7. Controlling pollution and managing wastes

Nutrients are defined as substances that promote the growth of aquatic vegetation. The Canadian Environmental Protection Act, 1999 (CEPA 1999) provides the authority to regulate nutrients in cleaning products and water conditioners that degrade or have a negative impact on an aquatic ecosystem.

Inputs of nutrients, in the form of nitrogen and phosphorus, to aquatic ecosystems as a result of human activity can result in excessive aquatic plant growth, depletion of oxygen, and deleterious changes in abundance and diversity of aquatic invertebrates and fish. In March 2003, researchers at the National Water Research Institute completed an assessment of the impacts of nutrient loading from municipal and industrial sources on water quality in northern Alberta rivers (Athabasca and Wapiti).

Their studies produced an approach for setting scientifically credible nutrient guidelines for these cold-water rivers and specified recommended guidelines for nitrogen and phosphorus to prevent deterioration in water quality. Research conducted during the past several years on agricultural watersheds in Saskatchewan, Manitoba, and Ontario examined effects of land management practices on nutrient transport from cropland to surface water and groundwater. These studies resulted in the development and adoption of better management practices for reducing nutrient loss from agricultural lands.

The act provides authorities to issue nonregulatory objectives, guidelines, and codes of practice to help implement Canada’s National Programme of Action for the Protection of the Marine Environment from Land-based Activities. These provisions are intended to supplement the authorities that exist in other federal, provincial, territorial, and Aboriginal government laws.

In 1995, Canada, together with over 100 maritime nations, adopted the Global Programme of Action for the Protection of the Marine Environment from Land-based Activities in Washington, D.C. Developed under the auspices of the United Nations Environment Programme, and in response to Agenda 21, the Global Programme of Action is an international, non-legally binding agreement that calls on countries to develop national and regional programmes of action to protect human health and prevent, reduce, and control land-based activities that threaten the health, productivity, and biodiversity of marine and coastal environments and associated freshwater systems.

Recognizing the merits of an integrated and coordinated approach and that marine pollution from land-based sources is a significant threat to Canada’s marine and coastal environment, Canada was the first country to release a National Programme of Action in response to the Global Programme of Action in June 2000.

Canada’s National Programme of Action (NPA) aims to prevent marine pollution from land-based activities and protect habitat in the nearshore and coastal zones of Canada. In 2002-03, the NPA Advisory Committee developed a four-year (2002-06) National Action Plan to guide NPA implementation activities. Priority areas of activity in 2002-03 included the following:

Implementation of the NPA is now progressing at the national and regional levels as NPA partners work to integrate NPA objectives into ongoing federal/provincial/ territorial programs and activities. For example, the Atlantic regional NPA team initiated a project in 2002-03 to examine fish plant processing effluents and sustainability issues. The results of this project will provide useful information and data for other regions with similar issues, including the St. Lawrence (Quebec) and Pacific regions.

www.npa-pan.ca

In response to the 1995 Global Programme of Action, Canada and seven other circumpolar nations of the Arctic Council agreed to develop a Regional Programme of Action for the Protection of the Marine Environment from Land-based Activities (RPA) to address marine pollution issues in the Arctic. Canada played a major role in the development of the RPA, which was adopted by Arctic Council Ministers in 1998.

During 2002-03, Canada continued to promote the implementation of the RPA through its participation in the Arctic Council’s Working Group on Protection of the Arctic Marine Environment. The working group met in April 2002 in Iceland and in February 2003 in Sweden. It agreed to expand the RPA to better address land-based activities in the context of sustainable development through collaboration with the Arctic Marine and Assessment Programme, Arctic Council projects, and the other Arctic Council Working Groups. At the 2002 and 2003 meetings, Canada confirmed its continued financial and technical support of the implementation of the Global Environmental Facility project on the Russian National Programme of Action for the Arctic.

www.pame.is/

These provisions prohibit the disposal of wastes at sea within Canadian jurisdiction, and by Canadian ships in international waters, unless the disposal is done under a permit issued by the Minister. A permit for disposal at sea will be approved only if it is the environmentally preferable and practical option. Incineration at sea is banned except under emergency situations. CEPA 1999 provides additional controls on disposal at sea, including:

It should also be noted that the requirement for a CEPA 1999 permit also triggers an assessment under the Canadian Environmental Assessment Act.

Environment Canada’s Pacific and Yukon Region collaborated with Fisheries and Oceans Canada, the forest industry, dredging contractors and recycling companies in the development and implementation of a Log Bundling Strand Recycling Initiative. Prior to this initiative, an estimated 38 million feet of log bundling strand was deposited annually on the bottom of forest industry water lots and designated ocean disposal sites.

Since its inception, the initiative has had a profound effect on the amount of bundling strand deposited in coastal waterways. The recycling industry reported a 450% increase in bundling strand recovery between 2001 and 2002. The cooperative effort between the forest industry, dredging contractors, strand manufacturers, regulatory agencies and interested stakeholders has made the recycling of bundling strand simple and economically feasible. Further information on this initiative is available at:

www.pyr.ec.gc.ca/disposal_at_sea/index_e.htm

In 2002-03, 95 permits were issued in Canada for the disposal of 4.86 million tonnes of waste and other matter (see Tables 7 and 8).

Table 7: Quantities permitted (in tonnes) and permits issued in Canada in 2002-03
Material Quantity permitted* Permits issued Percentage of quantity Percentage of permits
Dredged material 4 010 500 40 82 42
Geological matter 741 000 4 15 4
Fisheries waste 110 025 48 2 51
Vessels 312 2 <1 2
Organic 200 1 <1 1
Total 4 862 037 95 100 100

* Dredged material and geological matter were converted to tonnes using an assumed density of 1.3 tonnes per cubic metre.

Table 8: Quantities Permitted (in tonnes) and Permits Issued by Region in 2002-03
Material Atlantic
quantity permitted
Atlantic
permits issued
Quebec
quantity permitted
Quantity
permits issued
Pacific and Yukon
quantity permitted
Pacific and Yukon
permits issued
Prairie and Northern
quantity permitted
Prairie and Northern
permits issued
Dredged material* 1 016 600 11 464 100 11 2 529 800 18 0 0
Geological matter* 0 0 0 0 741 000 4 0 0
Fish
waste
104 625 43 2 600 4 2 800 1 0 0
Vessels 0 0 0 0 312 2 0 0
Organic 0 0 0 0 0 0 200 1
Total 1 121 225 54 466 700 15 3 273 912 25 200 1

* Dredged material and geological matter were converted to tonnes using an assumed density of 1.3 tonnes per cubic metre.

Most of this was dredged material that was removed from harbours and waterways to keep them safe for navigation. The number of permits issued has remained relatively stable since 1995. The quantities permitted were higher than in 2001-02 but still remain well below totals seen in the previous decade (see Figure 1).

Figure 1 (see table 7 above for long description)

Quantities fluctuate each year as a result of several factors, such as how much sediment is deposited due to the spring freshets (the rise in river levels due to snowmelt in the spring) and changes in the market cycle or practices.

Overall, permitted quantities since 1999 are lower and will remain lower due to the more accurate estimation of quantities of dredged or excavated geological material to be disposed of. Historically, according to client reports and surveys, the quantity of dredged material permitted for disposal was greater than the actual quantity disposed of at sea (often by 30-50%). This was due to the industry practice of applying a "bulking factor" so that they would not have to amend their permit if they needed to dredge more than expected. However, in 1999, user fees, which charged by quantity permitted, were introduced for dredged material and geological matter, resulting in more precise estimates of the quantities.

One emergency permit was issued to dispose of fish from an aquaculture facility killed by an algal bloom. Any emergency permit requires consultation with the International Maritime Organization. As well, input was solicited from Fisheries and Oceans Canada, the Canadian Coast Guard, and the Enforcement and Emergencies Division of Environment Canada to ensure that all necessary measures were in place to limit impacts to the marine environment and avoid unacceptable risk to human health.

As required by CEPA 1999, disposal site monitoring is used to verify that permit conditions were met and that scientific assumptions made during the permit review and site selection process were correct and sufficient to protect the environment. In 2002-03, field monitoring was conducted at a total of eight sites. Details can be found in the Compendium of Monitoring Activities at Ocean Disposal Sites, which is sent to permittees and submitted to the International Maritime Organization annually.

www.ec.gc.ca/seadisposal/reports/index_e.htm#Compend

CEPA 1999 provides for a performance-based approach to fuel standards and allows for a range of fuel characteristics to be regulated to address emissions. Regulations may distinguish between different sources of fuels or the place or time of use of the fuel. There are also provisions for regulations to establish a “national fuels mark” that may be used only if a fuel conforms to specific requirements provided for by regulations.

Based on the information requested in a notice, a report on use and releases of methyl tertiary-butyl ether in Canada was released in March 2003. This information will be used to determine whether this substance is capable of becoming toxic and whether to control it under CEPA 1999.

Progress in 2002-03 included:

Vehicle and engine emissions are a major contributor to Canada’s air pollution problem. Provisions in CEPA 1999 include the authority to set emission standards for on-road vehicles and engines. CEPA 1999 also includes authorities to set emission standards for vehicles and engines used in a variety of off-road applications, such as lawnmowers, construction and agricultural equipment, hand-held equipment, and recreational vehicles.

Environment Canada, together with partners all across the country, holds free clinics across Canada each summer where motorists can have check-ups on their vehicles’ tailpipe emissions, tire pressure, and gas cap seal. Over the summer of 2002, 5914 vehicles were tested at 30 clinics across Canada.

www.ec.gc.ca/cleanair-airpur/Sustainable_Transportation/Let's_Drive_Green-WS50AA0640-1_En.htm

Forty-five light-duty vehicles (involving over 200 independent test sequences), 65 utility engines, and one heavy-duty engine were tested to assess conformance of emissions with standards at the Tier 1 and Tier 2 emissions levels.

Progress in 2002-03 included:

CEPA 1999 Environmental Registry -- Regulations

Environment Canada along with other countries, including the United States, participated in the United Nations World Forum for Harmonization of Vehicle Regulations (WP. 29). As a signatory to the June 25, 1998 “Agreement Concerning the Establishing of Global Technical Regulations for Wheeled Vehicles, Equipment and Parts which can be fitted and/or be Used on Wheeled Vehicles”, Canada promotes progressive emission standards while at the same time promoting economic availability of vehicles manufactured to one set of standards. Canada’s participation on environmental issues by Environment Canada and on safety issues by Transport Canada involves expert technical contributions as well as regulatory process contribution to standards development.

Environment Canada led the development of a new Code of Practice for On-Road Heavy-duty Vehicle Emission Inspection and Maintenance Programs, which was approved by the Canadian Council of Ministers of the Environment in November 2002.

This section reports on results that flow from commitments in several international agreements respecting air pollution. Progress in 2002-03 included:

These provisions provide the authority to enact regulations governing the export and import of hazardous waste, including hazardous recyclable materials. They also include authorities to:

CEPA 1999 contains provisions that require the Minister to publish notification information for exports, imports, and transits of hazardous waste and hazardous recyclable material.

In 2002, more than 7300 notices were processed for proposed exports, imports, and transits of hazardous wastes and hazardous recyclable materials. During the same period, more than 89 407 manifests were processed for tracking individual shipments approved under these notices.

In 2002, total imports of hazardous wastes were 423 067 tonnes, down 15.4% from 500 000 tonnes in 2001 (see Figure 2). Approximately half of these imports were destined for recycling. There was a 12.5% reduction in imports destined for final disposal from the 2001 calendar year. Exports from Canada increased marginally from 314 000 to 340 261 tonnes between 2001 and 2002.

Figure 2 (see table 9 below for long description)

In 2002, more than 70% of these exports were destined for recycling. Of all 2002 exports, all but 729 tonnes were sent to the United States. The balance was exported to Belgium, Germany, and Finland for recycling purposes. Table 9 compares the amounts recycled with total exports and imports.

Table 9: Hazardous waste management in Canada
  1999 imports 2000 imports 2001 imports 2002 imports 1999 exports 2000 exports 2001 exports 2002 exports
Recycling 40 % 50 % 47 % 46 % 77 % 73 % 76 % 70 %
Total
imports
(tonnes)
663 000 560 000 500 000 423 000 268 000 323 000 314 000 340 000

www.ec.gc.ca/tmb/resilog/eng/resinews.htm

Results in 2002-03 included:

CEPA 1999 Environmental Registry -- Regulations

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