts waste at the depot visually inspects waste before accepting it. O. Reg. 298/94, s. 1.

53.  Each operator and owner of a selected waste depot shall ensure that each type of selected waste stored at the depot is stored separate from each other type of selected waste, in storage containers and in accordance with the following rules:

1. Each storage container used to store selected waste shall bear a label or other identification that indicates the type of selected waste that it contains.

2. The label or other identification shall include the name and address of the depot.

3. In the case of an underground storage container, the label or other identification may be located on the fill pipe for the container and need not include the name and address of the depot.

4. The information required to be given on a label or other identification shall be set out so that it is clearly visible and legible.

5. Each storage container used to store selected waste shall be stored, handled and maintained so as to prevent leaks or spills of selected waste, damage or deterioration of the container, or any adverse effect.

6. Each storage container used to store selected waste shall be stored in a manner that facilitates the use of fire fighting equipment and spill containment and clean-up equipment throughout the depot and surrounding area.

7. Each storage container used to store selected waste shall be stored in a manner that facilitates inspection of the depot by a provincial officer. O. Reg. 298/94, s. 1.

54.  (1)  Each operator and owner of a selected waste depot at which selected waste is stored in an above ground container shall ensure that the depot has a secondary containment system capable of containing leaks or spills of selected waste from the above ground container and capable of preventing the leaks or spills from entering municipal sewers, other drainage systems or the natural environment except air. O. Reg. 298/94, s. 1.

(2)  In the case of a selected waste depot at which selected waste is stored outdoors in an above ground container the base of which rests on the ground, each operator and owner shall also ensure that the secondary containment system is capable of draining leaks or spills away from the outdoor above ground container. O. Reg. 298/94, s. 1.

55.  (1)  Each operator and owner of a selected waste depot shall ensure that the depot is equipped with fire fighting equipment and spill containment and clean-up equipment appropriate to the quantities and types of waste stored at the depot. O. Reg. 298/94, s. 1.

(2)  Each operator and owner of a selected waste depot shall ensure that the equipment mentioned in subsection (1) is stored in a way that makes it immediately accessible in the event that it is needed. O. Reg. 298/94, s. 1.

56.  (1)  Each operator and owner of a selected waste depot shall ensure that the depot is visually inspected for leaks or spills of selected waste at least once during each day on which the business associated with the depot is open for sales or service. O. Reg. 298/94, s. 1.

(2)  Each operator and owner of a selected waste depot shall ensure that each inspection performed under subsection (1) on a day on which the depot is open to accept waste is performed by a person knowledgeable about the matters set out in clauses 51 (1) (a) to (f). O. Reg. 298/94, s. 1.

(3)  Each operator and owner of a selected waste depot shall ensure that at the time of each inspection under subsection (1) the person performing the inspection legibly records his or her name, the date and the findings of the inspection. O. Reg. 298/94, s. 1.

(4)  Each operator and owner of a selected waste depot shall ensure that each record made at the depot under subsection (1) is kept at the depot during a period of two years after it is made. O. Reg. 298/94, s. 1.

57.  (1)  Each operator and owner of a selected waste depot shall ensure that each time selected waste is accepted at the depot, the person accepting the waste legibly records his or her name, the date, the name and address of the person who brought the waste to the depot and the type and approximate quantity of the waste. O. Reg. 298/94, s. 1.

(2)  Each operator and owner of a selected waste depot shall ensure that each record made at the depot under subsection (1) is kept at the depot during a period of two years after it is made. O. Reg. 298/94, s. 1.

58.  (1)  Each operator and owner of a selected waste depot shall ensure that no selected waste is accepted at the depot unless there is in effect one or more written agreements each of which meets the requirements of subsections (2) and (3) and that together provide for the ongoing removal of all selected waste from the depot. O. Reg. 298/94, s. 1.

(2)  An agreement under subsection (1) shall be between an operator or owner of the depot and a party to whom an environmental compliance approval has been issued that authorizes the party to transport one or more classes of waste that include the type or types of selected waste to be removed from the depot by the party under the agreement. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 35 (1).

(3)  An agreement under subsection (1) shall state the following:

1. The name and address of an owner or operator of the depot.

2. The name and address of the party responsible for removing waste, the type of selected waste to be removed by the party and the number of the environmental compliance approval that authorizes the party to transport the type of waste.

3. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the party responsible for removing the waste.

4. The approximate time intervals at which the party responsible for removing the waste will remove the waste.

5. The expiry date of the agreement. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 35 (2).

(4)  Each operator and owner of a selected waste depot shall ensure that selected waste is removed from the depot only by a party to an agreement under subsection (1) to whom an environmental compliance approval has been issued that authorizes the removal of the waste. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 35 (3).

(5)  Each operator and owner of a selected waste depot shall ensure that a copy of an agreement under subsection (1) is kept at the depot during the term of the agreement and during a period of two years after the termination or expiry of the agreement. O. Reg. 298/94, s. 1.

59.  (1)  Each operator and owner of a selected waste depot shall ensure that all selected waste is removed from the depot no later than 90 days after the depot ceases to be open to accept selected waste. O. Reg. 298/94, s. 1.

(2)  Each operator and owner of a selected waste depot shall ensure that written notice is given to the Chief Fire Official appointed under subsection 1.1.8 of Ontario Regulation 388/97 (Fire Code) made under the Fire Protection and Prevention Act, 1997 and to the Director responsible for the region in which the depot is located no later than 95 days after the depot ceases to be open to accept selected waste. O. Reg. 298/94, s. 1; O. Reg. 461/05, s. 12; O. Reg. 234/11, s. 36 (1).

(3)  The notice under subsection (2) shall include the following information:

1. The address of the depot and the location of the depot at the address.

2. The date on which the depot ceased being open to accept selected waste.

3. A statement that all selected waste has been removed from the depot. O. Reg. 298/94, s. 1.

(4)  Each operator and owner of a selected waste depot shall ensure that any documents required under sections 56 to 58 to be kept at the depot on the date referred to in paragraph 2 of subsection (3) are available to provincial officers for inspection at an address in Ontario during a period of two years after that date. O. Reg. 298/94, s. 1.

(5)  Each operator and owner of a selected waste depot shall ensure that the Chief Fire Official and the Director responsible for the region in which the depot is located are given timely written notice of the address referred to in subsection (4). O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 36 (2).

60.  In the event of conflict between sections 44 to 59 of this Regulation and Ontario Regulation 388/97 (Fire Code) made under the Fire Protection and Prevention Act, 1997 or Ontario Regulation 213/01 (Fuel Oil) made under the Technical Standards and Safety Act, 2000, Ontario Regulation 388/97 or 213/01 prevails. O. Reg. 461/05, s. 13.

Pesticide Container Depots

61.  In this section and in sections 62 to 73,

“empty pesticide container” means an empty container originally used to hold commercial pesticides;

“pesticide” means any organism, substance or thing that is manufactured, represented, sold or used as a means of directly or indirectly controlling, preventing, destroying, mitigating, attracting or repelling any pest or of altering the growth, development or characteristics of any plant life that is not a pest and includes any organism, substance or thing registered under the Pest Control Products Act (Canada). O. Reg. 298/94, s. 1.

62.  (1)  Sections 64 to 73 apply in relation to pesticide container depots that have the following characteristics:

1. The depot is at the place of business of a retail vendor licensed as such under the Pesticides Act.

2. The depot is managed by a person who owns or has the charge, management or control of the retail vendor business.

3. The depot is set up to accept, handle and store only empty pesticide containers.

4. The depot only accepts and stores empty pesticide containers that have been triple or jet rinsed and that do not exceed 23 litres in size if made of plastic or 20 litres in size if made of metal. O. Reg. 298/94, s. 1.

(2)  For the purposes of sections 64 to 73, a retail vendor business and a pesticide container depot are associated if they have the relationship to each other set out in paragraphs 1, 2 and 3 of subsection (1). O. Reg. 298/94, s. 1.

63.  (1)  Sections 27, 40 and 41 of the Act do not apply in relation to a pesticide container depot that has the characteristics set out in subsection 62 (1). O. Reg. 298/94, s. 1.

(2)  Sections 27 and 41 of the Act and section 16 of this Regulation do not apply to the transportation of empty pesticide containers by the generator of the waste to a pesticide container depot that has the characteristics set out in subsection 62 (1). O. Reg. 298/94, s. 1.

64.  (1)  Each owner and operator of a pesticide container depot shall ensure that no empty pesticide container is accepted at a pesticide container depot until 15 days after written notice of intent to operate the depot is given to the Director. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 37 (1).

(2)  The notice of intent to operate a pesticide container depot shall include the following information:

1. The address of the pesticide container depot and the location of the pesticide collection depot at that address.

2. The name under which the retail vendor business associated with the pesticide container depot carries on business.

3. The vendor licence number or operator licence number given under the Pesticides Act.

4. The name of the person who owns or has charge, management or control of the retail vendor business. O. Reg. 298/94, s. 1.

(3)  Each operator and owner of a pesticide container depot shall notify the Director in writing of any change in respect of the information submitted under this section, no later than 15 days before the change occurs. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 37 (2).

65.  Each operator and owner of a pesticide container depot shall ensure, by means of gates, fencing, locks, guards or otherwise, that only people authorized by an operator or owner have access to the empty pesticide containers at the pesticide container depot. O. Reg. 298/94, s. 1.

66.  Each operator and owner of a pesticide container depot shall ensure that notice of the days and hours during which empty pesticide containers will be accepted at the depot is clearly posted at the depot and shall ensure that empty pesticide containers are accepted at the depot only during those days and hours. O. Reg. 298/94, s. 1.

67.  Each operator and owner of a pesticide container depot shall ensure that any empty pesticide containers accepted at the depot are deposited immediately into a storage area at the pesticide container depot. O. Reg. 298/94, s. 1.

68.  (1)  Each operator and owner of a pesticide container depot shall ensure that each person who accepts, handles, stores or deposits empty pesticide containers at the depot is knowledgeable about,

(a) legislation, regulations and Ministry guidelines relevant to the operation of the depot;

(b) environmental issues related to the empty pesticide containers to be handled at the depot;

(c) occupational health and safety issues related to the empty pesticide containers to be handled at the depot;

(d) the use and operation of any equipment likely to be used in the safe operation of the depot;

(e) procedures for dealing with emergencies, including fire and explosion, that might arise at the depot in connection with the empty pesticide containers to be handled there; and

(f) procedures for dealing with spills relating to the empty pesticide containers at the depot, including clean-up, disposal and reporting procedures. O. Reg. 298/94, s. 1.

(2)  Each operator and owner of a pesticide container depot shall ensure that each person who accepts, handles, stores or deposits empty pesticide containers at the depot is,

(a) an employee of the business associated with the depot;

(b) an owner of the business associated with the depot or a person who has the charge, management or control of the business associated with the depot; or

(c) an employee of a person mentioned in clause (b). O. Reg. 298/94, s. 1.

69.  Each operator and owner of a pesticide container depot shall take all reasonable steps to ensure that each person who accepts empty pesticide containers at the depot visually inspects the empty pesticide containers before accepting them for handling and storage. O. Reg. 298/94, s. 1.

70.  Each operator and owner of a pesticide container depot shall ensure that empty pesticide containers stored at the depot are stored in containers or areas in accordance with the following rules:

1. Each container or area used to store empty pesticide containers shall bear a label or other identification that indicates empty pesticide containers are stored within the container or area.

2. The information on the label or other identification shall be clearly visible and legible.

3. Each container used to store empty pesticide containers shall be stored, handled and maintained so as to prevent damage or deterioration of the containers, or any adverse effect.

4. Each container or area used to store empty pesticide containers shall be covered in such a manner so as to prevent rain water infiltration into or on the empty pesticide containers.

5. Each container used to store empty pesticide containers shall be stored in a manner that facilitates the use of fire fighting equipment and spill containment and clean-up equipment throughout the depot and surrounding area.

6. Each container used to store empty pesticide containers shall be stored in a manner that facilitates inspection of the depot by a provincial officer.

7. Each container or area used to store empty pesticide containers shall have ventilation to the outside atmosphere. O. Reg. 298/94, s. 1.

71.  Each operator and owner of a pesticide container depot shall ensure that records are kept of the type and quantity of empty pesticide containers accepted at the pesticide container depot. O. Reg. 298/94, s. 1.

72.  (1)  Each operator and owner of a pesticide container depot shall ensure that no empty pesticide containers are accepted at the depot unless there is in effect one or more written agreements each of which meets the requirements of subsections (2) and (3) and that together provide for the ongoing removal of all empty pesticide containers from the depot. O. Reg. 298/94, s. 1.

(2)  An agreement under subsection (1) shall be between an operator or owner of the depot and a party to whom an environmental compliance approval has been issued that authorizes the party to transport the empty pesticide containers to be removed from the depot. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 38 (1).

(3)  The agreement shall state the following:

1. The name and address of the owner or operator of the pesticide container depot.

2. The name and address of the party responsible for removing the empty pesticide containers and the number of the environmental compliance approval that authorizes the party to transport them.

3. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the party responsible for removing the empty pesticide containers.

4. The approximate time intervals at which the party responsible for removing the waste will remove the waste.

5. The expiry date of the agreement. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 38 (2).

(4)  Each operator and owner of a pesticide container depot shall ensure that the empty pesticide containers are removed from the depot only by a party to an agreement under subsection (1) to whom an environmental compliance approval has been issued that authorizes the removal of the waste. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 38 (3).

(5)  Each operator and owner of a pesticide container depot shall ensure that a copy of the agreement is kept at the depot during the term of the agreement and for two years after the termination or expiration of the agreement. O. Reg. 298/94, s. 1.

73.  (1)  Each operator and owner of a pesticide container depot shall ensure that all empty pesticide containers are removed from the depot no later than 90 days after the depot ceases to operate as a pesticide container depot. O. Reg. 298/94, s. 1.

(2)  Each operator and owner of a pesticide container depot shall ensure that written notice is given to the Director no later than 95 days after the depot ceases to be open to accept empty pesticide containers. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 39 (1).

(3)  The notice under subsection (2) shall include the following information:

1. The address of the depot and the location of the depot at the address.

2. The date on which the depot ceased to operate as a pesticide container depot.

3. A statement that all empty pesticide containers have been removed from the pesticide container depot. O. Reg. 298/94, s. 1.

(4)  Each operator and owner of a pesticide container depot shall ensure that any documents required under sections 71 and 72 are kept at the depot and are available to provincial officers for inspection at an address in Ontario during a period of two years after the date on which the depot ceased to operate as a pesticide container depot. O. Reg. 298/94, s. 1.

(5)  Each operator and owner of a pesticide container depot shall ensure that the Director is given timely written notice of the address referred to in subsection (4). O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 39 (2).

Land Disposal of Hazardous Waste

74.  No person shall dispose of PCB waste by land disposal. O. Reg. 461/05, s. 14.

75.  (1)  No person shall dispose of hazardous waste that is hazardous industrial waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 1 if the waste is an aqueous waste:

i. If Column 5 of Schedule 1 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 1 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 5 of Schedule 1 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 1 if the waste is a non-aqueous waste:

i. If Column 6 of Schedule 1 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 1 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Schedule 1 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 6 of Schedule 1 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

3. If treatment subcategories are set out for the waste in Schedule 1, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 15.

(2)  Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1). O. Reg. 461/05, s. 15.

(3)  Despite subsection (1), a person may dispose of hazardous waste that is hazardous industrial waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 15.

(4)  Subsections (1) to (3) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 10. O. Reg. 461/05, s. 15.

76.  (1)  No person shall dispose of hazardous waste that is acute hazardous waste chemical by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part A of Schedule 2 if the waste is an aqueous waste:

i. If Column 6 of Part A of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part A of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Part A of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part A of Schedule 2 if the waste is a non-aqueous waste:

i. If Column 7 of Part A of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part A of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 7 of Part A of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 7 of Part A of Schedule 2 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

3. If treatment subcategories are set out for the waste in Part A of Schedule 2, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 15.

(2)  Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1). O. Reg. 461/05, s. 15.

(3)  Despite subsection (1), a person may dispose of hazardous waste that is acute hazardous waste chemical by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 15.

(4)  Subsections (1) to (3) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 11. O. Reg. 461/05, s. 15.

77.  (1)  No person shall dispose of hazardous waste that is hazardous waste chemical by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part B of Schedule 2 if the waste is an aqueous waste:

i. If Column 6 of Part B of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part B of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Part B of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part B of Schedule 2 if the waste is a non-aqueous waste:

i. If Column 7 of Part B of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Part B of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 7 of Part B of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 7 of Part B of Schedule 2 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

3. If treatment subcategories are set out for the waste in Part B of Schedule 2, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 15.

(2)  Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1). O. Reg. 461/05, s. 15.

(3)  Despite subsection (1), a person may dispose of hazardous waste that is hazardous waste chemical by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 15.

(4)  Subsections (1) to (3) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 12. O. Reg. 461/05, s. 15.

78.  (1)  No person shall dispose of hazardous waste that is severely toxic waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. If the waste is an aqueous waste, the waste must be treated so that, in the treated waste, based on an analysis of composite samples, the concentration of the regulated constituent set out for the waste in Schedule 3 is less than the numerical concentration set out for that regulated constituent in Column 6 of Schedule 3.

2. If the waste is a non-aqueous waste, the waste must be treated so that, in the treated waste, based on an analysis of grab samples, the concentration of the regulated constituent set out for the waste in Schedule 3 is less than the numerical concentration set out for that regulated constituent in Column 7 of Schedule 3. O. Reg. 461/05, s. 16.

(2)  Dilution may not be used to comply with paragraph 1 or 2 of subsection (1). O. Reg. 461/05, s. 16.

(3)  Despite subsection (1), a person may dispose of hazardous waste that is severely toxic waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 16.

79.  (1)  No person shall dispose of characteristic waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules:

1. Subject to paragraphs 3 and 4, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 5 if the waste is an aqueous waste:

i. If Column 5 of Schedule 5 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 5 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 5 of Schedule 5 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

iv. If Column 5 of Schedule 5 contains the words “meet Schedule 6 standards” in respect of a land disposal treatment requirement for the waste and, on or after December 31, 2009, the waste is treated in accordance with that requirement, the waste must also be treated so that, based on an analysis of composite samples, the concentration in the treated waste of each regulated constituent listed in Schedule 6 is less than the concentration set out for that regulated constituent in Column 3 of Schedule 6.

2. Subject to paragraphs 3 and 4, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 5 if the waste is a non-aqueous waste:

i. If Column 6 of Schedule 5 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste,

A. the waste must be treated in accordance with Schedule 5 using the treatment methods set out for those treatment codes in Schedule 7, and

B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7.

ii. If Column 6 of Schedule 5 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration.

iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs.

iv. If Column 6 of Schedule 5 contains the words “meet Schedule 6 standards” in respect of a land disposal treatment requirement for the waste and, on or after December 31, 2009, the waste is treated in accordance with that requirement, the waste must also be treated so that, based on an analysis of grab samples, the concentration in the treated waste of each regulated constituent listed in Schedule 6 is less than the concentration set out for that regulated constituent in Column 4 of Schedule 6.

v. For the purpose of subparagraphs ii and iv, if the numerical concentration set out in Column 6 of Schedule 5 or Column 4 of Schedule 6 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure.

3. If Column 5 or 6 of Schedule 5 contains the words “best efforts to achieve” in respect of a numerical concentration that is set out as the land disposal treatment requirement for that regulated constituent of the waste, it is not necessary for the concentration of the regulated constituent in the treated waste to be less than that concentration, but the person treating the waste must use the person’s best efforts to achieve that standard.

4. If treatment subcategories are set out for the waste in Schedule 5, paragraphs 1 to 3 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 17.

(2)  Dilution may not be used to comply with subparagraph 1 ii or iv or 2 ii or iv of subsection (1). O. Reg. 461/05, s. 17.

(3)  Nothing in this section requires further treatment for a regulated constituent of a waste if,

(a) treatment that is required for the waste by subsection (1) causes the concentration of the regulated constituent in the treated waste to increase;

(b) a numerical concentration is set out as the land disposal treatment requirement for that regulated constituent of the waste in,

(i) Column 5 of Schedule 5, if the waste is an aqueous waste, or

(ii) Column 6 of Schedule 5, if the waste is a non-aqueous waste; and

(c) the concentration of the regulated constituent in the untreated waste was less than the concentration referred to in clause (b). O. Reg. 461/05, s. 17.

(4)  For the purpose of subsection (3), if the numerical concentration referred to in clause (3) (b) is expressed as a TCLP concentration, the concentration of the regulated constituent in the untreated waste and in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure. O. Reg. 461/05, s. 17.

(5)  Despite subsection (1), a person may dispose of characteristic waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 17.

(6)  This section does not apply to a hazardous waste that is a characteristic waste and that is also a listed waste if all of the regulated constituents set out for the waste in Schedule 5 are regulated constituents set out for the waste in Schedule 1, Part A of Schedule 2, Part B of Schedule 2 or Schedule 3. O. Reg. 461/05, s. 17.

(7)  Subsections (1) to (5) do not apply to a waste until December 31, 2009 unless the waste is listed in Schedule 13. O. Reg. 461/05, s. 17.

80.  (1)  Sections 75, 77 and 79 do not apply to the land disposal of a sealed container if,

(a) a certificate described in subsection (3) is affixed to the container;

(b) the container does not appear to be broken or leaking; and

(c) the seal does not appear to be broken or tampered with. O. Reg. 461/05, s. 18.

(2)  A generator who transfers a sealed container containing waste shall affix a certificate described in subsection (3) to the container if,

(a) all the waste in the container is hazardous industrial waste, hazardous waste chemical or characteristic waste;

(b) the waste in the container was produced at the generator’s waste generation facility;

(c) the waste generation facility produces a total of less than 100 kilograms of hazardous industrial waste, hazardous waste chemical and characteristic waste in any month;

(d) no waste in the container has been mixed, blended, bulked or in any other way intermingled with any other waste or material;

(e) the container and its seal comply with any requirements of the Manual; and

(f) the total weight of the container and its contents does not exceed 250 kilograms. O. Reg. 461/05, s. 18.

(3)  The certificate referred to in clause (1) (a) and subsection (2) must contain the following:

1. The name, address and telephone number of the generator.

2. A statement that, pursuant to subsection (1), sections 75, 77 and 79 do not apply to the land disposal of the sealed container, as long as,

i. the container does not appear to be broken or leaking, and

ii. the seal does not appear to be broken or tampered with.

3. A description of the contents of the container, including,

i. a statement that all the waste in the container is hazardous industrial waste, hazardous waste chemical or characteristic waste,

ii. a statement that no waste in the container has been mixed, blended, bulked or in any other way intermingled with any other waste or material, and

iii. a statement that the waste in the container was produced at the generator’s waste generation facility.

4. A statement that the waste generation facility produces a total of less than 100 kilograms of hazardous industrial waste, hazardous waste chemical and characteristic waste in any month.

5. A statement that the container and its seal comply with any requirements of the Manual.

6. A statement that the total weight of the container and its contents does not exceed 250 kilograms. O. Reg. 461/05, s. 18.

81.  Sections 75 to 79 do not apply to the land disposal of hazardous waste that is composed only of combined quantities of individual wastes described in one or more of clauses (n), (p), (q), (r), (s), (t) and (u) of the definition of “hazardous waste” in subsection 1 (1) if,

(a) each of the individual wastes was brought to and accepted by a waste disposal site that accepts that type of waste from the general public, handles and temporarily stores it, but does not process or dispose of it; and

(b) each of the individual wastes would be hazardous waste if it were produced by a commercial or industrial generator or if it were produced in a larger quantity. O. Reg. 461/05, s. 18.

82.  (1)  Despite sections 75 to 79, a person may dispose of listed waste or characteristic waste by land disposal if the waste is soil or a soil mixture and the waste is first treated in accordance with the following rules:

1. If the soil or soil mixture is corrosive waste, ignitable waste or reactive waste, it must be treated so that it ceases to be corrosive waste, ignitable waste or reactive waste, as the case may be.

2. For each regulated constituent listed in Schedule 6 that can reasonably be expected to be present in the soil or soil mixture at a concentration that exceeds 10 times the standard set out for that regulated constituent in Column 4 of that Schedule, the soil or soil mixture must be treated so that,

i. the concentration of the regulated constituent after the treatment is not more than 10 per cent of the concentration of the regulated constituent before the treatment, or

ii. the concentration of the regulated constituent after the treatment is not more than 10 times the standard set out for the regulated constituent in Column 4 of Schedule 6.

3. For the purpose of subparagraph 2 i, the concentration of the regulated constituent shall be based on,

i. the total concentration of the regulated constituent in the soil or soil mixture, measured in milligrams per kilogram, if,

A. the regulated constituent is a metal, and the soil or soil mixture is treated using a metals removal technology,

B. the regulated constituent is carbon disulfide, cyclohexanone or methanol, and the soil or soil mixture is treated using a metals removal technology, or

C. the regulated constituent is not a metal and is not carbon disulfide, cyclohexanone or methanol, or

ii. if subparagraph i does not apply, the concentration of the regulated constituent in leachate from the treated media, measured in milligrams per litre, when the soil or soil mixture is tested using the Toxicity Characteristic Leaching Procedure.

4. If soil or a soil mixture is treated in accordance with paragraphs 1 to 3 and the residuals from the treatment are characteristic waste that is soil or a soil mixture, paragraphs 1 to 3 also apply to those residuals. O. Reg. 461/05, s. 19.

(2)  If soil or a soil mixture is treated in accordance with paragraphs 1 to 3 of subsection (1) and the residuals from the treatment are characteristic waste that is not soil or a soil mixture, section 79 applies to those residuals. O. Reg. 461/05, s. 19.

83.  (1)  In this section,

“debris” means solid waste that has a particle size of more than 60 millimetres, and includes material that remains with debris when simple mechanical means or simple physical means are used to separate material that is debris from material that is not debris;

“debris mixture” means a mixture of debris and other material where, based on visual inspection, the volume of the mixture is made up primarily of debris. O. Reg. 461/05, s. 19.

(2)  Despite sections 75 to 79, a person may dispose of a listed waste or a characteristic waste by land disposal if the waste is debris or a debris mixture and the waste is first treated in accordance with the following rules:

1. One or more of the treatment methods listed in Schedule 8 must be used.

2. If Schedule 8 sets out restrictions applicable to a treatment method, that method may be used only in accordance with those restrictions.

3. When a treatment method listed in Schedule 8 is used, the treatment must achieve the standard set out for that treatment method in that Schedule.

4. If more than one treatment method listed in Schedule 8 is used and one of the treatment methods uses an immobilization technology, the method that uses the immobilization technology must be the last treatment method to be used.

5. After the waste is treated, the residuals from the treatment must be separated by simple mechanical means or simple physical means into,

i. residuals that are debris, and

ii. residuals that are not debris.

6. After the waste is treated, the residuals from the treatment that are debris must not be,

i. corrosive waste,

ii. ignitable waste,

iii. leachate toxic waste, or

iv. reactive waste.

7. If waste that is reactive waste because of the presence of cyanide is treated, the residuals from the treatment that are debris must be treated so that they may be land disposed in accordance with section 79 and, for that purpose, the residuals shall be deemed to be waste that is reactive waste because of the presence of cyanide.

8. If waste is treated by spalling, layers of the waste that are removed by spalling must be treated in accordance with the rules set out in this subsection and, for that purpose, the removed layers shall be deemed to be debris.

9. After the waste is treated, residuals from the treatment that are not debris must be treated in accordance with the following rules:

i. Residuals that are hazardous waste and are hazardous industrial waste must be treated so that they may be land disposed in accordance with section 75.

ii. Residuals that are hazardous waste and are acute hazardous waste chemical must be treated so that they may be land disposed in accordance with section 76.

iii. Residuals that are hazardous waste and are hazardous waste chemical must be treated so that they may be land disposed in accordance with section 77.

iv. Residuals that are hazardous waste and are severely toxic waste chemical must be treated so that they may be land disposed in accordance with section 78.

v. Residuals that are hazardous waste and are leachate toxic waste must be treated so that they may be land disposed in accordance with section 79.

vi. Residuals that are hazardous waste and are corrosive waste, ignitable waste or reactive waste must be treated so that they are no longer corrosive waste, ignitable waste or reactive waste, unless subparagraph vii applies.

vii. The following residuals from the treatment must be treated so that they may be land disposed in accordance with section 79 if they are hazardous waste:

A. Residuals that are reactive waste because of the presence of cyanide.

B. Residuals that are ignitable waste, are non-aqueous waste and contain 10 per cent total organic carbon or more. O. Reg. 461/05, s. 19.

(3)  If debris or a debris mixture is treated in accordance with the rules set out in subsection (2) and an immobilization technology described in Schedule 8 was not used, residuals from the treatment that are debris shall be deemed, for the purposes of this Regulation, not to be listed waste. O. Reg. 461/05, s. 19.

(4)  Subsection (2) does not apply to debris or a debris mixture that includes any of the following:

1. Lead acid batteries, cadmium batteries or radioactive lead solids.

2. Process residuals, including,

i. smelter slag,

ii. residues from the treatment of wastewater or other waste,

iii. sludge and residues from the treatment of sludge, and

iv. residues from air pollution control equipment.

3. Intact containers of hazardous waste that are not ruptured and that retain at least 75 per cent of the volume of the original container. O. Reg. 461/05, s. 19.

84.  (1)  A generator who transfers any of the following waste to a receiving facility shall, before or at the time the waste is received at the receiving facility, give the receiver notice of the information referred to in subsection (2):

1. Characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed.

2. Waste that was characteristic waste but has been treated so that it is no longer characteristic waste, if the waste may not be disposed of by land disposal under subsection 79 (1). O. Reg. 461/05, s. 20.

(2)  The information referred to in subsection (1) is the current information relating to the waste that is contained in,

(a) the most recent annual Generator Registration Report submitted by the generator or, if no annual Generator Registration Report has been submitted, the initial Generator Registration Report submitted by the generator; and

(b) any subsequent supplementary Generator Registration Reports submitted by the generator. O. Reg. 461/05, s. 20.

(3)  The generator shall comply with subsection (1) by giving the information, or a specific Internet address where the information can be found,

(a) to the carrier who transports the waste to the receiving facility, with instructions to deliver it to the receiver when the waste is delivered;

(b) to the receiver, in accordance with section 182 of the Act; or

(c) to the receiver, by fax or another form of delivery. O. Reg. 461/05, s. 20.

(4)  The generator is only required to comply with subsection (1) in respect of,

(a) the first transfer to the receiving facility of each type of characteristic waste or listed waste identified in,

(i) the most recent annual Generator Registration Report submitted by the generator or, if no annual Generator Registration Report has been submitted, the initial Generator Registration Report submitted by the generator, and

(ii) any subsequent supplementary Generator Registration Reports submitted by the generator; and

(b) the first transfer to the receiving facility of a type of waste referred to in clause (a) following each significant change to information previously given to the receiver under subsection (1), if the change relates to the description or physical or chemical properties of that type of waste. O. Reg. 461/05, s. 20.

(5)  The generator shall make a record of its compliance with subsection (1), including the receiver to whom information was given under subsection (1) and the date the information was given. O. Reg. 461/05, s. 20.

(6)  The generator shall keep every record made under subsection (5) at the waste generation facility for two years. O. Reg. 461/05, s. 20.

(7)  If waste is transferred by a generator to a receiving facility, the waste was characteristic waste and the waste can be disposed of by land disposal under section 79,

(a) the generator shall, before or at the time the waste is received at the receiving facility, give the receiver notice that the waste was characteristic waste and that the waste can be disposed of by land disposal under section 79; and

(b) subsections (3) to (6) apply, with necessary modifications, in respect of a notice required by clause (a). O. Reg. 461/05, s. 20.

85.  (1)  A generator or operator of a waste disposal site who treats waste in accordance with section 75, 76, 77, 78, 79, 82 or 83 shall develop and follow a written plan that requires regular and detailed chemical and physical testing of representative samples of the waste. O. Reg. 461/05, s. 21.

(2)  The person who develops the plan shall ensure that,

(a) the plan includes requirements to ensure that the testing will provide all information necessary to treat the waste in accordance with section 75, 76, 77, 78, 79, 82 or 83, as the case may be;

(b) the plan specifies the frequency with which testing will be conducted. O. Reg. 461/05, s. 21.

(3)  A person who develops a plan under subsection (1) shall keep a copy of the plan while that subsection applies to the person and for at least two years after that subsection ceases to apply to the person. O. Reg. 461/05, s. 21.

(4)  A person who is required to keep a copy of a plan under subsection (3) shall keep it at,

(a) the waste generation facility, if the person is a generator, or

(b) the waste disposal site, if the person is the operator of a waste disposal site. O. Reg. 461/05, s. 21.

(5)  The person who is required to follow a plan under subsection (1) shall make a record of the result of every test conducted in accordance with the plan. O. Reg. 461/05, s. 21.

(6)  A person who makes a record under subsection (5) shall keep the record for at least two years. O. Reg. 461/05, s. 21.

FORMS 1, 2 Revoked: O. Reg. 501/01, s. 12.

SCHEDULE 1
HAZARDOUS INDUSTRIAL WASTE

Hazardous Industrial Waste from Non-Specific Sources

Hazardous Industrial Waste

Regulated Constituents
(and Treatment Subcategories1)

Land Disposal Treatment Requirements

Aqueous Waste

Non-aqueous Waste

Column 1

Column 2

Column 3

Column 4

Column 5

Column 6

Haz. Waste Number2

Waste

Generic Name or other description

CAS Number3

Treatment Code4 or Concentration5 (mg/L)

Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated)

F001

The following spent halogenated solvents used in degreasing: Tetrachloroethylene, trichloroethylene, methylene chloride, 1,1,1-trichloroethane, carbon tetrachloride and chlorinated fluorocarbons; all spent solvent mixtures/blends used in degreasing containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

Acetone

67-64-1

0.28

160

Benzene

71-43-2

0.14

10

n-Butyl alcohol

71-36-3

5.6

2.6

Carbon disulfide

75-15-0

3.8

NA

Carbon tetrachloride

56-23-5

0.057

6.0

Chlorobenzene

108-90-7

0.057

6.0

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations)

1319-77-3

0.88

11.2

Cyclohexanone

108-94-1

0.36

NA

o-Dichlorobenzene

95-50-1

0.088

6.0

Ethyl acetate

141-78-6

0.34

33

Ethyl benzene

100-41-4

0.057

10

Ethyl ether

60-29-7

0.12

160

Isobutyl alcohol

78-83-1

5.6

170

Methanol

67-56-1

5.6

NA

Methylene chloride

75-9-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Nitrobenzene

98-95-3

0.068

14

Pyridine

110-86-1

0.014

16

Tetrachloroethylene

127-18-4

0.056

6.0

Toluene

108-88-3

0.08

10

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

1,1,2-Trichloro-1,2,2-trifluoroethane

76-13-1

0.057

30

Trichloroethylene

79-01-6

0.054

6.0

Trichlorofluoromethane

75-69-4

0.02

30

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

F002

The following spent halogenated solvents: Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, chlorobenzene, 1,1,2-trichloro-1,2,2- trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane and 1,1,2-trichloro-ethane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those listed in F001, F004 or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

same as F001

     

F003

The following spent non-halogenated solvents: Xylene, acetone, ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone and methanol; all spent solvent mixtures/blends containing, before use, only the above spent non-halogenated solvents; and all spent solvent mixtures/blends containing, before use, one or more of the above non-halogenated solvents, and, a total of ten per cent or more (by volume) of one or more of those solvents listed in F001, F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

Treatment Subcategory 1

All F003 wastes, except those identified in Subcategory 2:

same as F001

     

Treatment Subcategory 2

F003 solvent wastes, that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone and/or methanol:

Carbon disulfide

75-15-0

3.8

4.8 mg/L TCLP

Cyclohexanone

108-94-1

0.36

0.75 mg/L TCLP

Methanol

67-56-1

5.6

0.75 mg/L TCLP

       

F004

The following spent non-halogenated solvents: Cresols and cresylic acid, and nitrobenzene; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

same as F001

     

F005

The following spent non-halogenated solvents: Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 or F004; and still bottoms from the recovery of these spent solvents and spent solvent mixtures.

Treatment Subcategory 1

All F003 wastes, except those identified in Subcategory 2:

same as F001

     

Treatment Subcategory 2

F003 solvent wastes, that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone and/or methanol:

same as F003 Subcategory 2

     

Treatment Subcategory 3

F005 solvent waste containing 2-Nitropropane as the only listed F001-5 solvents:

2-Nitropropane

79-46-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

Treatment Subcategory 4

F005 solvent waste containing 2-Ethoxyethanol as the only listed F001-5 solvents:

2-Ethoxyethanol

110-80-5

BIODG; or CMBST

CMBST

F006

Wastewater treatment sludges from electroplating operations except from the following processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum.

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

       

F007

Spent cyanide plating bath solutions from electroplating operations.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F008

Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F009

Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F010

Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process.

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

NA

       

F011

Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F012

Quenching waste water treatment sludges from metal heat treating operations where cyanides are used in the process.

Cadmium

7440-43-9

NA

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

F019

Wastewater treatment sludges from the chemical conversion coating of aluminum except from the following: (1) Zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process; (2) Wastewater treatment sludges from the manufacturing of motor vehicles at a referenced manufacturing facility7.1 using a zinc phosphating process, if the wastes are not placed outside on the land prior to shipment for disposal at a waste disposal site approved to accept the waste.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

       

F020

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives. (This listing does not include wastes from the production of Hexachlorophene from highly purified 2,4,5- trichlorophenol.)

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

Hx CDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachlorophenol

87-86-5

0.089

7.4

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

F021

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of pentachlorophenol, or of intermediates used to produce its derivatives.

Same as F020

     

F022

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzenes under alkaline conditions.

Same as F020

     

F023

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of Hexachlorophene from highly purified 2,4,5-trichlorophenol.)

Same as F020

     

F024

Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor cleanout wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in Part A or B of Schedule 2.)

All F024 wastes

NA

CMBST8

CMBST8

2-Chloro-1,3-butadiene

126-99-8

0.057

0.28

3-Chloropropylene

107-05-1

0.036

30

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,2-Dichloropropane

78-87-5

0.85

18

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Hexachloroethane

67-72-1

0.055

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

       

F025

Condensed light ends, spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated aliphatic hydrocarbons, by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution.

Treatment Subcategory 1

F025 Light Ends:

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

Methylene chloride

75-9-2

0.089

30

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Vinyl chloride

75-01-4

0.027

6.0

Treatment Subcategory 2

F025 Spent Filters/Aids and Desiccants:

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Methylene chloride

75-9-2

0.089

30

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Vinyl chloride

75-01-4

0.27

6.0

F026

Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzene under alkaline conditions.

Same as F020

     

F027

Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing Hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.)

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachlorophenol

87-86-5

0.089

7.4

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

F028

Residues resulting from the incineration or thermal treatment of soil contaminated with Hazardous Waste Numbers F020, F021, F022, F023, F026 and F027.

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachlorophenol

87-86-5

0.089

7.4

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

F032

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with s. 261.359 or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes (i.e., F034 or F035), and where the generator does not resume or initiate use of chlorophenolic formulations). This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Acenaphthene

83-32-9

0.059

3.4

Anthracene

120-12-7

0.059

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

2,4-Dimethyl phenol

105-67-9

0.036

14

Fluorene

86-73-7

0.059

3.4

Hexachlorodibenzo-p-dioxins

NA

0.000063 or CMBST8

0.001 or CMBST8

Hexachlorodibenzofurans

NA

0.000063 or CMBST8

0.001 or CMBST8

Indeno (1,2,3-cd) pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Pentachlorodibenzo-p-dioxins

NA

0.000063 or CMBST8

0.001 or CMBST8

Pentachlorodibenzofurans

NA

0.000035 or CMBST8

0.001 or CMBST8

Pentachlorophenol

87-86-5

0.089

7.4

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Tetrachlorodibenzo-p-dioxins

NA

0.000063 or CMBST8

0.001 or CMBST8

Tetrachlorodibenzofurans

NA

0.000063 or CMBST8

0.001 or CMBST8

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

F034

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Acenaphthene

83-32-9

0.059

3.4

Anthracene

120-12-7

0.059

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Fluorene

86-73-7

0.059

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

F035

Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol.

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

       

F037

Petroleum refinery primary oil/water/solids separation sludge - Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in s. 261.31(b)(2)9 (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing. This listing does include residuals generated from processing or recycling oil-bearing hazardous secondary materials excluded under s.261.4(a)(12)(i)9, if those residuals are to be disposed of.

Acenaphthene

83-32-9

0.059

NA

Anthracene

120-12-7

0.059

3.4

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

84-74-2

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

       
       
       
       
       
       
       
       
       
       
       
       
       
       
       
       

F038

Petroleum refinery secondary (emulsified) oil/water/solids separation sludge - Any sludge and/or float generated from the physical and/or chemical separation of oil/ water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in: induced air flotation (IAF) units, tanks and impoundments, and all sludges generated in DAF units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges and floats generated in aggressive biological treatment units as defined in s. 261.31(b)(2)9 (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and F037, K048, and K051 wastes are not included in this listing.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

84-74-2

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

       

F039

Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one hazardous waste. (Leachate resulting from the disposal of one or more of the following Hazardous Wastes and no other Hazardous Wastes retains its Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.)

Acenaphthylene

208-96-8

0.059

3.4

Acenaphthene

83-32-9

0.059

3.4

Acetone

67-64-1

0.28

160

Acetonitrile

75-05-8

5.6

NA

Acetophenone

96-86-2

0.01

9.7

2-Acetylaminofluorene

53-96-3

0.059

140

Acrolein

107-02-8

0.29

NA

Acrylonitrile

107-13-1

0.24

84

Aldrin

309-00-2

0.021

0.066

4-Aminobiphenyl

92-67-1

0.13

NA

Aniline

62-53-3

0.81

14

Anthracene

120-12-7

0.059

3.4

Aramite

140-57-8

0.36

NA

alpha-BHC

319-84-6

0.00014

0.066

beta-BHC

319-85-7

0.00014

0.066

delta-BHC

319-86-8

0.023

0.066

gamma-BHC

58-89-9

0.0017

0.066

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Benzo(a)pyrene

50-32-8

0.061

3.4

Bromodichloromethane

75-27-4

0.35

15

Methyl bromide (Bromomethane)

74-83-9

0.11

15

4-Bromophenyl phenyl ether

101-55-3

0.055

15

n-Butyl alcohol

71-36-3

5.6

2.6

Butyl benzyl phthalate

85-68-7

0.017

28

2-sec-Butyl-4,6-dinitrophenol (Dinoseb)

88-85-7

0.066

2.5

Carbon disulfide

75-15-0

3.8

NA

Carbon tetrachloride

56-23-5

0.057

6.0

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

p-Chloroaniline

106-47-8

0.46

16

Chlorobenzene

108-90-7

0.057

6.0

Chlorobenzilate

510-15-6

0.1

NA

2-Chloro-1,3-butadiene

126-99-8

0.057

NA

Chlorodibromomethane

124-48-1

0.057

15

Chloroethane

75-00-3

0.27

6

bis(2-Chloroethoxy)methane

111-91-1

0.036

7.2

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

Chloroform

67-66-3

0.046

6.0

bis(2-Chloroisopropyl)ether

39638-32-9

0.055

7.2

p-Chloro-m-cresol

59-50-7

0.018

14

Chloromethane (Methyl chloride)

74-87-3

0.19

30

2-Chloronaphthalene

91-58-7

0.055

5.6

2-Chlorophenol

95-57-8

0.044

5.7

3-Chloropropylene

107-05-1

0.036

30

Chrysene

218-01-9

0.059

3.4

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

Cyclohexanone

108-94-1

0.36

NA

1,2-Dibromo-3-chloropropane

96-12-8

0.11

15

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

Dibromomethane

74-95-3

0.11

15

2,4-D (2,4-Dichlorophenoxyacetic acid)

94-75-7

0.72

10

o,p'-DDD

53-19-0

0.023

0.087

p,p'-DDD

72-54-8

0.023

0.087

o,p'-DDE

3424-82-6

0.031

0.087

p,p'-DDE

72-55-9

0.031

0.087

o,p'-DDT

789-02-6

0.0039

0.087

p,p'-DDT

50-29-3

0.0039

0.087

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Dibenz(a,e)pyrene

192-65-4

0.061

NA

m-Dichlorobenzene

541-73-1

0.036

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Dichlorodifluoromethane

75-71-8

0.23

7.2

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

trans-1,2-Dichloroethylene

156-60-5

0.054

30

2,4-Dichlorophenol

120-83-2

0.044

14

2,6-Dichlorophenol

87-65-0

0.044

14

1,2-Dichloropropane

78-87-5

0.85

18

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

Dieldrin

60-57-1

0.017

0.13

Diethyl phthalate

84-66-2

0.2

28

2,4-Dimethyl phenol

105-67-9

0.036

14

Dimethyl phthalate

131-11-3

0.047

28

Di-n-butyl phthalate

84-74-2

0.057

28

1,4-Dinitrobenzene

100-25-4

0.32

2.3

4,6-Dinitro-o-cresol

534-52-1

0.28

160

2,4-Dinitrophenol

51-28-5

0.12

160

2,4-Dinitrotoluene

121-14-2

0.32

140

2,6-Dinitrotoluene

606-20-2

0.55

28

Di-n-octyl phthalate

117-84-0

0.017

28

Di-n-propylnitrosamine

621-64-7

0.4

14

1,4-Dioxane

123-91-1

12

170

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

NA

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

NA

1,2-Diphenylhydrazine

122-66-7

0.087

NA

Disulfoton

298-04-4

0.017

6.2

Endosulfan I

939-98-8

0.023

0.066

Endosulfan II

33213-6-5

0.029

0.13

Endosulfan sulfate

1031-07-8

0.029

0.13

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

Ethyl acetate

141-78-6

0.34

33

Ethyl cyanide (Propanenitrile)

107-12-0

0.24

360

Ethyl benzene

100-41-4

0.057

10

Ethyl ether

60-29-7

0.12

160

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

Ethyl methacrylate

97-63-2

0.14

160

Ethylene oxide

75-21-8

0.12

NA

Famphur

52-85-7

0.017

15

Fluoranthene

206-44-0

0.068

3.4

Fluorene

86-73-7

0.059

3.4

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035

0.0025

1,2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035

0.0025

1,2,3,4,7,8,9-Heptachlorodibenzofuran, (1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035

0.0025

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

Hexachloroethane

67-72-1

0.055

30

Hexachloropropylene

1888-71-7

0.035

30

Indeno (1,2,3-cd) pyrene

193-39-5

0.0055

3.4

Iodomethane

74-88-4

0.019

65

Isobutyl alcohol

78-83-1

5.6

170

Isodrin

465-73-6

0.021

0.066

Isosafrole

120-58-1

0.081

2.6

Kepone

143-50-8

0.0011

0.13

Methacrylonitrile

126-98-7

0.24

84

Methanol

67-56-1

5.6

NA

Methapyrilene

91-80-5

0.081

1.5

Methoxychlor

72-43-5

0.25

0.18

3-Methylcholanthrene

56-49-5

0.0055

15

4,4'-Methylene bis(2-chloroaniline)

101-14-4

0.5

30

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Methyl methacrylate

80-62-6

0.14

160

Methyl methanesulfonate

66-27-3

0.018

NA

Methyl parathion

298-00-0

0.014

4.6

Naphthalene

91-20-3

0.059

5.6

2-Naphthylamine

91-59-8

0.52

NA

p-Nitroaniline

100-01-6

0.028

28

Nitrobenzene

98-95-3

0.068

14

5-Nitro-o-toluidine

99-55-8

0.32

28

p-Nitrophenol

100-02-7

0.12

29

N-Nitrosodiethylamine

55-18-5

0.4

28

N-Nitrosodimethylamine

62-75-9

0.4

NA

N-Nitroso-di-n-butylamine

924-16-3

0.4

17

N-Nitrosomethylethylamine

10595-95-6

0.4

2.3

N-Nitrosomorpholine

59-89-2

0.4

2.3

N-Nitrosopiperidine

100-75-4

0.013

35

N-Nitrosopyrrolidine

930-55-2

0.013

35

1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD)

3268-87-9

0.000063

0.005

1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF)

39001-02-0

0.000063

0.005

Parathion

56-38-2

0.014

4.6

Total PCBs (sum of all PCB isomers, or all Aroclors)

1336-36-3

0.1

10

Pentachlorobenzene

608-93-5

0.055

10

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

Pentachloronitrobenzene

82-68-8

0.055

4.8

Pentachlorophenol

87-86-5

0.089

7.4

Phenacetin

62-44-2

0.081

16

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Phorate

298-02-2

0.021

4.6

Phthalic anhydride

85-44-9

0.055

NA

Pronamide

23950-58-5

0.093

1.5

Pyrene

129-00-0

0.067

8.2

Pyridine

110-86-1

0.014

16

Safrole

94-59-7

0.081

22

Silvex (2,4,5-TP)

93-72-1

0.72

7.9

2,4,5-T

93-76-5

0.72

7.9

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

Toluene

108-88-3

0.08

10

Toxaphene

8001-35-2

0.0095

2.6

Bromoform (Tribromomethane)

75-25-2

0.63

15

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Trichlorofluoromethane

75-69-4

0.02

30

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

1,2,3-Trichloropropane

96-18-4

0.85

30

1,1,2-Trichloro-1,2,2-trifluoroethane

76-13-1

0.057

30

Tris(2,3-Dibromopropyl) phosphate

126-72-7

0.11

NA

Vinyl chloride

75-01-4

0.27

6.0

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Barium

7440-39-3

1.2

21 mg/L TCLP

Beryllium

7440-41-7

0.82

NA

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

NA

Fluoride

16984-48-8

35

NA

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.25 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

Silver

7440-22-4

0.43

0.14 mg/L TCLP

Sulfide

8496-25-8

14

NA

Thallium

7440-28-0

1.4

NA

Vanadium

7440-62-2

4.3

NA

Hazardous Industrial Waste from Specific Sources

Hazardous Industrial Waste

Regulated Constituents
(and Treatment Subcategories1)

Land Disposal Treatment Requirements

Aqueous Waste

Non-aqueous Waste

Column 1

Column 2

Column 3

Column 4

Column 5

Column 6

Haz. Waste Number2

Waste

Generic Name or other description

CAS Number3

Treatment Code4 or Concentration5 (mg/L)

Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated)

Wood preservation:

K001

Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.

Naphthalene

91-20-3

0.059

5.6

Pentachlorophenol

87-86-5

0.089

7.4

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Inorganic Pigments:

K002

Wastewater treatment sludge from the production of chrome yellow and orange pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

       

K003

Wastewater treatment sludge from the production of molybdate orange pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

       

K004

Wastewater treatment sludge from the production of zinc yellow pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K005

Wastewater treatment sludge from the production of chrome green pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

K006

Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).

Treatment Subcategory 1

Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous):

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Treatment Subcategory 2

Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated):

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

K007

Wastewater treatment sludge from the production of iron blue pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

       

K008

Oven residue from the production of chrome oxide green pigments.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Organic chemicals:

K009

Distillation bottoms from the production of acetaldehyde from ethylene.

Chloroform

67-66-3

0.046

6.0

K010

Distillation side cuts from the production of acetaldehyde from ethylene.

Chloroform

67-66-3

0.046

6.0

K011

Bottom stream from the wastewater stripper in the production of acrylonitrile.

Acetonitrile

75-05-8

5.6

38

Acrylonitrile

107-13-1

0.24

84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanides (Total)7

57-12-5

1.2

590

K013

Bottom stream from the acetonitrile column in the production of acrylonitrile.

Acetonitrile

75-05-8

5.6

38

Acrylonitrile

107-13-1

0.24

84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanides (Total)7

57-12-5

1.2

590

K014

Bottoms from the acetonitrile purification column in the production of acrylonitrile.

Acetonitrile

75-05-8

5.6

38

Acrylonitrile

107-13-1

0.24

84

Acrylamide

79-06-1

19

23

Benzene

71-43-2

0.14

10

Cyanides (Total)7

57-12-5

1.2

590

K015

Still bottoms from the distillation of benzyl chloride.

Anthracene

120-12-7

0.059

3.4

Benzal chloride

98-87-3

0.055

6.0

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Phenanthrene

85-01-8

0.059

5.6

Toluene

108-88-3

0.08

10

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K016

Heavy ends or distillation residues from the production of carbon tetrachloride.

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

Hexachloroethane

67-72-1

0.055

30

Tetrachloroethylene

127-18-4

0.056

6.0

K017

Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

1,2-Dichloropropane

78-87-5

0.85

18

1,2,3-Trichloropropane

96-18-4

0.85

30

K018

Heavy ends from the fractionation column in ethyl chloride production.

Chloroethane

75-00-3

0.27

6.0

Chloromethane

74-87-3

0.19

NA

1,1-Dichloroethane

75-34-3

0.059

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

Hexachlorobenzene

118-74-1

0.055

10

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

NA

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K019

Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

Chlorobenzene

108-90-7

0.057

6.0

Chloroform

67-66-3

0.046

6.0

p-Dichlorobenzene

106-46-7

0.09

NA

1,2-Dichloroethane

107-06-2

0.21

6.0

Fluorene

86-73-7

0.059

NA

Hexachloroethane

67-72-1

0.055

30

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

NA

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K020

Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

       

K021

Aqueous spent antimony catalyst waste from fluoromethanes production.

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

K022

Distillation bottom tars from the production of phenol/acetone from cumene.

Toluene

108-88-3

0.08

10

Acetophenone

96-86-2

0.01

9.7

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

13

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

13

Phenol

108-95-2

0.039

6.2

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K023

Distillation light ends from the production of phthalic anhydride from naphthalene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K024

Distillation bottoms from the production of phthalic anhydride from naphthalene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K025

Distillation bottoms from the production of nitrobenzene by the nitration of benzene.

Distillation bottoms from the production of nitrobenzene by the nitration of benzene.

NA

LLEXT fb SSTRP fb CARBN; or CMBST

CMBST

K026

Stripping still tails from the production of methyl ethyl pyridines.

Stripping still tails from the production of methyl ethyl pyridines.

NA

CMBST

CMBST

K027

Centrifuge and distillation residues from toluene diisocyanate production.

Centrifuge and distillation residues from toluene diisocyanate production.

NA

CARBN; or CMBST

CMBST

K028

Spent catalyst from the hydrochlorinator reactor in the productions of 1,1,1trichloroethane.

1,1-Dichloroethane

75-34-3

0.059

6.0

trans-1,2-Dichloroethylene

156-60-5

0.054

30

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

NA

6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Cadmium

7440-43-9

0.69

NA

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

K029

Waste from the product stream stripper in the production of 1,1,1trichloroethane.

Chloroform

67-66-3

0.046

6.0

1,2-Dichloroethane

107-06-2

0.21

6.0

1,1-Dichloroethylene

75-35-4

0.025

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

Vinyl chloride

75-01-4

0.27

6.0

K030

Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene.

o-Dichlorobenzene

95-50-1

0.088

NA

p-Dichlorobenzene

106-46-7

0.09

NA

Hexachlorobutadiene

87-68-3

0.055

5.6

Hexachloroethane

67-72-1

0.055

30

Hexachloropropylene

1888-71-7

NA

30

Pentachlorobenzene

608-93-5

NA

10

Pentachloroethane

76-01-7

NA

6.0

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Tetrachloroethylene

127-18-4

0.056

6

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K083

Distillation bottoms from aniline production.

Aniline

62-53-3

0.81

14

Benzene

71-43-2

0.14

10

Cyclohexanone

108-94-1

0.36

NA

Diphenylamine (difficult to distinguish from diphenylnitrosamine)

122-39-4

0.92

13

Diphenylnitrosamine (difficult to distinguish from diphenylamine)

86-30-6

0.92

13

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

Nickel

7440-02-0

3.98

11 mg/L TCLP

K085

Distillation or fractionation column bottoms from the production of chlorobenzenes.

Benzene

71-43-2

0.14

10

Chlorobenzene

108-90-7

0.057

6.0

m-Dichlorobenzene

541-73-1

0.036

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Hexachlorobenzene

118-74-1

0.055

10

Total PCBs (sum of all PCB isomers, or all Aroclors)

1336-36-3

0.1

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K093

Distillation light ends from the production of phthalic anhydride from orthoxylene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K094

Distillation bottoms from the production of phthalic anhydride from orthoxylene.

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0;
85-44-9

0.055

28

K095

Distillation bottoms from the production of 1,1,1trichloroethane.

Hexachloroethane

67-72-1

0.055

30

Pentachloroethane

76-01-7

0.055

6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-1

0.054

6.0

K096

Heavy ends from the heavy ends column from the production of 1,1,1trichloroethane.

m-Dichlorobenzene

541-73-1

0.036

6.0

Pentachloroethane

76-01-1

0.055

6.0

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

1,1,2,2-Tetrachloroethane

79-34-6

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

1,1,2-Trichloroethane

79-00-5

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

K103

Process residues from aniline extraction from the production of aniline.

Aniline

62-53-3

0.81

14

Benzene

71-43-2

0.14

10

2,4-Dinitrophenol

51-28-5

0.12

160

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

K104

Combined wastewater streams generated from nitrobenzene/aniline production.

Aniline

62-53-3

0.81

14

Benzene

71-43-2

0.14

10

2,4-Dinitrophenol

51-28-5

0.12

160

Nitrobenzene

98-95-3

0.068

14

Phenol

108-95-2

0.039

6.2

Cyanides (Total)7

57-12-5

1.2

590

K105

Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.

Benzene

71-43-2

0.14

10

Chlorobenzene

108-90-7

0.057

6.0

2-Chlorophenol

95-57-8

0.044

5.7

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Phenol

108-95-2

0.039

6.2

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

K107

Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines.

Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K108

Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K109

Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K110

Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K111

Product washwaters from the production of dinitrotoluene via nitration of toluene.

2,4-Dinitrotoluene

121-1-2

0.32

140

2,6-Dinitrotoluene

606-20-2

0.55

28

K112

Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.

Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CMBST; or CHOXD fb CARBN; or BIODG fb CARBN

CMBST

K113

Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CARBN; or CMBST

CMBST

K114

Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CARBN; or CMBST

CMBST

K115

Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

Nickel

7440-02-0

3.98

11 mg/L TCLP

Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.

NA

CARBN; or CMBST

CMBST

K116

Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.

Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.

NA

CARBN; or CMBST

CMBST

K117

Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Chloroform

67-66-3

0.046

6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K118

Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Chloroform

67-66-3

0.046

6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K136

Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Chloroform

67-66-3

0.46

6.0

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

K149

Distillation bottoms from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillation of benzyl chloride.)

Chlorobenzene

108-90-7

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Chloromethane

74-87-3

0.19

30

p-Dichlorobenzene

106-46-7

0.09

6.0

Hexachlorobenzene

118-74-1

0.055

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Toluene

108-88-3

0.08

10

K150

Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of alpha-( or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Chloromethane

74-87-3

0.019

30

p-Dichlorobenzene

106-46-7

0.09

6.0

Hexachlorobenzene

118-74-1

0.055

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,1,2,2-Tetrachloroethane

79-34-5

0.057

6.0

Tetrachloroethylene

127-18-4

0.056

6.0

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K151

Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups.

Benzene

71-43-2

0.14

10

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Hexachlorobenzene

118-74-1

0.055

10

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

Tetrachloroethylene

127-18-4

0.056

6.0

Toluene

108-88-3

0.08

10

       

K156

Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2- propynyl n-butylcarbamate.)

Acetonitrile

75-05-8

5.6

1.8

Acetophenone

96-86-2

0.01

9.7

Aniline

62-53-3

0.81

14

Benomyl

17804-35-2

0.056

1.4

Benzene

71-43-2

0.14

10

Carbaryl

63-25-2

0.006

0.14

Carbendazim

10605-21-7

0.056

1.4

Carbofuran

1563-66-2

0.006

0.14

Carbosulfan

55285-14-8

0.028

1.4

Chlorobenzene

108-90-7

0.057

6.0

Chloroform

67-66-3

0.046

6.0

o-Dichlorobenzene

95-50-1

0.088

6.0

Methomyl

16752-77-5

0.028

0.14

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Naphthalene

91-20-3

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyridine

110-86-1

0.014

16

Toluene

108-88-3

0.08

10

Triethylamine

101-44-8

0.081

1.5

K157

Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Chloromethane

74-87-3

0.19

30

Methomyl

16752-77-5

0.028

0.14

Methylene chloride

75-09-2

0.089

30

Methyl ethyl ketone

78-93-3

0.28

36

Pyridine

110-86-1

0.014

16

Triethylamine

121-44-8

0.081

1.5

       

K158

Bag house dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.)

Benomyl

17804-35-2

0.056

1.4

Benzene

71-43-2

0.14

10

Carbendazim

10605-21-7

0.056

1.4

Carbofuran

1563-66-2

0.006

0.14

Carbosulfan

55285-14-8

0.028

1.4

Chloroform

67-66-3

0.046

6.0

Methylene chloride

75-09-2

0.089

30

Phenol

108-95-2

0.039

6.2

K159

Organics from the treatment of thiocarbamate wastes.

Benzene

71-43-2

0.14

10

Butylate

2008-41-5

0.042

1.4

EPTC (Eptam)

759-94-4

0.042

1.4

Molinate

2212-67-1

0.042

1.4

Pebulate

1114-71-2

0.042

1.4

Vernolate

1929-77-7

0.042

1.4

K161

Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.)

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Carbon disulfide

75-15-0

3.8

4.8 mg/L TCLP

Dithiocarbamates (total)

NA

0.028

28

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

11.0 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

K174

Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer.

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,7,8,9-Heptachlorodibenzofuran,

(1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035 or CMBST8

0.0025 or CMBST8

HxCDDs (All Hexachlorodibenzo-p-dioxins)

34465-46-8

0.000063 or CMBST8

0.001 or CMBST8

HxCDFs (All Hexachlorodibenzofurans)

55684-94-1

0.000063 or CMBST8

0.001 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD)

3268-87-9

0.000063 or CMBST8

0.005 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF)

39001-02-0

0.000063 or CMBST8

0.005 or CMBST8

PeCDDs (All Pentachlorodibenzo-p-dioxins

36088-22-9

0.000063 or CMBST8

0.001 or CMBST8

PeCDFs (All Pentachlorodibenzofurans)

30402-15-4

0.000035 or CMBST8

0.001 or CMBST8

TCDDs (All tetachlorodibenzo-p-dioxins)

41903-57-5

0.000063 or CMBST8

0.001 or CMBST8

TCDFs (All tetrachlorodibenzofurans)

55722-27-5

0.000063 or CMBST8

0.001 or CMBST8

Arsenic

7440-36-0

1.4

5.0 mg/L TCLP

K175

Wastewater treatment sludge from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process.

Mercury

7439-97-6

0.15

0.025 mg/L TCLP10

pH

 

NA

pH≤ 6.010

Inorganic chemicals:

K071

Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.

Treatment Subcategory 1

Non-aqueous wastes that are residues from RMERC:

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Treatment Subcategory 2

Non-aqueous wastes that are not residues from RMERC:

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Treatment Subcategory 3

All K071 aqueous wastes:

Mercury

7439-97-6

0.15

NA

K073

Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.

Carbon tetrachloride

56-23-5

0.057

6.0

Chloroform

67-66-3

0.046

6.0

Hexachloroethane

67-72-1

0.055

30

Tetrachloroethylene

127-18-4

0.056

6.0

1,1,1-Trichloroethane

71-55-6

0.054

6.0

K106

Wastewater treatment sludge from the mercury cell process in chlorine production.

Treatment Subcategory 1

Non-aqueous wastes that contain greater than or equal to 260 mg/kg total mercury:

Mercury

7439-97-6

NA

RMERC

Treatment Subcategory 2

Non-aqueous wastes that contain less than 260 mg/kg total mercury that are residues from RMERC:

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Treatment Subcategory 3

Other K106 non-aqueous wastes that contain less than 260 mg/kg total mercury and are not residues from RMERC:

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Treatment Subcategory 4

All K106 aqueous wastes:

Mercury

7439-97-6

0.15

NA

K176

Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide).

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.025 mg/L TCLP

       

K177

Slag from the production of antimony oxide that is speculatively accumulated or disposed, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide).

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

       

K178

Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process.

1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD)

35822-46-9

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,6,7,8-Heptachlorodibenzofuran,

(1,2,3,4,6,7,8-HpCDF)

67562-39-4

0.000035 or CMBST8

0.0025 or CMBST8

1,2,3,4,7,8,9-Heptachlorodibenzofuran,

(1,2,3,4,7,8,9-HpCDF)

55673-89-7

0.000035 or CMBST8

0.0025 or CMBST8

HxCDDs (All Hexachlorodibenzo-p-dioxins)

34465-46-8

0.000063 or CMBST8

0.001 or CMBST8

HxCDFs (All Hexachlorodibenzofurans)

55684-94-1

0.000063 or CMBST8

0.001 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD)

3268-87-9

0.000063 or CMBST8

0.005 or CMBST8

1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF)

39001-02-0

0.000063 or CMBST8

0.005 or CMBST8

PeCDDs (All Pentachlorodibenzo-p-dioxins

36088-22-9

0.000063 or CMBST8

0.001 or CMBST8

PeCDFs (All Pentachlorodibenzofurans)

30402-15-4

0.000035 or CMBST8

0.001 or CMBST8

TCDDs (All tetachlorodibenzo-p-dioxins)

41903-57-5

0.000063 or CMBST8

0.001 or CMBST8

TCDFs (All tetrachlorodibenzofurans)

55722-27-5

0.000063 or CMBST8

0.001 or CMBST8

Thallium

7440-28-0

1.4

0.20 mg/L TCLP

Pesticides:

K031

Byproduct salts generated in the production of MSMA and cacodylic acid.

Arsenic

7440-38-2

14

5.0 mg/L TCLP

K032

Wastewater treatment sludge from the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

K033

Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K034

Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K035

Wastewater treatment sludges generated in the production of creosote.

Acenaphthene

83-32-9

NA

3.4

Anthracene

120-12-7

NA

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

Dibenz(a,h)anthracene

53-70-3

NA

8.2

Fluoranthene

206-44-0

0.068

3.4

Fluorene

86-73-7

NA

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

NA

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-1

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

K036

Still bottoms from toluene reclamation distillation in the production of disulphoton.

Disulfoton

298-04-4

0.017

6.2

K037

Wastewater treatment sludges from the production of disulphoton.

Disulfoton

298-04-4

0.017

6.2

Toluene

108-88-3

0.08

10

K038

Wastewater from the washing and stripping of phorate production.

Phorate

298-02-2

0.021

4.6

K039

Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate.

Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate.

NA

CARBN; or CMBST

CMBST

K040

Wastewater treatment sludge from the production of phorate.

Phorate

298-02-2

0.021

4.6

K041

Wastewater treatment sludge from the production of toxaphene.

Toxaphene

8001-35-2

0.0095

2.6

K042

Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5T.

o-Dichlorobenzene

95-50-1

0.088

6.0

p-Dichlorobenzene

106-46-7

0.09

6.0

Pentachlorobenzene

608-93-5

0.055

10

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

1,2,4-Trichlorobenzene

120-82-1

0.055

19

K043

2,6-Dichlorophenol waste from the production of 2,4D.

2,4-Dichlorophenol

120-83-2

0.044

14

2,6-Dichlorophenol

187-65-0

0.044

14

2,4,5-Trichlorophenol

95-95-4

0.18

7.4

2,4,6-Trichlorophenol

88-06-2

0.035

7.4

2,3,4,6-Tetrachlorophenol

58-90-2

0.03

7.4

Pentachlorophenol

87-86-5

0.089

7.4

Tetrachloroethylene

127-18-4

0.056

6.0

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

K097

Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

K098

Untreated process wastewater from the production of toxaphene.

Toxaphene

8001-35-2

0.0095

2.6

K099

Untreated wastewater from the production of 2,4-D.

2,4-Dichlorophenoxyacetic acid

94-75-7

0.72

10

HxCDDs (All Hexachlorodibenzo-p-dioxins)

NA

0.000063

0.001

HxCDFs (All Hexachlorodibenzofurans)

NA

0.000063

0.001

PeCDDs (All Pentachlorodibenzo-p-dioxins)

NA

0.000063

0.001

PeCDFs (All Pentachlorodibenzofurans)

NA

0.000035

0.001

TCDDs (All Tetrachlorodibenzo-p-dioxins)

NA

0.000063

0.001

TCDFs (All Tetrachlorodibenzofurans)

NA

0.000063

0.001

K123

Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt.

Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K124

Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.

Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K125

Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.

Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K126

Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.

Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.

NA

CMBST; or CHOXD fb (BIODG or CARBN)

CMBST

K131

Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

K132

Spent absorbent and wastewater separator solids from the production of methyl bromide.

Methyl bromide (Bromomethane)

74-83-9

0.11

15

Explosives:

K044

Wastewater treatment sludges from the manufacturing and processing of explosives.

Wastewater treatment sludges from the manufacturing and processing of explosives.

NA

DEACT

DEACT

K045

Spent carbon from the treatment of wastewater containing explosives.

Spent carbon from the treatment of wastewater containing explosives.

NA

DEACT

DEACT

K046

Wastewater treatment sludges from the manufacturing formulation and loading of leadbased initiating compounds.

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K047

Pink/red water from TNT operations.

Pink/red water from TNT operations.

NA

DEACT

DEACT

Petroleum refining:

K048

Dissolved air flotation (DAF) float from the petroleum refining industry.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Chrysene

218-01-9

0.059

3.4

Di-n-butyl phthalate

84-74-2

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-33

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K049

Slop oil emulsion solids from the petroleum refining industry.

Anthracene

120-12-7

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Carbon disulfide

75-15-0

3.8

NA

Chrysene

2218/01/09

0.059

3.4

2,4-Dimethylphenol

105-67-9

0.036

NA

Ethylbenzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Cyanides (Total)7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K050

Heat exchanger bundle cleaning sludge from the petroleum refining industry.

Benzo(a)pyrene

50-32-8

0.061

3.4

Phenol

108-95-2

0.039

6.2

Cyanides (Total)7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K051

API separator sludge from the petroleum refining industry.

Acenaphthene

83-32-9

0.059

NA

Anthracene

120-12-7

0.059

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

bis(2-Ethylhexyl)phthalate

117-81-7

0.28

28

Chrysene

2218/01/09

0.059

3.4

Di-n-butyl phthalate

105-67-9

0.057

28

Ethylbenzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

NA

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Cyanides (Total)7

57-12-5

1.2

590

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K052

Tank bottoms (leaded) from the petroleum refining industry.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

2,4-Dimethylphenol

105-67-9

0.036

NA

Ethylbenzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Phenol

108-95-2

0.039

6.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

NA

Nickel

7440-02-0

NA

11 mg/L TCLP

K169

Crude oil storage tank sediment from petroleum refining operations.

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Ethyl benzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

81-05-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

K170

Clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operations.

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Ethyl benzene

100-41-4

0.057

10

Fluorene

86-73-7

0.059

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

81-05-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

K171

Spent Hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).

Benz(a)anthracene

56-55-3

0.059

3.4

Benzene

71-43-2

0.14

10

Chrysene

218-01-9

0.059

3.4

Ethyl benzene

100-41-4

0.057

10

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

81-05-8

0.059

5.6

Pyrene

129-00-0

0.67

8.2

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

Arsenic

7740-38-2

1.4

5 mg/L TCLP

Nickel

7440-02-0

3.98

11.0 mg/L TCLP

Vanadium

7440-62-2

4.3

1.6 mg/L TCLP

Reactive sulfides

NA

DEACT

DEACT

K172

Spent Hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media).

Benzene

71-43-2

0.14

10

Ethyl benzene

100-41-4

0.57

10

Toluene (Methyl Benzene)

108-88-3

0.08

10

Xylene(s) (Total)

1330-20-7

0.32

30

Antimony

7740-36-0

1.9

1.15 mg/L TCLP

Arsenic

7740-38-2

1.4

5 mg/L TCLP

Nickel

7440-02-0

3.98

11.0 mg/L TCLP

Vanadium

7440-62-2

4.3

1.6 mg/L TCLP

Reactive sulfides

NA

DEACT

DEACT

Iron and steel:

K061

Emission control dust/sludge from the primary production of steel in electric furnaces.

Antimony

7440-36-0

NA

1.15 mg/L TCLP

Arsenic

7440-38-2

NA

5.0 mg/L TCLP

Barium

7440-39-3

NA

21 mg/L TCLP

Beryllium

7440-41-7

NA

1.22 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

NA

5.7 mg/L TCLP

Silver

7440-22-4

NA

0.14 mg/L TCLP

Thallium

7440-28-0

NA

0.20 mg/L TCLP

Zinc

7440-66-6

NA

4.3 mg/L TCLP

K062

Spent pickle liquor generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry.

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Nickel

7440-02-0

3.98

NA

       

Primary aluminum:

K088

Spent potliners from primary aluminum reduction.

Acenaphthene

83-32-9

0.059

3.4

Anthracene

120-12-7

0.059

3.4

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene

205-99-2

0.11

6.8

Benzo(k)fluoranthene

207-08-9

0.11

6.8

Benzo(g,h,i)perylene

191-24-2

0.0055

1.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Fluoranthene

206-44-0

0.068

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Antimony

7440-36-0

1.9

1.15 mg/L TCLP

Arsenic

7440-38-2

1.4

26.1

Barium

7440-39-3

1.2

21 mg/L TCLP

Beryllium

7440-41-7

0.82

1.22 mg/L TCLP

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Mercury

7439-97-6

0.15

0.025 mg/L TCLP

Nickel

7440-02-0

3.98

11 mg/L TCLP

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

Silver

7440-22-4

0.43

0.14 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Fluoride

16984-48-8

35

NA

Secondary lead:

K069

Emission control dust/sludge from secondary lead smelting, not including sludge generated from secondary acid scrubber systems.

Treatment Subcategory 1

Calcium Sulfate (Low Lead)

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Treatment Subcategory 2

Non- Calcium Sulfate (High Lead)

Non- Calcium Sulfate (High Lead)

NA

NA

RLEAD

K100

Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.

Cadmium

7440-43-9

0.69

0.11 mg/L TCLP

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Veterinary pharmaceuticals:

K084

Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

K101

Distillation tar residues from the distillation of anilinebased compounds in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

o-Nitroaniline

88-74-4

0.27

14

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Cadmium

7440-43-9

0.69

NA

Lead

7439-92-1

0.69

NA

Mercury

7439-97-6

0.15

NA

K102

Residue from the use of activated carbon for decolourization in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.

o-Nitrophenol

88-75-5

0.028

13

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

Cadmium

7440-43-9

0.69

NA

Lead

7439-92-1

0.69

NA

Mercury

7439-97-6

0.15

NA

Ink formulation:

K086

Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead.

Acetone

67-64-1

0.28

160

Acetophenone

96-86-2

0.01

9.7

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

n-Butyl alcohol

71-36-3

5.6

2.6

Butyl benzyl phthalate

85-68-7

0.017

28

Cyclohexanone

108-94-1

0.36

NA

o-Dichlorobenzene

95-50-1

0.088

6.0

Diethyl phthalate

84-66-2

0.2

28

Dimethyl phthalate

131-11-3

0.047

28

Di-n-butyl phthalate

84-74-2

0.057

28

Di-n-octyl phthalate

117-84-0

0.017

28

Ethyl acetate

141-78-6

0.34

33

Ethylbenzene

100-41-4

0.057

10

Methanol

67-56-1

5.6

NA

Methyl ethyl ketone

78-93-3

0.28

36

Methyl isobutyl ketone

108-10-1

0.14

33

Methylene chloride

75-09-2

0.089

30

Naphthalene

91-20-3

0.059

5.6

Nitrobenzene

98-95-3

0.068

14

Toluene

108-88-3

0.08

10

1,1,1-Trichloroethane

71-55-6

0.054

6.0

Trichloroethylene

79-01-6

0.054

6.0

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Lead

7439-92-1

0.69

0.75 mg/L TCLP

Coking:

K060

Ammonia still lime sludge from coking operations.

Benzene

71-43-2

0.14

10

Benzo(a)pyrene

50-32-8

0.061

3.4

Naphthalene

91-20-3

0.059

5.6

Phenol

108-95-2

0.039

6.2

Cyanides (Total)7

57-12-5

1.2

590

K087

Decanter tank tar sludge from coking operations.

Acenaphthylene

208-96-8

0.059

3.4

Benzene

71-43-2

0.14

10

Chrysene

218-01-9

0.059

3.4

Fluoranthene

206-44-0

0.068

3.4

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Naphthalene

91-20-3

0.059

5.6

Phenanthrene

85-01-8

0.059

5.6

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

K141

Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludges from coking operations).

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-2-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K142

Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K143

Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

K144

Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)pyrene

56-55-3

0.059

3.4

Benzo(a)anthracene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

K145

Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Naphthalene

91-20-3

0.059

5.6

K147

Tar storage tank residues from coal tar refining.

Benzene

71-43-2

0.14

10

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

K148

Residues from coal tar distillation, including but not limited to, still bottoms.

Benz(a)anthracene

56-55-3

0.059

3.4

Benzo(a)pyrene

50-32-8

0.061

3.4

Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene)

205-99-2

0.11

6.8

Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene)

207-08-9

0.11

6.8

Chrysene

218-01-9

0.059

3.4

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

Indeno(1,2,3-cd)pyrene

193-39-5

0.0055

3.4

Notes to Schedule 1:

1 Treatment subcategories are shown for some wastes. In these cases, it is necessary to identify the treatment subcategory that most closely describes the particular waste for which treatment is required. The land disposal treatment requirements for that waste are those shown for that treatment subcategory.

2 Haz. Waste Number means Hazardous Waste Number. These numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment.

3 CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only.

4 See Schedule 7 for a description of the treatment methods and treatment standards associated with each treatment code. In some cases, the entries in this Schedule may set out more than one treatment code for a regulated constituent. An entry may permit a choice of treatment methods. For example, the entry “CHOXD; BIODG; or CMBST” means that the waste may be treated using any of the treatment methods that are set out for those treatment codes in Schedule 7. An entry may require treatment methods to be applied in a particular sequence. For this purpose, the abbreviation “fb” means “followed by”. For example, the entry “CHOXD fb CARBN” means that the waste must first be treated using the treatment method that is set out for CHOXD in Schedule 7 and, following that treatment, it must be treated using the treatment method that is set out for CARBN in Schedule 7. An entry may combine a choice of treatment methods and a requirement to apply treatment methods in a particular sequence (for example, “(WETOX or CHOXD) fb CARBN; or CMBST”).

5 Concentration requirements for aqueous wastes are based on analysis of composite samples.

6 Concentration requirements for non-aqueous wastes are based on analysis of grab samples.

7 Both Cyanides (Total) and Cyanides (Amenable) for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.

7.1 The manufacturing of complete motor vehicles (body and chassis or unibody) or chassis only at a facility identified by NAICS code 336110 (Automobile and light-duty motor vehicle manufacturing), where “NAICS” means the North American Industry Classification System (NAICS) Canada 2012, dated January 2012 and maintained for Canada by Statistics Canada.

8 For these wastes, the treatment method described by the CMBST treatment code must be carried out at a facility that is authorized under an environmental compliance approval to treat these types of waste.

9 Resource Conservation and Recovery Act (RCRA), United States Congress, 42 U.S.C. s/s 6901 et seq. (1976), Subtitle C, Code of Federal Regulations, 40CFR, Chapter I - Environmental Protection Agency, Subchapter I - Solid Wastes, Part 261 - Identification and Listing of Hazardous Waste.

10 K175 non-aqueous wastes that have been treated in compliance with Schedule 1 land disposal treatment requirements must also be macroencapsulated in accordance with Schedule 8 (Alternative Treatment for Hazardous Debris), unless the waste is placed in:

(1) A hazardous waste monofill containing only K175 wastes that meet all applicable Schedule 1 treatment standards; or

(2) A dedicated hazardous waste landfill cell in which all other wastes being co-disposed are at pH≤ 6.0.

O. Reg. 337/09, s. 20; O. Reg. 234/11, s. 40; O. Reg. 233/13, s. 1.

SCHEDULE 1.1
EXEMPT HAZARDOUS INDUSTRIAL WASTES

Industry and Site

Waste

ICI Canada Inc., Cornwall

Brine purification muds (K071), saturator and clarifier sludges only, without mixing with other wastes or materials) generated from mercury cells at the chloralkali chlorine plant.

Iron and steel industry, any site

Sludge generated by lime stabilization of spent pickle liquor (K062) generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry.

Iron and steel industry, any site

Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of K061 or K062 waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces.

Electroplating industry, any site

Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of F006 waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces.

Organic chemical industry, any site

Biological treatment sludge from the treatment of organic waste (K156) and wastewaters (K157) from the production of carbamates and carbamoyl oximes.

Petroleum refining industry, any site

Catalyst inert support media separated from spent hydrotreating catalyst (K171) or spent hydrorefining catalyst (K172).

O. Reg. 461/05, s. 23.

SCHEDULE 2
PART A — ACUTE HAZARDOUS WASTE CHEMICAL

Acute Hazardous Waste Chemical

Regulated Constituents
(and Treatment Subcategories1)

Land Disposal Treatment Requirements

   

Aqueous Waste

Non-aqueous Waste

Column 1

Column 2

Column 3

Column 4

Column 5

Column 6

Column 7

Haz. Waste Number2

CAS Number3

Generic Name

Generic Name or other description

CAS Number3

Treatment Code4 or Concentration5 (mg/L)

Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated)

P026

5344-82-1

1-(o-Chlorophenyl)thiourea

1-(o-Chlorophenyl)thiourea

5344-82-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P081

55-63-0

1,2,3-Propanetriol, trinitrate

Nitroglycerin

55-63-0

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P042

51-43-4

1,2-Benzenediol,4-[1-hydroxy-2-(methylamino)ethyl]-

Epinephrine

51-43-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P067

75-55-8

1,2-Propylenimine

2-Methyl-aziridine

75-55-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P185

26419-73-8

1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-[(methylamino)-carbonyl]oxime

Tirpate

26419-73-8

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 0.28

P004

309-00-2

1,4,5,8-Dimethanonaphthalene,1,2,3,4,10,10-hexa-chloro-1,4,4a,5,8,8a,-hexahydro-, (1alpha,4alpha, 4abeta, 5alpha,8alpha,8abeta)

Aldrin

309-00-2

0.021

0.066

P060

465-73-6

1,4,5,8-Dimethanonaphthalene,1,2,3,4,10,10-hexa-chloro-1,4,4a,5,8,8a-hexahydro-, (1alpha,4alpha, 4abeta, 5beta, 8beta, 8abeta)-

Isodrin

465-73-6

0.021

0.066

P002

591-08-2

1-Acetyl-2-thiourea

1-Acetyl-2-thiourea

591-08-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P048

51-28-5

2,4-Dinitrophenol

2,4-Dinitrophenol

51-28-5

0.12

160

P051

72-20-8

2,7:3,6-Dimethanonaphth [2,3-b]oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-,(1aalpha,2beta,2abeta,3alpha,6alpha,6 abeta,7beta, 7aalpha)-, & metabolites

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

P037

60-57-1

2,7:3,6-Dimethanonaphth[2,3-b]oxirene,3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1aalpha,2beta,2aalpha,3beta,6beta,6a alpha,7beta, 7aalpha)-[b]oxirene, 3,4,5,6,9,9-hexachloro-

Dieldrin

60-57-1

0.017

0.13

P045

39196-18-4

2-Butanone,3,3-dimethyl-1-methylthio)-,O-[methylamino)carbonyl] oxime

Thiofanox

39196-18-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P034

131-89-5

2-Cyclohexyl-4,6-dinitrophenol

2-Cyclohexyl-4,6-dinitrophenol

131-89-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P001

81-81-2

2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, & salts, when present at concentrations greater than 0.3%

Warfarin

81-81-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P069

75-86-5

2-Methyllactonitrile

2-Methyllactonitrile

75-86-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P017

598-31-2

2-Propanone, 1-bromo-

Bromoacetone

598-31-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P005

107-18-6

2-Propen-1-ol

Allyl alcohol

107-18-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P003

107-02-8

2-Propenal

Acrolein

107-02-8

0.29

CMBST

P102

107-19-7

2-Propyn-1-ol

Propargyl alcohol

107-19-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P007

2763-96-4

3(2H)-Isoxazolone, 5-(aminomethyl)-

5-Aminomethyl 3-isoxazolol

2763-96-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P027

542-76-7

3-Chloropropionitrile

3-Chloropropionitrile

542-76-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P202

64-00-6

3-Isopropylphenyl N-methylcarbamate

m-Cumenyl methylcarbamate

64-00-6

0.056

1.4

P047

534-52-1

4,6-Dinitro-o-cresol, & salts

Treatment Subcategory 1

4,6-Dinitro-o-cresol:

4,6-Dinitro-o-cresol

543-52-1

0.28

160

Treatment Subcategory 2

4,6-Dinitro-o-cresol salts:

4,6-Dinitro-o-cresol salts

NA

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P059

76-44-8

4,7-Methano-1H-indene, 1,4,5,6,7,8,8- heptachloro-3a,4,7,7a-tetrahydro-

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

P008

504-24-5

4-Aminopyridine

4-Aminopyridine

504-24-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P008

504-24-5

4-Pyridinamine

4-Aminopyridine

504-24-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P007

2763-96-4

5-(Aminomethyl)-3-isoxazolol

5-Aminomethyl 3-isoxazolol

2763-96-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P050

115-29-7

6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9, 10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide

Endosulfan I

939-98-8

0.023

0.066

Endosulfan II

33213-6-5

0.029

0.13

Endosulfan sulfate

1031-07-8

0.029

0.13

       

P127

1563-66-2

7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate

Carbofuran

1563-66-2

0.006

0.14

P088

145-73-3

7-Oxabicyclo[2.2.1]heptane-2,3-dicarboxylic acid

Endothall

145-73-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P023

107-20-0

Acetaldehyde, chloro-

Chloroacetaldehyde

107-20-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P057

640-19-7

Acetamide, 2-fluoro-

Fluoroacetamide

640-19-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P002

591-08-2

Acetamide, N-(aminothioxomethyl)-

1-Acetyl-2-thiourea

591-08-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P058

62-74-8

Acetic acid, fluoro-, sodium salt

Fluoroacetic acid, sodium salt

62-74-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P003

107-02-8

Acrolein

Acrolein

107-02-8

0.29

CMBST

P070

116-06-3

Aldicarb

Aldicarb

116-06-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P203

1646-88-4

Aldicarb sulfone

Aldicarb sulfone

1646-88-4

0.056

0.28

P004

309-00-2

Aldrin

Aldrin

309-00-2

0.021

0.066

P005

107-18-6

Allyl alcohol

Allyl alcohol

107-18-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P046

122-09-8

alpha,alpha-Dimethylphenethylamine

alpha, alpha-Dimethylphenethylamine

122-09-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P072

86-88-4

alpha-Naphthylthiourea

1-Naphthyl-2-thiourea

86-88-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P006

20859-73-8

Aluminum phosphide

Aluminum phosphide

20859-73-8

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

P009

131-74-8

Ammonium picrate

Ammonium picrate

131-74-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P119

7803-55-6

Ammonium vanadate

Vanadium (measured in aqueous wastes only)

7440-62-2

4.3

STABL

P099

506-61-6

Argentate(1-), bis(cyano-C)-, potassium

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Silver

7440-22-4

0.43

0.14 mg/L TCLP

P010

7778-39-4

Arsenic acid H3AsO4

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P012

1327-53-3

Arsenic oxide As2O3

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P011

1303-28-2

Arsenic oxide As2O5

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P011

1303-28-2

Arsenic pentoxide

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P012

1327-53-3

Arsenic trioxide

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P038

692-42-2

Arsine, diethyl-

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P036

696-28-6

Arsonous dichloride, phenyl-

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P054

151-56-4

Aziridine

Aziridine

151-56-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P067

75-55-8

Aziridine, 2-methyl-

2-Methyl-aziridine

75-55-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P013

542-62-1

Barium cyanide

Barium

7440-39-3

NA

21 mg/L TCLP

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P024

106-47-8

Benzenamine, 4-chloro-

p-Chloroaniline

106-47-8

0.46

16

P077

100-01-6

Benzenamine, 4-nitro-

p-Nitroaniline

100-01-6

0.028

28

P028

100-44-7

Benzene, (chloromethyl)-

Benzyl chloride

100-44-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P046

122-09-8

Benzeneethanamine, alpha,alpha-dimethyl-

alpha, alpha-Dimethylphenethylamine

122-09-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P014

108-98-5

Benzenethiol

Thiophenol (Benzene thiol)

108-98-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P188

57-64-7

Benzoic acid, 2-hydroxy-, compd. With (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo[2,3-b]indol-5-yl methylcarbamate ester (1:1)

Physostigmine salicylate

57-64-7

0.056

1.4

P028

100-44-7

Benzyl chloride

Benzyl chloride

100-44-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P015

7440-41-7

Beryllium powder

Beryllium

7440-41-7

RMETL; or RTHRM

RMETL; or RTHRM

P017

598-31-2

Bromoacetone

Bromoacetone

598-31-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P018

357-57-3

Brucine

Brucine

357-57-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P021

592-01-8

Calcium cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P021

592-01-8

Calcium cyanide Ca(CN)2

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P189

55285-14-8

Carbamic acid, [(dibutylamino)-thio]methyl-, 2,3-dihydro-2,2-dimethyl- 7-benzofuranyl ester

Carbosulfan

55285-14-8

0.028

1.4

P191

644-64-4

Carbamic acid, dimethyl-, 1-[(dimethyl-amino)carbonyl]- 5-methyl-1H- pyrazol-3-yl este

Dimetilan

644-64-4

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

P190

1129-41-5

Carbamic acid, methyl-, 3-methylphenyl ester

Metolcarb

1129-41-5

0.056

1.4

P192

119-38-0

Carbamic acid,dimethyl-,3-methyl-1-(1methylethyl)-1H-pyrazol-5-yl ester

Isolan

119-38-0

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

P127

1563-66-2

Carbofuran

Carbofuran

1563-66-2

0.006

0.14

P022

75-15-0

Carbon disulfide

Carbon disulfide

75-15-0

3.8

CMBST or 4.8 mg/L TCLP

P095

75-44-5

Carbonic dichloride

Phosgene

75-44-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P189

55285-14-8

Carbosulfan

Carbosulfan

55285-14-8

0.028

1.4

P023

107-20-0

Chloroacetaldehyde

Chloroacetaldehyde

107-20-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P029

544-92-3

Copper cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P029

544-92-3

Copper cyanide Cu(CN)

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P030

N/A

Cyanides (soluble cyanide salts), not otherwise specified

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

       

P031

460-19-5

Cyanogen

Cyanogen

460-19-5

CHOXD: WETOX; or CMBST

CHOXD: WETOX; or CMBST

P033

506-77-4

Cyanogen chloride

Cyanogen chloride

506-77-4

CHOXD: WETOX; or CMBST

CHOXD: WETOX; or CMBST

P033

506-77-4

Cyanogen chloride (CN)Cl

Cyanogen chloride

506-77-4

CHOXD: WETOX; or CMBST

CHOXD: WETOX; or CMBST

P016

542-88-1

Dichloromethyl ether

Dichloromethyl ether

542-88-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P036

696-28-6

Dichlorophenylarsine

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P037

60-57-1

Dieldrin

Dieldrin

60-57-1

0.017

0.13

P038

692-42-2

Diethylarsine

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

P041

311-45-5

Diethyl-p-nitrophenyl phosphate

Diethyl-p-nitrophenyl phosphate

311-45-5

CARBN; or CMBST

CMBST

P043

55-91-4

Diisopropylfluorophosphate (DFP)

Diisopropylfluorophosphate (DFP)

55-91-4

CARBN; or CMBST

CMBST

P044

60-51-5

Dimethoate

Dimethoate

60-51-5

CARBN; or CMBST

CMBST

P191

644-64-4

Dimetilan

Dimetilan

644-64-4

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

P020

88-85-7

Dinoseb

2-sec-Butyl-4,6-dinitrophenol (Dinoseb)

88-85-7

0.066

2.5

P085

152-16-9

Diphosphoramide, octamethyl-

Octamethylpyrophosphoramide

152-16-9

CARBN; or CMBST

CMBST

P111

107-49-3

Diphosphoric acid, tetraethyl ester

Tetraethylpyrophosphate

107-49-3

CARBN; or CMBST

CMBST

P039

298-04-4

Disulfoton

Disulfoton

298-04-4

0.017

6.2

P049

541-53-7

Dithiobiuret

Dithiobiuret

541-53-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P050

115-29-7

Endosulfan

Endosulfan I

939-98-8

0.023

0.066

Endosulfan II

33213-6-5

0.029

0.13

Endosulfan sulfate

1031-07-8

0.029

0.13

P088

145-73-3

Endothall

Endothall

145-73-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P051

72-20-8

Endrin

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

P051

72-20-8

Endrin, & metabolites

Endrin

72-20-8

0.0028

0.13

Endrin aldehyde

7421-93-4

0.025

0.13

P042

51-43-4

Epinephrine

Epinephrine

51-43-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P031

460-19-5

Ethanedinitrile

Cyanogen

460-19-5

CHOXD: WETOX; or CMBST

CHOXD: WETOX; or CMBST

P194

23135-22-0

Ethanimidothioc acid, 2-(dimethylamino)-N-[[(methylamino)carbonyl]oxy]-2-oxo-, methyl ester

Oxamyl

23135-22-0

0.056

0.28

P066

16752-77-5

Ethanimidothioic acid, N-[[(methylamino)carbonyl]oxy]-,methyl ester

Methomyl

16752-77-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P101

107-12-0

Ethyl cyanide

Ethyl cyanide (Propanenitrile)

107-12-0

0.24

360

P054

151-56-4

Ethyleneimine

Aziridine

151-56-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P097

52-85-7

Famphur

Famphur

52-85-7

0.017

15

P056

7782-41-4

Fluorine

Fluoride (measured in aqueous wastes only)

16984-48-8

35

ADGAS fb NEUTR

P057

640-19-7

Fluoroacetamide

Fluoroacetamide

640-19-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P058

62-74-8

Fluoroacetic acid, sodium salt

Fluoroacetic acid, sodium salt

62-74-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P198

23422-53-9

Formetanate hydrochloride

Formetanate hydrochloride

23422-53-9

0.056

1.4

P197

17702-57-7

Formparanate

Formparante

17702-57-7

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

P065

628-86-4

Fulminic acid, mercury(2+) salt

Treatment Subcategory 1

Mercury fulminate non-aqueous wastes, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC:

Mercury

7439-97-6

NA

IMERC

Treatment Subcategory 2

Mercury fulminate non-aqueous wastes that are either incinerator residues or are residues from RMERC; and contain greater than or equal to 260 mg/kg total mercury:

Mercury

7439-97-6

NA

RMERC

Treatment Subcategory 3

Mercury fulminate non-aqueous wastes that are residues from RMERC and contain less than 260 mg/kg total mercury:

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Treatment Subcategory 4

Mercury fulminate non-aqueous wastes that are incinerator residues and contain less than 260 mg/kg total mercury:

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Treatment Subcategory 5

All mercury fulminate aqueous wastes:

Mercury

7439-97-6

0.15

NA

P059

76-44-8

Heptachlor

Heptachlor

76-44-8

0.0012

0.066

Heptachlor epoxide

1024-57-3

0.016

0.066

P062

757-58-4

Hexaethyl tetraphosphate

Hexaethyl tetraphosphate

757-58-4

CARBN; or CMBST

CMBST

P068

60-34-4

Hydrazine, methyl-

Methyl hydrazine

60-34-4

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P116

79-19-6

Hydrazinecarbothioamide

Thiosemicarbazide

79-19-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P063

74-90-8

Hydrocyanic acid

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P063

74-90-8

Hydrogen cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P096

7803-51-2

Hydrogen phosphide

Phosphine

7803-51-2

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

P060

465-73-6

Isodrin

Isodrin

465-73-6

0.021

0.066

P192

119-38-0

Isolan

Isolan

119-38-0

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

P196

15339-36-3

Manganese dimethyl dithiocarbamate

Dithiocarbamates (total)

NA

BIODG; CARBN; CHOXD; CMBST or 0.028

CMBST or 28

P196

15339-36-3

Manganese,bis(dimethylcarbamodithioato-S,S')-

Dithiocarbamates (total)

NA

BIODG; CARBN; CHOXD; CMBST or 0.028

CMBST or 28

P202

64-00-6

M-Cumenyl methylcarbamate

m-Cumenyl methylcarbamate

64-00-6

0.056

1.4

P065

628-86-4

Mercury fulminate

See Fulminic acid, mercury(2+) salt

P092

62-38-4

Mercury, (acetato-O)phenyl-

Treatment Subcategory 1

Phenyl mercuric acetate non-aqueous wastes, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC:

Mercury

7439-97-6

NA

IMERC; or RMERC

Treatment Subcategory 2

Phenyl mercuric acetate non-aqueous wastes that are either incinerator residues or are residues from RMERC; and still contain greater than or equal to 260 mg/kg total mercury:

Mercury

7439-97-6

NA

RMERC

Treatment Subcategory 3

Phenyl mercuric acetate non-aqueous wastes that are residues from RMERC and contain less than 260 mg/kg total mercury:

Mercury

7439-97-6

NA

0.20 mg/L TCLP

Treatment Subcategory 4

Phenyl mercuric acetate non-aqueous wastes that are incinerator residues and contain less than 260 mg/kg total mercury:

Mercury

7439-97-6

NA

0.025 mg/L TCLP

Treatment Subcategory 5

All phenyl mercuric acetate aqueous wastes:

Mercury

7439-97-6

0.15

NA

P082

62-75-9

Methanamine, N-methyl-N-nitroso-

N-Nitrosodimethylamine

62-75-9

0.4

2.3

P064

624-83-9

Methane, isocyanato-

Isocyanic acid, ethyl ester

624-83-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P016

542-88-1

Methane, oxybis[chloro-

Dichloromethyl ether

542-88-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P112

509-14-8

Methane, tetranitro-

Tetranitromethane

509-14-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P118

75-70-7

Methanethiol, trichloro-

Trichloromethanethiol

75-70-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P197

17702-57-7

Methanimidamide,N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]-

Formparante

17702-57-7

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

P198

23422-53-9

Methanimidamide,N,N-dimethyl-N'-[3-[[(methylamino)-carbonyl]oxy]phenyl]-, monohydrochloride

Formetanate hydrochloride

23422-53-9

0.056

1.4

P199

2032-65-7

Methiocarb

Methiocarb

2032-65-7

0.056

1.4

P066

16752-77-5

Methomyl

Methomyl

16752-77-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P068

60-34-4

Methyl hydrazine

Methyl hydrazine

60-34-4

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P064

624-83-9

Methyl isocyanate

Isocyanic acid, ethyl ester

624-83-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P071

298-00-0

Methyl parathion

Methyl parathion

298-00-0

0.014

4.6

P190

1129-41-5

Metolcarb

Metolcarb

1129-41-5

0.056

1.4

P128

315-18-4

Mexacarbate

Mexacarbate

315-18-4

0.056

1.4

P073

13463-39-3

Nickel carbonyl

Nickel

7440-02-0

3.98

11 mg/L TCLP

P073

13463-39-3

Nickel carbonyl Ni(CO)4,(T-4)-

Nickel

7440-02-0

3.98

11 mg/L TCLP

P074

557-19-7

Nickel cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Nickel

7440-02-0

3.98

11 mg/L TCLP

P074

557-19-7

Nickel cyanide Ni(CN)2

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Nickel

7440-02-0

3.98

11 mg/L TCLP

P075

54-11-5

Nicotine, & salts

Nicotine and salts

54-11-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P076

10102-43-9

Nitric oxide

Nitric oxide

10102-43-9

ADGAS

ADGAS

P078

10102-44-0

Nitrogen dioxide

Nitrogen dioxide

10102-44-0

ADGAS

ADGAS

P076

10102-43-9

Nitrogen oxide NO

Nitric oxide

10102-43-9

ADGAS

ADGAS

P078

10102-44-0

Nitrogen oxide NO2

Nitrogen dioxide

10102-44-0

ADGAS

ADGAS

P081

55-63-0

Nitroglycerine

Nitroglycerin

55-63-0

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P082

62-75-9

N-Nitrosodimethylamine

N-Nitrosodimethylamine

62-75-9

0.4

2.3

P084

4549-40-0

N-Nitrosomethylvinylamine

N-Nitrosomethylvinylamine

4549-40-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P040

297-97-2

O,O-Diethyl O-pyrazinyl phosphorothioate

0,0-Diethyl O-pyrazinyl phosphorothioate

297-97-2

CARBN; or CMBST

CMBST

P085

152-16-9

Octamethylpyrophosphoramide

Octamethylpyrophosphoramide

152-16-9

CARBN; or CMBST

CMBST

P087

20816-12-0

Osmium oxide OsO4,(T-4)-

Osmium tetroxide

20816-12-0

RMETL; or RTHRM

RMETL; or RTHRM

P087

20816-12-0

Osmium tetroxide

Osmium tetroxide

20816-12-0

RMETL; or RTHRM

RMETL; or RTHRM

P194

23135-22-0

Oxamyl

Oxamyl

23135-22-0

0.056

0.28

P089

56-38-2

Parathion

Parathion

56-38-2

0.014

4.6

P024

106-47-8

p-Chloroaniline

p-Chloroaniline

106-47-8

0.46

16

P020

88-85-7

Phenol, 2-(1-methylpropyl)-4,6-dinitro-

2-sec-Butyl-4,6-dinitrophenol (Dinoseb)

88-85-7

0.066

2.5

P009

131-74-8

Phenol, 2,4,6-trinitro-, ammonium salt

Ammonium picrate

131-74-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P048

51-28-5

Phenol, 2,4-dinitro-

2,4-Dinitrophenol

51-28-5

0.12

160

P034

131-89-5

Phenol, 2-cyclohexyl-4,6-dinitro-

2-Cyclohexyl-4,6-dinitrophenol

131-89-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P047

534-52-1

Phenol, 2-methyl-4,6-dinitro-, & salts

See 4,6-Dinitro-o-cresol, & salts

   

P202

64-00-6

Phenol, 3-(1-methylethyl)-, methyl carbamate

m-Cumenyl methylcarbamate

64-00-6

0.056

1.4

P201

2631-37-0

Phenol, 3-methyl-5-(1-methylethyl)-,methyl carbamate

Promecarb

2631-37-0

0.056

1.4

P199

2032-65-7

Phenol,(3,5-dimethyl-4-(methylthio)-,methylcarbamate

Methiocarb

2032-65-7

0.056

1.4

P128

315-18-4

Phenol,4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester)

Mexacarbate

315-18-4

0.056

1.4

P092

62-38-4

Phenylmercury acetate

See Mercury, (acetato-O)phenyl-

   

P093

103-85-5

Phenylthiourea

Phenylthiourea

103-85-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P094

298-02-2

Phorate

Phorate

298-02-2

0.021

4.6

P095

75-44-5

Phosgene

Phosgene

75-44-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P096

7803-51-2

Phosphine

Phosphine

7803-51-2

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

P041

311-45-5

Phosphoric acid, diethyl 4-nitrophenyl ester

Diethyl-p-nitrophenyl phosphate

311-45-5

CARBN; or CMBST

CMBST

P094

298-02-2

Phosphorodithioic acid, O,O-diethyl S-[(ethylthio)methyl] ester

Phorate

298-02-2

0.021

4.6

P039

298-04-4

Phosphorodithioic acid, O,O-diethyl S-[2-(ethylthio)ethyl] ester

Disulfoton

298-04-4

0.017

6.2

P044

60-51-5

Phosphorodithioic acid,O,O-dimethylS-[2-(methylamino)-2-oxoethyl] ester

Dimethoate

60-51-5

CARBN; or CMBST

CMBST

P043

55-91-4

Phosphorofluoridic acid, bis(1-methylethyl) ester

Diisopropylfluorophosphate (DFP)

55-91-4

CARBN; or CMBST

CMBST

P071

298-00-0

Phosphorothioic acid, O,O,-dimethyl O-(4-nitrophenyl) ester

Methyl parathion

298-00-0

0.014

4.6

P089

56-38-2

Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester

Parathion

56-38-2

0.014

4.6

P040

297-97-2

Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester

0,0-Diethyl O-pyrazinyl phosphorothioate

297-97-2

CARBN; or CMBST

CMBST

P097

52-85-7

Phosphorothioic acid, O-[4-[(dimethylamino)sulfonyl]phenyl] O,O-r dimethyl ester

Famphur

52-85-7

0.017

15

P188

57-64-7

Physostigmine salicylate.

Physostigmine salicylate

57-64-7

0.056

1.4

P204

57-47-6

Physostigmine.

Physostigmine

57-47-6

0.056

1.4

P110

78-00-2

Plumbane, tetraethyl-

Lead

7439-92-1

0.69

0.75 mg/L TCLP

P077

100-01-6

p-Nitroaniline

p-Nitroaniline

100-01-6

0.028

28

P098

151-50-8

Potassium cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P098

151-50-8

Potassium cyanide K(CN)

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P099

506-61-6

Potassium silver cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Silver

7440-22-4

0.43

0.14 mg/L TCLP

P201

2631-37-0

Promecarb

Promecarb

2631-37-0

0.056

1.4

P203

1646-88-4

Propanal,2-methyl-2-(methyl-sulfonyl)-,O-[(methylamino)carbonyl] oxime

Aldicarb sulfone

1646-88-4

0.056

0.28

P070

116-06-3

Propanal,2-methyl-2-(methylthio)-,O-[(methylamino)carbonyl]oxime

Aldicarb

116-06-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P101

107-12-0

Propanenitrile

Ethyl cyanide (Propanenitrile)

107-12-0

0.24

360

P069

75-86-5

Propanenitrile, 2-hydroxy-2-methyl-

2-Methyllactonitrile

75-86-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P027

542-76-7

Propanenitrile, 3-chloro-

3-Chloropropionitrile

542-76-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P102

107-19-7

Propargyl alcohol

Propargyl alcohol

107-19-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P075

54-11-5

Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)-, & salts

Nicotine and salts

54-11-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P204

57-47-6

Pyrrolo[2,3-b]indol-5-ol,1,2,3,3a,8,8a-hexahydro-1,3a,8- trimethyl-,methylcarbamate (ester),(3aS-cis)-

Physostigmine

57-47-6

0.056

1.4

P114

12039-52-0

Selenious acid, dithallium(1+) salt

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

P103

630-10-4

Selenourea

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

P104

506-64-9

Silver cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Silver

7440-22-4

0.43

0.14 mg/L TCLP

P104

506-64-9

Silver cyanide Ag(CN)

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

Silver

7440-22-4

0.43

0.14 mg/L TCLP

P105

26628-22-8

Sodium azide

Sodium azide

26628-22-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P106

143-33-9

Sodium cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P106

143-33-9

Sodium cyanide Na(CN)

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P108

57-24-9

Strychnidin-10-one, & salts

Strychnine and salts

57-24-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P018

357-57-3

Strychnidin-10-one, 2,3-dimethoxy-

Brucine

357-57-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P108

57-24-9

Strychnine, & salts

Strychnine and salts

57-24-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P115

7446-18-6

Sulfuric acid, dithallium(1+) salt

Thallium (measured in aqueous wastes only)

7440-28-0

1.4

RTHRM; or STABL

P110

78-00-2

Tetraethyl lead

Lead

7439-92-1

0.69

0.75 mg/L TCLP

P111

107-49-3

Tetraethyl pyrophosphate

Tetraethylpyrophosphate

107-49-3

CARBN; or CMBST

CMBST

P109

3689-24-5

Tetraethyldithiopyrophosphate

Tetraethyldithiopyrophosphate

3689-24-5

CARBN; or CMBST

CMBST

P112

509-14-8

Tetranitromethane

Tetranitromethane

509-14-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

P062

757-58-4

Tetraphosphoric acid, hexaethyl ester

Hexaethyl tetraphosphate

757-58-4

CARBN; or CMBST

CMBST

P113

1314-32-5

Thallic oxide

Thallium (measured in aqueous wastes only)

7440-28-0

1.4

RTHRM; or STABL

P113

1314-32-5

Thallium oxide Tl2O3

Thallium (measured in aqueous wastes only)

7440-28-0

1.4

RTHRM; or STABL

P114

12039-52-0

Thallium(I) selenite

Selenium

7782-49-2

0.82

5.7 mg/L TCLP

P115

7446-18-6

Thallium(I) sulfate

Thallium (measured in aqueous wastes only)

7440-28-0

1.4

RTHRM; or STABL

P109

3689-24-5

Thiodiphosphoric acid, tetraethyl ester

Tetraethyldithiopyrophosphate

3689-24-5

CARBN; or CMBST

CMBST

P045

39196-18-4

Thiofanox

Thiofanox

39196-18-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P049

541-53-7

Thioimidodicarbonic diamide [(H2N)C(S)]2NH

Dithiobiuret

541-53-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P014

108-98-5

Thiophenol

Thiophenol (Benzene thiol)

108-98-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P116

79-19-6

Thiosemicarbazide

Thiosemicarbazide

79-19-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P026

5344-82-1

Thiourea, (2-chlorophenyl)-

1-(o-Chlorophenyl)thiourea

5344-82-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P072

86-88-4

Thiourea, 1-naphthalenyl-

1-Naphthyl-2-thiourea

86-88-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P093

103-85-5

Thiourea, phenyl-

Phenylthiourea

103-85-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P185

26419-73-8

Tirpate

Tirpate

26419-73-8

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 0.28

P123

8001-35-2

Toxaphene

Toxaphene

8001-35-2

0.0095

2.6

P118

75-70-7

Trichloromethanethiol

Trichloromethanethiol

75-70-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P119

7803-55-6

Vanadic acid, ammonium salt

Vanadium (measured in aqueous wastes only))

7440-62-2

4.3

STABL

P120

1314-62-1

Vanadium oxide, V2O5

Vanadium (measured in aqueous wastes only)

7440-62-2

4.3

STABL

P120

1314-62-1

Vanadium pentoxide

Vanadium (measured in aqueous wastes only)

7440-62-2

4.3

STABL

P084

4549-40-0

Vinylamine, N-methyl-N-nitroso-

N-Nitrosomethylvinylamine

4549-40-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P001

81-81-2

Warfarin, & salts, when present at concentrations greater than 0.3%

Warfarin

81-81-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

P121

557-21-1

Zinc cyanide

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P121

557-21-1

Zinc cyanide Zn(CN)2

Cyanides (Total)7

57-12-5

1.2

590

Cyanides (Amenable)7

57-12-5

0.86

30

P122

1314-84-7

Zinc phosphide Zn3P2, when present at concentrations greater than 10%

Zinc Phosphide

1314-84-7

CHOXD; CHRED; or CMBST

CHOXD; CHRED; or CMBST

P205

137-30-4

Zinc, bis(dimethylcarbamodithioato-S,S')-

Dithiocarbamates (total)

NA

0.028

28

P205

137-30-4

Ziram

Dithiocarbamates (total)

NA

0.028

28

Notes to Part A of Schedule 2:

1 Treatment subcategories are shown for some wastes. In these cases, it is necessary to identify the treatment subcategory that most closely describes the particular waste for which treatment is required. The land disposal treatment requirements for that waste are those shown for that treatment subcategory.

2 Haz. Waste Number means Hazardous Waste Number. These numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment.

3 CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only.

4 See Schedule 7 for a description of the treatment methods and treatment standards associated with each treatment code. In some cases, the entries in this Schedule may set out more than one treatment code for a regulated constituent. An entry may permit a choice of treatment methods. For example, the entry “CHOXD; BIODG; or CMBST” means that the waste may be treated using any of the treatment methods that are set out for those treatment codes in Schedule 7. An entry may require treatment methods to be applied in a particular sequence. For this purpose, the abbreviation “fb” means “followed by”. For example, the entry “CHOXD fb CARBN” means that the waste must first be treated using the treatment method that is set out for CHOXD in Schedule 7 and, following that treatment, it must be treated using the treatment method that is set out for CARBN in Schedule 7. An entry may combine a choice of treatment methods and a requirement to apply treatment methods in a particular sequence (for example, “(WETOX or CHOXD) fb CARBN; or CMBST”).

5 Concentration requirements for aqueous wastes are based on analysis of composite samples.

6 Concentration requirements for non-aqueous wastes are based on analysis of grab samples.

7 Both Cyanides (Total) and Cyanides (Amenable) for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes.

SCHEDULE 2
PART B — HAZARDOUS WASTE CHEMICAL

Hazardous Waste Chemical

Regulated Constituents
(and Treatment Subcategories1)

Land Disposal Treatment Requirements

   

Aqueous Waste

Non-aqueous Waste

Column 1

Column 2

Column 3

Column 4

Column 5

Column 6

Column 7

Haz. Waste Number2

CAS Number3

Generic Name

Generic Name or other description

CAS Number3

Treatment Code4 or Concentration5 (mg/L)

Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated)

U021

92-87-5

[1,1-Biphenyl]-4,4-diamine

Benzidine

92-87-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U073

91-94-1

[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dichloro-

3,3'-Dichlorobenzidine

91-94-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U091

119-90-4

[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethoxy-

3,3'-Dimethoxybenzidine

119-90-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U095

119-93-7

[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethyl-

3,3'-Dimethylbenzidine

119-93-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U208

630-20-6

1,1,1,2-Tetrachloroethane

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

U209

79-34-5

1,1,2,2-Tetrachloroethane

1,1,2,2-Tetrachloroethane

79-34-5

0.057

6.0

U227

79-00-5

1,1,2-Trichloroethane

1,1,2-Trichloroethane

79-00-5

0.054

6.0

U078

75-35-4

1,1-Dichloroethylene

1,1-Dichloroethylene

75-35-4

0.025

6.0

U098

57-14-7

1,1-Dimethylhydrazine

1,1-Dimethylhydrazine

57-14-7

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U207

95-94-3

1,2,4,5-Tetrachlorobenzene

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

U085

1464-53-5

1,2:3,4-Diepoxybutane

1,2:3,4-Diepoxybutane

1464-53-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U069

84-74-2

1,2-Benzenedicarboxylic acid, dibutyl ester

Di-n-butyl phthalate

84-74-2

0.057

28

U088

84-66-2

1,2-Benzenedicarboxylic acid, diethyl ester

Diethyl phthalate

84-66-2

0.20

28

U102

131-11-3

1,2-Benzenedicarboxylic acid, dimethyl ester

Dimethyl phthalate

131-11-3

0.047

28

U107

117-84-0

1,2-Benzenedicarboxylic acid, dioctyl ester

Di-n-octyl phthalate

117-84-0

0.017

28

U028

117-81-7

1,2-Benzenedicarboxylic acid,bis(2-ethylhexyl) ester

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

U202

81-07-2

1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, & salts

Saccharin

81-07-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U066

96-12-8

1,2-Dibromo-3-chloropropane

1,2-Dibromo-3-chloropropane

96-12-8

0.11

15

U079

156-60-5

1,2-Dichloroethylene

trans-1,2-Dichloroethylene

156-60-5

0.054

30

U099

540-73-8

1,2-Dimethylhydrazine

1,2-Dimethylhydrazine

540-73-8

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U109

122-66-7

1,2-Diphenylhydrazine

1,2-Diphenylhydrazine

122-66-7

CHOXD; CHRED; CARBN; BIODG; CMBST or 0.087

CHOXD; CHRED; or CMBST

U155

91-80-5

1,2-Ethanediamine,N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)-

Methapyrilene

91-80-5

0.081

1.5

U193

1120-71-4

1,2-Oxathiolane, 2,2-dioxide

1,3-Propane sultone

1120-71-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U142

143-50-0

1,3,4-Metheno-2H-cyclobuta[cd]pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro-

Kepone

143-50-0

0.0011

0.13

U234

99-35-4

1,3,5-Trinitrobenzene

1,3,5-Trinitrobenzene

99-35-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U182

123-63-7

1,3,5-Trioxane, 2,4,6-trimethyl-

Paraldehyde

123-63-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U201

108-46-3

1,3-Benzenediol

Resorcinol

108-46-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U364

22961-82-6

1,3-Benzodioxol-4-ol, 2,2-dimethyl-,

Bendiocarb phenol

22961-82-6

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

U278

22781-23-3

1,3-Benzodioxol-4-ol, 2,2-dimethyl-,methyl carbamate

Bendiocarb

22781-23-3

0.056

1.4

U141

120-58-1

1,3-Benzodioxole, 5-(1-propenyl)-

Isosafrole

120-58-1

0.081

2.6

U203

94-59-7

1,3-Benzodioxole, 5-(2-propenyl)-

Safrole

94-59-7

0.081

22

U090

94-58-6

1,3-Benzodioxole, 5-propyl-

Dihydrosafrole

94-58-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U128

87-68-3

1,3-Butadiene, 1,1,2,3,4,4-hexachloro-

Hexachlorobutadiene

87-68-3

0.055

5.6

U130

77-47-4

1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro-

Hexachlorocyclopentadiene

77-47-4

0.057

2.4

U084

542-75-6

1,3-Dichloropropene

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

U190

85-44-9

1,3-Isobenzofurandione

Phthalic anhydride (measured as Phthalic acid or Terephthalic acid)

100-21-0; 85-44-9

0.055

28

U186

504-60-9

1,3-Pentadiene

1,3-Pentadiene

504-60-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U193

1120-71-4

1,3-Propane sultone

1,3-Propane sultone

1120-71-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U074

764-41-0

1,4-Dichloro-2-butene

cis,1,4-Dichloro-2-butene

1476-11-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

trans-1,4-Dichloro-2-butene

764-41-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U108

123-91-1

1,4-Diethyleneoxide

1,4-Dioxane

123-91-1

(WETOX or CHOXD) fb CARBN; or CMBST or 12

CMBST or 170

U108

123-91-1

1,4-Dioxane

1,4-Dioxane

123-91-1

(WETOX or CHOXD) fb CARBN; or CMBST or 12

CMBST or 170

U166

130-15-4

1,4-Naphthalenedione

1,4-Naphthoquinone

130-15-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U166

130-15-4

1,4-Naphthoquinone

1,4-Naphthoquinone

130-15-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U172

924-16-3

1-Butanamine, N-butyl-N-nitroso-

N-Nitroso-di-n-butylamine

924-16-3

0.04

17

U031

71-36-3

1-Butanol

n-Butyl alcohol

71-36-3

5.6

2.6

U011

61-82-5

1H-1,2,4-Triazol-3-amine

Amitrole

61-82-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U186

504-60-9

1-Methylbutadiene

1,3-Pentadiene

504-60-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U167

134-32-7

1-Naphthalenamine

1-Naphthylamine

134-32-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U279

63-25-2

1-Naphthalenol, methylcarbamate

Carbaryl

63-25-2

0.006

0.14

U194

107-10-8

1-Propanamine

n-Propylamine

107-10-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U111

621-64-7

1-Propanamine, N-nitroso-N-propyl-

Di-n-propylnitrosamine

621-64-7

0.40

14

U110

142-84-7

1-Propanamine, N-propyl-

Dipropylamine

142-84-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U235

126-72-7

1-Propanol, 2,3-dibromo-, phosphate (3:1)

Tris(2,3-Dibromopropyl) phosphate

126-72-7

0.11

0.10

U140

78-83-1

1-Propanol, 2-methyl-

Isobutyl alcohol

78-83-1

5.6

170

U243

1888-71-7

1-Propene, 1,1,2,3,3,3-hexachloro-

Hexachloropropylene

1888-71-7

0.035

30

U084

542-75-6

1-Propene, 1,3-dichloro-

cis-1,3-Dichloropropylene

10061-01-5

0.036

18

trans-1,3-Dichloropropylene

10061-02-6

0.036

18

U085

1464-53-5

2,2-Bioxirane

1,2:3,4-Diepoxybutane

1464-53-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

See F027

58-90-2

2,3,4,6-Tetrachlorophenol

See F027 in Schedule 1

     

U237

66-75-1

2,4-(1H,3H)-Pyrimidinedione, 5-[bis(2-chloroethyl)amino]-

Uracil mustard

66-75-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

See F027

93-76-5

2,4,5-T

See F027 in Schedule 1

     

See F027

95-95-4

2,4,5-Trichlorophenol

See F027 in Schedule 1

     

See F027

88-06-2

2,4,6-Trichlorophenol

See F027 in Schedule 1

     

U240

94-75-7

2,4-D, salts & esters

Treatment Subcategory 1

2,4-D (2,4-Dichlorophenoxyacetic acid):

2,4-D(2,4-Dichlorophenoxyacetic acid)

94-75-7

0.72

10

Treatment Subcategory 2

2,4-D (2,4-Dichlorophenoxyacetic acid) salts and esters:

2,4-D (2,4-Dichlorophenoxyacetic acid) salts and esters

NA

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U081

120-83-2

2,4-Dichlorophenol

2,4-Dichlorophenol

120-83-2

0.044

14

U101

105-67-9

2,4-Dimethylphenol

2,4-Dimethylphenol

105-67-9

0.036

14

U105

121-14-2

2,4-Dinitrotoluene

2,4-Dinitrotoluene

121-14-2

0.32

140

U197

106-51-4

2,5-Cyclohexadiene-1,4-dione

p-Benzoquinone

106-51-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U147

108-31-6

2,5-Furandione

Maleic anhydride

108-31-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U082

87-65-0

2,6-Dichlorophenol

2,6-Dichlorophenol

87-65-0

0.044

14

U106

606-20-2

2,6-Dinitrotoluene

2,6-Dinitrotoluene

606-20-2

0.55

28

U236

72-57-1

2,7-Naphthalenedisulfonic acid, 3,3'-[(3,3'-dimethyl[1,1'-biphenyl]-4,4'-diyl)bis(azo)bis[5-amino-4-hydroxy]-,tetrasodium salt

Trypan Blue

72-57-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U005

53-96-3

2-Acetylaminofluorene

2-Acetylaminofluorene

53-96-3

0.059

140

U159

78-93-3

2-Butanone

Methyl ethyl ketone

78-93-3

0.28

36

U160

1338-23-4

2-Butanone, peroxide

Methyl ethyl ketone peroxide

1338-23-4

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U053

4170-30-3

2-Butenal

Crotonaldehyde

4170-30-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U074

764-41-0

2-Butene, 1,4-dichloro-

cis,1,4-Dichloro-2-butene

1476-11-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

trans-1,4-Dichloro-2-butene

764-41-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U143

303-34-4

2-Butenoic acid, 2-methyl-, 7-[[2,3-dihydroxy-2-(1-methoxyethyl)-3-methyl-1-oxobutoxy]methyl]-2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl ester,[1S-[1alpha(Z),7(2S*,3R*), 7aalpha]]-

Lasiocarpine

303-34-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U042

110-75-8

2-Chloroethyl vinyl ether

2-Chloroethyl vinyl ether

110-75-8

0.062

CMBST

U125

98-01-1

2-Furancarboxaldehyde

Furfural

98-01-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U058

50-18-0

2H-1,3,2-Oxazaphosphorin-2-amine,N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide

Cyclophosphamide

50-18-0

CARBN; or CMBST

CMBST

U248

81-81-2

2H-1-Benzopyran-2-one,4-hydroxy-3-(3-oxo-1-phenyl-butyl)-, & salts, when present at concentrations of 0.3% or less

Warfarin

81-81-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U116

96-45-7

2-Imidazolidinethione

Ethylene thiourea

96-45-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U168

91-59-8

2-Naphthalenamine

2-Naphthylamine

91-59-8

0.52

CMBST

U171

79-46-9

2-Nitropropane

2-Nitropropane

79-46-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U191

109-06-8

2-Picoline

2-Picoline

109-06-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U002

67-64-1

2-Propanone

Acetone

67-64-1

0.28

160

U007

79-06-1

2-Propenamide

Acrylamide

79-06-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U009

107-13-1

2-Propenenitrile

Acrylonitrile

107-13-1

0.24

84

U152

126-98-7

2-Propenenitrile, 2-methyl-

Methacrylonitrile

126-98-7

0.24

84

U008

79-10-7

2-Propenoic acid

Acrylic acid

79-10-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U118

97-63-2

2-Propenoic acid, 2-methyl-, ethyl ester

Ethyl methacrylate

97-63-2

0.14

160

U162

80-62-6

2-Propenoic acid, 2-methyl-, methyl ester

Methyl methacrylate

80-62-6

0.14

160

U113

140-88-5

2-Propenoic acid, ethyl ester

Ethyl acrylate

140-88-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U073

91-94-1

3,3'-Dichlorobenzidine

3,3'-Dichlorobenzidine

91-94-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U091

119-90-4

3,3'-Dimethoxybenzidine

3,3'-Dimethoxybenzidine

119-90-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U095

119-93-7

3,3'-Dimethylbenzidine

3,3'-Dimethylbenzidine

119-93-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U148

123-33-1

3,6-Pyridazinedione, 1,2-dihydro-

Maleic hydrazide

123-33-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U157

56-49-5

3-Methylcholanthrene

3-Methylcholanthrene

56-49-5

0.0055

15

U164

56-04-2

4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo-

Methylthiouracil

56-04-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U158

101-14-4

4,4'-Methylenebis(2-chloroaniline)

4,4'-Methylene bis(2-chloroaniline)

101-14-4

0.50

30

U036

57-74-9

4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro-

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

U030

101-55-3

4-Bromophenyl phenyl ether

4-Bromophenyl phenyl ether

101-55-3

0.055

15

U049

3165-93-3

4-Chloro-o-toluidine, hydrochloride

4-Chloro-o-toluidine hydrochloride

3165-93-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U161

108-10-1

4-Methyl-2-pentanone

Methyl isobutyl ketone

108-10-1

0.14

33

U059

20830-81-3

5,12-Naphthacenedione,8-acetyl-10-[(3-amino-2,3,6-trideoxy)-alpha-L-lyxo-hexopyranosyl)oxy]-7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-methoxy-, (8S-cis)-

Daunomycin

20830-81-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U181

99-55-8

5-Nitro-o-toluidine

5-Nitro-o-toluidine

99-55-8

0.32

28

U094

57-97-6

7,12-Dimethylbenz[a]anthracene

7,12-Dimethylbenz(a)anthracene

57-97-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U367

1563-38-8

7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-

Carbofuran phenol

1563-38-8

0.056

1.4

U394

30558-43-1

A2213

A2213

30558-43-1

BIODG; CARBN; CHOXD; CMBST or 0.042

CMBST or 1.4

U001

75-07-0

Acetaldehyde

Acetaldehyde

75-07-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U034

75-87-6

Acetaldehyde, trichloro-

Trichloroacetaldehyde (Chloral)

75-87-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U187

62-44-2

Acetamide, N-(4-ethoxyphenyl)-

Phenacetin

62-44-2

0.081

16

U005

53-96-3

Acetamide, N-9H-fluoren-2-yl-

2-Acetylaminofluorene

53-96-3

0.059

140

U112

141-78-6

Acetic acid ethyl ester

Ethyl acetate

141-78-6

0.34

33

See F027

93-76-5

Acetic acid, (2,4,5-trichlorophenoxy)-

See F027 in Schedule 1

     

U240

94-75-7

Acetic acid, (2,4-dichlorophenoxy)-,salts & esters

See 2,4-D, salts & esters

     

U144

301-04-2

Acetic acid, lead(2+) salt

Lead

7439-92-1

0.69

0.75 mg/L TCLP

U214

563-68-8

Acetic acid, thallium(1+) salt

Thallium (measured in aqueous wastes only)

7440-28-0

1.4

RTHRM; or STABL

U002

67-64-1

Acetone

Acetone

67-64-1

0.28

160

U003

75-05-8

Acetonitrile

Acetonitrile

75-05-8

5.6

CMBST or 38

U004

98-86-2

Acetophenone

Acetophenone

98-86-2

0.010

9.7

U006

75-36-5

Acetyl chloride

Acetyl Chloride

75-36-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U007

79-06-1

Acrylamide

Acrylamide

79-06-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U008

79-10-7

Acrylic acid

Acrylic acid

79-10-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U009

107-13-1

Acrylonitrile

Acrylonitrile

107-13-1

0.24

84

U096

80-15-9

alpha,alpha-Dimethylbenzylhydroperoxide

alpha, alpha-Dimethyl benzyl hydroperoxide

80-15-9

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U167

134-32-7

alpha-Naphthylamine

1-Naphthylamine

134-32-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U011

61-82-5

Amitrole

Amitrole

61-82-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U012

62-53-3

Aniline

Aniline

62-53-3

0.81

14

U136

75-60-5

Arsinic acid, dimethyl-

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

U014

492-80-8

Auramine

Auramine

492-80-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U015

115-02-6

Azaserine

Azaserine

115-02-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U010

50-07-7

Azirino[2,3_3,4]pyrrolo[1,2-a]indole-4,7-dione,6-amino-8-[[(aminocarbonyl)oxy]methyl]-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, [1aS-(1aalpha,8beta,8aalpha,8balpha)]-

Mitomycin C

50-07-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U280

101-27-9

Barban

Barban

101-27-9

0.056

1.4

U278

22781-23-3

Bendiocarb

Bendiocarb

22781-23-3

0.056

1.4

U364

22961-82-6

Bendiocarb phenol

Bendiocarb phenol

22961-82-6

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

U271

17804-35-2

Benomyl

Benomyl

17804-35-2

0.056

1.4

U018

56-55-3

Benz[a]anthracene

Benz(a)anthracene

56-55-3

0.059

3.4

U094

57-97-6

Benz[a]anthracene, 7,12-dimethyl-

7,12-Dimethylbenz(a)anthracene

57-97-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U016

225-51-4

Benz[c]acridine

Benz(c)acridine

225-51-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U157

56-49-5

Benz[j]aceanthrylene, 1,2-dihydro-3-methyl-

3-Methylcholanthrene

56-49-5

0.0055

15

U017

98-87-3

Benzal chloride

Benzal chloride

98-87-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U192

23950-58-5

Benzamide,3,5-dichloro-N-(1,1-dimethyl-2-propynyl)-

Pronamide

23950-58-5

0.093

1.5

U012

62-53-3

Benzenamine

Aniline

62-53-3

0.81

14

U328

95-53-4

Benzenamine, 2-methyl-

o-Toluidine

95-53-4

CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN.

CMBST

U222

636-21-5

Benzenamine, 2-methyl-, hydrochloride

o-Toluidine hydrochloride

636-21-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U181

99-55-8

Benzenamine, 2-methyl-5-nitro-

5-Nitro-o-toluidine

99-55-8

0.32

28

U014

492-80-8

Benzenamine, 4,4-carbonimidoylbis[N,N-dimethyl-

Auramine

492-80-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U158

101-14-4

Benzenamine, 4,4-methylenebis[2-chloro-

4,4'-Methylene bis(2-chloroaniline)

101-14-4

0.50

30

U049

3165-93-3

Benzenamine, 4-chloro-2-methyl-,hydrochloride

4-Chloro-o-toluidine hydrochloride

3165-93-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U353

106-49-0

Benzenamine, 4-methyl-

p-Toluidine

106-49-0

CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN.

CMBST

U093

60-11-7

Benzenamine, N,N-dimethyl-4-(phenylazo)-

p-Dimethylaminoazobenzene

60-11-7

0.13

CMBST

U019

71-43-2

Benzene

Benzene

71-43-2

0.14

10

U055

98-82-8

Benzene, (1-methylethyl)-

Cumene

98-82-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U017

98-87-3

Benzene, (dichloromethyl)-

Benzal chloride

98-87-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U023

98-07-7

Benzene, (trichloromethyl)-

Benzotrichloride

98-07-7

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U247

72-43-5

Benzene, 1,1-(2,2,2-trichloroethylidene)bis[4- methoxy-

Methoxychlor

72-43-5

0.25

0.18

U207

95-94-3

Benzene, 1,2,4,5-tetrachloro-

1,2,4,5-Tetrachlorobenzene

95-94-3

0.055

14

U070

95-50-1

Benzene, 1,2-dichloro-

o-Dichlorobenzene

95-50-1

0.088

6.0

U234

99-35-4

Benzene, 1,3,5-trinitro-

1,3,5-Trinitrobenzene

99-35-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U071

541-73-1

Benzene, 1,3-dichloro-

m-Dichlorobenzene

541-73-1

0.036

6.0

U223

26471-62-5

Benzene, 1,3-diisocyanatomethyl-

Toluene diisocyanate

26471-62-5

CARBN; or CMBST

CMBST

U072

106-46-7

Benzene, 1,4-dichloro-

p-Dichlorobenzene

106-46-7

0.09

6.0

U030

101-55-3

Benzene, 1-bromo-4-phenoxy-

4-Bromophenyl phenyl ether

101-55-3

0.055

15

U105

121-14-2

Benzene, 1-methyl-2,4-dinitro-

2,4-Dinitrotoluene

121-14-2

0.32

140

U106

606-20-2

Benzene, 2-methyl-1,3-dinitro-

2,6-Dinitrotoluene

606-20-2

0.55

28

U037

108-90-7

Benzene, chloro-

Chlorobenzene

108-90-7

0.057

60

U239

1330-20-7

Benzene, dimethyl-

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

U127

118-74-1

Benzene, hexachloro-

Hexachlorobenzene

118-74-1

0.055

10

U056

110-82-7

Benzene, hexahydro-

Cyclohexane

110-82-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U220

108-88-3

Benzene, methyl-

Toluene

108-88-3

0.08

10

U169

98-95-3

Benzene, nitro-

Nitrobenzene

98-95-3

0.068

14

U183

608-93-5

Benzene, pentachloro-

Pentachlorobenzene

608-93-5

0.055

10

U185

82-68-8

Benzene, pentachloronitro-

Pentachloronitrobenzene

82-68-8

0.055

4.8

U061

50-29-3

Benzene,1,1-(2,2,2-trichloroethylidene)bis[4-chloro-

o,p'-DDT

789-02-6

0.0039

0.087

p,p'-DDT

50-29-3

0.0039

0.087

o,p'-DDD

53-19-0

0.023

0.087

p,p'-DDD

72-54-8

0.023

0.087

o,p'-DDE

3424-82-6

0.031

0.087

p,p'-DDE

72-55-9

0.031

0.087

U060

72-54-8

Benzene,1,1-(2,2-dichloroethylidene)bis[4-chloro-

o,p'-DDD

53-19-0

0.023

0.087

p,p'-DDD

72-54-8

0.023

0.087

       

U038

510-15-6

Benzeneacetic acid,4-chloro-alpha- (4-chlorophenyl)-alpha-hydroxy-, ethyl ester

Chlorobenzilate

510-15-6

0.10

CMBST

U035

305-03-3

Benzenebutanoic acid, 4-[bis(2-chloroethyl)amino]-

Chlorambucil

305-03-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U221

25376-45-8

Benzenediamine, ar-methyl-

Toluenediamine

25376-45-8

CARBN; or CMBST

CMBST

U020

98-09-9

Benzenesulfonic acid chloride

Benzenesulfonyl chloride

98-09-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U020

98-09-9

Benzenesulfonyl chloride

Benzenesulfonyl chloride

98-09-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U021

92-87-5

Benzidine

Benzidine

92-87-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U022

50-32-8

Benzo[a]pyrene

Benzo(a)pyrene

50-32-8

0.061

3.4

U064

189-55-9

Benzo[rst]pentaphene

Dibenz(a,i)pyrene

189-55-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U023

98-07-7

Benzotrichloride

Benzotrichloride

98-07-7

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U047

91-58-7

beta-Chloronaphthalene

2-Chloronaphthalene

91-58-7

0.055

5.6

U168

91-59-8

beta-Naphthylamine

2-Naphthylamine

91-59-8

0.52

CMBST

U225

75-25-2

Bromoform

Bromoform (Tribromomethane)

75-25-2

0.63

15

U136

75-60-5

Cacodylic acid

Arsenic

7440-38-2

1.4

5.0 mg/L TCLP

U032

13765-19-0

Calcium chromate

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

U280

101-27-9

Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester

Barban

101-27-9

0.056

1.4

U409

23564-05-8

Carbamic acid, [1,2-phenylenebis (iminocarbonothioyl)]bis-, dimethyl ester

Thiophanate-methyl

23564-05-8

0.056

1.4

U271

17804-35-2

Carbamic acid, [1-[(butylamino)carbonyl]-1H-benzimidazol-2-yl]-, methyl ester

Benomyl

17804-35-2

0.056

1.4

U372

10605-21-7

Carbamic acid, 1H-benzimidazol-2-yl,methyl ester

Carbendazim

10605-21-7

0.056

1.4

U238

51-79-6

Carbamic acid, ethyl ester

Urethane (Ethyl carbamate)

51-79-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U178

615-53-2

Carbamic acid, methylnitroso-, ethyl ester

N-Nitroso-N-methylurethane

615-53-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U373

122-42-9

Carbamic acid, phenyl-, 1-methylethyl ester

Propham

122-42-9

0.056

1.4

U097

79-44-7

Carbamic chloride, dimethyl-

Dimethylcarbamoyl chloride

79-44-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U114

111-54-6

Carbamodithioic acid, 1,2-ethanediylbis-,salts & esters

Ethylenebisdithiocarbamic acid

111-54-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U389

2303-17-5

Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl)ester

Triallate

2303-17-5

0.042

1.4

U062

2303-16-4

Carbamothioic acid, bis(1-methylethyl)-S-(2,3-dichloro-2-propenyl) ester

Diallate

2303-16-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U387

52888-80-9

Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester

Prosulfocarb

52888-80-9

0.042

1.4

U279

63-25-2

Carbaryl.

Carbaryl

63-25-2

0.006

0.14

U372

10605-21-7

Carbendazim

Carbendazim

10605-21-7

0.056

1.4

U367

1563-38-8

Carbofuran phenol

Carbofuran phenol

1563-38-8

0.056

1.4

U033

353-50-4

Carbon oxyfluoride

Carbon oxyfluoride

353-50-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U211

56-23-5

Carbon tetrachloride

Carbon tetrachloride

56-23-5

0.057

6.0

U215

6533-73-9

Carbonic acid, dithallium(1+) salt

Thallium (measured in aqueous wastes only)

7440-28-0

1.4

RTHRM; or STABL

U033

353-50-4

Carbonic difluoride

Carbon oxyfluoride

353-50-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U156

79-22-1

Carbonochloridic acid, methyl ester

Methyl chlorocarbonate

79-22-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U034

75-87-6

Chloral

Trichloroacetaldehyde (Chloral)

75-87-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U035

305-03-3

Chlorambucil

Chlorambucil

305-03-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U036

57-74-9

Chlordane, alpha & gamma isomers

Chlordane (alpha and gamma isomers)

57-74-9

0.0033

0.26

U026

494-03-1

Chlornaphazin

Chlornaphazine

494-03-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U037

108-90-7

Chlorobenzene

Chlorobenzene

108-90-7

0.057

60

U038

510-15-6

Chlorobenzilate

Chlorobenzilate

510-15-6

0.10

CMBST

U044

67-66-3

Chloroform

Chloroform

67-66-3

0.046

6.0

U046

107-30-2

Chloromethyl methyl ether

Chloromethyl methyl ether

107-30-2

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U032

13765-19-0

Chromic acid H2CrO4, calcium salt

Chromium (Total)

7440-47-3

2.77

0.60 mg/L TCLP

U050

218-01-9

Chrysene

Chrysene

218-01-9

0.059

3.4

U051

N/A

Creosote

Naphthalene

91-20-3

0.059

5.6

Pentachlorophenol

87-86-5

0.089

7.4

Phenanthrene

85-01-8

0.059

5.6

Pyrene

129-00-0

0.067

8.2

Toluene

108-88-3

0.08

10

Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations)

1330-20-7

0.32

30

Lead

7439-92-1

0.69

0.75 mg/L TCLP

U052

1319-77-3

Cresol (Cresylic acid)

o-Cresol

95-48-7

0.11

5.6

m-Cresol (difficult to distinguish from p-cresol)

108-39-4

0.77

5.6

p-Cresol (difficult to distinguish from m-cresol)

106-44-5

0.77

5.6

Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations)

1319-77-3

0.88

11.2

U053

4170-30-3

Crotonaldehyde

Crotonaldehyde

4170-30-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U055

98-82-8

Cumene

Cumene

98-82-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U246

506-68-3

Cyanogen bromide (CN)Br

Cyanogen bromide

506-68-3

CHOXD; WETOX; or CMBST

CHOXD; WETOX; or CMBST

U056

110-82-7

Cyclohexane

Cyclohexane

110-82-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U129

58-89-9

Cyclohexane, 1,2,3,4,5,6-hexachloro-,(1alpha,2alpha,3beta,4alpha,5alpha,6 beta)-

alpha-BHC

319-84-6

0.00014

0.066

beta-BHC

319-85-7

0.00014

0.066

delta-BHC

319-86-8

0.023

0.066

gamma-BHC (Lindane)

58-89-9

0.0017

0.066

U057

108-94-1

Cyclohexanone

Cyclohexanone

108-94-1

0.36

CMBST or 0.75 mg/L TCLP

U058

50-18-0

Cyclophosphamide

Cyclophosphamide

50-18-0

CARBN; or CMBST

CMBST

U059

20830-81-3

Daunomycin

Daunomycin

20830-81-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U060

72-54-8

DDD

o,p'-DDD

53-19-0

0.023

0.087

p,p'-DDD

72-54-8

0.023

0.087

U061

50-29-3

DDT

o,p'-DDT

789-02-6

0.0039

0.087

p,p'-DDT

50-29-3

0.0039

0.087

o,p'-DDD

53-19-0

0.023

0.087

p,p'-DDD

72-54-8

0.023

0.087

o,p'-DDE

3424-82-6

0.031

0.087

p,p'-DDE

72-55-9

0.031

0.087

U206

18883-66-4

D-Glucose,2-deoxy-2-[[(methylnitrosoamino)-carbonyl]amino]-

Streptozotocin

18883-66-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U062

2303-16-4

Diallate

Diallate

2303-16-4

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U063

53-70-3

Dibenz[a,h]anthracene

Dibenz(a,h)anthracene

53-70-3

0.055

8.2

U064

189-55-9

Dibenzo[a,i]pyrene

Dibenz(a,i)pyrene

189-55-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U069

84-74-2

Dibutyl phthalate

Di-n-butyl phthalate

84-74-2

0.057

28

U075

75-71-8

Dichlorodifluoromethane

Dichlorodifluoromethane

75-71-8

0.23

7.2

U025

111-44-4

Dichloroethyl ether

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

U027

108-60-1

Dichloroisopropyl ether

bis(2-Chloroisopropyl)ether

39638-32-9

0.055

7.2

U024

111-91-1

Dichloromethoxy ethane

bis(2-Chloroethoxy)methane

111-91-1

0.036

7.2

U088

84-66-2

Diethyl phthalate

Diethyl phthalate

84-66-2

0.20

28

U395

5952-26-1

Diethylene glycol, dicarbamate

Diethylene glycol, dicarbamate

5952-26-1

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

U028

117-81-7

Diethylhexyl phthalate

bis(2-Ethylhexyl) phthalate

117-81-7

0.28

28

U089

56-53-1

Diethyl stilbesterol

Diethyl stilbestrol

56-53-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U090

94-58-6

Dihydrosafrole

Dihydrosafrole

94-58-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U102

131-11-3

Dimethyl phthalate

Dimethyl phthalate

131-11-3

0.047

28

U103

77-78-1

Dimethyl sulfate

Dimethyl sulfate

77-78-1

CHOXD; CHRED; CARBN; BIODG; or CMBST

CHOXD; CHRED; or CMBST

U092

124-40-3

Dimethylamine

Dimethylamine

124-40-3

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U097

79-44-7

Dimethylcarbamoyl chloride

Dimethylcarbamoyl chloride

79-44-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U107

117-84-0

Di-n-octyl phthalate

Di-n-octyl phthalate

117-84-0

0.017

28

U111

621-64-7

Di-n-propylnitrosamine

Di-n-propylnitrosamine

621-64-7

0.40

14

U110

142-84-7

Dipropylamine

Dipropylamine

142-84-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U041

106-89-8

Epichlorohydrin

Epichlorohydrin (1-Chloro-2,3-epoxypropane)

106-89-8

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U001

75-07-0

Ethanal

Acetaldehyde

75-07-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U404

121-44-8

Ethanamine, N,N-diethyl-

Triethylamine

121-44-8

0.081

1.5

U174

55-18-5

Ethanamine, N-ethyl-N-nitroso-

N-Nitrosodiethylamine

55-18-5

0.40

28

U208

630-20-6

Ethane, 1,1,1,2-tetrachloro-

1,1,1,2-Tetrachloroethane

630-20-6

0.057

6.0

U226

71-55-6

Ethane, 1,1,1-trichloro-

1,1,1-Trichloroethane

71-55-6

0.054

6.0

U209

79-34-5

Ethane, 1,1,2,2-tetrachloro-

1,1,2,2-Tetrachloroethane

79-34-5

0.057

6.0

U227

79-00-5

Ethane, 1,1,2-trichloro-

1,1,2-Trichloroethane

79-00-5

0.054

6.0

U024

111-91-1

Ethane, 1,1'-[methylenebis(oxy)]bis[2-chloro-

bis(2-Chloroethoxy)methane

111-91-1

0.036

7.2

U076

75-34-3

Ethane, 1,1-dichloro-

1,1-Dichloroethane

75-34-3

0.059

6.0

U117

60-29-7

Ethane, 1,1'-oxybis-

Ethyl ether

60-29-7

0.12

160

U025

111-44-4

Ethane, 1,1'-oxybis[2-chloro-

bis(2-Chloroethyl)ether

111-44-4

0.033

6.0

U067

106-93-4

Ethane, 1,2-dibromo-

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

U077

107-06-2

Ethane, 1,2-dichloro-

1,2-Dichloroethane

107-06-2

0.21

6.0

U131

67-72-1

Ethane, hexachloro-

Hexachloroethane

67-72-1

0.055

30

U184

76-01-7

Ethane, pentachloro-

Pentachloroethane

76-01-7

(WETOX or CHOXD) fb CARBN; or CMBST or 0.055

CMBST or 6.0

U218

62-55-5

Ethanethioamide

Thioacetamide

62-55-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U394

30558-43-1

Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-,methyl ester

A2213

30558-43-1

BIODG; CARBN; CHOXD; CMBST or 0.042

CMBST or 1.4

U410

59669-26-0

Ethanimidothioic acid, N,N'-[thiobis[(methylimino)carbonyloxy]]bi s-, dimethyl ester

Thiodicarb

59669-26-0

0.019

1.4

U173

1116-54-7

Ethanol, 2,2'-(nitrosoimino)bis-

N-Nitrosodiethanolamine

1116-54-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U395

5952-26-1

Ethanol, 2,2'-oxybis-, dicarbamate

Diethylene glycol, dicarbamate

5952-26-1

BIODG; CARBN; CHOXD; CMBST or 0.056

CMBST or 1.4

U359

110-80-5

Ethanol, 2-ethoxy-

2-Ethoxyethanol

110-80-5

CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN.

CMBST

U004

98-86-2

Ethanone, 1-phenyl-

Acetophenone

98-86-2

0.010

9.7

U042

110-75-8

Ethene, (2-chloroethoxy)-

2-Chloroethyl vinyl ether

110-75-8

0.062

CMBST

U078

75-35-4

Ethene, 1,1-dichloro-

1,1-Dichloroethylene

75-35-4

0.025

6.0

U079

156-60-5

Ethene, 1,2-dichloro-, (E)-

trans-1,2-Dichloroethylene

156-60-5

0.054

30

U043

75-01-4

Ethene, chloro-

Vinyl chloride

75-01-4

0.27

6.0

U210

127-18-4

Ethene, tetrachloro-

Tetrachloroethylene

127-18-4

0.056

6.0

U228

79-01-6

Ethene, trichloro-

Trichloroethylene

79-01-6

0.054

6.0

U112

141-78-6

Ethyl acetate

Ethyl acetate

141-78-6

0.34

33

U113

140-88-5

Ethyl acrylate

Ethyl acrylate

140-88-5

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U238

51-79-6

Ethyl carbamate (urethane)

Urethane (Ethyl carbamate)

51-79-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U117

60-29-7

Ethyl ether

Ethyl ether

60-29-7

0.12

160

U118

97-63-2

Ethyl methacrylate

Ethyl methacrylate

97-63-2

0.14

160

U119

62-50-0

Ethyl methanesulfonate

Ethyl methane sulfonate

62-50-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U067

106-93-4

Ethylene dibromide

Ethylene dibromide (1,2-Dibromoethane)

106-93-4

0.028

15

U077

107-06-2

Ethylene dichloride

1,2-Dichloroethane

107-06-2

0.21

6.0

U359

110-80-5

Ethylene glycol monoethyl ether

2-Ethoxyethanol

110-80-5

CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN.

CMBST

U115

75-21-8

Ethylene oxide

Ethylene oxide

75-21-8

(WETOX or CHOXD) fb CARBN; or CMBST or 0.12

CHOXD; or CMBST

U114

111-54-6

Ethylenebisdithiocarbamic acid, salts & esters

Ethylenebisdithiocarbamic acid

111-54-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U116

96-45-7

Ethylenethiourea

Ethylene thiourea

96-45-7

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U076

75-34-3

Ethylidene dichloride

1,1-Dichloroethane

75-34-3

0.059

6.0

U120

206-44-0

Fluoranthene

Fluoranthene

206-44-0

0.068

3.4

U122

50-00-0

Formaldehyde

Formaldehyde

50-00-0

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U123

64-18-6

Formic acid

Formic acid

64-18-6

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U124

110-00-9

Furan

Furan

110-00-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U213

109-99-9

Furan, tetrahydro-

Tetrahydrofuran

109-99-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U125

98-01-1

Furfural

Furfural

98-01-1

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U124

110-00-9

Furfuran

Furan

110-00-9

(WETOX or CHOXD)
fb CARBN; or CMBST

CMBST

U206

18883-66-4

Glucopyranose,2-deoxy-2-(3-methyl-3-nitrosoureido)-, D-