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Soil Protection and Contaminated Sites Rehabilitation Policy
2. Scope and Target Clientele of the Policy
Figure 1: Principles, Objectives and Actions 1. IntroductionThe objectives of the new Soil Protection and Contaminated Sites Rehabilitation Policy and its associated implementation tools are to continue the work that began in 1988 with the introduction of the Contaminated Sites Rehabilitation Policy and to better respond to present-day problems and concerns. Like the 1988 Policy, its first and foremost aims are to protect human health, wildlife, flora, the environment and public property and to increase awareness among the general public and the principal stakeholders of the problem of contaminated sites. At the same time, it reiterates and strengthens the principle adopted in 1988 that contaminated sites must not become proscribed unusable zones but, on the contrary, their reuse must be encouraged and future users protected. Various new components have however been added to those already present. A "protection" aspect has been added with the goal of implementing monitored preventive measures when new businesses are set up to carry out industrial activities likely to contaminate the soils. The objective of these measures in to ensure the protection of the environment and to avoid any repetition of the problems we are facing today. The "rehabilitation" aspect is centred around a strategy aimed at ensuring the gradual rehabilitation of contaminated sites left over from past times, beginning with those most likely to have an impact on, or which represent a significant risk to, human health, wildlife, flora, the environment or property. It includes a step-by-step approach to deal with a variety of situations. Thus, contaminated sites for which a reuse project exists, sites having an obvious impact and sites of those industrial establishments most likely to contaminate the environment must be manage, if they are shown, after examination, to have a negative impact or constitute a significant risk. For each of the three priority situations, trigger components were established to initiate the knowledge acquisition process, the first stage in the strategy adopted. For the industrial establishments targeted, this involves the implementation of an intervention program extending over a ten year period. The application of the use-based generic criteria is maintained for soils and groundwater. However, B and C criteria for soils will be subject to validation. Revisions to A criteria for soils and the criteria for groundwater have already been made. As in the past, the criteria will continue to be used to assess the impact or risk that a site represents and to establish the decontamination objectives to be attained for a given use. However, assessment of the specific risk using a standardized procedure and recourse to various risk management measures, including on-site confinement of contaminants, is a possible option for the owner of a contaminated site, provided that monitoring and continuation of the proposed measures are assured and the safety of future users and protection of the environment are guaranteed. The obligation to conclude agreements with the Ministère de l’Environnement et de la Faune (MEF) before carrying out the work, to register with the Registry Office the level of contamination on the site, the risk management measures adopted and resulting restrictions on use will make it possible to ensure the permanence of the measures taken. Sections dealing with the impact on groundwater and the management of recovered soils, waters and demolition materials have also been added. Various elements such as recourse to recognized professionals and the implementation of a fee system and economic incentives will be analysed and, where appropriate, progressively implemented. The legal framework will also be assessed and certain additions or amendments to the Environment Quality Act will be proposed to allow the objectives of the Policy to be attained. The new Policy has been developed on the basis of the analysis of the work done on contaminated sites since 1988, the recommendations resulting from the targeted consultation carried out in 1996, the restricted consultation of 1997 and a number of discussions that took place during meetings with various stakeholder groups. It attempts to fill in the gaps and meet the needs identified and, in particular, to provide Québec society with an instrument that will help ensure its sustainable development. 2. Scope and Target Clientele of the PolicyThe Soil Protection and Contaminated Sites Rehabilitation Policy includes one aspect relating to prevention and one relating to rehabilitation. The Policy aims at protecting soils and groundwater by preventing local or dispersed contamination that may result from industrial and commercial activities, and rehabilitating sites damaged by such activities. This policy targets soil contamination resulting from the improper storage of raw materials (pesticides, solvents, petroleum products, etc.) as well as the management of dredged sediments brought onto dry land for treatment or disposal. However, the use of pesticides, herbicides, fertilizers and other materials spread on the soil for agricultural purposes and the accumulation of these substances as a result of such practices as well as the management of sediments in an aquatic environment are not covered by this policy. The Ministère de l’Environnement et de la Faune (MEF) acts on these potential sources of pollution through separate regulations or directives. This policy constitutes the response framework for all situations covered within its scope. However, certain situations might require the development of particular orientations or more specific strategies at a later date. Where appropriate, these would be developed in co-operation with the targeted stakeholders in compliance with the objectives of the Policy. The clients more particularly targeted by the Soil Protection and Contaminated Sites Rehabilitation Policy are the following:
3. Four Basic PrinciplesThe Soil Protection and Contaminated Sites Rehabilitation Policy is an instrument designed to contribute to the sustainable development of Québec society. The concept of sustainable development stipulates that present use of resources and the environment must not limit their potential for use by future generations. The following four principles1 underlie the Policy:
Applied to policy, these principles have the following meaning and scope. The Prevention Principle Contaminating the soil means making it lose one or more of its functions to a perceptible extent. Contamination of this resource constitutes a social and environmental disadvantage as well as a significant economic restraint. Impacts on human health, damage to the environment, loss of use of sites and groundwater, and investor uncertainty are all direct consequences of the presence of contamination in the soil. The rehabilitation of a site is an expensive process that does not always lead to the restoration of all uses. Thus, hundreds of sites today have been negatively affected to various degrees and cannot be freely used by future generations. The prevention principle2 aims to prevent such situations from being repeated in the future. Its objective is to preserve the integrity of the soil in order to safeguard its ecological functions and guarantee full use of this resource now and in the future. Three of these principles, prevention, polluter pays and fairness, are among the 12 general principles of sustainable development identified by the MEF. The rehabilitation-reclamation principle is specific to the problem of contaminated sites. 2 Other aspects of the prevention principle which are not properly speaking part of this policy, such as modification of procedures, reformulation of products or substitution of toxic raw materials by non-toxic raw materials, may also greatly contribute to protecting the soils.The Rehabilitation-Reclamation Principle It is the responsibility of present-day society to repair as much as possible of the damage resulting from past errors rather than passing it on to future generations. Even if it has no impact or does not constitute a significant danger in its present state, a contaminated site remains a site at risk. Poorly planned modifications (change in use, drainage or excavation work carried out on the site, etc.) can result in this risk becoming significant. Sites burdened by modes of production and consumption not focused on sustainable development cannot simply be abandoned and forgotten. Rehabilitation must not only correct the situation by decreasing the impact but must also aim at upgrading, that is, returning a maximum of uses to the site and reintegrating it into the cycle of sustainable development. In the same way, excavated contaminated soils and contaminated materials collected during the rehabilitation of a contaminated site must be managed so as to reclaim them and return them to use. If it cannot immediately rehabilitate all contaminated sites, the present generation has a duty, as a responsible society, to promote the general concept of rehabilitation, elaborate a strategy to make the concept reality and apply this strategy immediately to priority cases. The Polluter-Pays Principle Each person is responsible for the consequences of any action that affects a common asset. With respect to contaminated sites, this concept is expressed by the polluter-pays principle, which establishes that the polluter is liable for the contamination he has caused and the impact it may have, as well as the costs of characterizing and restoring the sites he has damaged, and he may not transfer this responsibility to other members of society or to future generations. The application of the polluter-pays principle, which means that environmental costs must be borne internally, allows society to hold the polluter responsible and to ensure that soils and sites regain their functions. If this principle is not applied, society risks being saddled with hundreds of seriously damaged sites scattered throughout the province, which, in order to protect the public and the environment, it will have to take charge of, that is, monitor changes and use and, where required, make them safe or restore them. The Fairness Principle The fairness principle presupposes that the rehabilitation of a contaminated site is first and foremost the responsibility of those who are profiting or have profited from the failure to protect it. From another point of view, it means that an individual or a business that in good faith applies MEF policies and directives to prevent the contamination of its site or to rehabilitate it must not be placed at a disadvantage with respect to those who fail to do so. This means that the action required from all owners in the same situation facing the same problems must be similar and apply equally to all at the same time, so that no one gains any advantage over his competitors by ignoring his responsibilities or making do with half-measures. 4. Five General ObjectivesIn the light of the principles set out above, the present Policy encompasses five major objectives:
To attain these objectives, the MEF intends to use the following four levers. Voluntary Service Many contaminated places have been characterized and rehabilitated to date on a voluntary basis. The MEF intends to continue working on this voluntary basis with any contaminated site owner or project promoter who is willing to co-operate. Market Dynamics The dynamics of the market were identified in 1988 as one of the main levers permitting the rehabilitation of contaminated sites. The commitment of lending institutions, investors, insurance companies, the Canadian Mortgage and Housing Corporation and many other economic stakeholders has confirmed that, when it comes to contaminated sites, economic and environmental concerns go hand in hand. This determining influence of the market will continue to make itself felt in the future. Economic Instruments and Other Mechanisms Economic instruments or other market mechanisms can be used to influence market dynamics and initiate or accelerate the process of reutilization-rehabilitation of contaminated sites. Such interventions may take the form of special programs involving direct government contributions, the implementation of trusts, tax holidays or credits, funds or any other form of applicable mechanisms. They may be designed to apply to a special problem, a given region or certain categories of users. The MEF intends to support, by agreement with the governmental, municipal and private stakeholders involved, the development of a range of instruments adapted to clients’ problems and needs. Coercion The MEF will, as the situation requires, make use of the powers it holds to require and force owners of contaminated sites to comply with the principles expressed in the Policy. It will use this power only if otherwise unable to ensure that the owners involved co-operate. Pursuant to the adoption and distribution of the policy, any additional means of intervention required to attain the stated objectives will be formulated in the form of sections added to the Act. The proposed amendments will be submitted to the usual consultation and review process, leading to the implementation of legislative measures. Voluntary service, market dynamics, economic instruments and coercion are the mechanisms that, to various degrees, will make it possible to attain the objectives of the Soil Protection and Contaminated Sites Rehabilitation Policy. The relations existing between the fundamental principles, the objectives and resulting action are shown in Figure 1. 5. ProtectionExperience acquired in Québec and elsewhere has demonstrated that although the adoption of more high-performance technologies and the introduction of monitoring programs by business may be more expensive at the beginning, this investment quickly becomes cost effective if we take into consideration the costs resulting from the obligation to decontaminate the environment or the handicap represented by the long-term liability incurred by the presence of contamination. The past also demonstrates that it is often very difficult, if not impossible, to return to a contaminated site all the soil functions and uses that it has lost. So it would be unproductive, from both the environmental and economic points of view, to continue to rehabilitate contaminated sites without, at the same time, taking the measures needed to prevent repetition of the scenarios that led to the situation that society is now facing. The objectives of the "protection" aspect of this policy are thus to favour the adoption by the targeted industries of "clean" technologies and the introduction of stricter monitoring prevention systems, in order to maintain the quality of non-damaged soils and permit quicker, more effective and less expensive responses. The sites targeted by the preventive measures in the protection aspect of the policy are those of new industrial installations included in areas of activity likely to contaminate the soils and groundwater identified in Appendix 1, which will be established in Québec after the date this policy comes into effect. After the date this policy goes into effect, the establishment of new industrial installations carrying out activities likely to contaminate the soils and groundwater listed in Appendix 1 shall, in order to be authorized, satisfy the following requirements:
The owner shall carry out a preliminary characterization of the site in order to establish the quality of the soils and groundwater present. A copy of the characterization report must be submitted to the MEF to be used later in case of an accidental spill or when production ends to determine the rehabilitation objectives that must be met.
Restrictions on the disposal of waste materials and requirements relating to their storage as well as improvements in industrial installations and modes of operation will greatly reduce the number and seriousness of cases of soil contamination. In some cases, however, it will be necessary to go farther, to insist on improved protection systems (ex.: a double lining for petroleum products tanks installed near drinking water wells), or, when the resource is irreplaceable (e.g.: ground water in the Îles-de-la-Madeleine), completely prohibit certain industrial activities. Various regulations and directives of the Ministère de l’Environnement et de la Faune (e.g., Hazardous Materials Regulation) and the Ministère des Ressources Naturelles (e.g., Petroleum Products Regulation) identify these requirements and support this aspect of prevention.
The implementation of a monitoring program, particularly in places where the equipment may pose a risk (such as tanks, transhipment areas, etc.), will allow the company to quickly detect the presence of contamination due to equipment failure or improper handling, and respond immediately. The detection of contamination present in groundwater or surface water must immediately trigger measures to find and remove the source of contamination and collect the contaminants. The MEF must be informed of the presence of contamination and the corrective measures put in place. The monitoring program must be designed to respond to each particular situation (presence of surface water, sensitive environment, etc.).
Over the past few years, the number of contaminated industrial properties (or those on which various industrial wastes are stored in bulk or in barrels) abandoned by bankrupt owners has increased. The work required to secure and decontaminate these sites has often had to be carried out by the municipalities involved and the government and at their expense. To end this state of affairs, the MEF plans to develop and put in place mechanisms making it possible to guarantee that the amounts required to secure and decontaminate the sites and equipment are available, even if the company goes bankrupt. The Ministère des Ressources Naturelles has already broken new ground in this area by bringing in amendments to the Mining Act in 1995 that make it possible to ensure restoration of sites affected by mining activities (see box in Section 6.4), by requiring the deposit of financial guarantees before the industry begins its activity. For its part, the MEF already requires financial guarantees under the Hazardous Materials Regulation and plans to put in place post-closure environmental management funds for final waste disposal. The development of a specific insurance product, although presenting certain difficulties, constitutes another path to be explored, as does the implementation of a preferred claim in case of bankruptcy. The MEF will continue discussions with experts in the field on these various mechanisms. When appropriate, the most promising mechanisms will be presented to environmental stakeholders for discussion. The mechanisms adopted must apply to both new industrial establishments and industries already in operation.
5.4 Levels of Decontamination to Be Achieved In accordance with the Environment Quality Act and the Hazardous Materials Regulation, the person responsible for an accidental spill must report it to the MEF, recover the contaminants and restore the environment. Thus, if soils or waters are contaminated following an accidental spill or an equipment breakdown, or for any other reason, the business must take action to restore the site to the quality it had before the incident. The results of the characterization carried out before the establishment of the plant will be used to determine the decontamination objectives to be met. If action is not taken immediately after the incident, because the contamination was not noticed or is located beneath the infrastructures, decontamination must take place when the industrial establishment ends its production. If monitoring has been diligently carried out and action taken at the time of each accidental spill, the measures to be taken to return the site to its initial state when the business ends production should be minimal. If monitoring is neglected, or action on active contamination sources or at the time of previous spills is postponed, larger-scale and therefore more expensive work may be necessary to meet the decontamination objectives. The decontamination objective of returning the site to its former condition also applies in cases of contamination occurring after the appearance of this policy, even if this contamination was caused by industrial or commercial activities not targeted by Appendix 1. | |||||