Draft Framework for the National Waste Management Strategy

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The deadline for public comments on the Draft Framework for the National Waste Management Strategy is the 18th May 2009.

1. Introduction

1.1
In terms of environmental policy development, these are both exciting and challenging times. They are challenging in that the serious nature of threats to the integrity of environment as a result of human activities is becoming steadily clearer. They are exciting in that governments all over the world have begun to recognize the importance of environmental policy and planning in sustaining the societies they serve.

1.2
Waste Management is in many ways the lynch-pin of environmental planning. Successful management of its own waste products is fundamental to the sustainability of any society. As human societies have evolved in scale and complexity, so too have the management problems in terms of waste – in some ways, exponentially.

1.3
The National Environmental Management Act: Waste Act passed by the South African Parliament in 2007 (“the Waste Act”) requires the development of a National Waste Management Strategy (NWMS) to achieve its objectives. The Waste Act is the result of an ongoing process of evolution of national legislation, policy, agreements and research on waste management. It has also been informed by the evolving international system of environmental governance. The NWMS will build on this process of policy development, and attempt to consolidate and advance in various areas.

1.4
In particular, the “new” NWMS will draw on the policy foundation and experience with implementing the existing NWMS, published by the Department of Environmental Affairs and Tourism (DEAT) and the Department of Water Affairs and Forestry (DWAF) in 1999. This 1999 strategy set out an integrated approach to waste management, cradle-to-grave management of waste products, and the waste hierarchy approach, which focused in descending order of priority on waste reduction, reuse and recycling. The strategy included a detailed series of action plans for implementing various aspects of the strategy.

1.5
Some of the actions envisaged in the strategy were not implemented in their entirety, partly as a result of the lack of institutional capacity at different levels of government and industry, and partly due to the absence of enabling legislation. Compliance with many of the strategy’s action plans was on a voluntary basis.

1.6
One of the salient features of the Waste Act is that it creates a powerful regulatory framework for waste management, granting significant regulatory powers to the Minister for Environmental Affairs and Tourism, and in so doing addresses one of the obstacles encountered in the implementation of the existing NWMS.

1.7
In describing a framework for the NWMS, this draft document sets out the policy context that should inform the drafting of the NWMS. This includes a high-level overview of the evolution of the legislative and policy framework for environmental policy with respect to waste management, an overview of our obligations in terms of International and multi-lateral agreements, and an overview of the existing NWMS and its implementation.

1.8
The NWMS should establish the context in which the measures provided in the act should be applied. Accordingly the framework for the NWMS also draws on an analysis of the waste measures, institutional arrangements, and planning requirements of the Waste Act itself.

2. The policy and legislative context

2.1
The Constitution of the Republic of South Africa, 1996 (Act 108 of 1996) is the foundation of the system of environmental regulation and policy, and creates a human rights foundation for society and government that includes ‘third generation’ development rights.
Section 24 of Chapter 2 – the Bill of Rights establishes that everyone has the right to an environment that is not harmful to their health and well being, and that legislative and other measures should be used to ensure that the environment is conserved and protected for future generations.

2.2
In 1995, following the first democratic elections, the Consultative National Environmental Policy Process (CONNEPP) was launched, resulting in the 1997 White Paper on National Environmental Management. In its objectives, the 1997 White Paper defined a hierarchy of waste management practices that remains a key principle of our waste management policy:

2.3
A main policy goal set out in the 1997 White Paper was a review of existing environmental legislation that would identify key legislative priorities and lead to the development of relevant and effective legislation. This policy goal resulted in the development of the National Environmental Management Act of 1998 (NEMA), which established the principles that govern all environmental management activities, building on the foundation provided by the 1997 White Paper and Section 24 of the Constitution. In relation to waste management in particular, NEMA establishes the following principles:

2.4
NEMA also provided an institutional framework, which included:

2.5
By providing a coherent framework of principles for environmental planning within the context of co-operative governance, NEMA paved the way for the development of the first National Waste Management Strategy (NWMS), published in October 1999.
The 1999 NWMS represented a significant advance in terms of providing a coherent, integrated approach to waste management and in many respects provides the context for the new NWMS. For this reason, it is discussed in greater depth elsewhere in this document.

2.6
In the process of developing the NWMS of 1999, the importance of developing an integrated approach to the management of pollution and waste became clear, resulting in the White Paper on Integrated Pollution and Waste Management for South Africa, 2000. The white paper specified the need to review legislation pertaining to waste management in light of the shift in focus from waste disposal to waste avoidance and minimization. This review process ultimately resulted in the Waste Act of 2007 that prescribes the formulation of the new NWMS.

2.7
The framework of environmental principles established by NEMA provides the basis for a series of Acts relevant to waste management, including:

2.8
The Minister has also created a detailed regulatory framework for the performance of Environmental Impact Assessments (EIAs) based on chapter 5 of NEMA, streamlining the previous system based on the Environment Conservation Act .
In terms of environmental policy, climate change has emerged as a priority area with implications for waste management. In October 2004, the DEAT launched the Climate Change Response Strategy, which was approved by Cabinet the following month.
During the financial year 2005/2006, the DEAT conducted intensive sector-specific consultation with a view to developing sector adaptation plans and mitigation plans.

2.9
The first National Climate Change Conference was held in October 2005. Owing to the crosscutting nature of climate change, the DEAT has established four formal stakeholder committees, which inform and coordinate climate change issues, including the implementation of the Climate Change Response Strategy.

3. International obligations

3.1
The Waste Act specifies as one of the requirements of the NWMS that it should give effect to South Africa’s international obligations in terms of waste management. Furthermore, the background of International declarations, agreements and treaties has provided an important context for the evolution of South African environmental policy in general, and waste management policy in particular.
In many respects, the United Nations Conference on Environment and Development (UNCED) held in Rio de Janeiro in June 1992 ushered in the modern period of global co-operation on environmental issues. The “Earth Summit” (as it became known) was significant for developing country negotiators because it linked the concepts of environment and development and thereby placed sustainable development firmly on the global agenda.

3.2
The principal outcomes of the Earth Summit included:

3.3
The Rio Summit was the pre-cursor to a series of multilateral environmental agreements (MEAs), including treaties on forests, regional trans-boundary air pollution, desertification, biotechnology safety, land-based sources of marine pollution, water quality, regional trans-boundary movement of hazardous waste, the management of toxic chemicals, and the trans-boundary movement of radioactive waste. Many of these instruments came into being during the 1990s, thereby creating the modern system of global environmental governance.

3.4
In the build up to the Rio Summit, the Basel Convention, held on 22 March 1989, called for control of the trans-boundary movement of hazardous waste and its disposal. Whilst South Africa subsequently acceded to this Convention, no legislation was passed at the time to give effect to it. The second Basel convention, held on 8 October 2005, set standards for the control of trans-boundary movements of hazardous wastes and their disposal, setting out the categorization of hazardous wastes and the policies for their disposal between member countries. South Africa accedes to this convention and implements its provisions.

3.5
The Rotterdam Convention was held in September 1998 to promote shared responsibilities in relation to importation of hazardous chemicals. One of the key provisions is the Prior Informed Consent (PIC) procedure, which lists information on hazardous chemicals in Annex III. It became legally binding on its parties in 2004. The convention promotes open exchange of information and calls on exporters of hazardous chemicals to use proper labelling, include directions on safe handling, and inform purchasers of any known restrictions or bans. Parties can decide whether to allow or ban the importation of chemicals listed in the treaty, and exporting countries are obliged make sure that producers within their jurisdiction comply. From this convention a PIC circular is distributed every six months giving updated information on the listed chemicals, member compliance and sources of supporting information.

3.6
In 1995 the United Nations Environment Programme called for global action to be taken on persistent organic pollutants (POPs), which pose a threat to both health and the environment. As a result, the negotiations for the Stockholm Convention on POPs were initiated and culminated in May 2001, with the convention entered into force in May 2004. South Africa accedes to this convention, whereby member countries have agreed to phase out POPs, and prevent their import or export.

3.7
Following the Millennium Summit convened by the General Assembly of the United Nations, which adopted the Millennium Development Goals, a ten year review progress on the implementation of Agenda 21 was convened in Johannesburg in 2002. In September 2002 the Johannesburg Plan of Implementation, which affirmed the United Nation’s commitment to the full implementation of Agenda 21, was agreed to at the World Summit for Sustainable Development (WSSD). The Johannesburg Plan of Implementation sets out 37 targets for achieving sustainable development, which are inclusive of the Millennium Development Goals.

3.8
In fulfilment of the Johannesburg Plan of Implementation DEAT developed the National Framework for Sustainable Development which initiates a broad framework for sustainable development and provides a platform for the development of a national strategy to give effect to the targets set out at WSSD. The National Framework for Sustainable Development was published in 2008.

3.9
In February 2006 the first session of the International Convention on Chemicals Management took place in Dubai, where it adopted the Strategic Approach to International Chemicals Management. This approach aims to support the achievement of the goals set at the 2002 WSSD in Johannesburg. Currently South Africa, represented by DEAT, is preparing for the second session of the International Convention on Chemicals Management which will take place in Geneva in May 2009.

3.10
South Africa has acceded to conventions intended to prevent pollution of the seas. These not only cover the obvious issue of dumping waste at sea, but also prescribe measures to prevent waste on land contaminating the seas and waterways. This waste includes oil, solid waste, nuclear waste and debris from landfill sites.

3.11
Several obligations exist around measures to protect the ozone layer and mitigate climate change. One of the roles that waste management can play in achieving these obligations is the reduction and efficient management of gases released from waste at landfill sites.
 

4. Review of the 1999 NWMS and its implementation

4.1
The 1999 NWMS was the first integrated strategy for addressing South Africa’s waste management challenges, and gave effect to the suite of policies and legislation which preceded it, including the Constitution (1996), the Environmental Management Policy for South Africa (1998), the Draft White Paper on Integrated Pollution & Waste Management (1998), the National Water Act (1998) and NEMA (1998). The overall objective of the strategy was to reduce the generation of waste and reduce the impact of all forms of waste on economic development, health and the quality of environmental resources.
 

4.2
The 1999 NWMS sought to achieve three key goals:

  1. Develop strategies for integrated waste management;
  2. Develop action plans to implement the strategies; and
  3. Build capacity within DEAT and DWAF to implement the action plans.

4.3
The 1999 NWMS was based on the waste hierarchy approach, and covers eight key elements which are: integrated waste management & planning, a waste information system, waste management & prevention, recycling, waste collection & transport, waste treatment, waste disposal, and implementing instruments.

4.4
The 1999 NWMS set out strategies up to the year 2010 in which national, provincial, and local government were assigned functions and responsibilities, and in which quantifiable plans, objectives and targets were set. Consisting of two main parts and several supporting annexures, the 1999 NWMS identified priority initiatives for the short, medium and long term. Each priority initiative was rated against the criteria identified in the Draft White Paper on Integrated Pollution & Waste Management. Part two of the 1999 NWMS provides detailed information on both the background of each priority initiative and the detailed planning for the achievement of these.
An overview of the main proposals and progress with their implementation is set out below, structured according to the thematic areas identified in terms of the 1999 NWMS priority initiatives.

4.1 Integrated Waste Management Planning

4.1.1
The implementation of an Integrated Waste Management Planning system was seen as key to aligning and coordinating the activities of government and industry, in order to optimise waste management, maximise efficiency and minimise the associated environmental impacts and financial costs of waste. This was identified as a high priority short term initiative in the 1999 NWMS.
 

4.1.2
The Action Plan for the integrated waste management planning system required the promulgation and enforcement of regulations for integrated waste management planning, preparation of guidelines for the development of the plans, and awareness campaigns to promote the need for and approach to integrated waste management planning.
 

4.1.3 The following diagram represents the core of the integrated waste management planning system, which requires integrated hazardous waste management plans, integrated general waste plans and industrial waste management plans.

4.1.4
Waste Management Plans

4.1.5
Two provinces have developed integrated hazardous waste plans, namely North West and Western Cape whilst the former has integrated this into its IWMP. Mpumalanga is in the process of developing its integrated hazardous waste plan. Whilst not a requirement of the 1999 NWMS, the North West has finalized its IWMP and the Northern Cape is in the process of doing so. However, the Waste Act addresses this by specifying that the provinces are required to prepare IWMPs as provided by Chapter 3 Section 11.
 

4.1.6
Over two thirds of district municipalities have developed integrated general waste management plans whilst just over three-fifths of the municipalities have developed theirs and the number of municipalities that have developed IWMPs in each province varies between 14% and 100%.
 

4.1.7
The status of the integrated waste management plans for industrial waste is unconfirmed since there no compulsory preparation or reporting requirements. This has been addressed by the Act, which provides that the Minister or MEC may obligate individual persons or category of persons or industries to submit integrated waste management plans.
 

4.1.8
With respect to guidelines for the preparation of IWMPs, the national framework guideline for the development of IWMPS has been drafted and three provinces, namely Gauteng, Western Cape and KwaZulu-Natal, have also produced provincial guidelines.
These guidelines will go a long way to ensuring consistency and uniformity in the development of the IWMPs, which currently show great variances in content and quality, as well as the extent to which they are included in municipal IDPs, which is important for aligning priorities and influencing the allocation of resources for implementation. As a result there are varying degrees of implementation of municipal IWMPs.
 

4.1.9
In terms of Industry IWMPs, the Department has developed draft guidelines and the Department of Minerals and Energy has developed a list of technologies to reduce the hazardous nature of waste.
 

4.1.10
In terms of regulations to enforce the required planning documents, these will be prepared in light of the promulgation of the Waste Act. At a provincial level, Gauteng province has drafted IWMP regulations obligating municipalities to prepare and submit IWMPs to province. The development of these regulations will be a significant enabling factor in the preparation of IWMPs by the provinces and municipalities.

 

4.2 Waste Information System

4.2.(1)
DEAT’s vision has been to establish a Waste Information System for South Africa which supports the needs of local, provincial and national government with respect to the management of waste, by collecting reliable, national data on waste, and by providing “accessible information to interested and affected parties, that will support effective integrated pollution and waste management” (DEAT, 2000).
 

4.2.(2)
It is also DEAT’s intent to collect this data without placing an undue financial and capacity burden onto industry and the private sector, which are responsible for providing the data, and government, which is responsible for collecting, verifying and disseminating the data and information.
 

4.2.(3)
Significant progress has been made in the development of the Waste Information System, which was one of the focal areas of the NWMS implementation project, with the development of the required software and launch of an online database. The system is currently underutilized as reporting has to date been done on a voluntary basis, but the Waste Act has now made the supply of this information mandatory, which will ensure that a comprehensive database of waste information can be generated. Furthermore, draft waste information regulations have been developed.
 

4.2.(4)
At a provincial level, Gauteng and Western Cape have Waste Information Systems with similar data fields, which ensures that the provincial information aligns with the national information requirements.
 

4.2.(5)
Key challenges with respect to the effective deployment of the Waste Information System will be to ensure that the database is populated and that the information is used to support effective integrated pollution and waste management, as anticipated by the White Paper.

4.3 Waste minimization and waste recycling

4.3.(1)
Waste minimization and recycling has been one of three focal areas for the NWMS implementation project. The objectives of this component of the project were to increase and extend waste recycling in selected pilot areas; identify new waste streams for recycling; expand existing recycling initiatives and improve as well as implement new recycling initiatives; and identify and develop appropriate mechanisms to promote sustainable recycling by all members of the recycling chain. Several demonstration projects have been launched in a bid to boost waste recycling in the country.
 

4.3.(2)
A great achievement in respect to waste minimization was the introduction of the Plastic Bag initiative, which was also the first use of a tax instrument to effect a change in consumer and industry behaviour. In the revision of the NWMS, careful consideration will be given to whether this form of tax instrument has produced the desired result and whether it can be extended to other areas of waste minimization.
 

4.3.(3)
Another milestone has been the drafting of the Cleaner Production Strategy in 2004, although it is yet to be approved by Cabinet. The implementation of the strategy resides with the Department of Trade and Industry, which has overseen the establishment of the National Cleaner Production Centre with demonstration projects in three industries.
 

4.3.(4)
In terms of the demonstration projects, one of these has been the implementation of an Industrial Waste Exchange Pilot Project Programme, which aimed to develop an industrial waste exchange programme for the Sedibeng District Municipality (comprising three local authorities, i.e. Emfuleni, Lesedi and Midvaal), as a model for reducing industrial waste currently disposed to the permitted landfill sites or illegal dumps.
 

4.3.(5)
A second leg to the programme was an investigation of Extended Producer Responsibility as a mechanism for bringing about waste reduction in South Africa, through the minimisation, reuse and recycling of waste products. A key finding of the investigation was that there is no single universal model of Extended Producer Responsibility. The systems implemented internationally share no common set of goals, no uniform regulatory structure, and no comparable pricing schemes. Hence, an Extended Producer Responsibility process for South Africa would need to be developed on a product specific basis.
 

4.3.(6)
The research process concluded that the following groups of products should be prioritised for further investigation and implementation for extended producer responsibility: plastic bags (the plastic bag initiative and introduction of plastic bag tax in 2006); glass (the Memorandum of Understanding); waste tyres (the Memorandum of Agreement on Waste Tyres and establishment of a tyre levy); and e-Waste (Waste from Electrical and Electronic Equipment). The study also recommended that the experience gained and lessons learnt from the implementation of the Plastic Bag Initiative could be used to guide more effective and efficient implementation of future Extended Producer Responsibility initiatives for other products/commodities.
 

4.3.(7)
A third component of the recycling and waste minimization programme was the establishment of the Mbombela Recycling Pilot project to determine whether a recycling initiative could yield sustainable incomes for a co-operative comprising historically disadvantaged women. The project recently received funding from Buyisa-e-Bag to establish a Materials Recovery Facility, and it is too early to assess whether such a project is viable and replicable.

4.4 Waste collection and transportation

4.4.(1)
The starting point with regard to waste collection and transportation was to develop an understanding of the status of waste collection, and associated backlogs, at municipal level, which was achieved through a comprehensive baseline study in 2006.
 

4.4.(2)
In terms of determining waste collection standards, the CSIR has been appointed to develop these per the requirements of the Waste Act, a process that will run in parallel with the development of the NWMS. At a provincial level, Gauteng has drafted minimum waste collection standards and DEAT has developed guidelines for waste collection in dense areas.
 

4.4.(3)
Alternative approaches to waste collection have been successfully explored throughout the country. This includes the use of community-based SME contractors to collect waste in traditionally unserviced areas and ‘food for waste’ programmes whereby poor households collect domestic waste weekly in exchange for food parcels. There is significant scope for replication of these models and this will be considered in the revision of the NWMS.

4.5 Waste treatment

4.5.1
The NWMS Action Plan for Waste Treatment and Disposal focused on improvements in the regulation of all waste treatment facilities, including the revision and enforcement of air emissions standards. It sought to establish the status quo of these facilities and what actions should be taken to ensure sufficient waste treatment options for different categories of waste. It also aimed to ensure that treatment procedures comply with environmental, health and safety requirements.
 

4.5.2
A number of interventions have been put into effect to achieve the objectives of the 1999 NWMS. From a regulatory perspective, air emission standards have been reviewed and revised, and enforcement of standards has been significantly improved by DEAT. A review of the classification of hazardous waste is underway and an incineration policy has been drafted and made available for public comment. With regards to the status quo of waste treatment facilities, a great deal of attention has been invested in understanding the status of healthcare risk waste treatment, and demonstration projects in both an urban and rural context have yielded interesting results, which may address the challenges with regard to the effective and safe disposal of healthcare risk waste in poorly resourced environments. While the Department has taken great strides in relation to the priorities and action plans for waste treatment, it will be useful to ensure that all elements of the 1999 NMWS are fully implemented with regard to waste treatment.

4.6 Waste disposal

4.6.1
The challenges with regard to waste disposal are multiple, and underline the need for an updated understanding of the state of waste disposal, the extent of unpermitted landfill sites, the lack of landfill space, and the need to update the classification of hazardous waste. There are various initiatives underway or in place to address these issues. In terms of the need to improve waste information and statistics, the Waste Information System has been designed and implemented although it is currently underutilized. There is a process underway to identify which landfill sites have not been permitted and to prioritise and fast-track their permitting. There is also a review of the classification of hazardous waste, which will culminate in a new classification system to replace DWAF’s minimum requirements for waste categorization (2nd version, 1988).

4.7 Healthcare risk waste management

4.7.1
Healthcare risk waste (HCRW) management cuts across the priority initiatives identified by the NWMS and comprises a third focal area of the 1999 NWMS Implementation Project. The overall objective has been to improve the standard of HCRW management in South Africa, starting with quantification of the HCW stream as well as the available treatment/disposal capacities for the country. Information requirements for the measurement and monitoring of HCW were developed for the Waste Information System. A study has recently been conducted to determine the available treatment and disposal capacity for the country. The Ekurhuleni Metropolitan Municipality has embarked upon a pilot project for improved HCRW management from smaller generators, which are those generators that generate up to 20kg per day of HCRW inclusive of all small health care facilities, health care private practitioners, other specialised institutions such as tattoo artists, traditional healers, mortuaries, and the like. A second pilot was developed for the Zeerust hospital complex as a means to develop a model to enhance HCRW management in a rural setting by developing safe, healthy and environmentally sound yet cost-effective systems for HCRW management. Lastly, draft HCRW management policy and regulations have been developed.

4.8 Key issues arising from the review of the implementation of NWMS 1999

4.8.1
The 1999 NWMS was an ambitious and comprehensive strategy that transformed the approach to waste management in the country, aiming for integrated waste management and implementing the concept of the waste hierarchy. Although the 1999 NWMS has not been implemented in its entirety due to institutional and regulatory constraints, a great deal has been achieved. These achievements are largely in three core areas, namely waste information, waste minimization and recycling, and healthcare risk waste management.
 
4.8.2
There are a number of regulations and guidelines that are in draft form that require finalization and implementation. A number of pilot projects have been designed and implemented as part of the NWMS Implementation Project and the recommendations and lessons from these must be considered for further application. The promulgation of the Waste Act will to a large extent address the stumbling blocks encountered during the implementation of the 1999 NWMS.

5. The Waste Act

5.1
The National Environmental Management: Waste Act of 2008 was promulgated after an extensive consultation process around the Waste Bill. In an important sense, the Waste Act is a direct achievement of the 1999 NWMS, and represents the distillation of important lessons learned in its implementation. More directly, the provisions of the Act are in many respects the result of legislative priorities established by the 1999 NWMS.
 
5.2
Prompted in part by the fragmentation, duplication and lack of co-ordination in waste legislation, the White Paper on Integrated Pollution and Waste Management of 2000 initiated the review of waste legislation that culminated in the publishing of the draft National Environmental Management: Waste Bill on 12 January 2007.
 
5.3
The publishing of the draft Waste Bill marked the start of a 90-day period of public comment on the Waste Bill, to guide its finalisation. During this period, in addition to public meetings in each province, DEAT held workshops with the following stakeholder groupings:

In addition, a two-day conference was convened to involve local government in the finalisation of the Waste Bill. Representatives from over one hundred metropolitan, district and local municipalities participated in deliberations.

5.1 Objects of the Act

5.1.1
The objects of the Act are:

  • To protect health, well-being and the environment by providing reasonable measures for—
    a.) minimising the consumption of natural resources;
    b.) avoiding and minimising the generation of waste;
    c.) reducing, re-using, recycling and recovering waste;
    d.) treating and safely disposing of waste as a last resort;
    e.) preventing pollution and ecological degradation;
    f.) securing ecologically sustainable development while promoting justifiable economic and social development;
    g.) promoting and ensuring the effective delivery of waste services;
    h.) remediating land where contamination presents, or may present, a significant risk of harm to health or the environment; and
    i.) achieving integrated waste management reporting and planning;
  • To ensure that people are aware of the impact of waste on their health, well-being and the environment;
  • Generally, to give effect to section 24 of the Constitution in order to secure an environment that is not harmful to health and well-being.

5.1.2
The Waste Act stipulates that its objects should be read in conjunction with the environmental principles established in NEMA.

5.2 National Waste Management Strategy

5.2.1
Chapter 2 Part 1 of the Waste Act requires a national waste management strategy to be established within two years of the Act coming into effect to achieve the Act’s objectives and give effect to the Republic’s obligations in terms of relevant international agreements.
 
5.2.2
The Waste Act places the NWMS firmly within the context of co-operative governance, providing for the NWMS to identify the responsibilities of the different spheres of government and organs of state in terms of its implementation. Furthermore, state organs are required to align their waste management activities with the national waste management strategy.
 
5.2.3
To provide a suitably differentiated approach to waste management and the provision of waste services, the NWMS may differentiate between classes and categories of waste, and geographical areas. The Waste Act explicitly provides for the inclusion of targets in the NWMS, and a phased approach to its implementation.
 
5.2.4
The Waste Act further stipulates a requirement for a consultation process before the finalisation of the NWMS, similar to the process undertaken for the Act itself.

5.3 Norms and standards

5.3.1
Chapter 2 Part 2 of the Waste Act requires the Minister to establish national norms and standards in relation to waste management. These will be of particular relevance to the NWMS since they will represent minimum standards in relation to the provision of waste management services and the storage, treatment and disposal of waste that the NWMS will need to meet.
 
5.3.2
The Waste Act envisages that norms and standards may be differentiated according to geographical areas and different types of waste. With respect to service delivery, the Act provides for equitable differentiation of services based upon both the type of service, and the type of user.
 
5.3.3
The Act explicitly provides for the development of norms and standards within the context of the waste hierarchy, including the separation of waste at the point of generation, and the setting of standards for extended producer responsibility.

5.4 Institutional arrangements

5.4.1
Chapter 3 of the Waste Act provides for the designation of a national waste management officer within DEAT with responsibility for co-ordinating waste management within government, as well as provincial waste management officers and municipal waste management officers within each municipality authorized to provide waste management services.

5.4.2
The NWMS will need to define the manner in which waste officers fulfil their responsibilities. One such responsibility is likely to be development and implementation of the integrated waste management plans contemplated by this chapter of the Waste Act.

5.5 Provincial and Municipal Waste Management Plans

5.5.1
The Waste Act requires the provinces and municipalities to develop integrated waste management strategies that are co-ordinated and aligned with the relevant integrated development plans and other plans and programmes of provincial and national government, as well as relevant legislation, such as the Municipal Systems Act.

5.5.2
Provincial and municipal waste management plans will play an important role in implementing the NWMS. The plans must include a situational analysis of waste management challenges that takes into account:

  • The population and development profiles of the relevant area to which the plan applies
  • Quantities and types of waste
  • Provision of waste management services, specifically persons not receiving such services.

5.5.3
The Waste Act further stipulates the content of waste management plans:

  • They must provide criteria for identifying the waste management measures that are required or need to be implemented
  • Establish targets for waste management in terms of the hierarchy of waste management measures
  • Include planning for new disposal facilities systems and decommissioning of existing systems if required
  • Include an implementation plan
  • Include an indication of the financial resources required.

5.5.(4)
The Waste Act requires annual reporting on implementation of waste management plans. The prescriptions in terms of the content of provincial and municipal waste management plans include many of the features that will be required in the NWMS, with which these plans must be aligned, but which, in another sense, give effect to the NWMS.

5.6 Waste Management Measures

5.6.1
An important feature of the Waste Act is that it provides specific waste management measures that can be incorporated into the NWMS. These measures grant regulatory powers to the Minister, to be exercised within the context of co-operative government principles established in the Constitution and relevant legislation.

5.6.2
The NWMS will provide the context for the implementation of the waste measures provided in the Waste Act. In addition to regulatory controls, the NWMS needs to encompass both negotiated and voluntary applications of waste management measures.

5.6.3
The Waste Act explicitly provides for the negotiated application of waste management measures in the form of industrial waste management plans. Currently, domestic and commercial recycling takes place almost entirely on a voluntary basis. The success of recycling initiatives in terms of waste minimizations is dependent on public awareness, ease of access to recycling services and facilities, and the presence or absence of incentives.

5.6.1 Waste Measures - Priority wastes

5.6.1.1
Waste that poses a particular threat to human health and the integrity of the environment can be declared a priority waste by the Minister. The 1999 NWMS uses the DWAF second edition classification, and a new edition is in the process of being developed.

5.6.1.2
Declaration of a waste as priority waste indicates that specific waste management measures are required for that waste in terms of reduction, recycling, re-use, and recovery. These measures may include a requirement for companies or persons generating a priority waste to submit an industry waste management plan that must be approved by the Minister.

5.6.1.3
Categorisation of a priority waste restricts economic activities that might generate such a waste, so declaration of priority wastes needs to involve consultation with the Department of Trade and Industry.

5.6.2 Waste Measures - General duty

5.6.2.1
The general duties in respect of waste management that apply by default to all holders of waste reflect the hierarchy of priorities in terms of waste management:

  1. Avoid or reduce waste
  2. Re-use
  3. Recycle
  4. Treat
  5. Dispose Responsibly

5.6.2.2
In general, the provisions of the NWMS should as far as is practical and wherever possible reflect this hierarchy.

5.6.2.3
Specific general duties apply to manufactures and/or retailers of products that may generate hazardous waste in relation to informing the public of the impact on health and the environment.
 

5.6.3 Reduction, re-use, recycling and recovery of waste

5.6.3.1
Reduction, re-use and recycling is only a viable option when it uses less natural resources and is less harmful to the environment than disposal. The Waste Act grants the Minister the power to:

  • require the reduction, re-use, recycling and recovery of particular products; and
  • require products to include a determined percentage of recycled material.

5.6.3.2
Extended Producer Responsibility is explicitly contemplated by the Waste Act as a mechanism for ensuring reduction, re-use, recycling, and recovery and the Minister is granted the powers to determine products to which Extended Producer Responsibility applies, and to specify the Extended Producer Responsibility measure that will apply.

5.6.4 Waste management activities

5.6.4.1
The Waste Act provides for the Minister to publish a list of waste management activities that negatively affect health and/or the environment. Waste disposal techniques such as incineration are an example of this. Listed waste management activities may be entirely prescribed, or may require licensing.

5.6.4.2
Chapter 5 of the Act establishes a detailed regulatory framework for the administration of licensing requirements that will need to be incorporated into the NWMS.

5.6.5 Storage, collection and transportation of waste

5.6.5.1
The Waste Act specifies general principles for the storage and transport of waste to prevent pollution of the environment and harm to health. The measures in this section include specific requirements in relation to waste collection services that need to inform the NWMS:

  • Municipalities should equitably allocate waste collection services
  • An obligation exists on persons receiving waste collection services to pay applicable service charges
  • Municipalities can withhold provision of services where there is failure to comply with reasonable provisions (such as payment), so long as not providing the service will not pose a risk to health or the environment
  • Municipalities can distinguish between different categories of users and geographical areas in terms of the services they provide
  • Municipalities are obligated to provide publically accessible containers and receptacles for the collection of recyclable waste.

5.6.6 Treatment, processing and disposal of waste

5.6.6.1
This section of the Act clearly establishes all disposal of waste as a regulated activity, including littering. It makes owners of private property to which the public has access responsible for providing receptacles for litter, and for disposing of litter in an authorised manner.

5.6.7 Industry waste management plans

5.6.7.1
The Waste Act provides for industry waste management plans at a national level for industries that cross provincial boundaries, as well as at a provincial level for industry specific to a particular province. The Act takes care to prevent unnecessary duplication by specifying that any requirement for a national plan supersedes and replaces provincial requirements.

5.6.8 Contaminated lands

5.6.8.1
This measure gives effect to the “polluter pays” principle. The Minister is required to identify and investigate land that is suspected of contamination. Once an investigation area has been declared the Minister may initiate a site assessment and direct the owner of the land, or the person responsible for the suspected contamination to conduct a site assessment to determine past, current, or future impact on the environment and health.

5.6.8.2
If a site assessment confirms land as contaminated, the Act grants the Minister the power to order remediation of the land, specify the time frame over which remediation must take place, identify who will be responsible for the remediation, and what measures must be taken. The Act obligates the Minister to maintain a contaminated land registry that includes investigation areas.

5.6.8.3
This registry of contaminated lands forms part of the Waste Information Management System described in Chapter 6 of the Act.

5.6.9 Other measures

5.6.9.1
Waste management officers are given authority to establish programmes for public recognition of achievements in relation to waste management, including programmes that include a public awareness component.

5.6.9.2
For the NWMS to be effective, it needs to take root at a local level. Community-based organisations, consumer organisations, civic organisations, and non-governmental organisations have an important role to play in the local implementation of the NWMS.

6. Framework for NWMS

6.1
The Waste Act establishes the NWMS as a statutory mechanism, which binds all organs of state in all spheres of government. An organ of state is obliged to give effect to the national strategy when exercising a power or performing a duty in terms of the Act or any other legislation regulating waste management. This clearly distinguishes the strategy from the 1999 NWMS, and the subsequent White Paper on Integrated Pollution and Waste Management, 2000. While these were solid policy documents, which spearheaded the new approach to integrated waste management, they lacked the regulatory “teeth” that will be invested in this new strategy.

6.2
The Waste Act obliges the Minister to publish the strategy within two years of coming into effect of the Act, and it specifies the contents of the strategy, which must include:

6.3
The Minister may prescribe additional items to be included in the strategy that are considered necessary for achieving the objects of the Act.

6.4
The Act indicates that the strategy must be reviewed by the Minister at intervals of not more than five years. While the time period to be covered by the strategy is not specified, it is assumed that the bulk of the provisions of the strategy should relate to the five year period prior to the next review of the strategy.

6.5
Before publishing the national strategy, or any amendment to the strategy, the Minister is obliged to follow a consultative process, which provides for public participation, as well as consultation with relevant national Ministers and provinces. This will inform the consultative approach to be adopted in developing the strategy.

6.6
The revised NWMS will be focused on measures to avoid or minimise the generation of waste, and where waste cannot be avoided or reduced, measures to ensure that it is re-used, recycled or recovered, and only treated and safely disposed of as a last resort. The strategy will deal with general, commercial and industrial waste streams, including hazardous waste, healthcare risk waste and waste streams from agriculture (including pesticides), mining and power generation.

6.7
The strategy explicitly excludes consideration of nuclear waste, which is the subject of a separate policy exercise under DME. While pollution by waste products clearly is an important issue, the strategy does not deal with pollution per se, and therefore only deals with the related fields of environmental impact management and remediation where these relate to waste products. The strategy also excludes consideration of air quality management and waste water and industrial effluent management, which are the subjects of detailed policy and regulatory processes in their own right. The strategy does deal with water quality issues, but only to the extent that they are relevant to the location and management of waste disposal and landfill sites.

6.8
The strategy covers the five period from 2009/10 to 2014/15, but it may present a longer term vision and targets to be achieved beyond this period. The strategy provides the framework within which more detailed plans will be drawn up by national departments, provinces and municipalities. The strategy will therefore provide sufficient guidance without being prescriptive as to the content of these more detailed action plans.

6.9
The development of the NWMS is a dynamic process that will be regularly reviewed (e.g. every 5 years) to take account of progress made, changing needs and priorities, as well as the realities of practical implementation.
A provisional Chapter outline for the NWMS has been included at the end of this document as a basis for discussion on how best to structure the revised NWMS.

7. Approach to development of NWMS

7.1
The development of the NWMS will be structured around four phases and prepared in a consultative manner as envisaged in the Waste Act, Part 1 Section 6(6), whereby the Minister is obliged to follow a consultative process, which provides for public participation, as well as consultation with relevant national Ministers and provinces.

7.2
The following diagram presents the approach to the development of the NWMS in terms of the timeframes, key activities and milestones for each of the four phases:

NWMS Phases

7.3
The NWMS will depend for its effectiveness on the support and buy-in from a wide range of stakeholders, and the process of drafting the strategy needs to be based as far as possible on a consensual approach. At the same time, the Department recognises that stakeholders may become fatigued as a result of the past and planned multiple consultation exercises in relation to different aspects of waste policy and legislation.

7.4
The Department has thus sought to streamline stakeholder involvement and a consultation plan has been approved by the Department, the main features of which are:

8. Conclusion

8.1
The promulgation of the Waste Act is a milestone in the evolution of environmental policy and legislation and gives effect to the principles of the Constitution, NEMA and the White Paper on Integrated Pollution and Waste Management. Apart from providing a coherent regulatory framework for sound waste management practices, it presents a great opportunity to ensure that the country’s approach to waste management contributes to environmental wellness as well as support the country’s economic and social priorities. Waste management has an important role to play in mitigating climate change or “bending the curve” and the successful implementation of the waste minimisation hierarchy would be a part of a range of responses aimed at reducing the country’s greenhouse gas emissions. A transition to a low carbon “green” economy as anticipated in a coherent national response to climate change would see a proliferation of green jobs in the waste sector ranging from life-cycle engineering to informal waste recovery.

8.2
The 1999 NWMS has laid the foundations for a coherent waste management regime with the development of a comprehensive Waste Information System, an integrated waste management planning system with the development of draft regulations and guidelines, significant advances in approaches to waste minimisation and recycling, innovations in the sphere of waste collection, and improvements in the way in which different forms of waste are disposed of and the regulation thereof.

8.3
The greatest challenge to its successful implementation was the absence of a coherent regulatory framework, a factor that has now been addressed through the promulgation of the Act. The revision of the NWMS is needed to align it with the provisions of the Act as well as reflect changing needs and emerging priorities such as the process of greening the economy. This document has set the context and imperatives for that revision and represents the framework for guiding the development of the NWMS in an engaging and consultative manner.

9. References

All of the documents and legislation referenced here can be linked to or downloaded from the Library page.

9.1
Constitution of the Republic of South Africa, 1996, Chapter 2: Bill of Rights and Chapter 3: Co-operative Government.

9.2
Department of Environmental Affairs and Tourism, 2000. White Paper on Integrated Pollution and Waste Management for South Africa. A Policy on Pollution Prevention, Waste Minimisation, Impact Management and Remediation. Government Gazette Vol.417, No.20978, 17 March 2000. General Notice 227 of 2000.

9.3
Department of Environmental Affairs and Tourism, 2005. National Waste Management Strategy Implementation South Africa: Draft report on survey conducted in the Ekurhuleni Metropolitan Municipality (Northern Region) for the Minor Healthcare Risk Waste Generators Pilot Project, 30th June 2005.

9.4
Department of Environmental Affairs and Tourism, 2005. National Waste Management Strategy Implementation South Africa: Recycling Extended Producer Responsibility, Report number 12/9/6 Annexure F, 3 May 2005.

9.5
Department of Environmental Affairs and Tourism, 2005. National Waste Management Strategy Implementation South Africa: Review of Industrial Waste Exchange, Report number 12/9/6 Annexure G, 4 April 2005.

9.6
Department of Environmental Affairs and Tourism, 2006. National Waste Management Strategy Implementation South Africa: Zeerust (Ramotshere Moiloa) subdistrict status quo report, Lehurutshe/Zeerust hospital complex, 20th June 2005.

9.7
Department of Environmental Affairs and Tourism, 2006. National Waste Management Strategy Implementation South Africa: Economic instruments for recycling of waste in the Mbombela Pilot Project, 13 June 2006, DEAT report number 12/9/6.

9.8
Department of Environmental Affairs and Tourism, 2008. Strategic Plan for the Environmental Sector 2008-2013: Department of Environmental Affairs and Tourism.

9.9
Intergovernmental Relations Framework Act, 2005: Passed by parliament on 15 August 2005.

9.10
National Environmental Management Act 107 of 1998, Chapter 1:National Environmental Management Principles, Revised.

9.11
National Environment Management: Air Quality Act 39 of 2004: Passed by parliament on 19 February 2005.

9.12
National Environmental Management: Protected Areas Act, 2003: Passed by parliament on 18 February 2004.

9.13
A National Industrial Policy Framework: Department of Trade and Industry 03-August-2007.

9.14
National Waste Management Strategy, Version D, 15 October 1999: Department of Environmental Affairs and Tourism and Department of Water Affairs and Forestry.