R.R.O. 1990, Reg. 347: GENERAL - WASTE MANAGEMENT

 

Environmental Protection Act
Loi sur la protection de l’environnement

R.R.O. 1990, REGULATION 347

Amended to O. Reg. 326/03

GENERAL — WASTE MANAGEMENT

Historical version for the period December 6, 2003 to August 9, 2005.

This Regulation is made in English only.

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CONTENTS

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 having a generic name listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of the acute hazardous waste chemical from which it was derived;

“agricultural waste” means waste, other than sewage, resulting from farm operations, including animal husbandry and where a farm operation is carried on in respect of food packing, food preserving, animal slaughtering or meat packing, includes the waste from such operations;

“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;

“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;

“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 subparagraph i, ii or iii, does not include a waste stream or waste material contaminated with material of the specified generic name;

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

“corrosive waste” means a waste that,

(a) 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, or

(b) 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;

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

“dead animal” means an animal that dies naturally or from disease or by reason of accident and includes parts thereof;

“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;

“Director” means the Director of the Waste Management Policy Branch of the Ministry and includes an alternate named by him or her;

“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 a certificate of approval or provisional certificate of approval for 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;

“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;

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

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

“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 the 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 from a sewage works approved under section 53 of the Ontario Water Resources Act that is conveyed away from the site where it is produced by a sewer approved under that section, or

(ii) waste in a vehicle sewage holding tank;

“hazardous industrial waste” means,

(a) a generic or specific waste listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of 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 or the Atomic Energy Control Board,

(i) pathological waste,

(j) leachate toxic waste, or

(k) PCB waste as defined in Regulation 362 of the Revised Regulations of Ontario, 1990,

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 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 having a generic name listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of the hazardous waste chemical from which it was derived;

“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 an ignitable compressed gas (Class 2, Division 1) as defined in the regulations under the Transportation of Dangerous Goods Act (Canada), or

(d) is an oxidizing substance (Class 5, Divisions 1 and 2) as defined in the regulations 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 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, or

(e) schools, laboratories or hospitals;

“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;

“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;

“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, Method 1311 that appears in the 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 an equivalent test method approved by the Director;

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

(a) hauled sewage,

(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,

(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 a sewage works subject to the Ontario Water Resources Act or established before April 3, 1957 or into a sewage system regulated under Part 8 of the building code made under the Building Code Act, 1992,

(f) waste that results directly from food processing and preparation operations, including food packing, food preserving, wine making, cheese making and restaurants,

(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;

“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;

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

“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;

“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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of pathological waste referred to in clause (a), (b) or (c);

“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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of 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 an explosive (Class 1) as defined in the regulations under the Transportation of Dangerous Goods Act (Canada);

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

“Regional Director” means a Director appointed under section 5 of the Act and responsible for a region established by the Ministry for administrative purposes, but does not mean the Director of the Waste Management Branch of the Ministry or an alternate named by him or her;

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

“Section 39 Director” means a Director appointed under section 5 of the Act for purposes of section 39 of the Act;

“severely toxic waste” means,

(a) a waste that contains a contaminant listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of 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;

“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, and

(b) hazardous waste,

but does not include 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 management of such waste with a waste management system approved under Part V of the Act for the purposes and does not include waste from,

(c) a nursing home under the Nursing Homes Act,

(d) a home under the Homes for the Aged and Rest Homes Act,

(e) a home for special care under the Homes for Special Care Act,

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

(g) the professional office of a member of the College of Physicians and Surgeons of Ontario;

“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;

“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 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 or waste described in clause (p), (q), (r), (s), (t) or (u) of the definition of “hazardous waste” in section 1 or in clause (d) of the definition of “liquid industrial waste” in section 1,

(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 incinerated 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.

(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).

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.  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.

(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. Condemned animals or parts thereof at a plant licensed under the Meat Inspection Act (Ontario) or an establishment operating under the Meat Inspection Act (Canada).

3. Dead animals to which the Dead Animal Disposal Act applies

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.

(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, transferred by a generator for direct transportation to a site,

i. to be wholly used 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,

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

iii. 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, 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.  O. Reg. 105/94, s. 3 (2); O. Reg. 128/98, s. 2 (1).

(3) Despite subsection (1), material referred to in subparagraph i of paragraph 1 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 agreeing to accept the material, specifying what use will be made of it and stipulating that the process or operation described in that subparagraph is ongoing at the time the material is being transported.  O. Reg. 105/94, s. 3 (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).

Classification and Exemption of Waste Disposal Sites

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.  R.R.O. 1990, Reg. 347, s. 5 (1).

(2) Dust suppression sites designated in a certificate of approval or provisional certificate of approval for a dust suppression waste management system and established and operated in accordance therewith are exempt from the requirement to have a waste disposal site certificate of approval or provisional certificate of approval.  R.R.O. 1990, Reg. 347, s. 5 (2).

(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).

5.1 (1) A waste disposal site that is the subject of an application for a certificate of approval referred to in subsection 30 (1) of the Act is exempt from the requirements of subsection 30 (1) of the Act, but only in relation to the application, and only if the application is not for an approval for,

(a) the deposit of waste at a dump;

(b) the landfilling of waste; or

(c) the incineration of waste.  O. Reg. 457/93, s. 1.

(2) For the purposes of clause (1) (a), the deposit of waste at a dump does not include the handling, storing, transferring, treating or processing of waste at a dump.  O. Reg. 457/93, s. 1.

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 a certificate of approval or a provisional certificate of approval, to receive municipal waste.  O. Reg. 299/94, s. 1.

(2) A municipality that owns or operates a landfilling site is exempt from sections 27, 30 and 32 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 land filling 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. 299/94, s. 1.

(3) A municipality that owns or operates a landfilling site is exempt from sections 30 and 32 of the Act with respect to an increase in the rate at which municipal waste may be received at the site from areas within its service area.  O. Reg. 299/94, s. 1.

(4) If a municipality owns or operates a landfilling site that has been filled in accordance with an exemption under this section, the municipality is exempt from sections 27, 30 and 32 with respect to increasing the service area of another landfilling site that it owns and operates if the additional area from which the other site will receive municipal waste is part or all of the area from which the filled site received municipal waste.  O. Reg. 299/94, s. 1.

(5) A person, other than a municipality, who owns or operates a landfilling site is exempt from sections 27, 30 and 32 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 a certificate of approval or a provisional certificate of approval, the terms or conditions of which establish a periodic quantity limit for deliveries of waste to the landfilling site.  O. Reg. 299/94, s. 1.

(6) A person, other than a municipality, who owns or operates a landfilling site is exempt from sections 30 and 32 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;

(c) the site has a certificate of approval or a provisional certificate of 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. 299/94, s. 1.

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 incinerated or buried at the site.  O. Reg. 183/92, s. 1; O. Reg. 555/92, s. 5 (1).

(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.

Classification and Exemption of Waste Management Systems

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) Waste generation facilities are exempt from the requirement to have a waste management system certificate of approval in respect of the production, collection, handling and temporary storage of waste.  R.R.O. 1990, Reg. 347, s. 8 (2); O. Reg. 105/94, s. 6.

(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).

9. The standards, procedures and requirements set out in this Regulation do not apply to the extent that terms and conditions set out in a certificate of approval or a provisional certificate of approval issued under section 39 of the Act impose different standards, procedures or requirements.  R.R.O. 1990, Reg. 347, s. 9.

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.

12. The following are prescribed as standards for the location, maintenance and operation of an incineration site:

1. The location of the incineration 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. the TRICIL Limited landfilling site located on Lot 9, Concession 10, Township of Moore, County of Lambton, or

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. a certificate of approval or provisional certificate of approval issued after the 1st day of January, 1990, or

B. an amendment to a certificate of approval or provisional certificate of approval made after the 1st day of January, 1990.

4. The incinerator 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 incinerator are available, including facilities for the disposal of residue and of quenching and scrubbing water.

5. The design and capacity of the incinerator shall be in accordance with accepted engineering practices and 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 an incinerator.

7. The incineration 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 incineration 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.

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) Subject to subsection (2), no dump shall be established or operated in a city, borough, town, separated town, township, village or police village in any county, regional municipality or the County of Haliburton.  R.R.O. 1990, Reg. 347, s. 14 (1).

(2) A dump may be established in the following parts of Ontario:

1. The townships of Albemarle, Eastnor, Lindsay and St. Edmunds, in the County of Bruce.

2. The townships of Barrie, Bedford, Clarendon and Miller, Howe Island, Kennebec, Olden and Palmerston and North and South Canonto, in the County of Frontenac.

3. The townships of Bangor, Wicklow and McClure, Carlow, Dungannon, Elzevir and Grimsthorpe, Herschel, Limerick, Madoc, Marmora and Lake, Mayo, Monteagle, Tudor and Cashel, and Wollaston, in the County of Hastings.

4. The townships of Dalhousie and North Sherbrooke, Darling, Lavant, North Burgess, and South Sherbrooke, in the County of Lanark.

5. The townships of Asphodel, Belmont and Methuen, Chandos, Ennismore, Galway and Cavendish, and Harvey, in the County of Peterborough.

6. The townships of Bagot and Blithfield, Brougham, Brudenell and Lyndoch, Griffith and Matawatchan, Head, Clara, and Maria, North Algona, Radcliffe, Raglan, Sebastopol, and South Algona, in the County of Renfrew.

7. The townships of Carden, Dalton, and Laxton, Digby and Longford, in the County of Victoria.

8. The Improvement District of Bicroft, the townships of Anson, Hindon and Minden, Cardiff, Dysart, Bruton, Clyde, Dudley, Eyre, Guilford, Harburn, Harcourt and Havelock, Glamorgan, Lutterworth, Monmouth, Sherborne, McClintock and Livingstone, and Snowdon and Stanhope, in the County of Haliburton.  R.R.O. 1990, Reg. 347, s. 14 (2).

(3) No dump shall be established or operated in the following parts of the territorial districts of Ontario:

1. The City of Sault Ste. Marie, the towns of Blind River, Bruce Mines, Thessalon and Elliot Lake, and the villages of Hilton Beach and Iron Bridge, in the Territorial District of Algoma.

2. The City of Timmins, the towns of Cochrane, Hearst, Iroquois Falls, Kapuskasing and Smooth Rock Falls, and the townships of Glackmeyer, Tisdale and Whitney, in the Territorial District of Cochrane.

3. The towns of Dryden, Keewatin, Kenora, and Sioux Lookout, and the townships of Jaffray and Melick, in the Territorial District of Kenora.

4. The towns of Gore Bay and Little Current, in the Territorial District of Manitoulin.

5. That part of The District Municipality of Muskoka that, on the 31st day of December, 1970, was the towns of Bala, Bracebridge, Gravenhurst and Huntsville, and the villages of Port Carling, Port Sydney and Windermere.

6. The City of North Bay, the towns of Cache Bay, Mattawa and Sturgeon Falls, and the townships of Bonfield, East Ferris, Field and Springer, in the Territorial District of Nipissing.

7. The towns of Kearney, Parry Sound, Powassan and Trout Creek, the villages of Burk’s Falls, Magnetawan, Rosseau, South River and Sundridge, and the townships of Foley, McDougall, North Himsworth, and South Himsworth, in the Territorial District of Parry Sound.

8. The towns of Fort Frances and Rainy River, and the Township of Atikokan, in the Territorial District of Rainy River.

9. That part of The Regional Municipality of Sudbury and the Territorial District of Sudbury that, on the 31st day of December, 1972, was the City of Sudbury, the towns of Capreol, Coniston, Copper Cliff, Espanola, Levack, Lively, Massey and Webbwood, and the townships of Balfour, Falconbridge, and Neelon and Garson, in the Territorial District of Sudbury.

10. The City of Thunder Bay, the Town of Geraldton and the townships of Beardmore, Manitowadge, Neebing, Nipigon, Oliver, Paipoonge, Schreiber, Shuniah, and Terrace Bay, and the improvement districts of Nakina and Red Rock, in the Territorial District of Thunder Bay.

11. The towns of Charlton, Cobalt, Englehart, Haileybury, Kirkland Lake, Latchford, and New Liskeard, the Village of Thornloe, and the townships of Armstrong, Bucke, Larder Lake and McGarry, in the Territorial District of Timiskaming.  R.R.O. 1990, Reg. 347, s. 14 (3).

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 a certificate of approval for the site, obtain written authorization from the owner for the proposed use of the site.  O. Reg. 157/98, s. 5.

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 has been issued a certificate of approval or provisional certificate of 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 has been issued a certificate of approval or provisional certificate of 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 has been issued a certificate of approval or provisional certificate of approval for the final disposal of hauled sewage;

(d) at a sewage works that has been approved under section 53 of the Ontario Water Resources Act to receive sanitary sewage or hauled sewage; or

(e) at a site that has been issued a certificate of approval or provisional certificate of approval permitting the processing of waste and that 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.

(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 has been issued a certificate of approval or provisional certificate of 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.

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.

Standards for Waste Management Systems

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.

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 certificate of approval or provisional certificate of 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 certificate of approval or provisional certificate of 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 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 certificate of approval or provisional certificate of approval that authorizes the transportation.

11. Where a waste transportation vehicle is used for transporting municipal waste, a copy of the certificate of approval or provisional certificate of 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 a certificate of approval, provisional certificate of 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).

(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 that is exempt from the requirement of having a certificate of approval or provisional certificate of approval.  O. Reg. 105/94, s. 7 (2).

(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 operating under a certificate of approval or provisional certificate of 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 operating under a certificate of approval or provisional certificate of 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.

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, submit an initial Generator Registration Report to the Director in respect of the facility; and

(b) on or before February 15 in each year, submit an annual Generator Registration Report to the Director in respect of each waste generation facility operated by the generator.  O. Reg. 501/01, s. 2 (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 such data, analysis and information as will enable the Director to satisfy himself or herself as to the quality and nature of the waste.  O. Reg. 501/01, s. 2 (1).

(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) A generator registration document issued to a generator before January 1, 2002 remains valid until the earlier of the posting of a generator registration document under subsection (3) and February 15, 2002.  O. Reg. 501/01, s. 2 (1).

(6) Where there is a change from the information submitted in an initial Generator Registration Report or in the most recent annual Generator Registration Report or any previous supplementary Generator Registration Reports in respect of the generator’s name, address or telephone number, the name of the contact for the generator, the name of the responsible official for the generator or the addition of subject wastes or where there is a significant change from such previously submitted information in respect of the description or physical or chemical characteristics of the subject wastes, the generator who submitted the applicable report shall send a supplementary Generator Registration Report to the Director within 15 days after the change.  O. Reg. 501/01, s. 2 (1).

(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) When any subject waste is retained at a waste generation facility for a period longer than three months, the generator, unless there is a waste disposal site certificate of approval or provisional certificate of approval in respect of the facility, shall submit a report to the Regional Director of the Ministry within five business days after the three month period which report shall comply with the Manual and shall include the name and waste number of the waste, the quantity involved, the manner in which it is stored, the reasons for the retention and the anticipated time and manner of disposal of the waste.  R.R.O. 1990, Reg. 347, s. 18 (10); O. Reg. 460/99, s. 2 (3).

(11) Every generator who transfers subject waste to a waste transportation system shall orally report to the Director any transferred subject waste that the generator is not able, within four weeks, to confirm was delivered to the intended receiving facility or to another receiving facility approved to accept the waste.  R.R.O. 1990, Reg. 347, s. 18 (11).

(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 Regional Director of the Ministry or an alternate named by him or her may assign a generator registration number or accept a waste number identified by the generator.  R.R.O. 1990, Reg. 347, s. 18 (12).

(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) For purposes of this section,

“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 5.  O. Reg. 558/00, s. 2.

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 operating under a certificate of approval or provisional certificate of 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 subject to the Ontario Water Resources Act or established before August 3, 1957 or into a sewage system regulated under Part 8 of the 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.

(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.  R.R.O. 1990, Reg. 347, s. 20.

(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 a Regional Director of the Ministry or an alternate named by him or her, may transfer subject waste in Ontario to another vehicle in the same waste transportation system or to a waste transportation system operating under a certificate of approval or provisional certificate of approval or to a receiving facility to alleviate a dangerous situation.  R.R.O. 1990, Reg. 347, s. 22 (2).

(3) Where a truckload or less of subject waste has been transferred by a generator to a waste transportation system, the carrier shall promptly 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).

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 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 part 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 a period of two years, and

(iv) return the remaining four copies of the manifest to the carrier at the time of the transfer.  O. Reg. 558/00, s. 3; O. Reg. 501/01, s. 7 (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 a Regional Director of the Ministry or an alternate named by him or her, to another vehicle of the same waste transportation system, to a waste transportation system operating under a certificate of approval or provisional certificate of 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 operating under a certificate of approval or provisional certificate of approval authorizing acceptance of the waste;

(c) with the consent of the owner of the sewage works, to a sewage works for which an approval under the Ontario Water Resources Act has been issued and that is not in contravention of the approval; or

(d) to a waste-derived fuel site having a combustion unit operating under a certificate of approval issued under section 9 of the Act authorizing acceptance and combustion of the waste.  R.R.O. 1990, Reg. 347, s. 23 (3).

(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 obtain from the carrier the remaining four parts of the manifest completed for that load and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(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 two years; 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. 23 (5); O. Reg. 501/01, s. 7 (4).

(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) (c) and shall retain it for a period of two years.  R.R.O. 1990, Reg. 347, s. 23 (6).

(7) Where a paper manifest is used, every carrier who is the operator of a waste transportation system for which a certificate of approval or provisional certificate of approval as a dust suppression waste management system is issued 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) (iv);

(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).

(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 two years, 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).

(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 Transportation of Dangerous Goods Act (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).

(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 operating under a certificate of approval or provisional certificate of approval authorizing acceptance of the waste;

(b) with the consent of the owner of the sewage works, to a sewage works for which an approval under the Ontario Water Resources Act has been issued, and that is not in contravention of the approval; or

(c) to a waste-derived fuel site having a combustion unit operating under a certificate of approval issued under section 9 of the Act authorizing acceptance and combustion of the waste.  R.R.O. 1990, Reg. 347, s. 25 (5).

(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;

(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 two years; 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).

(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 for which a certificate of approval or provisional certificate of approval as a dust suppression waste management system is issued 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).

(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 Transportation of Dangerous Goods Act (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).

Refusals

27. (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 Incinerators

28. (1) On-site incinerators are exempt from the operation of section 27 of the Act on condition that no hazardous waste or liquid industrial waste is incinerated therein.  R.R.O. 1990, Reg. 347, s. 28 (1).

(2) On-site incinerators are exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act.  R.R.O. 1990, Reg. 347, s. 28 (2).

(3) This section does not apply to woodwaste combustor sites or waste-derived fuel sites.  O. Reg. 555/92, s. 7.

Woodwaste Combustor Sites

28.1 (1) A woodwaste combustor site for residential heating is exempt from section 27 of the Act if not more than fifty cubic metres of woodwaste is stored at the woodwaste combustor site at any time.  O. Reg. 555/92, s. 8.

(2) A woodwaste combustor site is exempt from section 27 of the Act if,

(a) not more than 500 cubic metres of woodwaste is stored at the woodwaste combustor site at any time;

(b) not more than 100 tonnes of woodwaste is combusted at the woodwaste combustor site on any day; and

(c) none of the woodwaste stored at the woodwaste combustor site is stored there for more than six months.  O. Reg. 555/92, s. 8.

(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 (1) A woodwaste combustor site is exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act if not more than 100 tonnes of woodwaste is combusted at the woodwaste combustor site on any day.  O. Reg. 555/92, s. 8.

(2) A woodwaste combustor site is exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act if the heat from the combustion is recovered and utilized.  O. Reg. 191/98, s. 1.

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.

(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 A waste-derived fuel site is exempt from the requirement of being the subject-matter of a hearing under subsection 30 (1) of the Act if not more than ten tonnes of waste-derived fuel is utilized at the site on any day.  O. Reg. 555/92, s. 8.

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.

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.

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 with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste.  R.R.O. 1990, Reg. 347, s. 30 (1); O. Reg. 190/94, s. 2 (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 with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste.  R.R.O. 1990, Reg. 347, s. 30 (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 a certificate of approval or provisional certificate of approval under Part V of the Act.  R.R.O. 1990, Reg. 347, s. 33.

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 with a certificate of approval or provisional certificate of 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.

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 27.  R.R.O. 1990, Reg. 347, s. 35.

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 with a certificate of approval or provisional certificate of approval to handle mobile refrigerant waste.  R.R.O. 1990, Reg. 347, s. 37 (1); O. Reg. 190/94, s. 4 (1).

(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 a certificate of approval or provisional certificate of approval under Part V of the Act.  R.R.O. 1990, Reg. 347, s. 40.

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 34.  R.R.O. 1990, Reg. 347, s. 42.

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 as defined in subsection 1.2.1 of Regulation 454 of the Revised Regulations of Ontario, 1990 and to the Regional Director responsible for the region in which the depot is located.  O. Reg. 298/94, s. 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 Regional 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.

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 a certificate of approval or provisional certificate of approval has been issued under Part V of the Act authorizing 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.

(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 certificate of approval or provisional certificate of 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.

(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 a certificate of approval or provisional certificate of approval has been issued authorizing the removal of the waste.  O. Reg. 298/94, s. 1.

(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 as defined in subsection 1.2.1 of Regulation 454 of the Revised Regulations of Ontario, 1990 and to the Regional 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.

(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 Regional 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.

60. In the event of conflict between sections 44 to 59 and the provisions of Regulation 532 of the Revised Regulations of Ontario, 1990 or Regulation 454 of the Revised Regulations of Ontario, 1990, the provisions of Regulation 532 and Regulation 454 prevail.  O. Reg. 298/94, s. 1.

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 Regional Director responsible for the region in which the pesticide container depot is located.  O. Reg. 298/94, s. 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 in writing the Regional Director responsible for the region in which the pesticide container 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.

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 a certificate of approval or provisional certificate of approval has been issued under Part V of the Act authorizing the party to transport the empty pesticide containers to be removed from the depot.  O. Reg. 298/94, s. 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 certificate of approval or provisional certificate of 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.

(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 a certificate of approval or provisional certificate of approval has been issued authorizing the removal of the waste.  O. Reg. 298/94, s. 1.

(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 Regional 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 empty pesticide containers.  O. Reg. 298/94, s. 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 Regional Director responsible for the region in which the depot is located is given timely written notice of the address referred to in subsection (4).  O. Reg. 298/94, s. 1.

Form 1 Revoked:  O. Reg. 501/01, s. 12.

Form 2 Revoked:  O. Reg. 501/01, s. 12.

Schedule 1
HAZARDOUS INDUSTRIAL WASTES

Hazardous Industrial Waste from Non-Specific Sources
USEPA  Hazardous Waste No.	Industry and No.	Waste
F001	NA9301	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.
F002	NA9302	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.
F003	NA9303	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.
F004	NA9304	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.
F005	NA9305	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.
F006	NA9306	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.
F007	NA9308	Spent cyanide plating bath solutions from electroplating operations
F008	NA9309	Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.
F009	NA9310	Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.
F010	NA9311	Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process.
F011	NA9312	Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.
F012	NA9313	Quenching waste water treatment sludges from metal heat treating operations where cyanides are used in the process.
F019	NA9307	Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process.
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.).
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.
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.
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.).
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 Schedules 2A or 2B.).
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.
F026		Wastes (except wastewater and spent carbon rom 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.
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.).
F028		Residues resulting from the incineration or thermal treatment of soil contaminated with EPA Hazardous Waste Nos. F020, F021, F022, F023, F026 and F027.
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. 261.351 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.
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.
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.
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)1 (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)1, if those residuals are to be disposed of.
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)1 (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.
F039		Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under subpart D of this part. (Leachate resulting from the disposal of one or more of the following EPA Hazardous Wastes and no other Hazardous Wastes retains its EPA Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.).

 

Hazardous Industrial Waste from Specific Sources
USEPA  HazardousWaste No.	Industry and No.	Waste
Wood preservation:
K001	NA9316	Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.
Inorganic pigments:
K002	NA9317	Wastewater treatment sludge from the production of chrome yellow and orange pigments.
K003	NA9318	Wastewater treatment sludge from the production of molybdate orange pigments.
K004	NA9319	Wastewater treatment sludge from the production of zinc yellow pigments.
K005	NA9320	Wastewater treatment sludge from the production of chrome green pigments.
K006	NA9321	Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).
K007	NA9322	Wastewater treatment sludge from the production of iron blue pigments.
K008	NA9323	Oven residue from the production of chrome oxide green pigments.
Organic chemicals:
K009	NA9324	Distillation bottoms from the production of acetaldehyde from ethylene.
K010	NA9325	Distillation side cuts from the production of acetaldehyde from ethylene.
K011	NA9326	Bottom stream from the wastewater stripper in the production of acrylonitrile.
K013	NA9327	Bottom stream from the acetonitrile column in the production of acrylonitrile.
K014	NA9328	Bottoms from the acetonitrile purification column in the production of acrylonitrile.
K015	NA9329	Still bottoms from the distillation of benzyl chloride.
K016	NA9330	Heavy ends or distillation residues from the production of carbon tetrachloride.
K017	NA9331	Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.
K018	NA9332	Heavy ends from the fractionation column in ethyl chloride production.
K019	NA9333	Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.
K020	NA9334	Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.
K021	NA9335	Aqueous spent antimony catalyst waste from fluoromethanes production.
K022	NA9336	Distillation bottom tars from the production of phenol/acetone from cumene.
K023	NA9337	Distillation light ends from the production of phthalic anhydride from naphthalene.
K024	NA9338	Distillation bottoms from the production of phthalic anhydride from naphthalene.
K025	NA9341	Distillation bottoms from the production of nitrobenzene by the nitration of benzene.
K026	NA9342	Stripping still tails from the production of methyl ethyl pyridines.
K027	NA9343	Centrifuge and distillation residues from toluene diisocyanate production.
K028	NA9344	Spent catalyst from the hydrochlorinator reactor in the productions of 1,1,1trichloroethane.
K029	NA9345	Waste from the product stream stripper in the production of 1,1,1trichloroethane.
K030	NA9348	Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene.
K083	NA9349	Distillation bottoms from aniline production.
K085	NA9352	Distillation or fractionation column bottoms from the production of chlorobenzenes.
K093	NA9339	Distillation light ends from the production of phthalic anhydride from orthoxylene.
K094	NA9340	Distillation bottoms from the production of phthalic anhydride from orthoxylene.
K095	NA9346	Distillation bottoms from the production of 1,1,1trichloroethane.
K096	NA9347	Heavy ends from the heavy ends column from the production of 1,1,1trichloroethane.
K103	NA9350	Process residues from aniline extraction from the production of aniline.
K104	NA9351	Combined wastewater streams generated from nitrobenzene/aniline production.
K105	NA9353	Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.
K107		Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines.
K108		Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
K109		Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
K110		Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
K111		Product washwaters from the production of dinitrotoluene via nitration of toluene.
K112		Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.
K113		Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
K114		Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
K115		Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
K116		Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.
K117		Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.
K118		Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.
K136		Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.
K140		Floor sweepings, off-specification product and spent filter media from the production of 2,4,6-tribromophenol.
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.)
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.
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.
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.).
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.)
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.).
K159		Organics from the treatment of thiocarbamate wastes.
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.)
Inorganic chemicals:
K071	NA9390	Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.
K073	NA9391	Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.
K106	NA9392	Wastewater treatment sludge from the mercury cell process in chlorine production.
Pesticides:
K031	NA9354	Byproduct salts generated in the production of MSMA and cacodylic acid.
K032	NA9355	Wastewater treatment sludge from the production of chlordane.
K033	NA9356	Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.
K034	NA9357	Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.
K035	NA9359	Wastewater treatment sludges generated in the production of creosote.
K036	NA9360	Still bottoms from toluene reclamation distillation in the production of disulphoton.
K037	NA9361	Wastewater treatment sludges from the production of disulphoton.
K038	NA9362	Wastewater from the washing and stripping of phorate production.
K039	NA9363	Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate.
K040	NA9364	Wastewater treatment sludge from the production of phorate.
K041	NA9365	Wastewater treatment sludge from the production of toxaphene.
K042	NA9367	Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5T.
K043	NA9368	2,6Dichlorophenol waste from the production of 2,4D.
K097	NA9358	Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.
K098	NA9366	Untreated process wastewater from the production of toxaphene.
K099	NA9369	Untreated wastewater from the production of 2,4D.
K123		Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt.
K124		Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.
K125		Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.
K126		Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.
K131		Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.
K132		Spent absorbent and wastewater separator solids from the production of methyl bromide.
Explosives:
K044	NA9370	Wastewater treatment sludges from the manufacturing and processing of explosives.
K045	NA9371	Spent carbon from the treatment of wastewater containing explosives.
K046	NA9372	Wastewater treatment sludges from the manufacturing formulation and loading of leadbased initiating compounds.
K047	NA9373	Pink/red water from TNT operations.
Petroleum refining:
K048	NA9374	Dissolved air flotation (DAF) float from the petroleum refining industry.
K049	NA9375	Slop oil emulsion solids from the petroleum refining industry.
K050	NA9376	Heat exchanger bundle cleaning sludge from the petroleum refining industry.
K051	NA9377	API separator sludge from the petroleum refining industry.
K052	NA9378	Tank bottoms (leaded) from the petroleum refining industry.
K169		Crude oil storage tank sediment from petroleum refining operations.
K170		Clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operations.
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).
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).
Iron and steel:
K061	NA9380	Emission control dust/sludge from the primary production of steel in electric furnaces.
K062	NA9381	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.
Primary copper:
K064	NA9383	Acid plant blowdown slurry/sludge resulting from the thickening of blowdown slurry from primary copper production.
Primary lead:
K065	NA9384	Surface impoundment solids contained in and dredged from surface impoundments at primary lead smelting facilities.
Primary zinc:
K066	NA9385	Sludge from treatment of process wastewater and/or acid plant blowdown from primary zinc production.
Primary aluminum:
K088		Spent potliners from primary aluminum reduction.
Ferroalloys:
K090		Emission control dust or sludge from ferrochromiumsilicon production.
K091		Emission control dust or sludge from ferrochromium production.
Secondary lead:
K069	NA9388	Emission control dust/sludge from secondary lead smelting. (NOTE: This listing is stayed administratively for sludge generated from secondary acid scrubber systems.  The stay will remain in effect until further administrative action is taken. If EPA takes further action effecting this stay, EPA will publish a notice of the action in the Federal Register.
K100	NA9389	Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.
Veterinary pharmaceuticals:
K084	NA9394	Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.
K101	NA9395	Distillation tar residues from the distillation of anilinebased compounds in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.
K102	NA9396	Residue from the use of activated carbon for decolourization in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.
Ink formulation:
K086	NA9393	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.
Coking:
K060	NA9379	Ammonia still lime sludge from coking operations.
K087	NA9397	Decanter tank tar sludge from coking operations.
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).
K142		Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.
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.
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.
K145		Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.
K147		Tar storage tank residues from coal tar refining.
K148		Residues from coal tar distillation, including but not limited to, still bottoms.
1 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

O. Reg. 558/00, s. 4.

Schedule 1.1
EXEMPT HAZARDOUS INDUSTRIAL WASTES

Industry and Site	Waste
ICI Canada Inc., Cornwall	Brine purification muds (known either as K071 or No. NA9390, 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 (known either as K062 or No. NA9381) 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 (known also as No. NA9380) or K062 (known also as No. NA9381) 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 (known also as No. NA9306) 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. 558/00, s. 4.

Schedule 2
Part A — acute Hazardous Waste Chemicals

Hazardous Waste No.	Chemical Abstracts No.	Substance	Reference Number
P026	5344-82-1	1-(o-Chlorophenyl)thiourea	ON1037
P081	55-63-0	1,2,3-Propanetriol, trinitrate	ON1089
P042	51-43-4	1,2-Benzenediol,4-[1-hydroxy-2-(methylamino)ethyl]-	ON1025
P067	75-55-8	1,2-Propylenimine	ON1082
P185	26419-73-8	1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-[(methylamino)-carbonyl]oxime
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)	ON1010
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)-	ON1070
P002	591-08-2	1-Acetyl-2-thiourea	ON1002
P048	51-28-5	2,4-Dinitrophenol	ON1055
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	ON1062
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-	ON1043
P045	39196-18-4	2-Butanone,3,3-dimethyl-1-methylthio)-,O-[methylamino)carbonyl] oxime	ON1049
P034	131-89-5	2-Cyclohexyl-4,6-dinitrophenol	ON1054
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%	ON1006
P069	75-86-5	2-Methyllactonitrile	ON1005
P017	598-31-2	2-Propanone, 1-bromo-	ON1029
P005	107-18-6	2-Propen-1-ol	ON1011
P003	107-02-8	2-Propenal	ON1007
P102	107-19-7	2-Propyn-1-ol	ON1097
P007	2763-96-4	3(2H)-Isoxazolone, 5-(aminomethyl)-	ON1008
P027	542-76-7	3-Chloropropionitrile	ON1038
P202	64-00-6	3-Isopropylphenyl N-methylcarbamate
P047	**534-52-1	4,6-Dinitro-o-cresol, & salts	ON1053
P059	76-44-8	4,7-Methano-1H-indene, 1,4,5,6,7,8,8- heptachloro-3a,4,7,7a-tetrahydro-	ON1069
P008	504-24-5	4-Aminopyridine	ON1013
P008	504-24-5	4-Pyridinamine	ON1013
P007	2763-96-4	5-(Aminomethyl)-3-isoxazolol	ON1008
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	ON1060
P127	1563-66-2	7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate
P088	145-73-3	7-Oxabicyclo[2.2.1]heptane-2,3-dicarboxylic acid	ON1061
P023	107-20-0	Acetaldehyde, chloro-	ON1001
P057	640-19-7	Acetamide, 2-fluoro-	ON1003
P002	591-08-2	Acetamide, N-(aminothioxomethyl)-	ON1002
P058	62-74-8	Acetic acid, fluoro-, sodium salt	ON1067
P003	107-02-8	Acrolein	ON1007
P070	116-06-3	Aldicarb	ON1009
P203	1646-88-4	Aldicarb sulfone
P004	309-00-2	Aldrin	ON1010
P005	107-18-6	Allyl alcohol	ON1011
P046	122-09-8	alpha,alpha-Dimethylphenethylamine	ON1052
P072	86-88-4	alpha-Naphthylthiourea	ON1083
P006	20859-73-8	Aluminum phosphide	ON1012
P009	131-74-8	Ammonium picrate	ON1015
P119	7803-55-6	Ammonium vanadate	ON1014
P099	506-61-6	Argentate(1-), bis(cyano-C)-, potassium	ON1096
P010	7778-39-4	Arsenic acid H3AsO4	ON1016
P012	1327-53-3	Arsenic oxide As2O3	ON1017
P011	1303-28-2	Arsenic oxide As2O5	ON1018
P011	1303-28-2	Arsenic pentoxide	ON1018
P012	1327-53-3	Arsenic trioxide	ON1017
P038	692-42-2	Arsine, diethyl-	ON1019
P036	696-28-6	Arsonous dichloride, phenyl-	ON1042
P054	151-56-4	Aziridine	ON1020
P067	75-55-8	Aziridine, 2-methyl-	ON1082
P013	542-62-1	Barium cyanide	ON1021
P024	106-47-8	Benzenamine, 4-chloro-	ON1022
P077	100-01-6	Benzenamine, 4-nitro-	ON1023
P028	100-44-7	Benzene, (chloromethyl)-	ON1024
P046	122-09-8	Benzeneethanamine, alpha,alpha-dimethyl-	ON1052
P014	108-98-5	Benzenethiol	ON1026
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)
P028	100-44-7	Benzyl chloride	ON1024
P015	7440-41-7	Beryllium powder	ON1027
P017	598-31-2	Bromoacetone	ON1029
P018	357-57-3	Brucine	ON1030
P021	592-01-8	Calcium cyanide	ON1031
P021	592-01-8	Calcium cyanide Ca(CN)2	ON1031
P189	55285-14-8	Carbamic acid, [(dibutylamino)-thio]methyl-, 2,3-dihydro-2,2-dimethyl- 7-benzofuranyl ester
P191	644-64-4	Carbamic acid, dimethyl-, 1-[(dimethyl-amino)carbonyl]- 5-methyl-1H- pyrazol-3-yl este
P190	1129-41-5	Carbamic acid, methyl-, 3-methylphenyl ester
P192	119-38-0	Carbamic acid,dimethyl-,3-methyl-1-(1methylethyl)-1H-pyrazol-5-yl ester
P127	1563-66-2	Carbofuran
P022	75-15-0	Carbon disulfide	ON1034
P095	75-44-5	Carbonic dichloride	ON1035
P189	55285-14-8	Carbosulfan
P023	107-20-0	Chloroacetaldehyde	ON1001
P029	544-92-3	Copper cyanide	ON1039
P029	544-92-3	Copper cyanide Cu(CN)	ON1039
P030	N/A	Cyanides (soluble cyanide salts), not otherwise specified	ON1040
P031	460-19-5	Cyanogen	ON1041
P033	506-77-4	Cyanogen chloride	ON1036
P033	506-77-4	Cyanogen chloride (CN)Cl	ON1036
P016	542-88-1	Dichloromethyl ether	ON1028
P036	696-28-6	Dichlorophenylarsine	ON1042
P037	60-57-1	Dieldrin	ON1043
P038	692-42-2	Diethylarsine	ON1019
P041	311-45-5	Diethyl-p-nitrophenyl phosphate	ON1045
P043	55-91-4	Diisopropylfluorophosphate (DFP)	ON1047
P044	60-51-5	Dimethoate	ON1048
P191	644-64-4	Dimetilan.
P020	88-85-7	Dinoseb	ON1056
P085	152-16-9	Diphosphoramide, octamethyl-	ON1057
P111	107-49-3	Diphosphoric acid, tetraethyl ester	ON1098
P039	298-04-4	Disulfoton	ON1044
P049	541-53-7	Dithiobiuret	ON1058
P050	115-29-7	Endosulfan	ON1060
P088	145-73-3	Endothall	ON1061
P051	72-20-8	Endrin	ON1062
P051	72-20-8	Endrin, & metabolites	ON1062
P042	51-43-4	Epinephrine	ON1025
P031	460-19-5	Ethanedinitrile	ON1041
P194	23135-22-0	Ethanimidothioc acid, 2-(dimethylamino)-N-[[(methylamino)carbonyl]oxy]-2-oxo-, methyl ester
P066	16752-77-5	Ethanimidothioic acid, N-[[(methylamino)carbonyl]oxy]-,methyl ester	ON1004
P101	107-12-0	Ethyl cyanide	ON1064
P054	151-56-4	Ethyleneimine	ON1020
P097	52-85-7	Famphur	ON1065
P056	7782-41-4	Fluorine	ON1066
P057	640-19-7	Fluoroacetamide	ON1003
P058	62-74-8	Fluoroacetic acid, sodium salt	ON1067
P198	23422-53-9	Formetanate hydrochloride
P197	17702-57-7	Formparanate
P065	628-86-4	Fulminic acid, mercury(2+) salt	ON1068
P059	76-44-8	Heptachlor	ON1069
P062	757-58-4	Hexaethyl tetraphosphate	ON1072
P068	60-34-4	Hydrazine, methyl-	ON1074
P116	79-19-6	Hydrazinecarbothioamide	ON1073
P063	74-90-8	Hydrocyanic acid	ON1075
P063	74-90-8	Hydrogen cyanide	ON1075
P096	7803-51-2	Hydrogen phosphide	ON1077
P060	465-73-6	Isodrin	ON1070
P192	119-38-0	Isolan
P196	15339-36-3	Manganese dimethyl dithiocarbamate
P196	15339-36-3	Manganese,bis(dimethylcarbamodithioato-S,S')-
P202	64-00-6	M-Cumenyl methylcarbamate
P065	628-86-4	Mercury fulminate	ON1068
P092	62-38-4	Mercury, (acetato-O)phenyl-	ON1079
P082	62-75-9	Methanamine, N-methyl-N-nitroso-	ON1051
P064	624-83-9	Methane, isocyanato-	ON1078
P016	542-88-1	Methane, oxybis[chloro-	ON1028
P112	509-14-8	Methane, tetranitro-	ON1080
P118	75-70-7	Methanethiol, trichloro-	ON1081
P197	17702-57-7	Methanimidamide,N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]-
P198	23422-53-9	Methanimidamide,N,N-dimethyl-N'-[3-[[(methylamino)-carbonyl]oxy]phenyl]-, monohydrochloride
P199	2032-65-7	Methiocarb
P066	16752-77-5	Methomyl	ON1004
P068	60-34-4	Methyl hydrazine	ON1074
P064	624-83-9	Methyl isocyanate	ON1078
P071	298-00-0	Methyl parathion	ON1050
P190	1129-41-5	Metolcarb
P128	315-8-4	Mexacarbate
P073	13463-39-3	Nickel carbonyl	ON1084
P073	13463-39-3	Nickel carbonyl Ni(CO)4,(T-4)-	ON1084
P074	557-19-7	Nickel cyanide	ON1085
P074	557-19-7	Nickel cyanide Ni(CN)2	ON1085
P075	**54-11-5	Nicotine, & salts	ON1086
P076	10102-43-9	Nitric oxide	ON1087
P078	10102-44-0	Nitrogen dioxide	ON1088
P076	10102-43-9	Nitrogen oxide NO	ON1087
P078	10102-44-0	Nitrogen oxide NO2	ON1088
P081	55-63-0	Nitroglycerine	ON1089
P082	62-75-9	N-Nitrosodimethylamine	ON1051
P084	4549-40-0	N-Nitrosomethylvinylamine	ON1063
P040	297-97-2	O,O-Diethyl O-pyrazinyl phosphorothioate	ON1046
P085	152-16-9	Octamethylpyrophosphoramide	ON1057
P087	20816-12-0	Osmium oxide OsO4,(T-4)-	ON1090
P087	20816-12-0	Osmium tetroxide	ON1090
P194	23135-22-0	Oxamyl
P089	56-38-2	Parathion	ON1091
P024	106-47-8	p-Chloroaniline	ON1022
P020	88-85-7	Phenol, 2-(1-methylpropyl)-4,6-dinitro-	ON1056
P009	131-74-8	Phenol, 2,4,6-trinitro-, ammonium salt	ON1015
P048	51-28-5	Phenol, 2,4-dinitro-	ON1055
P034	131-89-5	Phenol, 2-cyclohexyl-4,6-dinitro-	ON1054
P047	**534-52-1	Phenol, 2-methyl-4,6-dinitro-, & salts	ON1053
P202	64-00-6	Phenol, 3-(1-methylethyl)-, methyl carbamate
P201	2631-37-0	Phenol, 3-methyl-5-(1-methylethyl)-,methyl carbamate
P199	2032-65-7	Phenol,(3,5-dimethyl-4-(methylthio)-,methylcarbamate
P128	315-18-4	Phenol,4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester)
P092	62-38-4	Phenylmercury acetate	ON1079
P093	103-85-5	Phenylthiourea	ON1092
P094	298-02-2	Phorate	ON1093
P095	75-44-5	Phosgene	ON1035
P096	7803-51-2	Phosphine	ON1077
P041	311-45-5	Phosphoric acid, diethyl 4-nitrophenyl ester	ON1045
P094	298-02-2	Phosphorodithioic acid, O,O-diethyl S-[(ethylthio)methyl] ester	ON1093
P039	298-04-4	Phosphorodithioic acid, O,O-diethyl S-[2-(ethylthio)ethyl] ester	ON1044
P044	60-51-5	Phosphorodithioic acid,O,O-dimethylS-[2-(methylamino)-2-oxoethyl] ester	ON1048
P043	55-91-4	Phosphorofluoridic acid, bis(1-methylethyl) ester	ON1047
P071	298-00-0	Phosphorothioic acid, O,O,-dimethyl O-(4-nitrophenyl) ester	ON1050
P089	56-38-2	Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester	ON1091
P040	297-97-2	Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester	ON1046
P097	52-85-7	Phosphorothioic acid, O-[4-[(dimethylamino)sulfonyl]phenyl] O,O-r dimethyl ester	ON1065
P188	57-64-7	Physostigmine salicylate.
P204	57-47-6	Physostigmine.
P110	78-00-2	Plumbane, tetraethyl-	ON1094
P077	100-01-6	p-Nitroaniline	ON1023
P098	151-50-8	Potassium cyanide	ON1095
P098	151-50-8	Potassium cyanide K(CN)	ON1095
P099	506-61-6	Potassium silver cyanide	ON1096
P201	2631-37-0	Promecarb
P203	1646-88-4	Propanal,2-methyl-2-(methyl-sulfonyl)-,O-[(methylamino)carbonyl] oxime
P070	116-06-3	Propanal,2-methyl-2-(methylthio)-,O-[(methylamino)carbonyl]oxime	ON1009
P101	107-12-0	Propanenitrile	ON1064
P069	75-86-5	Propanenitrile, 2-hydroxy-2-methyl-	ON1005
P027	542-76-7	Propanenitrile, 3-chloro-	ON1038
P102	107-19-7	Propargyl alcohol	ON1097
P075	**54-11-5	Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)-, & salts	ON1086
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)-
P114	12039-52-0	Selenious acid, dithallium(1+) salt	ON1106
P103	630-10-4	Selenourea	ON1033
P104	506-64-9	Silver cyanide	ON1099
P104	506-64-9	Silver cyanide Ag(CN)	ON1099
P105	26628-22-8	Sodium azide	ON1100
P106	143-33-9	Sodium cyanide	ON1101
P106	143-33-9	Sodium cyanide Na(CN)	ON1101
P108	**57-24-9	Strychnidin-10-one, & salts	ON1103
P018	357-57-3	Strychnidin-10-one, 2,3-dimethoxy-	ON1030
P108	**57-24-9	Strychnine, & salts	ON1103
P115	7446-18-6	Sulfuric acid, dithallium(1+) salt	ON1105
P110	78-00-2	Tetraethyl lead	ON1094
P111	107-49-3	Tetraethyl pyrophosphate	ON1098
P109	3689-24-5	Tetraethyldithiopyrophosphate	ON1059
P112	509-14-8	Tetranitromethane	ON1080
P062	757-58-4	Tetraphosphoric acid, hexaethyl ester	ON1072
P113	1314-32-5	Thallic oxide	ON1104
P113	1314-32-5	Thallium oxide Tl2O3	ON1104
P114	12039-52-0	Thallium(I) selenite	ON1106
P115	7446-18-6	Thallium(I) sulfate	ON1105
P109	3689-24-5	Thiodiphosphoric acid, tetraethyl ester	ON1059
P045	39196-18-4	Thiofanox	ON1049
P049	541-53-7	Thioimidodicarbonic diamide [(H2N)C(S)]2NH	ON1058
P014	108-98-5	Thiophenol	ON1026
P116	79-19-6	Thiosemicarbazide	ON1073
P026	5344-82-1	Thiourea, (2-chlorophenyl)-	ON1037
P072	86-88-4	Thiourea, 1-naphthalenyl-	ON1083
P093	103-85-5	Thiourea, phenyl-	ON1092
P185	26419-73-8	Tirpate
P123	8001-35-2	Toxaphene	ON1032
P118	75-70-7	Trichloromethanethiol	ON1081
P119	7803-55-6	Vanadic acid, ammonium salt	ON1014
P120	1314-62-1	Vanadium oxide V2O5	ON1107
P120	1314-62-1	Vanadium pentoxide	ON1107
P084	4549-40-0	Vinylamine, N-methyl-N-nitroso-	ON1063
P001	**81-81-2	Warfarin, & salts, when present at concentrations greater than 0.3%	ON1006
P121	557-21-1	Zinc cyanide	ON1108
P121	557-21-1	Zinc cyanide Zn(CN)2	ON1108
P122	1314-84-7	Zinc phosphide Zn3P2, when present at concentrations greater than 10%	ON1109
P205	137-30-4	Zinc, bis(dimethylcarbamodithioato-S,S')-,
P205	137-30-4	Ziram

 

schedule 2
Part B — Hazardous Waste Chemicals

Hazardous Waste No.		Chemical Abstracts No.	Substance	Reference Number
U021		92-87-5	[1,1-Biphenyl]-4,4-diamine	ON2064
U073		91-94-1	[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dichloro-	ON2071
U091		119-90-4	[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethoxy-	ON2072
U095		119-93-7	[1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethyl-	ON2073
U208		630-20-6	1,1,1,2-Tetrachloroethane	ON2158
U209		79-34-5	1,1,2,2-Tetrachloroethane	ON2159
U227		79-00-5	1,1,2-Trichloroethane	ON2162
U078		75-35-4	1,1-Dichloroethylene	ON2128
U098		57-14-7	1,1-Dimethylhydrazine	ON2144
U207		95-94-3	1,2,4,5-Tetrachlorobenzene	ON2061
U085		1464-53-5	1,2:3,4-Diepoxybutane	ON2070
U069		84-74-2	1,2-Benzenedicarboxylic acid, dibutyl ester	ON2037
U088		84-66-2	1,2-Benzenedicarboxylic acid, diethyl ester	ON2038
U102		131-11-3	1,2-Benzenedicarboxylic acid, dimethyl ester	ON2039
U107		117-84-0	1,2-Benzenedicarboxylic acid, dioctyl ester	ON2040
U028		117-81-7	1,2-Benzenedicarboxylic acid,bis(2-ethylhexyl) ester	ON2036
U202		**81-07-2	1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, & salts	ON2065
U066		96-12-8	1,2-Dibromo-3-chloropropane	ON2124
U079		156-60-5	1,2-Dichloroethylene	ON2129
U099		540-73-8	1,2-Dimethylhydrazine	ON2145
U109		122-66-7	1,2-Diphenylhydrazine	ON2148
U155		91-80-5	1,2-Ethanediamine,N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)-	ON2202
U193		1120-71-4	1,2-Oxathiolane, 2,2-dioxide	ON2216
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-	ON2118
U234		99-35-4	1,3,5-Trinitrobenzene	ON2063
U182		123-63-7	1,3,5-Trioxane, 2,4,6-trimethyl-	ON2217
U201		108-46-3	1,3-Benzenediol	ON2046
U364		22961-82-6	1,3-Benzodioxol-4-ol, 2,2-dimethyl-,
U278		22781-23-3	1,3-Benzodioxol-4-ol, 2,2-dimethyl-,methyl carbamate
U141		120-58-1	1,3-Benzodioxole, 5-(1-propenyl)-	ON2054
U203		94-59-7	1,3-Benzodioxole, 5-(2-propenyl)-	ON2053
U090		94-58-6	1,3-Benzodioxole, 5-propyl-	ON2055
U128		87-68-3	1,3-Butadiene, 1,1,2,3,4,4-hexachloro-	ON2079
U130		77-47-4	1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro-	ON2112
U084		542-75-6	1,3-Dichloropropene	ON2135
U190		85-44-9	1,3-Isobenzofurandione	ON2035
U186		504-60-9	1,3-Pentadiene	ON2203
U193		1120-71-4	1,3-Propane sultone	ON2216
U074		764-41-0	1,4-Dichloro-2-butene	ON2086
U108		123-91-1	1,4-Diethyleneoxide	ON2136
U108		123-91-1	1,4-Dioxane	ON2136
U166		130-15-4	1,4-Naphthalenedione	ON2208
U166		130-15-4	1,4-Naphthoquinone	ON2208
U172		924-16-3	1-Butanamine, N-butyl-N-nitroso-	ON2080
U031		71-36-3	1-Butanol	ON2082
U011		61-82-5	1H-1,2,4-Triazol-3-amine	ON2016
U186		504-60-9	1-Methylbutadiene	ON2203
U167		134-32-7	1-Naphthalenamine	ON2210
U279		63-25-2	1-Naphthalenol, methylcarbamate
U194		107-10-8	1-Propanamine	ON2224
U111		621-64-7	1-Propanamine, N-nitroso-N-propyl-	ON2150
U110		142-84-7	1-Propanamine, N-propyl-	ON2149
U235		126-72-7	1-Propanol, 2,3-dibromo-, phosphate (3:1)	ON2225
U140		78-83-1	1-Propanol, 2-methyl-	ON2189
U243		1888-71-7	1-Propene, 1,1,2,3,3,3-hexachloro-	ON2184
U084		542-75-6	1-Propene, 1,3-dichloro-	ON2135
U085		1464-53-5	2,2-Bioxirane	ON2070
F027		58-90-2	2,3,4,6-Tetrachlorophenol	ON2219
U237		66-75-1	2,4-(1H,3H)-Pyrimidinedione, 5-[bis(2-chloroethyl)amino]-	ON2237
F027		93-76-5	2,4,5-T	ON2233
F027		95-95-4	2,4,5-Trichlorophenol	ON2220
U408		118-79-6	2,4,6-Tribromophenol
F027		88-06-2	2,4,6-Trichlorophenol	ON2221
U240		**94-75-7	2,4-D, salts & esters	ON2114
U081		120-83-2	2,4-Dichlorophenol	ON2132
U101		105-67-9	2,4-Dimethylphenol	ON2146
U105		121-14-2	2,4-Dinitrotoluene	ON2051
U197		106-51-4	2,5-Cyclohexadiene-1,4-dione	ON2068
U147		108-31-6	2,5-Furandione	ON2177
U082		87-65-0	2,6-Dichlorophenol	ON2133
U106		606-20-2	2,6-Dinitrotoluene	ON2052
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	ON2209
U005		53-96-3	2-Acetylaminofluorene	ON2004
U159		78-93-3	2-Butanone	ON2083
U160		1338-23-4	2-Butanone, peroxide	ON2084
U053		4170-30-3	2-Butenal	ON2085
U074		764-41-0	2-Butene, 1,4-dichloro-	ON2086
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]]-	ON2190
U042		110-75-8	2-Chloroethyl vinyl ether	ON2103
U125		98-01-1	2-Furancarboxaldehyde	ON2176
U058		50-18-0	2H-1,3,2-Oxazaphosphorin-2-amine,N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide	ON2113
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	ON2009
U116		96-45-7	2-Imidazolidinethione	ON2169
U168		91-59-8	2-Naphthalenamine	ON2211
U171		79-46-9	2-Nitropropane	ON2213
U191		109-06-8	2-Picoline	ON2223
U002		67-64-1	2-Propanone	ON2226
U007		79-06-1	2-Propenamide	ON2012
U009		107-13-1	2-Propenenitrile	ON2014
U152		126-98-7	2-Propenenitrile, 2-methyl-	ON2195
U008		79-10-7	2-Propenoic acid	ON2013
U118		97-63-2	2-Propenoic acid, 2-methyl-, ethyl ester	ON2170
U162		80-62-6	2-Propenoic acid, 2-methyl-, methyl ester	ON2205
U113		140-88-5	2-Propenoic acid, ethyl ester	ON2167
U073		91-94-1	3,3'-Dichlorobenzidine	ON2071
U091		119-90-4	3,3'-Dimethoxybenzidine	ON2072
U095		119-93-7	3,3'-Dimethylbenzidine	ON2073
U148		123-33-1	3,6-Pyridazinedione, 1,2-dihydro-	ON2141
U157		56-49-5	3-Methylcholanthrene	ON2021
U164		56-04-2	4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo-	ON2206
U158		101-14-4	4,4'-Methylenebis(2-chloroaniline)	ON2028
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-	ON2099
U030		101-55-3	4-Bromophenyl phenyl ether	ON2033
U049		3165-93-3	4-Chloro-o-toluidine, hydrochloride	ON2026
U161		108-10-1	4-Methyl-2-pentanone	ON2204
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)-	ON2115
U181		99-55-8	5-Nitro-o-toluidine	ON2030
U094		57-97-6	7,12-Dimethylbenz[a]anthracene	ON2025
U367		1563-38-8	7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-
U394		30558-43-1	A2213
U001		75-07-0	Acetaldehyde	ON2001
U034		75-87-6	Acetaldehyde, trichloro-	ON2002
U187		62-44-2	Acetamide, N-(4-ethoxyphenyl)-	ON2003
U005		53-96-3	Acetamide, N-9H-fluoren-2-yl-	ON2004
U112		141-78-6	Acetic acid ethyl ester	ON2005
See F027		93-76-5	Acetic acid, (2,4,5-trichlorophenoxy)-	ON2233
U240		**94-75-7	Acetic acid, (2,4-dichlorophenoxy)-,salts & esters	ON2114
U144		301-04-2	Acetic acid, lead(2+) salt	ON2006
U214		563-68-8	Acetic acid, thallium(1+) salt	ON2007
U002		67-64-1	Acetone	ON2226
U003		75-05-8	Acetonitrile	ON2008
U004		98-86-2	Acetophenone	ON2010
U006		75-36-5	Acetyl chloride	ON2011
U007		79-06-1	Acrylamide	ON2012
U008		79-10-7	Acrylic acid	ON2013
U009		107-13-1	Acrylonitrile	ON2014
U096		80-15-9	alpha,alpha-Dimethylbenzylhydroperoxide	ON2143
U167		134-32-7	alpha-Naphthylamine	ON2210
U011		61-82-5	Amitrole	ON2016
U012		62-53-3	Aniline	ON2017
U136		75-60-5	Arsinic acid, dimethyl-	ON2087
U014		492-80-8	Auramine	ON2018
U015		115-02-6	Azaserine	ON2019
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)]-	ON2020
U280		101-27-9	Barban.
U364		22961-82-6	Bendiocarb phenol
U278		22781-23-3	Bendiocarb.
U271		17804-35-2	Benomyl.
U018		56-55-3	Benz[a]anthracene	ON2024
U094		57-97-6	Benz[a]anthracene, 7,12-dimethyl-	ON2025
U016		225-51-4	Benz[c]acridine	ON2022
U157		56-49-5	Benz[j]aceanthrylene, 1,2-dihydro-3-methyl-	ON2021
U017		98-87-3	Benzal chloride	ON2023
U192		23950-58-5	Benzamide,3,5-dichloro-N-(1,1-dimethyl-2-propynyl)-	ON2127
U012		62-53-3	Benzenamine	ON2017
U328		95-53-4	Benzenamine, 2-methyl-
U222		636-21-5	Benzenamine, 2-methyl-, hydrochloride	ON2029
U181		99-55-8	Benzenamine, 2-methyl-5-nitro-	ON2030
U014		492-80-8	Benzenamine, 4,4-carbonimidoylbis[N,N-dimethyl-	ON2018
U158		101-14-4	Benzenamine, 4,4-methylenebis[2-chloro-	ON2028
U049		3165-93-3	Benzenamine, 4-chloro-2-methyl-,hydrochloride	ON2026
U353		106-49-0	Benzenamine, 4-methyl-
U093		60-11-7	Benzenamine, N,N-dimethyl-4-(phenylazo)-	ON2027
U019		71-43-2	Benzene	ON2031
U055		98-82-8	Benzene, (1-methylethyl)-	ON2056
U017		98-87-3	Benzene, (dichloromethyl)-	ON2023
U023		98-07-7	Benzene, (trichloromethyl)-	ON2062
U247		72-43-5	Benzene, 1,1-(2,2,2-trichloroethylidene)bis[4- methoxy-	ON2163
U207		95-94-3	Benzene, 1,2,4,5-tetrachloro-	ON2061
U070		95-50-1	Benzene, 1,2-dichloro-	ON2041
U234		99-35-4	Benzene, 1,3,5-trinitro-	ON2063
U071		541-73-1	Benzene, 1,3-dichloro-	ON2042
U223		26471-62-5	Benzene, 1,3-diisocyanatomethyl-	ON2044
U072		106-46-7	Benzene, 1,4-dichloro-	ON2043
U030		101-55-3	Benzene, 1-bromo-4-phenoxy-	ON2033
U105		121-14-2	Benzene, 1-methyl-2,4-dinitro-	ON2051
U106		606-20-2	Benzene, 2-methyl-1,3-dinitro-	ON2052
U037		108-90-7	Benzene, chloro-	ON2034
U239		1330-20-7	Benzene, dimethyl-	ON2045
U127		118-74-1	Benzene, hexachloro-	ON2047
U056		110-82-7	Benzene, hexahydro-	ON2048
U220		108-88-3	Benzene, methyl-	ON2050
U169		98-95-3	Benzene, nitro-	ON2057
U183		608-93-5	Benzene, pentachloro-	ON2058
U185		82-68-8	Benzene, pentachloronitro-	ON2059
U061		50-29-3	Benzene,1,1-(2,2,2-trichloroethylidene)bis[4-chloro-	ON2117
U060		72-54-8	Benzene,1,1-(2,2-dichloroethylidene)bis[4-chloro-	ON2116
U038		510-15-6	Benzeneacetic acid,4-chloro-alpha- (4-chlorophenyl)-alpha-hydroxy-, ethyl ester	ON2032
U035		305-03-3	Benzenebutanoic acid, 4-[bis(2-chloroethyl)amino]-	ON2081
U221		25376-45-8	Benzenediamine, ar-methyl-	ON2121
U020		98-09-9	Benzenesulfonic acid chloride	ON2060
U020		98-09-9	Benzenesulfonyl chloride	ON2060
U021		92-87-5	Benzidine	ON2064
U022		50-32-8	Benzo[a]pyrene	ON2067
U064		189-55-9	Benzo[rst]pentaphene	ON2123
U023		98-07-7	Benzotrichloride	ON2062
U047		91-58-7	beta-Chloronaphthalene	ON2106
U168		91-59-8	beta-Naphthylamine	ON2211
U225		75-25-2	Bromoform	ON2078
U136		75-60-5	Cacodylic acid	ON2087
U032		13765-19-0	Calcium chromate	ON2088
U280		101-27-9	Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester
U409		23564-05-8	Carbamic acid, [1,2-phenylenebis (iminocarbonothioyl)]bis-, dimethyl ester
U271		17804-35-2	Carbamic acid, [1-[(butylamino)carbonyl]-1H-benzimidazol-2-yl]-, methyl ester
U372		10605-21-7	Carbamic acid, 1H-benzimidazol-2-yl,methyl ester
U238		51-79-6	Carbamic acid, ethyl ester	ON2089
U178		615-53-2	Carbamic acid, methylnitroso-, ethyl ester	ON2090
U373		122-42-9	Carbamic acid, phenyl-, 1-methylethyl ester
U097		79-44-7	Carbamic chloride, dimethyl-	ON2094
U114		**111-54-6	Carbamodithioic acid, 1,2-ethanediylbis-,salts & esters	ON2155
U389		2303-17-5	Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl)ester
U062		2303-16-4	Carbamothioic acid, bis(1-methylethyl)-S-(2,3-dichloro-2-propenyl) ester	ON2119
U387		52888-80-9	Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester
U279		63-25-2	Carbaryl.
U372		10605-21-7	Carbendazim
U367		1563-38-8	Carbofuran phenol
U033		353-50-4	Carbon oxyfluoride	ON2097
U211		56-23-5	Carbon tetrachloride	ON2098
U215		6533-73-9	Carbonic acid, dithallium(1+) salt	ON2095
U033		353-50-4	Carbonic difluoride	ON2097
U156		79-22-1	Carbonochloridic acid, methyl ester	ON2096
U034		75-87-6	Chloral	ON2002
U035		305-03-3	Chlorambucil	ON2081
U036		57-74-9	Chlordane, alpha & gamma isomers	ON2099
U026		494-03-1	Chlornaphazin	ON2100
U037		108-90-7	Chlorobenzene	ON2034
U038		510-15-6	Chlorobenzilate	ON2032
U044		67-66-3	Chloroform	ON2104
U046		107-30-2	Chloromethyl methyl ether	ON2105
U032		13765-19-0	Chromic acid H2CrO4, calcium salt	ON2088
U050		218-01-9	Chrysene	ON2069
U051		N/A	Creosote	ON2108
U052		1319-77-3	Cresol (Cresylic acid)	ON2109
U053		4170-30-3	Crotonaldehyde	ON2085
U055		98-82-8	Cumene	ON2056
U246		506-68-3	Cyanogen bromide (CN)Br	ON2077
U056		110-82-7	Cyclohexane	ON2048
U129		58-89-9	Cyclohexane, 1,2,3,4,5,6-hexachloro-,(1alpha,2alpha,3beta,4alpha,5alpha,6 beta)-	ON2182
U057		108-94-1	Cyclohexanone	ON2111
U058		50-18-0	Cyclophosphamide	ON2113
U059		20830-81-3	Daunomycin	ON2115
U060		72-54-8	DDD	ON2116
U061		50-29-3	DDT	ON2117
U206		18883-66-4	D-Glucose,2-deoxy-2-[[(methylnitrosoamino)-carbonyl]amino]-	ON2179
U062		2303-16-4	Diallate	ON2119
U063		53-70-3	Dibenz[a,h]anthracene	ON2122
U064		189-55-9	Dibenzo[a,i]pyrene	ON2123
U069		84-74-2	Dibutyl phthalate	ON2037
U075		75-71-8	Dichlorodifluoromethane	ON2126
U025		111-44-4	Dichloroethyl ether	ON2130
U027		108-60-1	Dichloroisopropyl ether	ON2075
U024		111-91-1	Dichloromethoxy ethane	ON2074
U088		84-66-2	Diethyl phthalate	ON2038
U395		5952-26-1	Diethylene glycol, dicarbamate
U028		117-81-7	Diethylhexyl phthalate	ON2036
U089		56-53-1	Diethylstilbesterol	ON2140
U090		94-58-6	Dihydrosafrole	ON2055
U102		131-11-3	Dimethyl phthalate	ON2039
U103		77-78-1	Dimethyl sulfate	ON2147
U092		124-40-3	Dimethylamine	ON2142
U097		79-44-7	Dimethylcarbamoyl chloride	ON2094
U107		117-84-0	Di-n-octyl phthalate	ON2040
U111		621-64-7	Di-n-propylnitrosamine	ON2150
U110		142-84-7	Dipropylamine	ON2149
U041		106-89-8	Epichlorohydrin	ON2102
U001		75-07-0	Ethanal	ON2001
U404		121-44-8	Ethanamine, N,N-diethyl-
U174		55-18-5	Ethanamine, N-ethyl-N-nitroso-	ON2151
U208		630-20-6	Ethane, 1,1,1,2-tetrachloro-	ON2158
U226		71-55-6	Ethane, 1,1,1-trichloro-	ON2161
U209		79-34-5	Ethane, 1,1,2,2-tetrachloro-	ON2159
U227		79-00-5	Ethane, 1,1,2-trichloro-	ON2162
U024		111-91-1	Ethane, 1,1'-[methylenebis(oxy)]bis[2-chloro-	ON2074
U076		75-34-3	Ethane, 1,1-dichloro-	ON2153
U117		60-29-7	Ethane, 1,1'-oxybis-	ON2137
U025		111-44-4	Ethane, 1,1'-oxybis[2-chloro-	ON2130
U067		106-93-4	Ethane, 1,2-dibromo-	ON2152
U077		107-06-2	Ethane, 1,2-dichloro-	ON2154
U131		67-72-1	Ethane, hexachloro-	ON2156
U184		76-01-7	Ethane, pentachloro-	ON2157
U218		62-55-5	Ethanethioamide	ON2160
U394		30558-43-1	Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-,methyl ester
U410		59669-26-0	Ethanimidothioic acid, N,N'-[thiobis[(methylimino)carbonyloxy]]bi s-, dimethyl ester
U173		1116-54-7	Ethanol, 2,2'-(nitrosoimino)bis-	ON2164
U395		5952-26-1	Ethanol, 2,2'-oxybis-, dicarbamate
U359		110-80-5	Ethanol, 2-ethoxy-	ON2239
U004		98-86-2	Ethanone, 1-phenyl-	ON2010
U042		110-75-8	Ethene, (2-chloroethoxy)-	ON2103
U078		75-35-4	Ethene, 1,1-dichloro-	ON2128
U079		156-60-5	Ethene, 1,2-dichloro-, (E)-	ON2129
U043		75-01-4	Ethene, chloro-	ON2165
U210		127-18-4	Ethene, tetrachloro-	ON2166
U228		79-01-6	Ethene, trichloro-	ON2236
U112		141-78-6	Ethyl acetate	ON2005
U113		140-88-5	Ethyl acrylate	ON2167
U238		51-79-6	Ethyl carbamate (urethane)	ON2089
U117		60-29-7	Ethyl ether	ON2137
U118		97-63-2	Ethyl methacrylate	ON2170
U119		62-50-0	Ethyl methanesulfonate	ON2171
U067		106-93-4	Ethylene dibromide	ON2152
U077		107-06-2	Ethylene dichloride	ON2154
U359		110-80-5	Ethylene glycol monoethyl ether	ON2239
U115		75-21-8	Ethylene oxide	ON2168
U114		**111-54-6	Ethylenebisdithiocarbamic acid, salts & esters	ON2155
U116		96-45-7	Ethylenethiourea	ON2169
U076		75-34-3	Ethylidene dichloride	ON2153
U120		206-44-0	Fluoranthene	ON2066
U122		50-00-0	Formaldehyde	ON2173
U123		64-18-6	Formic acid	ON2174
U124		110-00-9	Furan	ON2175
U213		109-99-9	Furan, tetrahydro-	ON2178
U125		98-01-1	Furfural	ON2176
U124		110-00-9	Furfuran	ON2175
U206		18883-66-4	Glucopyranose,2-deoxy-2-(3-methyl-3-nitrosoureido)-, D-	ON2179
U126		765-34-4	Glycidylaldehyde	ON2180
U163		70-25-7	Guanidine, N-methyl-N'-nitro-N-nitroso-	ON2181
U127		118-74-1	Hexachlorobenzene	ON2047
U128		87-68-3	Hexachlorobutadiene	ON2079
U130		77-47-4	Hexachlorocyclopentadiene	ON2112
U131		67-72-1	Hexachloroethane	ON2156
U132		70-30-4	Hexachlorophene	ON2183
U243		1888-71-7	Hexachloropropene	ON2184
U133		302-01-2	Hydrazine	ON2120
U098		57-14-7	Hydrazine, 1,1-dimethyl-	ON2144
U086		1615-80-1	Hydrazine, 1,2-diethyl-	ON2138
U099		540-73-8	Hydrazine, 1,2-dimethyl-	ON2145
U109		122-66-7	Hydrazine, 1,2-diphenyl-	ON2148
U134		7664-39-3	Hydrofluoric acid	ON2185
U134		7664-39-3	Hydrogen fluoride	ON2185
U135		7783-06-4	Hydrogen sulfide	ON2187
U135		7783-06-4	Hydrogen sulfide H2S	ON2187
U096		80-15-9	Hydroperoxide, 1-methyl-1-phenylethyl-	ON2143
U137		193-39-5	Indeno[1,2,3-cd]pyrene	ON2188
U140		78-83-1	Isobutyl alcohol	ON2189
U141		120-58-1	Isosafrole	ON2054
U142		143-50-0	Kepone	ON2118
U143		303-34-4	Lasiocarpine	ON2190
U144		301-04-2	Lead acetate	ON2006
U145		7446-27-7	Lead phosphate	ON2191
U146		1335-32-6	Lead subacetate	ON2192
U146		1335-32-6	Lead, bis(acetato-O)tetrahydroxytri-	ON2192
U129		58-89-9	Lindane	ON2182
U150		148-82-3	L-Phenylalanine, 4-[bis(2-chloroethyl)amino]-	ON2015
U015		115-02-6	L-Serine, diazoacetate (ester)	ON2019
U147		108-31-6	Maleic anhydride	ON2177
U148		123-33-1	Maleic hydrazide	ON2141
U149		109-77-3	Malononitrile	ON2193
U071		541-73-1	m-Dichlorobenzene	ON2042
U150		148-82-3	Melphalan	ON2015
U151		7439-97-6	Mercury	ON2194
U152		126-98-7	Methacrylonitrile	ON2195
U092		124-40-3	Methanamine, N-methyl-	ON2142
U029		74-83-9	Methane, bromo-	ON2196
U045		74-87-3	Methane, chloro-	ON2197
U046		107-30-2	Methane, chloromethoxy-	ON2105
U068		74-95-3	Methane, dibromo-	ON2125
U080		75-09-2	Methane, dichloro-	ON2131
U075		75-71-8	Methane, dichlorodifluoro-	ON2126
U138		74-88-4	Methane, iodo-	ON2198
U211		56-23-5	Methane, tetrachloro-	ON2098
U225		75-25-2	Methane, tribromo-	ON2078
U044		67-66-3	Methane, trichloro-	ON2104
U121		75-69-4	Methane, trichlorofluoro-	ON2200
U119		62-50-0	Methanesulfonic acid, ethyl ester	ON2171
U153		74-93-1	Methanethiol	ON2199
U154		67-56-1	Methanol	ON2201
U155		91-80-5	Methapyrilene	ON2202
U247		72-43-5	Methoxychlor	ON2163
U154		67-56-1	Methyl alcohol	ON2201
U029		74-83-9	Methyl bromide	ON2196
U045		74-87-3	Methyl chloride	ON2197
U156		79-22-1	Methyl chlorocarbonate	ON2096
U226		71-55-6	Methyl chloroform	ON2161
U159		78-93-3	Methyl ethyl ketone (MEK)	ON2083
U160		1338-23-4	Methyl ethyl ketone peroxide	ON2084
U138		74-88-4	Methyl iodide	ON2198
U161		108-10-1	Methyl isobutyl ketone	ON2204
U162		80-62-6	Methyl methacrylate	ON2205
U068		74-95-3	Methylene bromide	ON2125
U080		75-09-2	Methylene chloride	ON2131
U164		56-04-2	Methylthiouracil	ON2206
U010		50-07-7	Mitomycin C	ON2020
U163		70-25-7	MNNG	ON2181
U086		1615-80-1	N,N'-Diethylhydrazine	ON2138
U026		494-03-1	Naphthalenamine, N,N'-bis(2-chloroethyl)-	ON2100
U165		91-20-3	Naphthalene	ON2207
U047		91-58-7	Naphthalene, 2-chloro-	ON2106
U031		71-36-3	n-Butyl alcohol	ON2082
U217		10102-45-1	Nitric acid, thallium(1+) salt	ON2235
U169		98-95-3	Nitrobenzene	ON2057
U173		1116-54-7	N-Nitrosodiethanolamine	ON2164
U174		55-18-5	N-Nitrosodiethylamine	ON2151
U172		924-16-3	N-Nitrosodi-n-butylamine	ON2080
U176		759-73-9	N-Nitroso-N-ethylurea	ON2091
U177		684-93-5	N-Nitroso-N-methylurea	ON2092
U178		615-53-2	N-Nitroso-N-methylurethane	ON2090
U179		100-75-4	N-Nitrosopiperidine	ON2214
U180		930-55-2	N-Nitrosopyrrolidine	ON2215
U194		107-10-8	n-Propylamine	ON2224
U087		3288-58-2	O,O-Diethyl S-methyl dithiophosphate	ON2139
U048		95-57-8	o-Chlorophenol	ON2107
U070		95-50-1	o-Dichlorobenzene	ON2041
U328		95-53-4	o-Toluidine
U222		636-21-5	o-Toluidine hydrochloride	ON2029
U115		75-21-8	Oxirane	ON2168
U041		106-89-8	Oxirane, (chloromethyl)-	ON2102
U126		765-34-4	Oxiranecarboxyaldehyde	ON2180
U182		123-63-7	Paraldehyde	ON2217
U197		106-51-4	p-Benzoquinone	ON2068
U039		59-50-7	p-Chloro-m-cresol	ON2101
U072		106-46-7	p-Dichlorobenzene	ON2043
U093		60-11-7	p-Dimethylaminoazobenzene	ON2027
U183		608-93-5	Pentachlorobenzene	ON2058
U184		76-01-7	Pentachloroethane	ON2157
U185		82-68-8	Pentachloronitrobenzene (PCNB)	ON2059
F027		87-86-5	Pentachlorophenol	ON2218
U161		108-10-1	Pentanol, 4-methyl-	ON2204
U187		62-44-2	Phenacetin	ON2003
U188		108-95-2	Phenol	ON2049
U411		114-26-1	Phenol, 2-(1-methylethoxy)-,methylcarbamate
F027		58-90-2	Phenol, 2,3,4,6-tetrachloro-	ON2219
F027		95-95-4	Phenol, 2,4,5-trichloro-	ON2220
F027		88-06-2	Phenol, 2,4,6-trichloro-	ON2221
U081		120-83-2	Phenol, 2,4-dichloro-	ON2132
U101		105-67-9	Phenol, 2,4-dimethyl-	ON2146
U082		87-65-0	Phenol, 2,6-dichloro-	ON2133
U048		95-57-8	Phenol, 2-chloro-	ON2107
U089		56-53-1	Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)-	ON2140
U039		59-50-7	Phenol, 4-chloro-3-methyl-	ON2101
U170		100-02-7	Phenol, 4-nitro-	ON2212
U052		1319-77-3	Phenol, methyl-	ON2109
F027		87-86-5	Phenol, pentachloro-	ON2218
U132		70-30-4	Phenol,2,2'-methylenebis[3,4,6-trichloro-	ON2183
U145		7446-27-7	Phosphoric acid, lead(2+) salt (2:3)	ON2191
U087		3288-58-2	Phosphorodithioic acid, O,O-diethyl S-methyl ester	ON2139
U189		1314-80-3	Phosphorus sulfide	ON2222
U190		85-44-9	Phthalic anhydride	ON2035
U179		100-75-4	Piperidine, 1-nitroso-	ON2214
U170		100-02-7	p-Nitrophenol	ON2212
U192		23950-58-5	Pronamide	ON2127
U066		96-12-8	Propane, 1,2-dibromo-3-chloro-	ON2124
U083		78-87-5	Propane, 1,2-dichloro-	ON2134
U027		108-60-1	Propane, 2,2'-oxybis[2-chloro-	ON2075
U171		79-46-9	Propane, 2-nitro-	ON2213
U149		109-77-3	Propanedinitrile	ON2193
F027		93-72-1	Propanoic acid, 2-(2,4,5-0 trichlorophenoxy)-	ON2227
U373		122-42-9	Propham
U411		114-26-1	Propoxur.
U083		78-87-5	Propylene dichloride	ON2134
U387		52888-80-9	Prosulfocarb
U353		106-49-0	p-Toluidine
U196		110-86-1	Pyridine	ON2228
U191		109-06-8	Pyridine, 2-methyl-	ON2223
U180		930-55-2	Pyrrolidine, 1-nitroso-	ON2215
U200		50-55-5	Reserpine	ON2229
U201		108-46-3	Resorcinol	ON2046
U202		**81-07-2	Saccharin, & salts	ON2065
U203		94-59-7	Safrole	ON2053
U204		7783-00-8	Selenious acid	ON2230
U204		7783-00-8	Selenium dioxide	ON2230
U205		7488-56-4	Selenium sulfide	ON2232
U205		7488-56-4	Selenium sulfide SeS2	ON2232
F027		93-72-1	Silvex (2,4,5-TP)	ON2227
U206		18883-66-4	Streptozotocin	ON2179
U189		1314-80-3	Sulfur phosphide	ON2222
U103		77-78-1	Sulfuric acid, dimethyl ester	ON2147
U210		127-18-4	Tetrachloroethylene	ON2166
U213		109-99-9	Tetrahydrofuran	ON2178
U216		7791-12-0	Thallium chloride TlCl	ON2234
U214		563-68-8	Thallium(I) acetate	ON2007
U215		6533-73-9	Thallium(I) carbonate	ON2095
U216		7791-12-0	Thallium(I) chloride	ON2234
U217		10102-45-1	Thallium(I) nitrate	ON2235
U218		62-55-5	Thioacetamide	ON2160
U410		59669-26-0	Thiodicarb
U153		74-93-1	Thiomethanol	ON2199
U244		137-26-8	Thioperoxydicarbonic diamide[(H2N)C(S)]2S2, tetramethyl-	ON2076
U409		23564-05-8	Thiophanate-methyl
U219		62-56-6	Thiourea	ON2093
U244		137-26-8	Thiram	ON2076
U220		108-88-3	Toluene	ON2050
U223		26471-62-5	Toluene diisocyanate	ON2044
U221		25376-45-8	Toluenediamine	ON2121
U389		2303-17-5	Triallate
U228		79-01-6	Trichloroethylene	ON2236
U121		75-69-4	Trichloromonofluoromethane	ON2200
U404		121-44-8	Triethylamine
U235		126-72-7	Tris(2,3-dibromopropyl) phosphate	ON2225
U236		72-57-1	Trypan blue	ON2209
U237		66-75-1	Uracil mustard	ON2237
U176		759-73-9	Urea, N-ethyl-N-nitroso-	ON2091
U177		684-93-5	Urea, N-methyl-N-nitroso-	ON2092
U043		75-01-4	Vinyl chloride	ON2165
U248		** 81-81-2	Warfarin, & salts, when present at concentrations of 0.3% or less	ON2009
U239		1330-20-7	Xylene	ON2045
U200		50-55-5	Yohimban-16-carboxylic acid,11,17-dimethoxy-18-[(3,4,5-trimethoxybenzoyl)oxy]-,methyl ester,(3beta,16beta,17alpha, 18beta,20alpha)-	ON2229
U249		1314-84-7	Zinc phosphide Zn3P2, when present at concentrations of 10% or less	ON2238
	** CAS number given for parent compound only

O. Reg. 558/00, s. 4.

Schedule 2.1
Exempt Acute Hazardous Waste Chemicals

Industry and Site	Waste
	There are no wastes currently listed in this Schedule.

O. Reg. 460/99, s. 8.

Schedule 2.2
Exempt Hazardous Waste Chemicals

Industry and Site	Waste
	There are no wastes currently listed in this Schedule.

O. Reg. 460/99, s. 8.

Schedule 3
SEVERELY TOXIC CONTAMINANTS

ReferenceNumber	Contaminant
ON3001	Aflatoxin
ON3002	2,3,7,8-Tetrachlorodibenzo-p-dioxin
ON3003	1,2,3,7,8-Pentachlorodibenzo-p-dioxin
ON3004	1,2,3,4,7,8-Hexachlorodibenzo-p-dioxin
ON3005	1,2,3,6,7,8-Hexachlorodibenzo-p-dioxin
ON3006	1,2,3,7,8,9-Hexachlorodibenzo-p-dioxin
ON3007	2,3,7,8-Tetrachlorodlbenzo furan

R.R.O. 1990, Reg. 347, Sched. 3.

Schedule 4
LEACHATE QUALITY CRITERIA

Contaminant	Concentration (mg/l)
Aldicarb	0.9
Aldrin + Dieldrin	0.07
Arsenic	2.5
Atrazine + N-dealkylated metabolites (Weedex)	0.5
Azinphos-methyl	2.0
Barium	100.0
Bendiocarb	4.0
Benzene	0.5
Benzo(a)pyrene	0.001
Boron	500.0
Bromoxynil	0.5
Cadmium	0.5
Carbaryl/Sevin/1-Naphthyl-N methyl carbamate	9.0
Carbofuran	9.0
Carbon tetrachloride (Tetrachloromethane)	0.5
Chlordane	0.7
Chlorobenzene (Monochlorobenzene)	8.0
Chloroform	10.0
Chlorpyrifos	9.0
Chromium	5.0
Cresol (Mixture — total of all isomers, when isomers cannot be differentiated)	200.0
m-Cresol	200.0
o-Cresol	200.0
p-Cresol	200.0
Cyanazine	1.0
Cyanide	20.0
2,4-D / (2,4-dichlorophenoxy)acetic acid	10.0
2,4-DCP (2,4-Dichlorophenol)	90.0
DDT (total isomers)	3.0
Diazinon/Phosphordithioic acid, o,o-diethyl o-(2-isopropyl 6-methyl-4-pyrimidinyl) ester	2.0
Dicamba	12.0
1,2-Dichlorobenzene (o-Dichlorobenzene)	20.0
1,4-Dichlorobenzene (p-Dichlorobenzene)	0.5
1,2-Dichloroethane (Ethylene dichloride)	0.5
1,1-Dichloroethylene (Vinylidene chloride)	1.4
Dichloromethane (also see — methylene chloride)	5.0
Diclofop-methyl	0.9
Dimethoate	2.0
2,4-Dinitrotoluene	0.13
Dinoseb	1.0
Dioxin & Furan	0.0000015*
Diquat	7.0
Diuron	15.0
Endrin	0.02
Fluoride	150.0
Glyphosate	28.0
Heptachlor + Heptachlor epoxide	0.3
Hexachlorobenzene	0.13
Hexachlorobutadiene	0.5
Hexachloroethane	3.0
Lead	5.0
Lindane	0.4
Malathion	19.0
Mercury	0.1
Methoxychlor/1,1,1-Trichloro-2,2-bis(p-methoxyphenyl) ethane	90.0
Methyl ethyl ketone / Ethyl methyl ketone	200.0
Methyl Parathion	0.7
Methylene chloride / Dichloromethane	5.0
Metolachlor	5.0
Metribuzin	8.0
NDMA	0.0009
Nitrate + Nitrite (as Nitrogen)	1,000.0
Nitrilotriacetic acid (NTA)	40.0
Nitrobenzene	2.0
Paraquat	1.0
Parathion	5.0
PCBs	0.3
Pentachlorophenol	6.0
Phorate	0.2
Picloram	19.0
Pyridine	5.0
Selenium	1.0
Silver	5
Simazine	1.0
2,4,5-T (2,4,5-Trichlorophenoxyacetic acid)	28.0
2,4,5-TP/ Silvex/ 2-(2,4,5-Trichlorophenoxy)propionic acid	1.0
Temephos	28.0
Terbufos	0.1
Tetrachloroethylene	3.0
2,3,4,6-Tetrachlorophenol /(2,3,4,6-TeCP)	10.0
Toxaphene	0.5
Triallate	23.0
Trichloroethylene	5.0
2,4,5-Trichlorophenol (2,4,5-TCP)	400.0
2,4,6-Trichlorophenol (2,4,6-TCP)	0.5
Trifluralin	4.5
Uranium	10.0
Vinyl chloride	0.2
* Toxic equivalent (TEQ)

O. Reg. 558/00, s. 5.

Schedule 5
TEST METHOD FOR THE DETERMINATION OF “LIQUID WASTE” (SLUMP TEST)*

 (1) Sampling

Obtain a representative sample of the waste to be tested.

(2) Equipment

2.1 Mould — the representative waste sample shall be formed in a mould, in the form of the frustum of a cone with the base 200 mm in diameter, the top 100 mm in diameter, and the height 300 mm. The base and the top shall be open and parallel to each other and at right angles to the axis of the cone. The mould shall be made of a metal that is chemically resistant to the wastes to be tested and that has a thickness that is at least 1.5 mm. It shall be provided with foot pieces and handles as shown in Figure 1.

2.2 Tamping Rod — the rod shall be round, straight and steel with a diameter of 16 mm and a length of 600 mm. One end shall be rounded to a hemispherical tip with a diameter of 16 mm.

(3) Procedure

3.1 Dampen the mould and place it on a flat, moist, non-absorbent (rigid) surface. Hold the mould firmly in place during filling by standing on the two foot pieces. From the sample of the material obtained, immediately fill the mould in three layers, each approximately one-third the volume of the mould.

Notes:

1) The test must be carried out at a temperature of not less than 10°C.

2) One-third of the volume of the slump mould fills it to a depth of 70 mm. Two-thirds of the volume fills it to a depth of 160 mm.

3.2 Rod each layer with 25 strokes of the tamping rod. Uniformly distribute the strokes over the cross-section of each layer.  For the bottom layer this will necessitate inclining the rod slightly and making approximately half of the strokes near the perimeter, and then progressing with vertical strokes spirally toward the center.  Rod layers throughout their depth.  For the second layer and the top layer, the strokes must just penetrate into the underlying layers.

3.3 When filling and rodding the top layer, heap the material above the mould before rodding is started.  If the rodding operation results in subsidence of the material below the top edge of the mould, add additional material to maintain an excess of material above the top of the mould.  After the top layer has been rodded, the excess material shall be screeded off to the level of the top of the mould. Remove the spilled material from the base of the mould.

3.4 Withdraw the mould immediately from the material by raising it carefully in a vertical direction.  The operation of raising the mould shall be performed in approximately 5 seconds by a steady upward lift with no lateral or torsional motion.  The entire operation from the start of the filling through removal of the mould shall be carried out without interruption and shall be completed within 2 minutes.

3.5 Determine the slump immediately after by measuring the difference between the height of the mould and the average height of the top surface of the material after subsidence.

Notes:

1) Waste samples that break or slump laterally give incorrect results.  When this condition occurs, the test shall be repeated with a new sample.

2) If two consecutive tests on a sample of material show a falling away or shearing off of a portion of the material from the mass of the specimen, the material probably lacks necessary plasticity and cohesiveness for the slump test to be applicable.

3) Duplicate tests on two different portions of the sample should not vary more than 10 mm.

(4) Report

4.1 Record the slump in millimeters to the nearest 10 mm of subsidence of the sample during the test.

Insert regs\graphics\1990\347\347fg01a.tif

O. Reg. 558/00, s. 5.