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4651e1 INTRODUCTION 1
Ontario’s Waste Diversion Goal 1
Purpose of Discussion Paper 2
The Waste Management Challenge 2
2 THE WASTE WE PRODUCE 4
What We Throw Out and What We Recycle 4
How Ontario Compares 8
3 ONTARIO’S REGULATORY FRAMEWORK 12
Overview of Current Regulatory Framework for Waste Diversion 12
4 MOVING FORWARD 16
A. Setting Province-wide Waste Diversion Objectives and Targets 17
B. Residential Waste Diversion: Accelerating Centralized Composting 20
C. Developing a Financing Strategy for Increased Waste Diversion,including Centralized Composting for Residential Waste 22
D. Industrial, Commercial and Institutional Waste Diversion: A Renewed Commitment 24
E. Feasibility of Phasing-in a Ban on Disposal of Organics and Recyclable Materials 26
F. Finding New Waste Diversion Technologies 27
G. Reducing Packaging and Increasing the Recycled Content in Products and Packaging 28
H. Expanding Public Education and Awareness Activities to Promote the 3Rs 29
I. Initiating a Province-wide Monitoring System for Waste 30
5 FOR CONSIDERATION 33
Your Input is Needed 33
Consultation Questions 34
An expanding economy and a growing population are placing additional demands on Ontario’s natural resources and straining our ability to effectively manage the environmental impact of that growth. That is why the provincial government is proposing to take a new comprehensive approach to waste diversion, one that will reduce the amount of waste generated, increase the rates of reuse and recycling, and reduce the amount of waste going to disposal.
In order to achieve the results Ontarians need in waste management, the provincial government is setting a goal of diverting 60% of Ontario’s waste from disposal by the end of 2008, up from the current diversion rate of 28% .
Achieving a 60% diversion rate by 2008 is an ambitious goal, but it can be achieved if everyone — Ontario residents, businesses, industry, manufacturers and packagers, waste management experts, and environmental experts, as well as municipalities and the provincial government — commits to finding better waste management solutions. And, while the provincial government sets the overall goal and the policy framework, it will be up to municipalities and the business and commercial sectors to determine how best to get there.
Reaching this goal will be determined in large part by finding better ways of dealing with the large portion of solid waste that is made up of organic materials – organics currently make up about 38% of waste generated by households and about 11% of the waste generated by the industrial, commercial, and institutional (IC&I) sectors (e.g., factories, restaurants and schools).
It will also require progress to be made in reducing waste in many other areas such as improving the municipal Blue Box programs, requiring more waste diversion efforts from the IC&I sectors, and increased recycling of items such as electronic waste.
Though the challenges are many, Ontario is well positioned to become a leader in waste diversion, drawing on its existing environmental protection and resource conservation programs and building on the many waste reduction and recycling success stories of its municipalities, businesses and industries.
How Ontario Calculates the Waste Diversion RateThe diversion rate is the total quantity of waste diverted from disposal as a percentage of the total waste diverted plus disposed.
Waste Diversion Rate [%] = (Waste Diverted / Waste Diverted and Disposed ) X 100%
Waste disposed includes waste sent to landfill and to thermal energy from waste (EFW) facilities.
1Includes only residential and industrial, commercial and institutional (IC&I) sectors for 2002.
The provincial government is issuing this discussion paper to seek input from stakeholders and the public on ways to help Ontario reach its waste diversion goal – diverting 60% of waste from disposal by the end of 2008. The paper is organized into five sections:
Today, more than 12 million tonnes of solid waste are generated annually in Ontario. The amount of waste continues to increase, much of it destined for landfills both inside and outside the province.
Our reliance on landfill is driven largely by historical economics – currently it is generally less expensive to send waste to landfills than to establish and operate diversion programs. However, long-term environmental costs have not been factored into these cost comparisons. In addition, many large urban centres do not have access to suitable landfills within their boundaries and have to rely on disposal sites in other communities. As the market demand for recyclables increases, and public pressure against locating landfills continues, this economic imbalance may be reduced. A challenge still remains to find acceptable disposal options for the 40% of waste that will not be diverted, even if Ontario reaches its 60% goal.
Recent amendments to the State of Michigan’s waste laws provide additional motivation for diverting waste that Ontario communities and industries currently send there for disposal. These new Michigan state requirements prohibit the disposal in landfills of certain materials in domestic or imported waste, including tires, beverage containers, yard waste, sewage, and used oil.
Ontario’s challenge is to find innovative ways to extend and enhance Ontarians’ access to 3Rs programs – reducing, reusing and recycling – at home and in the workplace.
Part of the challenge is to construct an effective and efficient system that connects homes, offices, factories and schools to the industries that need and want waste materials to make new products. We know there is a tremendous amount of valuable recyclable material in our waste stream that could be put to good use. In fact, the demand for some waste materials, especially paper, is so high that some Ontario industries currently import large quantities from other countries. For example, every kilogram of aluminum that could be recovered effectively from the waste stream can be used by industry.
Ontario needs to build on the ability of industry to use recovered materials in the place of precious non-renewable resources. Spurring investment in Ontario recycling and waste management sectors will contribute to economic growth – a 2000 Statistics Canada survey found that Ontario’s waste management businesses generated revenues of $1.55 billion, 45% of all Canadian revenues for waste management.
There are many economic benefits associated with increased waste diversion. By reducing the need for landfilling, waste diversion avoids the accompanying costs of siting, constructing and operating a landfill site, as well as long-term operating and maintenance costs.
By encouraging increased recycling, waste diversion makes a contribution to economic development and job creation, by creating or expanding businesses that collect, process and broker recovered materials, as well as companies that manufacture and distribute products made with recovered materials.
In addition, waste diversion provides manufacturers with many of the raw materials they need to operate more efficiently, helping to improve competitiveness and sustainability. The paper industry, for example, depends on recovered materials. Processing of recovered, recyclable materials into feedstock provides added value in manufacturing sectors that use that feedstock.
By encouraging the reuse of products that still have significant value, waste diversion creates or expands the reuse and remanufacturing sectors. Examples include pallet rebuilders (reuse of wood), tire retreaders, electronic appliance remanufacturers, resale and thrift shops, and repair shops. These businesses focus on refurbishing products.
By encouraging source reduction (i.e. the redesign of products and processes so that less material is used to achieve the same function), waste diversion reduces the cost of doing business. For example, manufacturers can save on the use of packaging for their products.
Ontario has a long history of promoting the 3Rs and residential recycling programs such as the Blue Box and home composting, and waste reduction efforts in office buildings and other industrial, commercial and institutional enterprises have been relatively successful. We must build on that success if we are to reduce our dependence on disposal.
In 2002, Ontario threw out a total of about 9.4 million tonnes of waste. This waste went either to landfills here in Ontario or in the United States, or to incineration. Waste from residential sources, and the industrial, commercial and institutional (IC&I) sectors accounted for about 7.2 million tonnes of the waste thrown out. Waste from construction and demolition (C&D) activities accounted for the remaining 2.2 million tonnes of waste thrown out.
In 2002, about 2.8 million tonnes of solid waste generated by the residential and IC&I sectors was managed through 3Rs activities, equivalent to about 28% of the total. This included 1.2 million tonnes of residential waste and 1.6 million tonnes of IC&I waste. The residential portion of diverted waste was comprised of:
Current recycling programs have been relatively effective but, as the above shows, they deal with only a limited portion of the waste stream. For example, much more organic waste from households could be recovered. The three categories of waste generators and wastes that are the focus of this discussion paper – residential, IC&I and C&D – are described briefly below.
Paper and organic wastes (food and yard waste) represent about 62% of the total residential waste generated. The rest is made up of a wide
variety of materials, including non-recycled materials such as ceramics, textiles, leather, rubber, batteries, ashes, rubble, fibreglass, and drywall.
A 60% diversion rate is achievable through actions such as maximizing Blue Box recycling, enhancing organics diversion, and pursuing diversion opportunities in the “Other” category.
The composition of waste varies from one particular industry or commercial sector to another. Within the manufacturing sector, the composition of the waste produced depends to a large extent on the products being made. For example, waste from an electronics manufacturer would have more plastics, metal and paper than waste from a furniture manufacturer, whose waste has more wood. Similarly, waste from different retail establishments may vary. Restaurants and retail food establishments generate more organic materials than office establishments.
However, some materials such as cardboard packaging are in such common use that they appear in the waste stream of virtually all IC&I sectors.
For the IC&I sectors to achieve 60% diversion, actions must be geared toward maximizing recycling under the 3Rs regulations. Greater organics diversion should also be pursued, particularly by restaurants and food retailers. There must also be more proactive investigation of diversion solutions for materials in the “Other” category.
C&D waste is generated from the construction, renovation, repair and demolition of structures such as residential and commercial buildings, roads and bridges. The composition of C&D waste varies for these different activities and structures. Overall, C&D waste is composed mainly of wood products, asphalt, drywall, and masonry. Other components that are often present in significant quantities include metals, plastics, earth, shingles, insulation, and paper and cardboard.
As in many industrial waste streams, C&D debris also contains wastes that can even be hazardous, such as:
The C&D sector can reach the 60% waste diversion goal by taking appropriate actions to maximize the diversion of wastes covered by the 3Rs regulations. Taking measures to reduce the 17% of total waste that falls into the “Other Organic” category is also likely to be part of the sector’s strategy to meet its waste diversion goal.
There are many examples of municipal best practices in waste diversion. For example, the City of Guelph has consistently improved its waste diversion system over the past 20 years, incorporating new technologies as they became available. Its current system requires residents and businesses to separate their waste into three ‘streams’: i) wet (compostable) stream; ii) a dry recyclable stream; and, iii) a dry non-recyclable stream (garbage). When fully implemented, this system is capable of diverting 70& of Guelph’s waste.
The City of Peterborough operates a comprehensive waste diversion system for Blue Box materials, leaf and yard waste, household hazardous waste, and electronics. For 2003, Peterborough is reporting a 50% diversion rate for residential waste from landfill. Plans are underway to expand waste diversion activities by introducing a city-wide source separated organics program in 2005.
Quinte Waste Solutions (QWS) operates waste diversion programs for Centre & South Hastings Waste Services Board, whose members represent Belleville, Quinte West, Tyendinaga, Prince Edward County, Centre Hastings, Tweed and Marmora & Lake. QWS has achieved a 65% diversion rate for Blue Box materials, household hazardous waste, and organics. A ‘pay as you throw’ policy is in effect, supporting the waste diversion efforts of the participating municipalities.
Ontario’s municipal sector continues to make progress in waste diversion. In fact, based on 2002 data collected through the Municipal Performance Measurement Program (MPMP) of the Ministry of Municipal Affairs and Housing, the median waste diversion rate of Ontario’s municipalities was 27%. Table 1 shows the range of diversion rates in Ontario’s larger municipalities and regions. While final performance figures are not yet available, preliminary results indicate that municipalities achieved significantly better diversion rates in 2003.
| Municipality/Corporations | Population | Diversion Rate (%) |
|---|---|---|
| City of Toronto | 2,500,000 | 27 |
| Regional Municipality of Peel | 988,940 | 35 |
| City of Ottawa | 822,600 | 32 |
| Region of York | 634,000 | 24 |
| Regional Municipality of Durham | 551,000 | 30 |
| City of Hamilton | 494,928 | 20 |
| Regional Municipality of Waterloo | 469,800 | 40 |
| Regional Municipality of Niagara | 424,900 | 39 |
| Regional Municipality of Halton | 394,636 | 38 |
| Essex-Windsor Solid Waste Authority | 374,779 | 31 |
| City of London | 355,800 | 35 |
| County of Simcoe | 231,955 | 32 |
| City of Greater Sudbury | 155,601 | 30 |
| City of Kingston | 114,195 | 42 |
| City of Thunder Bay | 113,318 | 28 |
| Municipality of Chatham-Kent | 109,945 | 32 |
| City of Barrie | 109,720 | 32 |
| City of Guelph | 106,170 | 38 |
Diversion rates as reported to the Ministry of the Environment in a recent survey
Calculated based on a definition which includes incineration as disposal
Some municipalities are already making significant progress towards 60% diversion:
Two examples of successful waste diversion in the IC&I sectors are:
The amount of waste landfilled in Ontario, on a percentage basis, is relatively high compared to many other jurisdictions. The amount of waste diverted in Ontario (compost and recycle) is similar to countries like the U.S.A., but well behind other countries such as Austria and the Netherlands.
A scan of practices being used internationally reveals that most jurisdictions use a combination of tools to achieve their waste diversion goals:
Ontario’s diversion rate of 28% (residential and IC&I waste) is comparable to the United States (including the Great Lakes and area states) which has a 30% diversion rate for what is referred to as Municipal Solid Waste or MSW (residential, commercial and institutional waste). The largest difference between our waste disposal practices is that Ontario sends less than 2% of its waste to incineration, or energy from waste (EFW) systems, whereas the U.S. sends about 15%.
The Great Lakes states in the U.S. have varied waste diversion programs. While there are differences in the definitions used for “diversion”, high level comparisons between the current waste diversion rate of Ontario and those of the Great Lakes and area states suggest that, like Ontario, many states are investing in waste diversion.
| Jurisdiction | Current Waste Diversion Rate2 |
|---|---|
| Minnesota | 45.60% |
| Indiana | 35% |
| Illinois | 32.50% |
| New York | 29.80% |
| Ontario | 28% |
| Pennsylvania | 26.80% |
| Wisconsin | 24.60% |
| Ohio | 23.50% |
| Michigan | 15.10% |
2 Source: State of Garbage in America – 14th Annual Nationwide Survey of Solid Waste Management in the United States – BioCycle Journal, January 2004. Estimated rates using similar categories of materials for comparison.
In Canada, Nova Scotia has set an example by banning a number of wastes from disposal in landfill including: compostable organic material; newsprint; beverage containers; used tires; automotive lead-acid batteries; waste paint; and corrugated cardboard. These materials are collected through a widespread curbside recycling program and through depots. Nova Scotia’s curbside recycling and composting of organic waste was available to 76% of the population in 2002, resulting in a 46% diversion rate from disposal.
Nova Scotia has also established the Resource Recovery Fund Board (RRFB), a non-profit corporation, to lead provincial waste diversion and industry stewardship activities. It is funded by a portion of the deposit on beverage containers, as well as from fees on tires and paint. The RRFB develops and administers sustainable industry stewardship programs, helps set up new businesses based on the processing of materials diverted, and provide incentives to residents to reduce, reuse, recycle and compost. Voluntary industry stewardship programs are in operation for paint, dairy containers, beverage containers, newsprint, and used tires.
The City of Edmonton provides a good example of a comprehensive, multi-pronged waste diversion strategy. It has two curbside recycling programs:
Edmonton also has 20 Recycling Depots, called ‘Eco Stations’, throughout the city for use by residents and businesses. Eco Stations accept paper, cardboard, and boxboard, plastic, glass and metal containers, as well as household hazardous waste and almost all other waste materials.
The Edmonton Waste Management Centre combines several waste management facilities at one location, including a Materials Recovery Facility for sorting recyclables, a teaching theatre, the Clover Bar Landfill site, and the Edmonton Composting Facility, The latter facility is the largest of its type in North America with a capacity of 200,000 tonnes of municipal solid waste and 22,500 dry tonnes of biosolids each year. In 2002, Edmonton diverted 44% of its waste from landfill through composting.
For Ontario to reach its 60% diversion goal, action will be required by everyone.
For the residential sector to achieve 60% waste diversion by 2008, Blue Box recycling must be maximized and diversion of organics through composting must be enhanced. Opportunities to divert wastes in the “Other” category such as electronics must be pursued.
Currently, waste generation is almost equally split between the residential and IC&I sectors. However, as Figures 1 and 2 illustrate, the composition of the two waste streams is quite different. In the residential sector, the largest gains are likely to come from increased diversion of organics, both food and yard waste.
For IC&I sectors to achieve 60% diversion, recycling under the 3Rs regulations must be maximized. Certainly, greater organics diversion should be pursued, particularly by restaurants and food retailers. Also, more aggressive investigation of diversion solutions for the “Other” category of waste which make up about 26% of the total should be promoted.
The C&D sector will need to maximize its diversion of wastes currently covered by the 3Rs regulations in reaching the 60% diversion goal. It will also have to investigate diversion options for the 17% of their waste made up of “Other Organic”.
A focus on recycling began in Ontario in the 1980s with requirements for municipalities to undertake waste management planning and goal setting for waste diversion. Waste diversion strategies, primarily focused on the residential and IC&I sectors, took off in the early 1990s with the “3Rs Regulations”, described below. Notwithstanding these regulations, in recent years, more emphasis has been placed on residential diversion through the Blue Box program than on IC&I diversion requirements and deposit-return requirements.
This regulation requires municipalities with over 5,000 people to implement and operate recycling programs that follow certain minimum standards. Municipal recycling programs must source separate and recycle five specified materials plus two others as shown in the following table.
| Recycle All These Items | Recycle at Least Two of These Materials |
|---|---|
|
Newsprint |
Phone books Aluminum foil items Magazines Rigid plastic containers Cardboard Plastic film Boxboard Paper cups and plates Fine paper EPS3 FBC and packing Textiles Polycoat FBC |
1 Food and beverage containers 2 Polyethylene terephthalate 3 Expanded polystyrene
Ontario Regulation 101/94 also requires municipalities to implement certain composting programs:
Ontario Regulation 102/94 requires owners of the following establishments to conduct waste audits, develop and implement waste reduction plans, and update the audits and plans annually:
This regulation requires owners of the establishments listed in Ontario Regulation 102/94 and of multi-unit residential (apartment) buildings with six or more units to have source separation programs for specified wastes and to ensure that the wastes are recycled.
| School Over 350students |
Retail* Over 10000 m2 |
Construction Over 2000 m2 |
Hospital Class A,B,F |
Hotel/Motel Over 75 units |
Demolition Over 2000 m2 |
Office Over 10000 m2 |
Restaurant $3 million+ Sales | Manufacturer Over 16000 hrs worked per month |
Apartment 6 units + |
|
|---|---|---|---|---|---|---|---|---|---|---|
| Aluminum food & beverage cans | X | X | X | X | X | X | X | X | ||
| Cardboard | X | X | X | X | X | X | X | X | ||
| Fine paper | X | X | X | X | X | X | X | |||
| Glass food & beverage bottles/jars | X | X | X | X | X | X | X | X | ||
| Newsprint | X | X | X | X | X | X | X | X | ||
| Steel food & beverage cans | X | X | X | X | X | X | X | X | ||
| Brick & concrete | X | X | ||||||||
| Drywall(unpainted) | X | |||||||||
| Steel | X | X | X | |||||||
| Wood (untreated) | X | X | X | |||||||
| PET (#1) plastic food & beverage bottles | X | X | X | X | ||||||
| Aluminum | X | |||||||||
| Glass | X | |||||||||
| HDPE plastic jugs, crates, totes, drums | X | |||||||||
| LLDPE film | X | |||||||||
| Polystyrene expanded foam | X | |||||||||
| Polystyrene products | X | |||||||||
| Municipal Blue Box materials | X |
* Equivalent to a very large retail store or a mall
Ontario Regulation 103/94 only applies to establishments in municipalities with populations over 5,000, except for manufacturers, and construction or demolition projects. The wastes specified for each sector are shown in Table 2. Note that inclusion in the table does not mean that the entire sector is required to participate in recycling. For example, only about 10% of the businesses that could fit into “Manufacturer” are required to recycle under the current regulation.
Ontario Regulation 104/94 requires manufacturers, packagers and importers of packaged food, beverage, paper or chemical products to conduct a packaging audit and implement a packaging reduction work plan. The requirement applies only to manufacturers and packagers where 16,000 or more hours are worked per month, or importers whose annual cost of goods are $20 million or more.
A packaging audit must address the:
Ontario Regulation 347, under the Environmental Protection Act, exempts from waste management approval requirements wastes specified as recyclable materials. The exemption is intended to encourage recycling and waste diversion.
The regulation means that, subject to certain limitations, a waste approval is not required when materials are transported directly from the waste generator to the industrial user or manufacturer that will use it in their operations or in recycling activities.
Ontario Regulation 357 (Refillable Containers for Carbonated Soft Drinks) requires that all carbonated soft drinks be sold in refillable containers. It also requires that retail vendors refund deposits of 15¢-40¢ (depending on container size) to customers who return empty refillable containers for carbonated soft drinks.
Ontario Regulation 340 (Containers) provides an exemption to the refillable requirement for non-refillable containers that are recycled in a multi-material recycling system. The regulation allows the minimum share of sales in refillable containers to drop if the recycling rates for non-refillable containers go up.
The Waste Diversion Act (WDA), passed in June 2002, created Waste Diversion Ontario (WDO), a multi-stakeholder non-government corporation. The WDO’s mandate is to develop, implement and operate waste diversion programs for specific wastes, as requested by the Minister of the Environment.
One of the key concepts underlying Ontario’s Waste Diversion Act is Extended Producer Responsibility or EPR. The EPR concept is the foundation for the work that WDO does through the Blue Box Program and other programs under development. It gives producers or ‘stewards’ incentives to make products that generate less waste and that, consequently, impose fewer costs on the waste management system.
For each waste diversion program, WDO creates a sustainable funding method, based on fees paid by designated industry stewards. An industry funding organization (IFO), set up for each program, helps WDO with this part of the process. Each waste diversion program includes rules for industry fees to be charged, estimated costs for the program, and waste diversion targets. As part of developing a program, WDO engages in a public consultation process.
WDO is actively working with industry in a number of areas:
Electronics waste makes up a small but growing portion of the waste stream. Environment Canada estimates that, out of the 31,000,000 tonnes of waste generated in Canada in 2000, about 157,000 tonnes was composed of electronic wastes. While these wastes represent a small fraction of the waste stream in terms of quantity, there are good environmental reasons for diverting them – the toxic nature of some of their components such as metals and other contaminants, can pose serious environmental problems, Each item may contain only a small amount, but when disposed of in landfill, the quantity of these contaminants can become significant. Another potential benefit of diverting them is that some of these materials also contain valuable materials worth recovering.
Household Hazardous Wastes (HHW), because they are disposed of by homeowners, are not regulated as hazardous waste under current laws. HHW includes paints, solvents, acids, bases, antifreeze, flammables, oxidizers, pesticides, used crankcase oil, partially-empty aerosol cans, batteries, propane tanks and cylinders, and syringes.
In 2002, there were 76 municipal HHW collection programs in operation in Ontario and about 12,280 tonnes of HHW was diverted from municipal landfills, playing a significant role in reducing the environmental impact of HHW.
Any waste can be ‘designated’ under the Waste Diversion Act which would require WDO to develop and implement a waste diversion program. Some areas that could be considered for designation in the near future include: electronic products; household hazardous wastes; batteries; pharmaceuticals; fluorescent tubes.
Ontario’s challenge is to determine how best to manage waste in a way that is sustainable and protective of the health and well being of communities and the environment. Effective ways to increase the waste diversion rate are likely to require new ways of working, new ways of thinking, and new ways for all of us to participate in finding the solutions to our common problem of waste.
There are a number of factors that will help determine how successful Ontario will be in reaching its waste diversion goal. Most importantly, we must be able to create a sense of public ownership of the need to manage our wastes differently than we do now.
We will also need to effectively address some of the obstacles to waste diversion, including a recognition that landfill is currently cheaper than recycling programs. We must also build our waste diversion solutions on an understanding that convenience to the anticipated user of the system is a major determinant of its ultimate success.
There is considerable need to build sustainable markets for recovered materials. In the case of organics diversion, not only are sustainable markets for compost needed, but also new and expanded collection and processing technologies and processes, as well as effective compliance with regulations.
The provincial government also acknowledges that more effective enforcement of regulations as well as greater certainty and timeliness of environmental approvals would assist industry and commercial enterprises in meeting new waste disposal or diversion objectives.
Overall, the provincial government believes that a province-wide strategy for waste diversion is needed to take Ontario to the next level in waste management. Without taking action, Ontario will fall far short of its goal of reaching 60% diversion by the end of 2008 (see Figure 5).
The private sector has had some success at creating custom blends for the retail market (mixed with manures, peat etc.)
The value of compost sold in bulk is limited because it has to compete with topsoil and other materials which sell for about $20/tonne.
Composting can result in less Greenhouse Gas (GHG) emissions than is generated through other waste management options. Less GHG means a potential to benefit from the carbon credits and trading systems that may be available.
Anaerobic digestion has the potential for energy recovery which translates into an additional revenue stream and even more GHG savings.
There may be other uses for the compost such as rehabilitating mine tailings and brownfields.
The following discussion outlines a broad framework for better waste management through diversion in Ontario. It focuses on identifying the key areas where action is required if Ontario is to reach its desired waste diversion target in the proposed timeframe.
After considering all comments received from stakeholders and the public on the issues contained in this discussion paper, the provincial government will move forward on a comprehensive, province-wide waste diversion strategy for Ontario.
The provincial government has set an overall goal of diverting 60% of Ontario’s waste from disposal by the end of 2008. This goal raises the bar for many municipalities and businesses in Ontario and will require significant contributions from all waste generators – individuals, as well as industry. All sectors will be encouraged to look at what and how much waste they generate, where that waste goes now, and how much more can be diverted.
Achieving 60% diversion as a province could require establishing mandatory targets for some and objectives for others.
Setting mandatory targets could be appropriate for some groups where the greatest gains and results can be achieved. But for others, where targets are impractical, the government could seek other ways to encourage and promote further waste diversion, including the provision of incentives. And, even when targets are set, the provincial government plans to ensure municipalities and industries have the flexibility necessary to determine how they mobilize to meet them.
The industrial, commercial and institutional (IC&I) sectors generate a considerable amount of waste. Like municipalities, many companies have already implemented considerable measures to reduce their waste and some companies divert even more than 60% of the waste they produce. Convincing all companies in this sector to reach a 60% waste diversion rate by 2008 by managing more of their waste through reduction, reuse, recycling and composting would make a major contribution to the province-wide goal.
To ensure full participation in the IC&I sectors, the provincial government would enhance enforcement of the current 3Rs regulations (refer to Section 3: Ontario’s Regulatory Framework).
In addition, the Ministry of the Environment would also revisit Ontario Regulation 103/94 to ensure that it meets the government’s current waste diversion objectives and is appropriate for Ontario’s current business and industrial landscape. This could include consideration of the sectors now covered by the regulation, as well as the specific requirements contained in it.
New requirements could be introduced for waste generators in these regulated sectors to report to the public on their waste diversion rates, starting with the largest enterprises.
Residential waste, which is generated by household activities, and managed by municipalities, is a significant part of the waste stream. While there are a number of successful programs dealing with residential waste already in place, we want to build on that success.
To help support municipalities to increase diversion, the provincial government could set mandatory waste diversion targets for municipalities to achieve. The provincial government could set varying targets across the municipal sector to recognize demographic, geographic or technical factors. For example, diversion rates might vary according to the population of a municipality or the level of urbanization.
Mandatory targets for municipalities could be phased in. One option based on this approach could work as follows:
Progress would be monitored through the current system in which municipalities report their diversion rates on an annual basis to Waste Diversion Ontario, complemented by their reporting to the Municipal Performance and Measurement Program (MPMP), managed by the Ministry of Municipal Affairs and Housing.
To ensure everyone does their part, some degree of enforcement will be required. Municipalities have the authority to regulate compliance through bylaw enforcement. Typically, a municipality will establish standards based on provincial legislation and regulations governing what and how much waste residents are permitted to set out for collection and which materials must be separated for recycling. Some municipalities also establish bag limits and require the purchase of tags for bags that exceed the limit. Moreover, other municipalities require the use of translucent bags to monitor what is being set out. In some cases, multi-family buildings are audited. When compliance is absent, bylaw enforcement may fine the property owner or in some cases, ceases providing services.
In IC&I sectors, waste management is normally managed by the private sector and the contracts will often establish clear limits on what will be handled. For the waste generator, the incentive to reduce waste usually derives from the costs incurred for waste disposal. Quite often, though, recycling programs are associated with increased costs, reducing the incentive. There is a clear need for effective enforcement of compliance in order to ensure a fair playing field for all businesses.
Effective enforcement is the key to compliance. There may be opportunities to obtain greater diversion rates through stricter enforcement of the existing 3Rs regulations. Working within the existing regulatory framework may also allow for additional materials to be added to the amount of waste that is successfully diverted.
Organic waste materials hold great potential if they are considered as a resource, rather than as a something simply to be disposed of as they represent about 38% of the current residential waste stream and about 11% of the industrial, commercial and institutional waste stream. Many Ontario households are already dedicated to backyard organics composting. Currently, 1.25 million households are responsible for diverting about 125,000 tonnes of organic waste through backyard composting. Together with the centralized composting capacity developed in a few municipalities, about 485,000 tonnes of organic waste (the majority of which is leaf and yard waste) are now being diverted from disposal.
To achieve a 60% diversion rate, Ontario needs to increase the amount of organic waste that is being diverted from the current 485,000 tonnes to 1.2 million tonnes by 2008 – a significant increase.
Increasing the amount of household backyard composting is essential, though limited in terms of the volumes and kinds of materials involved. Each household composter diverts about 100 kilograms of organic material per year from disposal for a one-time cost of about $45 to $60 per composter. It can manage yard wastes, food residues from fruits and vegetables, and ornamental plants, but not other compostable household organics such as pet droppings and bedding, bones and meat scraps, disposable diapers, food wrappings, large quantities of leaf and yard waste.
Theoretically, if each one of the remaining two million single family households started using a composter, another 200,000 tonnes could be diverted. At $45 - $60 per composter, this initiative would cost between $90 million to $120 million and add 5% to the overall provincial waste diversion rate. This is the maximum diversion the province could achieve through backyard composting.
Clearly, backyard composting, while important, is not enough. To achieve a significant increase in the amount of household organic waste being diverted, centralized composting systems and facilities are necessary.
Fortunately, there is a record of success to build on:
municipalities such as Guelph and Toronto have started to collect and compost a wide variety of ‘wet’ kitchen and household wastes such as wet food, coffee grounds, and kitty litter. These ‘wet’processing systems differ from yard waste systems in that they are typically, large-scale centralized composting facilities usually housed in a building operated under controlled conditions. They are able to accelerate decomposition by aeration (fans), continuous turning and controlled moisture, or through the use of anaerobic digestion.
Toronto’s success with organics diversion in Scarborough and Etobicoke has led to their intended expansion of the program to an additional 210,000 homes in October, 2004. Similarly, Guelph has achieved a high diversion rate through their wet/dry diversion program.
To be able to divert 1.2 million tonnes of residential organic wastes by 2008 (and reach the 60% diversion target), Ontario must add about 600,000 tonnes of capacity to its current centralized composting capacity. This would require additional infrastructure able to deal with more than 2,000 tonnes of organic wastes per day. While a larger municipality might be served by its own facility with a capacity of up to100,000 tonnes/year, facilities with a capacity of up to 25,000 tonnnes/year could meet the needs of smaller municipalities. There may also be opportunities to maximize economic efficiencies by combining municipal and private sector composting facilities, or building larger regional facilities.
While the capital cost of building new plant capacity to process this amount of material varies based on the specific technology used, the overall capital costs are expected to be significant. A number of estimates have been developed by different organizations for their own purposes:
Based on this range of cost estimates, the cost of implementing a province-wide system to handle the additional 600,000 tonnes/year to achieve a 60% diversion rate for organics in 2008 could be significant. On an amortized capital cost basis, these estimates suggest that the costs of backyard composting and centralized composting can be relatively comparable to process the same amount of organics waste. A range of possible financing options for waste diversion infrastructure and ongoing operation is discussed in the next section.
3 A former interim group of stakeholders established to assist the Ministry with development of stewardship programs and waste diversion initiatives.
Considerations:
Diversion of waste from disposal, while it involves additional costs, serves a strategic purpose for the municipalities and industries seeking to better manage their wastes. Based on information submitted to WDO for the year 2002, costs per tonne to operate a Blue Box system, typically range from about $85 to $250 per tonne, with higher costs often being associated with travel costs in servicing a large rural area.
hus economies of scale can be assumed for larger municipalities. In addition, some of the costs associated with diverting more waste through the Blue Box system are offset by 50% contributions from industry through Waste Diversion Ontario’s Blue Box Program Plan.
Similarly, the range of operating costs for a centralized organics program will range significantly with size of municipality; typical processing facility operating costs are approximately $100 per tonne.
One major challenge in the development of more waste diversion, including expanded composting capacity in Ontario, is the issue of how to finance the construction and ongoing operation of the necessary infrastructure.
In order to meet the 60% target, the largest municipalities would have to accelerate and expand their residential organic waste collection and centralized composting in the near term. This would require significant up-front capital expenditures and additional resources would be required for ongoing operation. In addition, municipalities would incur ongoing operational costs for collection and processing. A financing strategy that could include financial support from the provincial government could be considered as part of developing this overall strategy.
The IC&I sectors include a wide range of businesses such as manufacturers, banks, retail shops, schools, apartment buildings, construction and demolition companies and many others. Waste generated by these IC&I sectors is an important candidate for waste diversion because it represents half or more of the total waste stream.
The existing regulatory requirements may need to be changed to better reflect a renewed commitment to waste diversion. A limited number of IC&I waste generators fall under the existing regulation: Ontario Regulation 103/94 covers the largest generators in select sectors. Also, the regulation currently does not include any requirements for organic waste diversion.
To monitor progress on meeting the 60% diversion objective, the provincial government could require the largest waste generators in the IC&I sectors to report their waste diversion rates publicly. This could be phased in on a sector-by-sector basis over a few years beginning with the sector that generates the largest quantity of waste.
Achieving waste diversion in small businesses may be better helped by providing needed training, rather than by regulation. The provincial government could work with different partners, such as industry associations, to provide sector-focused training on waste reduction.
Small businesses would continue to be exempt from Ontario’s 3Rs regulations, but would be encouraged to make progress in waste diversion. A 2000 survey completed by the Canadian Federation of Independent Business (CFIB) found that “the high concern that small and medium-sized enterprises (SMEs) have for the environment is also evident in the way they manage their own day-to-day affairs. In 2000, one in two small businesses (47.4% of respondents) threw out less or an equal amount of garbage compared to a household.” According to CFIB, this represents a significant improvement from 1990, when only 28.1% met that standard.
There are many examples of successful waste reduction programs operated by companies and organizations in the industrial, commercial and institutional sectors. Many have been recognized by the Recycling Council of Ontario in its annual Waste Reduction Awards. For example, in 2002/2003 RCO recognized the following companies, among others, for their achievements in waste minimization:
For example, California’s State Agency Buy Recycled Campaign (SABRC) requires all state agencies to purchase products with recycled content. SABRC complements the Integrated Waste Management Act which seeks to reduce the amount of waste going to California’s landfills.
Specifically, all state and local government agencies in California must ensure that 50% of their purchases are recycled-content product (RCP) purchases. Suppliers of RCP must certify the recycled content of all products offered or sold to the state. State agencies are required to report their RCP purchases annually to document compliance with the RCP procurement mandates of the SABRC.
This discussion paper has emphasized that diverting organics and recyclables from disposal is a critical component of achieving the 60% diversion goal in the residential sector. Preventing these materials from going to landfills will help preserve our natural resources and reduce the impact on the environment, reducing odours caused by the organics as they decompose and avoiding problems caused by landfill leachate on groundwater.
The provincial government could consider phasing in a ban on the disposal of certain organics (e.g., household organics) and recyclables (e.g., Blue Box materials) from disposal.
Many provinces are targeting organics in their diversion strategies. Both Prince Edward Island and British Columbia have established aggressive diversion targets with an emphasis on organics. Nova Scotia is the only province to have implemented a ban on organics – it banned compostable organic material from landfills in 1998. The ban includes food waste (including meat, fish, bones and dairy products), leaf and yard waste, and non-recyclable paper products. Now, 76% of Nova Scotians have curbside collection and centralized composting of food, leaf and yard waste, and paper products. In addition, 53 of 55 municipalities in the province offer centralized composting to businesses, including supermarkets, restaurants, food processing plants, etc. As a result of its success in waste diversion, Nova Scotia plans to close 15 landfill sites by 2005.
However, it is important to note that a ban on organics in landfill would only be enforceable if it applied to all waste generators. This would mean that the industrial, commercial and institutional sectors would also need to be subject to the ban. The greatest success would come from full participation, which would likely require additional efforts in enforcement.
Diverting more of these materials means that adequate alternatives to disposal must be made available. Alternatives could include residential and IC&I source separation programs and the provision of recycling containers or depots in public areas. Where adequate alternatives for managing these materials do not exist, time would be needed to put appropriate alternatives in place. This means that any ban would likely have to be phased in over a reasonable period of time.
New technologies may be able to help Ontario increase its waste diversion rate by helping us to recycle and manage materials more easily and at lower cost, and to enable diversion of a broader range of materials.
New technologies will be helpful in areas such as organics diversion. For example, collecting organic material such as food scraps from apartment buildings is difficult because of convenience and storage issues. Innovations may allow garbage chutes to be modified to direct organics, recyclables and garbage into separate containers below. Other innovations may include the use of “deep collection” systems which use in-ground containers to store organic wastes, keeping the collected wastes cool to prevent odours. In municipalities where many residents live in apartments or condominiums, a significant amount of organic material and other recyclables will be missed if new technologies are not developed.
Before a new waste diversion technology can be developed on a large scale, it must demonstrate that it reliably delivers on its promises and effectively protects the environment. Research or demonstration projects may be one way for that to happen.
To encourage the private sector to come forward with innovative technologies and investment, Ontario needs the right climate for research and development. In part, this means ensuring we have the right approvals process – one which protects the environment but also spurs investment, innovation, and economic development.
To help facilitate new technology development, the provincial government could consider streamlining the approvals process under the Environmental Protection Act (EPA) for small scale research or demonstration projects for new or emerging waste diversion technologies. Small scale research or demonstration projects are not normally subject to the Environmental Assessment Act (EAA) but the existing “research” exemption in Ontario Regulation 334 for municipal projects could be further clarified.
Approval could depend on the scale and length of the project, with approval requirements under the EPA streamlined so that they were proportional to the potential level of environmental effects of a project. All proposals would require clearly defined and documented research objectives and study protocols. Air approvals under the EPA would still be required for any air emissions. Municipal land use approval requirements and bylaws would still apply to all sites.
While packaging serves many useful functions, its utility is temporary. Packaging becomes waste as soon as it has fulfilled its intended purpose, regardless of how important and necessary that purpose may have been. In fact, its usefulness has made it a large component of almost all waste streams. Packaging makes up about 25% by weight of the residential waste stream and makes up a considerably higher percentage by volume.
Under Waste Diversion Ontario’s (WDO) Blue Box Program Plan, brand owners and importers of printed paper and packaging materials in the residential Blue Box system pay fees to cover half of the net cost incurred by municipalities for the operation of their Blue Box programs. The fees are based on the quantity and type of materials managed by municipalities.
The government expects that WDO’s Blue Box Program Plan will help reduce packaging. The Blue Box Program Plan’s financial incentives encourage companies to use less packaging, or use recyclable materials in their packaging that are marketable or cost less when they arrive in the Blue Box system. These companies will pay fewer fees when they package products in materials that are easily recycled and when they reduce the amount of materials in their packaging. The list of packaging materials and product stewardship activities will expand over the next few years so that there will be less and less non-recyclable materials used in packaging.
The provincial government could pursue opportunities at the national level to improve programs aimed at reducing packaging, and increasing recycled content of products, building on successful initiatives such as the CCME National Packaging Protocol which achieved a 50% packaging reduction by 1996, well ahead of the 2000 deadline. Additionally, the provincial government could continue development of useful information on how best to promote packaging reduction, reuse and recycling.
Under a deposit-return system, the product or product container is subject to a deposit when purchased which is refunded to the purchaser when the used product or product container is returned. The amount of the deposit would need to be enough, relative to the product cost or type of product, to encourage returns to be made. In some situations, deposit-return systems have proven to be a very effective way to ensure that a high percentage of waste is diverted.
Most people and businesses want to recycle, buy environmentally friendly products and reduce the amount of waste. Continuing promotion and education is important to help people recycle and to assist municipalities and industry to develop recycling and other waste diversion programs.
A promotion and education plan could meet information and education needs and determine how best to promote waste diversion. The plan should describe the benefits of recycling and waste diversion, give examples of successful and innovative recycling programs and technologies, provide information on how different types of recycling programs work (such as organics source separation programs), and identify what recycling information and reports are available and where to get them.
The provincial government would work in partnership with all stakeholders to develop and distribute information and educational materials to the public, municipalities, and the business community.
Comprehensive data is needed to measure progress towards Ontario’s waste diversion goal. We must measure our performance so that we can keep on track, make adjustments where necessary, and keep the public informed.
The provincial government could require all waste generators (municipalities and industry) to monitor and report waste statistics such as waste generated, diverted and disposed in order to monitor progress. Requirements for IC&I sectors would be phased-in, starting with the largest waste generators first. The provincial government could require waste management facilities (e.g., waste transfer stations and landfills) to develop a data monitoring and reporting system to enable the ongoing measurement of the success of waste diversion activities promoted under this strategy.
The data monitoring and reporting system would have to include data on facility capacity, and on waste types and quantities disposed or diverted. The reporting requirement could apply to all sites used for the management of waste including landfills, incinerators, transfer stations, and processing facilities.
Note that these are examples of actions that could be part of a provincial waste diversion strategy. They should not be considered as a government commitment, but rather as an area for consideration and discussion.
All interested individuals and groups including municipalities, industry, environmental groups, the recycling and waste management industry, waste management professionals, and the general public are being asked to participate.
No decisions have been made on the approaches and options described in the paper. All comments received from stakeholders and the public will be considered before any decisions are made.
If you are interested in responding to this paper with your ideas and suggestions, please contact the Ministry of the Environment by sending comments by mail, fax or email to:
Ontario Ministry of the Environment
Waste Management Policy Branch
Ontario’s 60% Waste Diversion Goal: A Discussion Paper
135 St. Clair Avenue West, 7th floor
Toronto, Ontario, M4V 1P5
Fax: (416) 325-4437
Email: wastediversion@ene.gov.on.ca
You can also provide comments directly through the Environmental Bill of Rights (EBR) Environmental Registry where you will find a copy of the Discussion Paper. www.ene.gov.on.ca/envregistry/022784ep.htm
Please provide your response by August 9, 2004.
In addition to formal written responses, you are encouraged to participate in a series of public and stakeholder consultation sessions being held throughout the Province. Sessions are currently planned in June. For further information about meetings in your area go to the website of the Ministry of the Environment at www.ene.gov.on.ca or call toll-free at 1 800 565-4923 or, in Toronto, 416 325-4000.
Your participation is greatly appreciated.
The provincial government welcomes comments on any topic raised in the discussion paper. The provincial government is particularly interested in advice and perspectives on the following:
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