Select Committee on Environment, Food and Rural Affairs Written Evidence


Memorandum submitted by SITA UK (X19)

SUMMARY

  While the UK Government can point to initiatives such as the Household Waste Recycling Act and the Landfill Allowance Trading Scheme as significant achievements, it has nevertheless failed to address the more practical bottlenecks that prevent the waste industry from investing in much needed treatment facilities. Poor delivery of regulations, guidance and processing of PPC applications by the Environment Agency, coupled with the complexities of our planning system and the perception of slack enforcement, continue to undermine investor confidence.

  The year to July 2005 to some extent represents business as usual, with concessions made to producers of fragmentiser waste and the partial application of the waste acceptance criteria to landfilled waste. The full force of the waste acceptance criteria will only apply after July 2005. It is by no means certain that the UK will have sufficient treatment capacity post-July 2005 to handle the diverted hazardous or municipal wastes. Even with the appropriate policies in place and with the industry prepared to invest, the UK's complex and elongated planning delivery system will prevent Government from providing the large numbers of treatment facilities in time for the UK to meet its targets.

  In order to move its domestic agenda forwards, we recommend that Government take the following actions:

    (a)  Prioritise Biodegradable Municipal Waste (BMW). Government should develop a sub-strategy specifically addressing the BMW component of municipal waste. The UK faces far more serious consequences if it fails to meet its BMW landfill diversion targets, than if Local Authorities fail to achieve their broader recycling targets.

    (b)  Prepare a cohesive national strategy for municipal and industrial/commercial waste. As the UK moves to a resource-based waste management system, the distinction between various sources of resource arisings will cease to have relevance in policy and planning terms. A key component of an integrated national strategy will be to develop a plan to reverse waste growth.

    (c)  Streamline the waste planning and permitting regimes. We recommend that Government develop systems and procedures that conflate the planning and permitting process into a shorter timeframe, while retaining the checks and balances required to ensure appropriate scrutiny of the applications and protection of the environment.

    (d)  Apply Producer Responsibility to householders. SITA has advocated direct charging as the most effective means of providing "up-front" financing of new collection and treatment facilities.

  In concert, the UK should anticipate legislative trends in the EU. The direction in which recent EU initiatives on waste and resource management have moved is clear, and there is no reason why informed and farsighted policymakers cannot foresee their impact on the UK.

1.  INTRODUCTION

1.1  Background to SITA

  1.  SITA is Europe's leading waste service operator and the third largest in the world. The Group's activities span the whole range of waste management, including collection, sorting, recovery and treatment and ultimate disposal of hazardous, domestic, commercial and industrial wastes.

  2.  SITA has provided waste management services in the UK since 1989. The Company has grown to become the country's largest service provider, operating more than 100 municipal service contracts, 103 landfill sites, several recycling and recovery facilities along with energy from waste facilities at Edmonton in North London, Cleveland on Teesside, Kirklees, and on the Isle of Man.

  3.  Landfilling within the context of the Government's waste management strategy and the Landfill Directive (LFD) has been a significant and critical component of SITA's portfolio of waste management services in the UK. SITA landfills approximately 6.5 million tonnes of waste per year in the UK in 40 operational landfill sites. Prior to 16 July 2002 SITA landfilled approximately 300,000 tonnes of special waste. A large proportion of this waste continued to be landfilled in our interim hazardous sites till 16 July 2004. Since this date landfilling of hazardous waste by SITA has virtually ceased—the company has not applied for hazardous status, and only one of the several PPC applications for stable non-reactive cells within SITA's non-hazardous landfills has been determined to date (for receipt of bonded asbestos).

  4.  SITA recycles 15% of the waste it handles, roughly in line with the national average recycling rate. The company is actively rolling out a business strategy designed to raise this rate in line with recycling and landfill diversion targets imposed on Local Authorities.

2.  LOOKING BACK—HAS GOVERNMENT DELIVERED?

  5.  In the UK the provision of waste management services relies on the laws of supply and demand to allow the industry to find its equilibrium in terms of the types, numbers and locations of appropriate facilities. In this free market system it is the responsibility of Government to create an environment in which the private sector and its funders are prepared to invest the considerable sums necessary to move UK waste management away from its reliance on landfilling.

  6.  Has the UK Government delivered this degree of certainty ? The industry view that it has not, is borne out by the fact that most of the major sector players have not opted for hazardous landfill status, while planning applications for alternative hazardous and municipal waste treatment facilities are well down on the numbers required to keep pace with national targets. Industry concerns have been repeatedly aired in fora such as the Hazardous Waste Forum, and the main issues will only be summarised here.

2.1  HAZARDOUS WASTE

  7.  The adequacy and effectiveness of preparations made for the management of hazardous waste (and landfill more generally) has been poor. Not wishing to weaken its negotiating position vis-a"-vis co-disposal, the UK elected to mount a rearguard action in Europe to preserve the status quo—a battle it unsurprisingly lost—rather than spend the years from 1999 to July 2002 preparing the country for a LFD-compliant future. In the event, the two years from July 2002 to July 2004 offered the UK only a temporary respite, and insufficient time to effect orderly change.

  8.  Government should not take the absence of an overt "crisis" as the UK passed 16 July 2004 as reason for self-congratulation. The waste industry has expressed serious concerns over the inability of the Environment Agency to track the fate of liquid waste streams since the landfill ban was enacted in July 2002. Concern has also been expressed over the non-arrival of previously codisposed hazardous waste at either waste treatment facilities or at hazardous landfills, post-July 2004. The lack of effective regulation and accountability erodes business confidence among legitimate waste operators and further delays investment in new treatment facilities.

  9.  In evidence to the EFRA Committee's Inquiry into hazardous waste (2001-02) the waste industry emphasised the need for certainty with respect to issues such as the Waste Acceptance Criteria and other forms of guidance required to interpret the relevant Regulations. As of October 2004 the industry still lacks key pieces of guidance, again impacting on investor confidence. Draft Waste Acceptance Criteria for monolithic waste forms were issued for consultation in May 2004, and are unlikely to be finalised before spring 2005. Consultation on the Hazardous Waste Regulations commenced in July 2004 while Defra's interpretation of the Landfill (England and Wales) Regulations was published in September 2004. Both are two years behind schedule.

2.2  Municipal and Other Waste

  10.  Government has launched some welcome initiatives addressing municipal waste notably the Household Waste Recycling Act, the Waste and Emissions Trading Bill, and the Landfill Allowance Trading Scheme. However, Government has failed to address many inherent weaknesses:

    (a)  The funding gap facing local authorities discharging their duties in a changing regulatory environment. Although expenditure on recycling services has increased year on year, it is still well short of the amounts required to bridge the gap between the present household waste recycling rate (15%) and the next target of 25% by 2005-06. Defra's highly dubious claim that the UK is "on course" to meet the latter target may in fact prevent the adoption of appropriate policy and fiscal measures in the coming year, owing to a misplaced desire to demonstrate political steadfastness.

    (b)  Key elements of Government guidance are awaited, for example on the testing of biodegradability, central to the operation of the Landfill Allowance Trading Scheme. Guidance on waste pre-treatment (consultation draft issued 2001) is still outstanding. Guidance from the Environment Agency on certain aspects of landfill operation under the PPC regime are also still in draft.

    (c)  Government policy continues to be piecemeal. The present policies perpetuate the notion that resources, raw materials, products and waste are somehow separate entities and should be regulated separately. Waste can arise at any point along the value chain leading into product manufacture, and from there to product use and discard. The term "sustainable waste management" has little meaning, except from a narrow operational standpoint.

    (d)  The UK strategic planning system is complex and a serious impediment to the timely provision of waste treatment facilities. The strategic framework for waste planning in the UK is caught in a web of waste local plans, municipal waste plans, regional plans, sub-regional plans, RTAB deliberations, etc, not helped by the fact that responsibility for collection and for disposal rests with different Authorities. The result is a log jam that has paralysed waste planning at all levels. There is also a disjoint in applying the concepts of the waste hierarchy and the Best Practicable Environmental Option (BPEO), which under some local circumstances can run counter to each other. Inappropriate and dogmatic insistence on the waste hierarchy has damaged the development of sensible and cost-effective solutions in some areas of the UK, even though a BPEO analysis has manifestly pointed to a different solution as being environmentally preferable (for example, incineration with energy recovery).

    (e)  Urgent action is also required on reform of the interminable process for gaining planning permissions and operating permits for waste management facilities of all descriptions. Presently, the planning and permitting processes in the UK are separate, unlike some systems in continental Europe. Thus, the developer has to prepare two sets of submissions and two sets of environmental and technology appraisals, respond to two sets of consultation processes, and thereafter potentially endure two sets of inquiries—a planning inquiry and a judicial review. Determination times currently can run to two to five years depending on the type of facility. This destroys any certainty in developing a robust business case, and has proved to be a serious hindrance to timely investment in the UK.

3.  LOOKING FORWARD—WHAT GOVERNMENT NEEDS TO DO

  11.  SITA recommends that the UK Government sets its priorities along two strands: addressing the domestic agenda, and preparing for (and influencing) likely forthcoming EU legislation.

3.1  The Domestic Agenda

  12.  Specific recommendations are as follows:

    (a)  Prioritise Biodegradable Municipal Waste (BMW). The UK faces far more serious consequences if it fails to meet its BMW landfill diversion targets, than if Local Authorities fail to achieve their broader recycling targets.

    We recommend that government develop a sub-strategy specifically addressing the BMW component of municipal waste, how the targets will be met, how many facilities (of what type) will be required, the funding requirements, and how the Local Authority recycling targets tie in with the BMW diversion targets. The reliance on the Landfill Allowance Trading Scheme as a market mechanism to achieve compliance is not sufficient—of particular note is the potential for industrial and commercial waste "similar" to household waste to be included within the definition of municipal waste.

    (b)  Prepare a cohesive national strategy for municipal and industrial/commercial waste. As the UK moves to a resource-based waste management system, the distinction between various sources of resource arisings will cease to have relevance in policy and planning terms. Separate legislative paths are presently followed—for example, the packaging waste regulations applying to paper and glass in the commercial sector, while the Best Value recycling targets apply to paper and glass in the domestic sector. Each waste stream is typically treated in separate facilities.

    A key component of an integrated national strategy will be to develop a plan to reverse waste growth (see paragraph 14(c) below).

    (c)  Streamline the waste planning and permitting regimes. The ultimate challenge facing government is to convert strategies and plans into operating facilities. As discussed above, the waste management industry has for many years faced inordinate delays in achieving planning and permitting for its facilities, be they incinerators or "greener" alternatives such as recycling and compost plants.

    We recommend that government develop systems and procedures that conflate the planning and permitting process into a shorter timeframe, while retaining the checks and balances required to ensure appropriate scrutiny of the applications and protection of the environment.

    SITA awaits the publication of the draft PPS10, which we hope will address the structural weaknesses inherent in the present system.

    (d)  Apply Producer Responsibility to householders. SITA has advocated direct charging as the most effective means of providing "up-front" financing of new collection and treatment facilities. In previous evidence to this Committee, we have recommended commencing immediately with full cost recovery through the existing Council tax system by raising the waste management element of the charge by £1 per household per week. We then recommended designing a reward based variable rate system introduced in step with the technological, operational and administrative support structures and after public outreach programmes have laid the necessary foundations.

3.2  Preparing for Likely EU Legislation

  13.  It is apparent from observing the waste management scene in Brussels that environmental legislation is driven by those Member States with the most stringent and/or farsighted controls and policy initiatives. Environmental legislation from the European Commission tends to level upwards, while domestic UK legislation tends to gravitate towards the lowest common (cost) dominator (hence our overwhelming dependence on landfilling over the past four decades). Hence in areas where typically the Northern European Member States have taken the policy lead, the UK has had to play catch-up. Waste management in general, and the Landfill Directive in particular, is a case in point. Germany, the Netherlands and Austria are already compliant with their 2016 BMW diversion targets.

  14.  With this in mind, we speculate on some the likely future issues that face the UK in the medium term, and for which we need to be prepared:

    (a)  A requirement to stabilise biowaste prior to landfilling. This requirement currently applies in Austria and Germany as a waste acceptance criterion for MBT-treated biodegradable waste destined for landfill. Its incorporation into the proposed Biowaste Directive was contemplated before the latter was removed from the Commission's legislative agenda. However, it is widely believed to represent a logical progression to the present BMW diversion requirement contained in the Landfill Directive, when the latter is reviewed. Its impact on the UK waste management scene will be of seismic proportions, since biodegradable waste will need to be pre-treated almost to compost quality in order to remove biological activity.

    (b)  Integrated Product Policy (IPP) and Producer Responsibility. Household hazardous waste is presently exempt from the Landfill Directive, but will eventually be addressed at EU level. The IPP initiative has stalled in the European Commission, but there is little doubt that the principle of Producer Responsibility will be extended beyond end of life vehicles and electronic goods, to other consumer items. The UK is ill-equipped to meet this challenge. Government should engage with trade associations and prepare the ground for such schemes, giving industry ample warning.

    (c)  Anticipating the EU's thematic strategies. The thematic strategies on resource conservation, waste prevention and recycling will require a different response from Member States than the present highly compartmentised single-issue strategies can deliver. The UK should be planning for "sustainable resource management", integrating within a single policy framework the management of materials and energy across the entire value chain and across all economic sectors. Waste should be embedded within an overall strategy for cradle to grave resource and energy management. Coherent policies and economic instruments can then be designed along this value chain, so as to deliver results at that or any other point. For example, an environmental tax on raw materials could be designed so as to have the effect of reducing resource consumption and hence reducing waste production.

    In formulating integrated policies, consideration should also be given to the rationalisation of the definitions of "waste", "product", "recovery" and "disposal" so that "waste" processes are not disadvantaged if they produce products of equal quality. The place of and shape of landfilling within a sustainable resource management agenda needs to be clarified.

4.  CONCLUSIONS

  15.  The UK Government's performance in implementing the Landfill Directive has been patchy at best. While Government can rightly point to innovations such as the Landfill Allowance Trading Scheme as examples of its commitment to progress in moving waste management forwards, it has failed to address the more practical bottlenecks that prevent the waste industry from investing in much needed treatment facilities. Poor delivery of regulations, guidance and processing of PPC applications by the Environment Agency, coupled with the complexities of our planning system and the perception of slack enforcement, continue to undermine investor confidence.

  16.  The year to July 2005 to some extent represents business as usual, with concessions made to producers of fragmentiser waste and the partial application of the waste acceptance criteria to landfilled waste. The full force of the waste acceptance criteria will only apply after July 2005. It is by no means certain that the UK will have sufficient treatment capacity post-July 2005 to handle the diverted hazardous or municipal wastes. Even with the appropriate policies in place and investors toeing the start line, the policy muddle between BPEO, proximity and the waste hierarchy, and the planning system will prevent government from delivering facilities in time for the UK to meet its targets.

  17.  The true test of the Government's success in meeting its waste management obligations has yet to come.

7 October 2004





 
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