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Notice

Vol. 140, No. 50 =97 December 16, 2006

Perfluorooctane Sulfonate and its Salts and Certain = Other=20 Compounds Regulations

Statutory authority

Canadian Environmental Protection Act, 1999

Sponsoring department

Department of the Environment

REGULATORY IMPACT = ANALYSIS=20 STATEMENT

(This statement is not part of the=20 Regulations.)

Description

The proposed Perfluorooctane Sulfonate and its Salts and = Certain=20 Other Compounds Regulations (hereinafter referred to as the = proposed=20 Regulations) are to be made under subsection 93(1) and section 319 = of the=20 Canadian Environmental Protection Act, 1999 (CEPA 1999). = The=20 purpose of the proposed Regulations is to prevent the risks posed = to=20 Canada's environment from the use and release of perfluorooctane=20 sulfonate, its salts and certain other compounds that contain the=20 C₈F₁₇SO₂,₌₂₀C₈F₁₇SO₃ or₌₂₀C₈F₁₇SO₂N group (referred = to=20 hereinafter as PFOS) by those that either use the substance as = such or use=20 certain products containing the substance (referred to hereinafter = as=20 "user" or "users"). The proposed Regulations would prohibit the=20 manufacture, use, sale, offer for sale and import of PFOS, as well = as=20 manufactured items containing PFOS, other than a limited number of = exemptions outlined in the proposed Regulations.

The proposed Regulations will come into force on the day they = are=20 registered by the Clerk of the Privy Council.

Background

On July 1, 2006, the Ministers of the Environment and of Health = published their final decision on the screening assessment of PFOS = in the=20 Canada Gazette, Part I, and proposed to recommend that = PFOS be=20 added to the List of Toxic Substances in Schedule 1 to CEPA 1999. = On July=20 1, 2006, an order was published in the Canada Gazette, = Part I,=20 proposing that PFOS be added to the List of Toxic Substances in = Schedule 1=20 of CEPA 1999. The screening assessment report concluded that PFOS = meets=20 the criteria set out in paragraph 64(a) of CEPA 1999 and = is or=20 may be entering the environment in a quantity or concentration or = under=20 conditions that have or may have an immediate or long-term harmful = effect=20 on the environment or its biological diversity. However, the human = health=20 screening assessment report concluded that current levels of = exposure for=20 PFOS are below levels which might affect human health.

PFOS, its salts and certain other compounds belong to the = larger class=20 of fluorochemicals referred to as perfluorinated alkyl (PFA) = compounds=20 which contain carbons that are completely saturated by fluorine. = It is the=20 strength of the carbon-fluorine bonds that contributes to the = extreme=20 stability and unique properties of these perfluorochemicals.

Use profile

PFOS substances are not manufactured in or exported from = Canada, but in=20 the past, were typically imported as raw chemicals, in products = and=20 formulations and in manufactured items. During the 1997 to 2000 = time=20 period, approximately 600 tonnes of PFA compounds were imported = into=20 Canada, with all PFOS substances accounting for 43% of imported = PFA=20 compounds. The primary uses of these substances were applications=20 involving water, oil, soil and grease repellents for fabric, = leather,=20 packaging and rugs and carpets, as well as additives in = firefighting foams=20 and paints and coatings.

Between 2000 and 2002, the primary international manufacturer = of PFOS=20 voluntarily phased out its production of PFOS. The use trend in = Canada,=20 therefore, significantly dropped after 2002. Background = information=20 collected in support of these Regulations indicates that, since = 2002,=20 imports of PFOS as raw chemicals, in products or formulations into = Canada=20 have essentially ceased. This finding was then confirmed by a use = pattern=20 survey published on January 15, 2005, under the authority of CEPA = 1999.=20 The survey targeted manufacturers, exporters and importers of PFOS = in=20 amounts exceeding 100 kg and in concentrations of greater than 10 = g/kg for=20 the 2004 calendar year. In summary, the survey results indicate = that

There are no manufacturers or exporters of PFOS in Canada;=20
Approximately 3 tonnes of PFOS were imported in 2004 for use = as a=20 surfactant in fume suppressants for the metal plating sector; = and=20
With the exception of an estimated 300 tonne stockpile of = aqueous=20 film forming foam (AFFF) [representing approximately 3 tonnes of = PFOS]=20 used for firefighting, it is very likely that most inventories = of PFOS=20 in all other sectors have been depleted.

Based on these survey results, the use of PFOS in areas of = concern is=20 discussed below:

Metal plating=20 sector: The chromium electroplating, anodizing and = reverse=20 etching sector in Canada represents the largest use of PFOS fume=20 suppressants in Canada. This sector consists of approximately 219 = users,=20 located in British Columbia (29), the Prairie Provinces (43), = Ontario=20 (91), Quebec (48), and Atlantic Canada (8). About half of these = facilities=20 use fume suppressants that contain PFOS.

PFOS-based surfactants are used in the chromium electroplating, = chromium anodizing, reverse etching, electroless=20 nickel-polytetrafluoroethylene plating and in the etching of = plastic=20 substrates prior to metallization operations. PFOS may enter the=20 environment via the rinse water that may be discharged to the = municipal=20 sewer systems from these operations. PFOS is not removed from = wastewater=20 in conventional treatment facilities and has been observed in = effluent=20 from primary and secondary wastewater treatment facilities and in = the=20 sewage sludge that is generated by wastewater treatment = facilities. PFOS=20 is also contained in the metal sludge that is sent off-site to = hazardous=20 waste or metal recycling facilities.

Aqueous film = forming foams=20 (AFFF) for fire fighting: AFFF is primarily = used for=20 fuel-related fires at industrial facilities, in municipalities, = military=20 establishments and airports. Releases of PFOS may occur when foam = is=20 discharged during testing and training exercises, when fighting = fuel=20 fires, during accidental releases or when out-of-date AFFF must be = retired=20 and sent for disposal. These activities may result in the direct = discharge=20 of AFFF to surface water, groundwater and land. Depending on the = nature of=20 the activity, it is not always possible to collect and pre-treat = or=20 contain the AFFF residual for proper disposal. With the voluntary=20 phase-out in production by the largest international PFOS = manufacturer=20 between 2000 and 2002, PFOS-based AFFF can no longer be purchased. = Alternative non-PFOS-based AFFFs now dominate the marketplace. = However,=20 since the average useful service life of AFFF can be in the order = of 25=20 years or longer, the existing PFOS-based AFFF stockpiles estimated = at 300=20 tonnes must be addressed. These stockpiles are located at = military,=20 petroleum and petrochemical facilities, airports, municipalities = and first=20 responder organizations across Canada.

Imported = manufactured=20 items: PFOS may also be contained in imported = manufactured=20 items. As discussed above, the majority of past PFOS use was as = water,=20 oil, soil and grease repellents (e.g. on fabric, leather, paper,=20 packaging, rugs and carpets) and as surfactants (e.g. coating = additives).=20 Before the announcement by the largest international PFOS = manufacturer in=20 May 2000 to phase out the production of PFOS between 2000 and = 2002,=20 approximately 80% of Canadian imports of manufactured items = containing=20 PFOS were produced in the United States, with the remaining 20% of = the=20 imports coming mainly from Germany and the East Asian countries, = namely=20 China and India. The risk of PFOS-related substances being = imported into=20 Canada has significantly decreased since the United States and the = European Union (EU), which represent a major source of all = Canadian=20 imports of products that historically contain PFOS, are currently=20 restricting or planning to restrict PFOS production, use and = importation.=20 However, the increasing rate of growth of Asian imports, = especially of=20 apparel products, highlights a compliance concern associated with = imported=20 products which may contain PFOS. Therefore, despite the voluntary=20 phase-out of PFOS production by the major global manufacturer, and = the=20 current low level of PFOS imports, the potential does exist for = PFOS and=20 PFOS-containing products and manufactured items to be imported = into Canada=20 in greater quantities in the future, as some PFOS production has = been=20 identified in other countries.

Environmental objective

The screening assessment report concluded that PFOS substances = are=20 entering into the environment in a quantity or concentration or = under=20 conditions that have or may have an immediate or long-term harmful = effect=20 on the environment or its biological diversity. Furthermore, the = screening=20 assessment report concluded that PFOS and its salts are persistent = and a=20 potential risk may occur through bioaccumulation and = biomagnification of=20 PFOS in wildlife.

PFOS is present in the environment primarily as a result of = human=20 activity and has been detected in animals worldwide. In Canada, = PFOS has=20 been detected in species such as fish, fish-eating birds, and = Arctic=20 marine mammals far from known sources or manufacturing = facilities.

Given the conclusions of the screening assessment report, PFOS, = its=20 salts and certain other compounds will be managed as a group under = the=20 provisions of CEPA 1999 with the objective of achieving the lowest = level=20 of releases to the environment that is technically and = economically=20 feasible from all sources.

International actions on PFOS

As detailed below, a number of countries and organizations have = either=20 put in place or are proposing management measures to control the=20 manufacture, import, use and releases of PFOS and manufactured = articles=20 containing PFOS.

(a) The United States Environmental Protection Agency = (US EPA)=20 has adopted federal Significant New Use Rules (SNURs) for 88 PFOS=20 substances which applies to new manufacturers and for new uses of = these=20 substances. A SNUR for 183 perfluoroalkyl sulfonate substances was = posted=20 in April 2006 for public consultations, and the final publication = of the=20 SNUR is expected to be published in 2007. The SNURs require = manufacturers=20 and importers to notify the US EPA at least 90 days before new = manufacture=20 or import of these substances. This provides the US EPA with the = necessary=20 time to evaluate the intended new use and prohibit or limit the = new=20 activity, if necessary. While the SNURs do not require current=20 manufacturers to stop manufacturing or selling the substances, the = primary=20 manufacturer in the United States voluntarily discontinued = production=20 between 2000 and 2002. Therefore, once existing stocks are = depleted, the=20 SNURs essentially restrict all manufacture and importation of = PFOS.=20 Certain critical use exemptions on manufacturing and imports are = provided=20 for in the SNURs, including

use in aviation hydraulic fluids;=20
as a component of a photoresist substance, or as a component = of an=20 anti-reflective coating used in a photomicrolithography process = to=20 produce semiconductors or similar components of electronic or = other=20 miniaturized devices;=20
in coatings for surface tension, static discharge, and = adhesion=20 control for analog or digital imaging films, papers and printing = plates;=20 and=20
as an intermediate only to produce other chemical substances = to be=20 used solely for the uses listed above.

(b) The Commission of the European Union published a = proposed=20 directive relating to restrictions on the marketing and use of = PFOS on=20 December 5, 2005. The European Parliament proposed amendments to = this=20 directive in June 2006 and approved the final text in October = 2006. The=20 restriction will now be introduced as an amendment to the EU = legislation=20 on dangerous substances and preparations (Directive 76/769/EEC) = and will=20 eventually be incorporated in the Registration, Evaluation and=20 Authorization of Chemicals (REACH) program when it comes into = force. The=20 restrictions include the following:

PFOS and related substances will be banned as substances or=20 constituents of preparations in concentrations equal to or = higher than=20 0.005%, in semi-finished products and articles at a level of = 0.1% except=20 for textiles or coated materials in which the restricted amount = of PFOS=20 will be 1 =B5g/m². Exemptions will be considered for = PFOS used=20 in anti-reflective coatings for photolithography process, = industrial=20 photographic coating, mist suppressants for chromium plating and = other=20 electroplating applications, as well as aviation hydraulic = fluids;=20
stocks of PFOS-based AFFF supplied in the 12 months before = the=20 legislation comes into force may be used for a period of 54 = months.=20

(c) Australia has produced two Alerts concerning PFOS = through=20 its National Industrial Chemicals Notification and Assessment = Scheme=20 (NICNAS). The first Alert indicated the phasing-out of water, oil, = soil=20 and grease repellent products containing PFOS by September 2002. = As well,=20 the use of PFOS for leather products was to be phased out by March = 2003.=20 All other products containing PFOS, including firefighting foams = and=20 industrial additives, were to be phased out in Australia by = December 2003.=20 The second Alert makes recommendations regarding PFOS, = perfluorosulfonates=20 (PFAS) and perfluorooctanic acid (PFOA). These recommendations = include

that PFOS (and PFAS-based chemicals) be used only for = essential uses=20 for which there is no suitable alternative, such as certain = class B=20 firefighting foams, but not for use in fire training exercises; = and=20
that caution be used in selecting PFOA as an alternative for = PFOS=20 since PFOA may show the same environmental and health concerns = as PFOS.=20

(d) In April 2005, Norway proposed major reductions in = releases of PFOS by 2010.

(e) Sweden proposed the listing of PFOS and its = precursors in=20 Annex A of the Stockholm Convention on Persistent Organic = Pollutants=20 (POPs) in June 2005. At the November 2005 meeting of the = Persistent=20 Organic Pollutants Review Committee, it was decided that the = screening=20 criteria of the Convention had been fulfilled for PFOS and that an = ad hoc=20 working group under the Convention would be established to review = the=20 proposal further and to prepare a draft risk profile.

(f) In October 2005, the United Kingdom published a = proposed=20 national action plan that would restrict the use and marketing of = PFOS and=20 substances that degrade to it.

(g) In December 2005, the Parties to the United = Nations=20 Economic Commission for Europe (UNECE) Long-Range Transboundary = Air=20 Pollution (LRTAP) Convention's Protocol on POPs agreed that PFOS = should be=20 considered as a nominated substance under consideration as a = persistent=20 organic pollutant. The Convention will explore management = strategies in=20 2006.

Canadian actions on PFOS

To date, Canada has not regulated the use, manufacture, import = or=20 release of PFOS. These proposed Regulations are being taken to = protect the=20 environment and in support of international action on PFOS.

The proposed Regulations

The proposed Regulations for PFOS will

prohibit the manufacture, use, sale, offer for sale and = import of=20 PFOS or products containing these substances;=20
exempt the use of PFOS-based AFFF manufactured or imported = before=20 the coming into force of the proposed Regulations for a period = of five=20 years after the coming into force of the proposed Regulations = (but this=20 AFFF may not be used for training or testing purposes);=20
exempt the use of PFOS-based fume suppressants, and sale, = offer for=20 sale and import for that use, for a period of five years after = the=20 coming into force of the Regulations for chromium = electroplating,=20 chromium anodizing, reverse etching, electroless=20 nickel-polytetrafluoroethylene plating and etching of plastic = substrates=20 prior to their metallization;=20
exempt the use, sale, offer for sale and import of the = following=20 manufactured items: semiconductor or similar components of = electronic or=20 other miniaturized devices and photographic films, papers and = printing=20 plates;=20
exempt the use, sale and offer for sale of manufactured = items, that=20 were manufactured or imported before the coming into force of = the=20 proposed Regulations; and=20
provide standard exemptions for laboratories, scientific = research=20 and laboratory analytical standards.

Importers of PFOS-based fume suppressants will be required to = submit=20 annual reports detailing types, quantities, sales and end uses for = the=20 substances that are imported.

Alternatives

There are a number of alternatives considered to achieve the = objective=20 of the proposed Regulations.

Status quo

The presence of PFOS in the environment is primarily due to = human=20 activity and evidence indicates that the substance is harmful to = wildlife=20 and ecosystem health. In Canada, PFOS are not regulated in any=20 jurisdiction and, therefore, federal action is required to prevent = further=20 increases of PFOS concentrations in the Canadian environment.

With the phase-out of PFOS production by the largest global=20 manufacturer between 2000 and 2002, its use has declined = significantly in=20 Canada. With the exception of the use of fume suppressants in the = chromium=20 electroplating sector, and the expected continued use of large = existing=20 stocks of PFOS-based fire fighting foam purchased prior to 2003, = in=20 Canada, all other known uses of PFOS have been discontinued and = all other=20 existing stockpiles have been depleted. However, the potential for = future=20 import, sale, manufacture and use of PFOS in Canada, along with = subsequent=20 environmental releases, will continue to exist if the status quo = is=20 allowed to continue and control measures are not implemented. = Therefore,=20 in order to prevent the re-entry of PFOS into Canada and = subsequent PFOS=20 releases to the environment, the status quo cannot be = maintained.

Voluntary measures

Since the phase-out of PFOS production by the largest global=20 manufacturer between 2000 and 2002, PFOS use has declined = significantly in=20 Canada. Existing inventories of PFOS-based AFFF and the continued = use of=20 PFOS-based fume suppressants in chromium electroplating, as well = as the=20 possible presence of PFOS in imported manufactured items, are the = main=20 areas of continued concern. The use of voluntary measures like=20 Environmental Performance Agreements (EPAs) requires agreement by = all=20 stakeholders on the terms of the EPA to ensure their = participation. Given=20 the diverse characteristics of the stakeholders and the large = numbers of=20 AFFF users, electroplaters and possible importers of manufactured = articles=20 containing PFOS, EPAs are not considered an effective tool for = phasing out=20 existing uses.

Other voluntary measures (such as the Responsible Care Program, = Environmental Leadership Initiatives) were also not considered = viable=20 options, as they do not provide sufficient incentives to encourage = existing PFOS users to shift away from the substance.

In addition, voluntary tools cannot provide the certainty in = achieving=20 the proposed risk management objective. Voluntary measures do not = ensure=20 an effective reduction in environmental risks and would not ensure = a fair=20 and level playing field. Therefore, the option of voluntary = measures is=20 not being considered any further.

Market-based instruments

Market-based tools, which include emission trading programs, = financial=20 incentives, deposit-refund systems, environmental charges and = other=20 market-based tools, were given due consideration. Tradable units = systems=20 were considered neither effective nor practical, as the quantity = of PFOS=20 in use is small and establishing an elaborate system of tradeable = permits=20 would be an ineffective use of resources. The costs associated = with=20 establishing a trading regime for a five-year period prior to the=20 prohibitions coming into force would be high. The efficiency gains = from=20 trading over a short time period would be outweighed by the cost = of=20 establishing the trading system. For imported manufactured items,=20 manufacturers are outside Canada's jurisdiction and a trading = system could=20 not be enforced.

Similarly, deposit-refund systems were also not considered an = effective=20 option as PFOS is released during the service life of the consumer = product. In some cases, by the end of the product life very small=20 quantities of PFOS remain in the product matrix. Moreover, PFOS = cannot be=20 recovered from a product and this makes a deposit-refund scheme=20 inapplicable.

Other market-based tools were also given due consideration. = PFOS uses=20 in Canada, other than AFFF, are relatively small and the cost of = subsidies=20 is not the most effective way of reducing PFOS use. Environmental = charges=20 were not considered to be effective, since the risk management = objective=20 is to achieve the lowest level of release to the environment that = is=20 technically and economically feasible from all release sources of = PFOS,=20 and the ability of a charge rate to achieve this effective = prohibition=20 would be highly uncertain. This is particularly the case in the = metal=20 plating sector where some firms could continue to pay a charge in = order to=20 use the product. A charge rate could be implemented in advance of = the=20 proposed Regulations coming into force. However, the number of = metal=20 plating and AFFF using facilities is small and, therefore, there = could be=20 a risk of high transaction costs. A charge is feasible for = imported=20 manufactured items containing PFOS, but the compliance costs = associated=20 with monitoring and verifying the content of PFOS in manufactured = items in=20 order to calculate the charge would likely be = cost-prohibitive.

The use of economic instruments, therefore, does not present = itself as=20 an effective option.

Regulations

To achieve the stated risk management objective, regulatory = measures=20 were found to be the most effective and efficient option. Based on = a=20 review of the regulatory measures available under CEPA 1999, = regulations=20 respecting substances on the List of Toxic Substances were = considered to=20 be the most effective. Regulations are able to address various = aspects of=20 substance life-cycles, including manufacture, use, sale, offer for = sale,=20 import as well as prescribing emissions levels. In addition, = exemptions=20 for critical uses can also be provided for specified time frames,=20 especially for uses where technically viable options to the use of = specified substances are not yet available. The proposed = regulatory=20 measures prohibit the manufacture, use, sale, offer for sale and = import of=20 PFOS and specifies the deadlines for the eventual elimination of = PFOS use.=20 These proposed regulatory measures are a timely and efficient = mechanism to=20 achieve the stated risk management objective.

Benefits and costs

The key assumptions used in the cost-benefit analysis = include

Regulatory time frame: The proposed Regulations would = come=20 into force in 2008, with the exemption for AFFF and the metal = plating=20 sector expiring 5 years later in 2012;

Time span for analysis: A time frame of 25 years is = selected=20 to account for the life span of PFOS containing AFFF as well as = the=20 service life of metal plating equipment. Thus, the analysis time = frame is=20 2008 to 2032;

Cost and benefit perspective: Only those costs and = benefits=20 which directly or indirectly affect Canadians are included in the=20 analysis; and

Discount rate: A discount rate of 5.5%, and all = monetized=20 costs and benefits are expressed in 2006 dollars.

The specific costs and benefits of the proposed Regulations are = described below.

Costs to the industry

Aqueous film forming foam

The costs associated with prohibiting AFFF will fall upon both = public=20 and private sector entities including airports, military = facilities and=20 refineries. These costs will relate to the safe disposal of = existing=20 stocks of PFOS-based AFFF, as well as the incremental cost of = replacing=20 the stock with alternatives. The use of PFOS-based AFFF for = training and=20 testing purposes will be prohibited.

Cost assumptions include the following:

The starting stock of PFOS-based AFFF in 2006 is 300 tonnes = of which=20 1% or 3 tonnes is PFOS. This stock will not increase as = PFOS-based AFFF=20 has not been available since 2002-2003. During the 5-year = exemption=20 period, the stock of PFOS-based AFFF is expected to decrease = marginally=20 at an annual rate in the order of 1% through use and accidental = losses.=20 It is also anticipated that users will dispose of their stock = during the=20 exemption period (2008 to 2012). This accelerated disposal is=20 attributable to the proposed Regulations. It is assumed that = during the=20 exemption period 5% of the stock will be sent annually for = thermal=20 destruction. This means that approximately 65 tonnes of AFFF = foam=20 containing 0.65 tonnes of PFOS will be disposed of in the 2008 = to 2012=20 exemption period;=20
Based on the proposed regulatory schedule, regulatees would = have to=20 phase out their use of PFOS-based AFFF by January 1, 2013. Since = AFFF=20 has a life span in the order of 25 years, it is reasonable to = assume=20 that the entire stock of PFOS-based AFFF will be disposed of and = replaced in 20 years (2013 to 2032) after the 5-year exemption = period=20 (2008 to 2012). For the cost-benefit analysis, it is assumed = that with=20 the prohibition in force, the remaining stock not sent for = thermal=20 destruction will be disposed of at a constant rate starting in = 2013=20 until it is entirely depleted in 2032;=20
The average disposal costs (thermal destruction) are = estimated to be=20 $1.65 per kg. This is a standard cost for disposing of hazardous = waste=20 at a licensed disposal facility using thermal destruction; and=20
Actual replacement costs for PFOS-free AFFF have been = estimated=20 between $3.12 per kg and $3.85 per kg with an average cost of = $3.50 per=20 kg for concentrate based on the prices that are available to = large=20 quantity users.

Based on these assumptions, it is estimated that the proposed=20 Regulations would reduce the release of PFOS-based AFFF into the=20 environment in the order of 2.83 tonnes over the 2008 to 2032 = period (see=20 Table 1). The present value of the disposal and replacement costs=20 experienced by airports, military facilities and refineries would = be in=20 the order of approximately $727,501 (in 2006 $) discounted at 5.5% = over=20 the 25-year time period.

Table 1: Quantity of PFOS-based AFFF = Disposed and=20 the Associated Replacement and Disposal Costs

(Central Value, 25 Years at 5.5% in 2006 = $)

	Exemption Period 2008 to 2012	Prohibition Period 2013 to = 2032	Entire Period 2008 to = 2032
AFFF and PFOS inventory=20 (tonnes)
AFFF quantities disposed	65	218	283
PFOS contained in AFFF	0.65	2.18	2.83
Costs (NPV)
Cost of disposal	$81,836	$148,835	$230,671
Cost of replacement	$176,263	$320,567	$496,830
Total cost	$258,100	$469,401	$727,501

Metal plating

Of the approximate 200 metal plating facilities in Canada, = about 110=20 use fume suppressants, of which in the order of 100 use PFOS-based = fume=20 suppressants. Under the proposed Regulations these 100 facilities = will=20 either need to switch to non-PFOS-based fume suppressants or move = to=20 another control technology such as composite mesh pads or closed = covers=20 after the end of the proposed 5-year exemption (by 2013). While = there are=20 some alternative formulations of fume suppressants on the market = that do=20 not contain PFOS, the industry has been unable to develop = formulations=20 with the required performance characteristics to meet the range of = technical specifications required in chromium electroplating, = chromium=20 anodizing and reverse etching, electroless = nickel-polytetrafluoroethylene=20 and etching of plastic prior to metallization. However, in most = other PFOS=20 use areas alternative formulations have emerged, as evidenced by = the fact=20 that continued PFOS-free alternatives are available in the market = since=20 the voluntary phase-out of PFOS between 2000 and 2002.

As a worst case scenario, if no drop-in fume suppressant = substitutes=20 become available, the metal plating sector would have to move to = an=20 emission control technique such as composite mesh pads or closed = covers.=20 Based on analysis conducted for the proposed Chromium = Electroplating,=20 Chromium Anodizing and Reverse Etching Regulations the = incremental=20 costs of moving from fume suppressants to composite mesh pads = would vary=20 by firm size, as indicated in Table 2. The distribution by firm = size for=20 the 100 metal platers that would need to upgrade to the new = emission=20 controls is also provided in Table 2. As indicated, the majority = of=20 facilities are in the medium category (52), followed by small (34) = and=20 large (14). This sector has been growing at an annual growth rate = in the=20 order of 0.8% and 1.4%, with an average of 1.1%. This range is = used to=20 grow the number of firms subject to the proposed Regulations over = the 2008=20 to 2032 time period.

Costs are, therefore, either zero if drop-in substitutes become = available at no incremental cost or equivalent to the upgrade = emission=20 control technology costs provided in Table 2.

Table 2: Incremental Cost per = Firm

Upgrading to Improved Emission Controls = (2006=20 $)

	Move to Composite Mesh Pads (CMP)	Current Cost of Fume Suppressant	Additional Cost to Move to CMP
Size	Capital Cost	Opera- tions and Mainte- nance = Cost	Capital Cost	Operations Cost	Capital Cost	Opera- tions and Mainte- nance = Cost
Small	$46,499	$2,981	$0	$1,822	$46,499	$1,159
Medium	$96,320	$10,965	$0	$6,011	$96,320	$4,954
Large	$176,033	$30,552	$0	$31,331	$176,033	($779)

Based on this range of possible costs, the anticipated costs of = the=20 proposed Regulations by firm size are $736,254 for 34 small firms, = $2,984,716 for 52 medium firms and $773,645 for 14 large firms. = The total=20 estimated compliance costs for facilities using PFOS fume = suppressants to=20 comply with the proposed Regulations is approximately $4.5 million = (discounted at 5.5% over 25 years). This would result in a = reduction in=20 PFOS releases of approximately 86 tonnes over the 2013 to 2032 = period.

Imported manufactured items

Import prohibitions are not anticipated to create impacts in = Canada, as=20 the European Union and the United States have put in place = prohibitions on=20 PFOS use, manufacture and import. Therefore, these impacts are not = considered in this analysis. However, there is some concern that = without=20 the prohibition in place, some items containing PFOS would enter = Canada,=20 as some countries have not banned PFOS use or manufacture. = Therefore, some=20 benefits (discussed below) can be attributed to the prohibitions = being=20 placed on imported manufactured items in the proposed = Regulations.

Costs to the Government

The costs incurred by the federal government would be as a = result of=20 enforcement and compliance promotion activities related to the = proposed=20 Regulations. For manufactured items, enforcement and compliance = promotion=20 activities are likely to benefit from international actions being = taken to=20 restrict the use of PFOS. Limited enforcement activities would = still be=20 required to ensure that products containing PFOS are not imported = into=20 Canada.

With respect to enforcement costs, for the first year following = the=20 coming into force of the proposed Regulations, a one-time amount = of=20 $250,000 will be required for the training of enforcement = officers. In=20 addition, for the first year following the delivery of the = training, the=20 enforcement costs are estimated to require an annual budget of = $56,220=20 broken down as follows: $37,750 for inspections (which includes = operations=20 and maintenance costs, transportation and sampling costs), $14,330 = for=20 investigations and $4,140 for measures to deal with alleged = violations=20 (including environmental protection compliance orders and=20 injunctions).

For years two through five, the enforcements costs are = estimated to=20 require an annual budget of $74,316 broken down as follows: = $37,750 for=20 inspections (which includes operations and maintenance costs,=20 transportation and sampling costs), $14,330 for investigations, = $4,140 for=20 measures to deal with alleged violations (including environmental=20 protection compliance orders and injunctions) and $18,096 for=20 prosecutions.

For subsequent years (years 6 to 25), the enforcements costs = are=20 estimated to require an annual budget of $5,552 for inspections = (which=20 includes operations and maintenance costs, transportation and = sampling=20 costs), $85,980 for six investigations and $18,096 for one = prosecution=20 over the 25-year time frame.

With respect to compliance promotion costs, the first year = following=20 the coming into force of the proposed Regulations is estimated to = cost=20 $128,000. Activities could include mail-outs, information = sessions, site=20 visits, developing and distributing compliance promotion material, = a Web=20 site, presentations and trade shows, conferences and industry = meetings,=20 responding to and tracking inquiries, and contributing to the = compliance=20 promotion database. Costs in years two through five are $41,000, = $6,500,=20 $34,000 and $6,500 respectively for a total five-year expenditure = on=20 compliance promotion activities of $216,000. The increase in = expenditures=20 for year four is to increase compliance promotion activities in = advance of=20 the planned end of the five-year exemptions for the use of = PFOS-based AFFF=20 and fume suppressants. Note that a higher level of effort for = compliance=20 promotion may be required if, following enforcement activities, = compliance=20 with the Regulations is found to be low.

The present value of federal government enforcement costs over = the=20 25-year time frame are in the order of approximately $570,450, = while=20 compliance promotion costs are approximately $176,203 (2006 $ at a = 5.5%=20 discount rate). Total government costs are, therefore, estimated = to be=20 approximately $746,653 (2006 $ at a 5.5% discount rate).

Total costs of the proposed Regulations

The present value of total industry and government costs = associated=20 with the proposed Regulations over the 25-year period are = estimated to be=20 approximately $5.97 million (2006 $ discounted at 5.5%).

Benefits to Canadians

The benefits of prohibiting PFOS include

the protection of wildlife and ecosystem health (including = in remote=20 locations such as the Canadian Arctic) from PFOS exposure, as a = result=20 of a reduction in the use of PFOS; and=20
avoided costs for alternate water supply sources by avoiding = contamination as a result of a reduction in the handling, = release and=20 use of PFOS.

Due to data limitations, not all of these benefits could be = monetized=20 and included in the analysis.

Ecosystem benefits

The scientific literature has identified that at current = exposure=20 levels, PFOS could harm certain wildlife organisms (e.g. polar = bear,=20 fish-eating birds), including those found in remote locations such = as in=20 the Canadian Arctic. The effects include growth inhibition of = birds and=20 aquatic invertebrates; liver and thyroid effects in mammals; = lethality to=20 fish and saltwater invertebrates; and changes in biodiversity. = While PFOS=20 is generally acknowledged to have the potential to cause serious,=20 irreversible impacts (bioaccumulation and persistence), the = current=20 science is unable to accurately predict the ecological effects of = these=20 substances. The absence of specific impacts on the environment on = which to=20 model the economic value of reductions in current releases makes = it=20 difficult to quantify and monetize the benefits from the proposed=20 Regulations. Although difficult to quantify, these benefits should = be=20 considered qualitatively in the assessment.

Avoided costs for alternate water supply

PFOS has been detected in surface water and sediment, in = wastewater=20 treatment plant effluent, sewage sludge and in landfill leachate. = PFOS=20 releases have been identified to cause groundwater contamination, = and PFOS=20 have been found to be detectable in groundwater at least five = years after=20 release. Among the indirect benefits, the proposed Regulations = would=20 prevent environmental and possible health impacts associated with = water=20 supply contamination resulting from the handling, release and use = of=20 PFOS.

As stated earlier, there are approximately 3 tonnes of PFOS = contained=20 in the 300 tonnes of AFFF inventories at airports, military = facilities and=20 refineries. The use of PFOS-based AFFF to fight actual fires and = in=20 training, and the risk of accidental releases will continue to = pose a=20 threat as long as the inventories of PFOS-based AFFF exist and its = use=20 remains uncontrolled. Although PFOS-based AFFF has not been = available in=20 the market since 2003, the existing inventories of PFOS-based AFFF = continue to pose a risk over their service life (estimated to be = 25 years)=20 that could result in a major contamination event. Once the = regulatory=20 provisions for PFOS-based AFFF come into effect in 2013, the risk = of a=20 contamination event would be significantly reduced. Although the = incidence=20 rate of PFOS contamination to groundwater or surface water supply = areas is=20 not known, for analytical purposes it can be assumed that two = extreme=20 contamination events involving fuel fires (e.g. refinery fires, = plane=20 crash) could occur every 25 years in the absence of the proposed=20 Regulations.

The avoided cost for alternate water supply sources is measured = in=20 terms of the probability of a contamination event at some point in = the=20 future, multiplied by the costs of alternate sources of water = supply. The=20 probability is simply the annual probability that a water = contamination=20 event will occur.

To address this type of contamination, affected municipalities = may be=20 required to incur expenses for the short-term provision of = alternative=20 water supplies, engineering studies and new infrastructure. = Existing=20 studies have estimated that the cost of providing alternate = sources of=20 water supply are in the order of $2.2 and $11 million, with a = central=20 value of $6.6 million. (see=20 footnote 1) The potential benefit from avoided alternate water = supply=20 expenditure attributable to the proposed Regulations is estimated = to=20 result in an average annual benefit of $560,000 per year. It is = recognized=20 that this benefit is uncertain; however, the value can be used to=20 approximate the benefits to be derived as a result of the proposed = Regulations. Total benefits to Canadians are, therefore, estimated = to be=20 approximately $6.35 million (2006 $ at a 5.5% discount rate).

Net benefit of the Regulations

The total discounted cost to the private sector and federal = government=20 is estimated at $5.97 million, while total benefits to Canadian = society is=20 estimated to be a minimum of $6.35 million. Overall, the present = value of=20 the proposed Regulations are estimated to result in a net benefit = to=20 Canadian society of approximately $384,410 (2006 $, discounted at = 5.5%=20 over a 25-year period). The benefits to Canadians do not include=20 non-quantified benefits such as value placed on ecosystem risk = reduction=20 associated with less PFOS use. The proposed Regulations are = estimated to=20 reduce PFOS releases by at least 89 tonnes (85.7 tonnes from metal = finishing and 2.87 tonnes from AFFF) over the 25-year period.

As the benefits to the ecosystem could not be quantified due to = data=20 limitations and uncertainties, it is realistic to assume that the = actual=20 net benefit would be greater than the estimated $384,410.

Consultation

All stakeholders were given the opportunity to comment during = the=20 60-day public comment period following the July 1, 2006 = publication in the=20 Canada Gazette, Part I, of the proposed Order to add the=20 substances to the List of Toxic Substances in Schedule 1 of CEPA = 1999. The=20 comments received were supportive of the proposal to add the = substances to=20 Schedule 1 of CEPA 1999.

The CEPA National Advisory Committee (CEPA NAC) and relevant = federal=20 government departments were consulted on the proposed Order as = well as the=20 proposed Risk Management Strategy (RMS) for PFOS. No concerns were = raised=20 by CEPA NAC.

Stakeholders were also consulted on the proposed RMS for PFOS = through=20 the posting of the RMS on Environment Canada's CEPA Registry Web = site and=20 a national mail-out to over 350 stakeholders. A total of 48 = comments were=20 received from industry representatives, industry associations,=20 environmental nongovernment organizations and other government=20 departments. While stakeholders are supportive of the proposed = risk=20 management approach, concern was raised about the approach to the = proposed=20 exemption for imported manufactured articles, as was originally = stated in=20 the strategy.

The comments and concerns raised by the various stakeholder = meetings=20 and Environment Canada's response to these are detailed below.

AFFF

Concern was raised on the proposed length of time allowed to = phase out=20 PFOS-based AFFF stockpiles. Some of the stakeholders advocated = increasing=20 the time frame while others proposed shortening the allowed = phase-out=20 time. The phase-out time frames for AFFF being proposed by = stakeholders=20 ranged from one year to ten years. In addition, stakeholders = called for=20 the inclusion of a financial incentive program to assist smaller = firms in=20 the proper disposal of expended AFFF; requirement to develop a = Pollution=20 Prevention (P2) Plan; and developing best practices for use, = storage and=20 disposal of AFFF.

After reviewing the comments, Environment Canada deems five = years to be=20 an appropriate time period to phase out existing AFFF stocks. With = the=20 voluntary discontinuation of production of PFOS by the global = manufacturer=20 between 2000 and 2002, users requiring new stocks have been able = to=20 purchase only PFOS-free products. Users would, therefore, have had = approximately thirteen years to complete the phase-out of the = existing=20 stocks from the time the major manufacturer announced = discontinuing PFOS=20 production to the time the proposed five-year exemption period = expires. In=20 addition, replacement products are readily available at similar = prices in=20 the market. Moreover, the time frame is also consistent with the = timelines=20 being proposed in another jurisdiction.

With respect to the other concerns, Environment Canada is of = the=20 opinion that existing federal, provincial/territorial and = municipal=20 standards and protocols for fire response and prevention = adequately define=20 the operational use procedures for AFFF. As well, the safe = disposal of=20 AFFF is provided for under the existing federal and provincial = hazardous=20 waste regulations. The disposal costs for AFFF would be similar to = other=20 hazardous waste material and as such does not warrant the = development of=20 an incentives or assistance program.

Imported manufactured articles

The majority of the comments received did not support exempting = imported manufactured articles in the proposed Regulations, with = the=20 exception of one comment. A couple of comments called for = developing=20 complimentary measures for managing imported manufactured articles = and=20 developing better use pattern data on imported manufactured = articles.

The comments were considered and, in the proposed Regulations, = imported=20 manufactured articles will not be exempt from the regulatory = requirements.=20 As described above, the global production and use data indicates = that PFOS=20 use is declining and alternatives to PFOS are readily available. = The areas=20 where the substance is still being used are the critical uses = previously=20 outlined, for which no viable alternative is available. Therefore, = with=20 viable alternatives available at similar costs and exemptions for = critical=20 uses, Environment Canada did not consider it necessary to provide=20 exemptions for imported manufactured articles containing PFOS.

Critical use exemptions

Comments were also received on critical use exemptions being = provided=20 for under the proposed Regulations. Stakeholders voiced the = concern that=20 these exemptions should be justified on the basis of a specific = set of=20 criteria and supporting documentation. Moreover, the critical use=20 exemptions should be time limited.

The critical use exemptions provided for under the proposed = Regulations=20 are for the use of existing stocks of PFOS-based AFFF and import = and use=20 of PFOS-based surfactants in chromium plating for a period of five = years.=20 Environment Canada, after taking into consideration the technical = aspects,=20 has determined that a period of five years is sufficient to manage = the=20 existing stocks of AFFF as well as identify alternatives for the=20 specialized manufacturing operations. With the voluntary phase-out = of PFOS=20 by the major manufacturer between 2000 and 2002, PFOS-based AFFF = has not=20 been available and all AFFF is now PFOS free. The five-year = phase-out=20 period is considered essential to allow facilities to replace = PFOS-based=20 AFFF with alternative PFOS-free fire fighting foam. Similarly, the = phase-out period for PFOS-based surfactants is required to allow = the=20 sector to develop alternatives. Similar exemptions are also = proposed in=20 other jurisdictions.

PFOS releases

A number of stakeholders were concerned about the issue of PFOS = releases from landfills as well as the efficiency of waste water = treatment=20 facilities to remove PFOS.

With the voluntary phase-out of PFOS by the global manufacturer = between=20 2000 and 2002, it is expected the use of PFOS in manufactured = articles has=20 steadily been declining and this is likely to have a positive = impact on=20 future releases of PFOS from landfills and waste water treatment=20 facilities. Moreover, the proposed Regulations intend to prohibit = the=20 import, sale, manufacture and use of PFOS substances, including=20 manufactured articles. This measure is expected to reduce the = future=20 stream of PFOS releases.

General comments

Several comments were received on some of the more general = aspects of=20 the proposed Regulations, as specified in the risk management = strategy.=20 Stakeholders identified the following issues:

Management of additional new PFOS type of substances;=20
Impact of international actions on domestic initiatives to = manage=20 PFOS;=20
Identification of safe alternatives to PFOS;=20
Virtual elimination of PFOS substances;=20
Provision of evidence to show why the use of weight of = evidence=20 approach was used with respect to bioaccumulation; and=20
Identification by Chemical Abstracts Service numbers of the=20 substances that will be subject to the proposed risk management = actions.=20

The concerns expressed by stakeholders have been taken into=20 consideration while drafting the proposed Regulations.

Compliance and enforcement

Since the Regulations will be made under CEPA 1999, enforcement = officers will, when verifying compliance with the Regulations, = apply the=20 Compliance and Enforcement Policy implemented under the Act. The = Policy=20 also sets out the range of possible responses to violations, = including=20 warnings, directions, environmental protection = compliance=20 orders, ticketing, ministerial orders, injunctions, prosecution, = and=20 environmental protection alternative measures (which are an = alternative to=20 a court trial after the laying of charges for a CEPA 1999 = violation). In=20 addition, the Policy explains when Environment Canada will resort = to civil=20 suits by the Crown for costs recovery.

When, following an inspection or an investigation, an = enforcement=20 officer discovers an alleged violation, the officer will choose = the=20 appropriate enforcement action based on the following factors:

Nature of the alleged violation: This includes=20 consideration of the damage, the intent of the alleged violator, = whether=20 it is a repeat violation, and whether an attempt has been made = to=20 conceal information or otherwise subvert the objectives and = requirements=20 of the Act.=20
Effectiveness in achieving the desired result with the = alleged=20 violator: The desired result is compliance within the = shortest=20 possible time and with no further repetition of the violation. = Factors=20 to be considered include the violator's history of compliance = with the=20 Act, willingness to co-operate with enforcement officers, and = evidence=20 of corrective action already taken.=20
Consistency: Enforcement officers will consider how = similar=20 situations have been handled in determining the measures to be = taken to=20 enforce the Act.

Contacts

Greg Carreau, Chemicals Sector Division, Environment Canada, = 351=20 Saint-Joseph Boulevard, 13th Floor, Gatineau, Quebec K1A 0H3, = 819-953-6072=20 (telephone), 819-994-0007 (fax), Greg. Carreau@ec.gc.ca (email); = or Markes=20 Cormier, Acting Senior Economist, Impact Analysis and Instrument = Choice=20 Division, Environment Canada, 10 Wellington Street, 24th Floor, = Gatineau,=20 Quebec K1A 0H3, 819-953-5236 (telephone), 819-997-2769 (fax),=20 Markes.Cormier@ec.gc.ca (email).

PROPOSED REGULATORY=20 TEXT

Notice is hereby given, pursuant to subsection 332(1) (see=20 footnote a) of the Canadian Environmental Protection Act,=20 1999 (see=20 footnote b), that the Governor in Council proposes, pursuant = to=20 subsection 93(1) and section 319 of that Act, to make the annexed=20 Perfluorooctane Sulfonate and its Salts and Certain Other = Compounds=20 Regulations.

Any person may, within 60 days after the date of publication of = this=20 notice, file with the Minister of the Environment comments with = respect to=20 the proposed Regulations or a notice of objection requesting that = a board=20 of review be established under section 333 of that Act and stating = the=20 reasons for the objection. All comments and notices must cite the=20 Canada Gazette, Part I, and the date of publication of = this=20 notice, and be sent to the Director, Chemicals Sector Division, = Pollution=20 Prevention, Department of the Environment, Ottawa, Ontario K1A = 0H3.

A person who provides information to the Minister may submit = with the=20 information a request for confidentiality under section 313 of = that=20 Act.

Ottawa, December 7, 2006

MARY O'NEILL
Assistant Clerk of the Privy=20 Council

PERFLUOROOCTANE SULFONATE AND ITS SALTS = AND=20 CERTAIN OTHER COMPOUNDS REGULATIONS

APPLICATION

1. Subject to sections 2 and 3, these = Regulations=20 apply to the following substances that are specified on the List = of Toxic=20 Substances in Schedule 1 to the Canadian Environmental = Protection Act,=20 1999:

(a) perfluorooctane sulfonate and it salts; and

(b) compounds that contain one of the following = groups:=20 C₈F₁₇SO₂,=20 C₈F₁₇SO₃ or=20 C₈F₁₇SO₂N.

EXCEPTIONS

2. These Regulations do not apply to any = substance=20 referred to in section 1 that is

(a) contained in a hazardous waste, hazardous = recyclable=20 material or non-hazardous waste to which Division 8 of Part 7 of = the=20 Canadian Environmental Protection Act, 1999 applies;

(b) contained in a pest control product within the = meaning of=20 subsection 2(1) of the Pest Control Products Act; or

(c) present as a contaminant in a chemical feedstock = used in a=20 process from which there are no releases of the substance and = provided=20 that the substance is destroyed or completely converted in that = process to=20 a substance other than one referred to in that section.

3. These Regulations do not apply to any = substance=20 referred to in section 1 or to any product containing such a = substance=20 that is for use

(a) in a laboratory for analysis;

(b) in scientific research; or

PROHIBITIONS

4. (1) In this section, "manufactured item" = means a=20 product that is formed into a specific physical shape or design = during=20 manufacture and that has, for its final use, a function or = functions=20 dependent in whole or in part on its shape or design.

(2) Subject to subsections (3) to (6), no person shall = manufacture,=20 use, sell, offer for sale or import any substance referred to in = section 1=20 or a product containing any such substance.

(3) The use, sale or offer for sale of a manufactured item = containing=20 any substance referred to in section 1, if manufactured or = imported before=20 the coming into force of these Regulations, is permitted.

(4) The use, other than for testing or training purposes, of = aqueous=20 film forming foam containing any substance referred to in section = 1, if=20 manufactured or imported before the coming into force of these=20 Regulations, is permitted for a period of five years from the day = on which=20 these Regulations come into force.

(5) The use of a substance referred to in section 1, or a = product=20 containing any such substance, as a fume suppressant in the = following=20 processes as well as their sale, offer for sale or import for = those uses,=20 is permitted for a period of five years from the day on which = these=20 Regulations come into force:

(a) chromium electroplating, chromium anodizing and = reverse=20 etching;

(b) electroless nickel-polytetrafluoroethylene = plating;=20 and

(6) The use, sale, offer for sale or import of the following=20 manufactured items containing any substance referred to in section = 1 is=20 permitted:

(a) semiconductors or similar components of electronic = or=20 other miniaturized devices; and

(b) photographic films, papers and printing = plates.

ANALYSIS BY ACCREDITED LABORATORY

5. The presence of any substance referred to = in=20 section 1 shall be determined by a laboratory that is accredited = under the=20 International Organization for Standardization standard ISO/IEC = 17025:=20 2005, entitled General requirements for the competence of = testing and=20 calibration laboratories, as amended from time to time, and = whose=20 accreditation includes the analysis of that substance within its = scope of=20 testing.

REPORTS

6. Every person that imports a substance or = product=20 referred to in subsection 4(5) shall submit to the Minister a = report=20 containing the information set out in the schedule no later than = March 31=20 of the calendar year following the calendar year during which the=20 substance or product was imported.

CERTIFICATION

7. (1) Any information required to be = submitted to the=20 Minister under these Regulations shall be submitted in a form = determined=20 by the Minister and accompanied by a certification, dated and = signed by=20 the person referred to in the applicable provisions, or the = person's=20 authorized representative, that the information is accurate and=20 complete.

(2) The certification may be submitted either in writing or in = an=20 electronic format that is compatible with the one that is used by = the=20 Minister and it shall bear the written or electronic signature, as = the=20 case may be, of the person or their authorized representative.

RECORD KEEPING

8. (1) Every person that submits information = to the=20 Minister under these Regulations shall keep, in writing or in an=20 electronic format that is compatible with the one used by the = Minister, a=20 copy of that information, the certification and any documents = supporting=20 the information for a period of at least five years beginning on = the date=20 of the submission of the information.

(2) The information, certification and supporting documents = that are=20 required to be kept by the person shall be kept at their principal = place=20 of business in Canada or at any other place in Canada where the=20 information, certification, results and supporting documents can = be=20 inspected. If those records are kept at any place other than the = person's=20 principal place of business, the person shall provide the Minister = with=20 the civic address of the place where they are kept.

COMING INTO FORCE

9. These Regulations come into force on the = day on=20 which they are registered.

SCHEDULE
(Section 6)

INFORMATION RELATED TO THE IMPORT OF CERTAIN = FUME=20 SUPPRESSANTS

1. Information respecting the importer:

(a) their name, the civic and postal addresses of = their=20 principal place of business, e-mail address, if any, telephone = number and=20 fax number, if any; and

(b) the name, title, civic and postal addresses, = e-mail=20 address, if any, telephone number and fax number, if any, of their = authorized representative, if any.

2. Information respecting the substance or=20 product:

(a) the name of the substance, alone or contained in a = product;

(b) the total quantity of the substance, alone or = contained in=20 a product, imported by the importer in the calendar year for which = the=20 report is submitted, as well as the identification of that = calendar year=20 and the unit of measurement;

(c) the total quantity of the substance, alone or = contained in=20 a product, sold in Canada by the importer in the calendar year for = which=20 the report is submitted, as well as the identification of that = calendar=20 year and the unit of measurement; and

(d) the identification of the process referred to in=20 paragraphs 4(5)(a) to (c) of these Regulations = for which=20 the substance or product is proposed to be used, if known.

3. An importer that submits a request, in = accordance=20 with section 313 of the Canadian Environmental Protection Act, = 1999, that information submitted be treated as confidential = must=20 include with that request the identification of the following:

(a) any information that constitutes a trade = secret;

(b) any information the disclosure of which would = likely cause=20 material financial loss to, or prejudice the competitive position = of, the=20 importer;

(c) any information the disclosure of which would = likely=20 interfere with contractual or other negotiations being conducted = by the=20 importer; and

(d) any financial, commercial, scientific or technical = information that is confidential and is treated consistently in a=20 confidential manner by the importer.

[50-1-o]

Footnote=20 1

Raven Beck Environmental Ltd. (1995)

Footnote=20 a

S.C. 2004, c. 15, s. 31

Footnote=20 b

S.C. 1999, c. 33

NOTICE:
The format=20 of the electronic version of this issue of the Canada = Gazette was=20 modified in order to be compatible with hypertext language (HTML). = Its=20 content is very similar except for the footnotes, the symbols and = the=20 tables.

Top of page

Maintained by the Canada Gazette=20 Directorate Important notic= es =0A= _uacct =3D "UA-518903-1";=0A= urchinTracker();=0A=

Updated: 2006-12-15 =

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