Select Committee on Environmental Audit Minutes of Evidence


Supplementary memorandum submitted by the Environmental Industries Commission

  1.   [Q27]  To what extent has the UK Government specifically sought to weaken EU regulations or directives? What specific examples would EIC cite? (Please provide details in each case of the manner in which regulations were weakened.)

  The conclusions of Regulatory Impact Assessments on the net benefit of proposed new EU legislation play an increasingly important part in Ministers' decision making on the UK position in negotiations.

  We consider, therefore, that an RIA which overestimates costs, or underplays benefits will have an effect on UK negotiating in the EU.

  It is difficult, however, to relate the conclusions of a UK RIA to specific clauses of EU legislation which are agreed following negotiations between all Members States, the Commission and MEPs.

  One example where the UK negotiating position was to weaken requirements was the WEEE Directive. The RIA published by the DTI in March 2003 estimates the costs to be in the region of 100 times the benefits. This would clearly have had an influence on Ministerial decision making on the UK negotiating position.

  The current initial RIA of the proposed new EU emission standards for light duty vehicles (see attached EIC response to the RIA, annex 1) provides an example of where, if the RIA is not improved, Ministers will be presented with overestimates of the cost figures and underestimations of the benefits.

  2.   [Q63-64]  Please provide written comments on the issue of gold plating.

    EIC believes the UK should look much more closely at the most economically advantageous way of implementing EU environmental policy measures. At present the view is simply that it must not be "gold-plated". This tends to mean we do the least possible thing at the last possible minute, with key detailed guidance coming out, at best, close to the wire.

  By taking a more proactive approach to implementation Government can enhance competitiveness in three ways:

      (a)  Innovation: it is widely accepted the earlier it is clear to business exactly what it has to achieve (in terms of environmental outcome), the more a regulation will encourage innovation.

      (b)  Environmental Technologies: early implementation of new environmental policies can give a first mover advantage in developing solutions to UK environmental technology and services providers.

  An example where the UK has looked for first mover advantage is in Emissions Trading by setting up a UK scheme first. This approach was endorsed by a National Audit Office report.

  An example of a major Directive currently being implemented is the Water Framework Directive. This will create demand for, inter alia: diffuse monitoring technologies; membranes to remove organics and nutrients from sewage; and technologies to deal with VOCs and PCBs. Those countries who start implementing the "programme of measures" required under the Directive earliest will get first mover advantage in these areas.

  However the recent Periodic Review of water prices explicitly ruled out investments which are specifically towards meeting the requirements of the Water Framework Directive.

      (c)  Implementation of Further Measures: there will be cases were a proper cost-benefit analysis will show that setting higher environmental standards than the minimum in an EU Directive will be economically beneficial. Currently it is assumed anything more than the minimum would be negative for the economy.

  The consultations on implementing the Water Framework Directive, for example, simply stated that the additional measures listed in the Directive were gold-plating, rather than analysing their cost benefit.

  3.   [Q69ff]  On resource productivity, does the EIC have a view on whether meaningful resource productivity targets could be set at a national level or for particular industry sectors, and whether this would be beneficial in terms of stimulating the market for environmental technologies?

  Please see attached EIC paper on Resource Efficiency (annex 2).

  4.   [Q25]  Please provide further written information on the deficiencies in the Euro 5 Standards for Passenger Cars RIA.

    Please see attached EIC response to the initial RIA of proposed new Euro standards for light duty vehicles

  5.   [Q35]  Please provide some more details on the Air Quality Assessment and the original forecasts of compliance costs.

  The Defra report "An Evaluation of the Air Quality Strategy" published in December 2004 provides extensive details. It concludes:

    "It has often been suggested that in `ex ante' studies, costs are systematically overestimated and the benefits underestimated. The analysis here, summarised in the table above, provides evidence to back this up for the two sectors considered [electricity and transport]. The analysis of individual ex ante and ex post costs has shown that in most cases, ex ante costs were over-estimates. In many cases, these over-estimates were very significant. Note this also leads us to the conclusion that legislation itself acts as a spur to research and innovation."

    For more detail see www.defra.gov.uk/environment/airquality/strategy/evaluation/pdf/exec-summary.pdf

  6.   [Q43]  EIC agreed to let the Committee know of any academic experts it was aware of in relation to RIAs and the evaluation of environmental impacts.

  RIA itself is too applied for most academics. However there are many academics looking at whether and to what extent environmental effects can be monetised.

    High profile and well respected ones include David Pearce (UCL); Nick Hanley (Stirling); Kerry Turner (UEA); Ken Willis (University of Newcastle); Anil Markandya (World Bank / Bath University).

  7.   [Q61]  Please provide more details of the DTI report alluded to [and any other relevant reports] in relation to the UK share of the world market for environmental technologies.

  The two key reports are "Global Environmental Markets and the UK Environmental Industry: Opportunities to 2010" published by the DTI/Defra Joint Environmental Markets Unit in 2002 and "Mapping The UK Environmental Goods and Services Sector: The Environmental Industry Unit's Analysis of the Sector in 2004 in conjunction with the English RDAs and Devolved Administrations".

  Both of these can be obtained from the DTI/Defra Environmental Industries Unit.

  8.   [Q67]  Could the EIC could confirm whether or not Johnson Matthey is also a member of the CBI?

    Johnson Matthey is not a member of the CBI.

Annex 1

Chris Parkin

Cleaner Fuels and Vehicles Division

Department for Transport

Dear Chris,

Re: Initial Regulatory Impact Assessment Issue 1a-29/10/04 on Emissions Standards for New Light Duty "Vehicles"

  Thank you for the opportunity to comment on the initial Regulatory Impact Assessment (RIA) concerning the forthcoming proposal for a European Directive concerning emissions standards for new light duty vehicles (Euro 5).

  The Transport Working Group of the Environmental Industries Commission (EIC) contains a number of companies actively involved in developing emissions control solutions for light and heavy duty vehicles, both for retrofitting to current in-service vehicles and for use on new vehicles to help meet emissions legislation.

  The TransportEnergy Programmes administered by the Energy Savings Trust have, for the last several years, been an important tool in the effort to achieve air quality targets under the EU First Air Quality Daughter Directive. The funding for these programmes has recently been cut. Given that the rationale for this decision lay, in part, in the Department's commitment to the use of emissions standards for new vehicles to help meet air quality objectives, EIC Members are particularly keen to see that the Department supports demanding emission standards. We believe that a rigorous cost benefit analysis will show the net benefit of high standards.

  The initial RIA is very detailed and thorough document and in many respects it represents a good example of current practice in the implementation of RIAs across Government Departments. However, EIC Members are concerned that the conclusions and future action presented are conservative, do not fully represent the severity of the environmental problems identified in the report and believe that the RIA would benefit greatly from additional analysis in line with the recommendations in EIC's recent "Position Paper on Regulatory Impact Assessments".

  Our recommendations and rationale follow, whilst additional feedback on detailed aspects of the report are also included for your information.

Yours sincerely,

Robert Evans, Chair

EIC Transport Pollution Control Working Group


RECOMMENDATION 1: A COMPLETE RIA SHOULD TAKE INTO ACCOUNT THE BENEFITS TO THE UK'S ENVIRONMENTAL TECHNOLOGY INDUSTRY OF ENVIRONMENTAL PROTECTION MEASURES.

  The RIA notes that "medium size businesses are likely to supply the technology to deliver the emissions control necessary and a proposal could therefore be a positive advantage for these bodies." However, it does not quantify these benefits, or offset them against the costs it reports for the UK motor industry.

  In recent testimony to the House of Commons Environment Audit Committee, Treasury officials accompanying the Economic Secretary to the Treasury clarified that RIAs must look at the "net impact over the entire economy", and that diversions from one industry sector to another that is less polluting or has greater export potential should be regarded as positive.

RECOMMENDATION 2: A COMPLETE RIA SHOULD TAKE FULL ACCOUNT OF THE ECONOMIC BENEFITS OF HIGH ENVIRONMENTAL STANDARDS TO THE UK'S HEALTH SERVICES THROUGH REDUCED HEALTH COSTS AND TO THE HEALTH OF THE WORKFORCE.

  The RIA focuses on particulate matter (PM) and oxides of nitrogen (NOx) as the two pollutants forecast not to meet UK air quality targets. It includes a quantification of health costs but has some specific exclusions that currently detract from the RIA. These exclusions include:

    —  Chronic mortality health effects from PM10 on children2

    —  Chronic morbidity health effects from PM102

    —  Morbidity and mortality health effects from chronic (long-term) exposure to ozone2

    It is also disappointing that the cost values for NOx do NOT include ozone formation and effects and it is not clear as to how many of the health costs of ozone and NO2 have been modelled.

  Transboundary effects are also excluded for the RIA. This represents another notable omission. Exposure of the population to NOx, PM and ozone pollution is a continuing source of concern for environmental and health reasons. The UK is not the only country in the European Union (EU) where the EU's binding targets for these pollutants will be exceeded.

  There is also concern about the rising levels of tropospheric backgrouind ozone. The importance of this is that there will be a time in the mid-term future when the background level by itself will exceed levels currently considered to be health thresholds. The principal driver for this will be NOx emissions and early action on the major sources, including vehicles will be the most cost effective response.

  Road transport is the main or a major contributor to the totals of these pollutants, within which the light-duty vehicles sector (cars and vans) is a major contributor. Consequently, the benefits of tougher regulations will be seen both in improvements in local and national (via transboundary) pollution levels.

  Recent trends in the vehicle parc include a more rapid than expected growth in light duty diesel and in the heavy passenger car, particularly Sports Utility Vehicles (SUVs). These tend to exacerbate the problems with PM and, especially NOx.

Further work on health costs needs to be undertaken in further iterations of this RIA.

  It should be noted that whilst the environmental modelling used in the report is credible, it is based on a number of assumptions and historic data that are no longer correct and which have a significant effect on the severity of the predicted outcome and, therefore, measures required to combat the effects. Specifically, it uses out-of-date forecasts for diesel penetration. This is critical because the population of diesels in the fleet is growing rapidly with high rates of diesel penetration at Euro III and IV. This is particularly critical given that diesels are currently much higher polluters (for PM and NOx) than petrol equivalents. To underestimate diesel penetration is to underestimate the health costs from PM, NO2 and ozone.

RECOMMENDATION 3: A COMPLETE RIA MUST TAKE INTO ACCOUNT THE ECONOMIC BENEFITS OF HIGH ENVIRONMENTAL STANDARDS TO THIRD PARTY INDUSTRIES SUCH AS TOURISM, AGRICULTURE, AND FORESTRY.The NOx modelling assumptions do not take into account values for the effect of ozone formation, or non-ozone effects on the ecosystem.

  Key exclusions include the effects of pollutant on:

    —  3ecosystems (acidification, eutrophication, etc)4

    —  3cultural or historic buildings4

    —  3change in visibility (visual range)4

    —  3effects of ozone on materials, particularly rubber4 5

    —  3non-ozone effects on agriculture4

RECOMMENDATION 4: A COMPLETE RIA NEEDS TO MAKE CLEAR THAT INNOVATION CAN HAVE A SUBSTANTIAL DOWNWARD IMPACT ON COSTS OF MEETING HIGH ENVIRONMENTAL STANDARDS.

  The scenarios modelled all assume costs are zero or higher. EIC believes that maintaining NOx limits for petrol cars at the current 80 mg/km would in fact result in negative costs, recognising the motor and emissions management industries' continual drive for resource productivity and innovation, directed both at performance improvement and cost reduction.

  Many motor manufacturers were able to move directly from Euro II to Euro IV for petrol cars, clearly illustrating the cost effectiveness of Euro IV compared with Euro III, as early as 2000. It is inconceivable that the cost of Euro IV technology will not be driven down further over the next decade, just as it is inconceivable not to seek lower emissions from such a large segment of the vehicle fleet between 2000 and 2015.

  The RIA notes (page 21) that "the potential for tightening the diesel NOx limit to levels as envisaged in Scenarios C (ie 50% to 125 mg/km) may be feasible by 2010 and one manufacturer maintains that it is; other manufacturers, however, question this." EIC members join the manufacturer in believing that 50% reduction in NOx emissions from diesel passenger cars is feasible and believe this kind of target is required to drive innovation.

  Developments in cleaner diesels will occur to some extent due to competitive forces and the wish by some companies to pursue the sale of diesel engines into the US market where emission regulations for diesels are already much more severe than those proposed for the future in Europe. However, in order to encourage development and to ensure European industry continues to be competitive in the global diesel engine market, clear requirements need to be set for low diesel NOx emissions in Europe.

  EIC believes the report is generally too pessimistic as to the capability of future NOx control technologies and uses current cost estimates. For all previous European emission legislation the predicted costs have always been too high and the technology capability has always performed better than expected.

CONCLUSIONS

EIC believes the RIA is very conservative and doesn't fully address the challenge of improving air quality such that everyone in the UK can breathe healthy air.

  The RIA concludes (page 11) that the reductions in pollutant emissions "would not be fully realised until some time after the new standards are introduced and would not help attainment of air quality objectives in 2010. This is because only new vehicles will be required to meet the tighter standards and it will therefore take some years for these vehicles to permeate the fleet." The RIA continues by noting that the scenarios modelled are insufficient to ensure air quality targets will be met by 2020.

  There is already a significant "latent" problem for the UK in not achieving national and EU 2005 and 2010 air quality targets, not helped by the Department for Transport's decision to cut grant funding support for TransportEnergy programmes. To set out to fail to achieve air quality targets out as far as 2020 shows a lamentable lack of ambition.

  The EIC believes that more aggressive scenarios should be modelled, especially for ultra low petrol NOx emissions, in order to try to reach air quality targets.

EIC believes the RIA underplays the economic benefits of emissions standards for the environmental industries sector.

  There are a number of UK-based companies with world-leading expertise in low emission vehicle technology, both within the environmental industries sector and additionally with the motor industry. The RIA doesn't quantify the economic benefits to these industry sectors.

EIC believes the RIA underplays the cost to the environment and health associated with not meeting tougher emissions standards.

  For diesel cars the RIA modelling is based on out of date figures for diesel penetration and does not fully quantify a number of environmental consequences associated with NOx and PM emissions and additionally excludes other harmful pollutant emissions (carbon monoxide and hydrocarbons) from the cost-benefit analysis.

EIC believes the RIA overstates the difficulties and costs to the motor industry of implementing the proposed emissions legislation.

PETROL

  The RIA concludes that "we are still considering whether tighter petrol NOx limits are feasible and would deliver cost effective, real world emissions savings."

  For petrol cars, the RIA analysis should better recognise the capabilities of lambda 1 gasoline engines for exceeding Euro IV NOx levels at very low additional cost and to realise these benefits during real driving.

  For lean burn (PDI) cars the RIA argues that low NOx levels aren't achievable when there is strong evidence to conclude that they are.

DIESELS

  Diesel cars are currently allowed to be higher emitters than equivalent petrol equivalents (250 mg/km versus 80 mg/km NOx) and this gap needs to be closed in order to improve air quality but not by holding petrol standards stationary.

  The EIC rejects the RIA recommendation of "a 20% tightening of diesel NOx limits as an interim position." This is a very conservative position, consistent with the RIA's very pessimistic assessment of the capability of future NOx control technologies, despite evidence from the motor industry arguing to the contrary. It is also disappointing that the report favours the use of current cost estimates rather than anticipating cost savings potential.

  EIC believes the cost effectiveness of fitting diesel particulate filters is clear and welcomes the modelling of scenarios that focus on low PM emissions consistent with fitting diesel particulate filters.

  For all previous European emission legislation the predicted costs have always been too high and the technology capability has always performed better than expected. Realisation of these new technologies does, however, require a strong direction from legislation to enable the levels of innovation and development required from industry.

EIC believes the RIA underestimates the importance of legislation as a driver for innovation.

  The RIA's weak conclusions regarding reductions in diesel NOx emissions do not provide a clear enough direction for European companies to invest in engine development and design and integration of emissions control devices. Without a clear lead from the legislators the need to meet tough US levels will dominate development programmes in companies trying to sell diesel engines into the US market while other companies will develop products purely for market competitiveness, rather than emissions. A clear indication that low NOx diesel engines will be required is needed to promote development to achieving this goal.

DETAILED FEEDBACK

PETROL EMISSIONS CONTROL

  EIC is disappointed that three of the four scenarios modelled (A, C and E) do not require a reduction in petrol NOx emissions. This runs counter to the evidence of air quality problems associated with NO2. It is also a concern that scenario H combines a reduction in petrol NOx emissions with the most challenging scenario modelled for diesel emissions control. EIC believes petrol NOx emissions is the most cost effective means of reducing vehicle emissions and therefore the benefits of reductions in petrol emissions should be modelled in scenarios C and E.

LAMBDA 1 PETROL

  Three way catalysts with lambda 1 engines and control systems are the most developed form of mobile source emission control.

  The report mentions real world operating conditions. Current VCA data shows both a significant number of gasoline cars being certified at emission levels significantly lower than Euro IV requirements. Recent data presented by the Association of Emissiions Control by Catalyst (AECC) indicates that these vehicles continue to be low emitters over more transient cycles such as those developed in the Artemis programme. This is in direct contrast to diesel vehicles using EGR to meet NOx emission requirements where vehicle emissions are very test cycle specific. In our view there is little, or no doubt that further limit reductions in NOx from this sector would result in real world emission savings and that this is the most proven, and cost effective method currently available to help reduce road transport NOx emissions.

PETROL DIRECT INJECTION

  EIC does not agree with the RIA's assertion that "for petrol direct injection (PDI) vehicles the NOx limits would probably be difficult or impossible to achieve." For NOx, current experience shows that with the latest generation engines and emission control Euro IV petrol levels are achievable, with the appropriate safety margin. It is reasonable to assume that with a further period of development further NOx reductions would be possible.

  These vehicles run lean at speeds up to around 90 kph and are essentially equivalent to lambda 1 vehicles for gaseous emissions at higher speeds. When operating under lean conditions, our experience with current engines indicates that these vehicles may have difficulty meeting more stringent hydrocarbon limits due to high engine out levels and relatively lower exhaust temperature, compared with lambda 1 engines. These engines, especially in lambda 1 form, are currently under development at all major European motor manufacturers and we might expect some progress in decreasing engine emission levels to be achieved in the next few years. The development of the lambda 1 form of these engines is due to the increase power available from direct injection allowing either "sports" type vehicles, or, increased fuel economy through use of a smaller PDI engine to replace a conventional (lambda 1) petrol engine with the same power output. Due to the absence of tax incentives for CO2 emissions over the drive cycle through most of Europe and little customer benefit obtained by running lean at low speeds, vehicles with lean running calibrations are only in limited development. Keeping both Euro V hydrocarbon and carbon monoxide levels equivalent to Euro IV for petrol vehicles would encourage lean PDI vehicle development.

  Particulate emissions from PDI engines in the lambda 1 mode are essentially equivalent to conventional petrol engines. When running lean we have measured values between 14 and 4 mg/km with the current particulate mass method. This would appear to present a difficulty in meeting a 2.5 to 5 mg/km standard, but a number of factors should be taken into account. Firstly, that the range of values measured from current lean vehicles, and the different composition of the particulates between engines, suggests that differing combustion technologies give different results, for example air guided or wall guided spray systems, side or top mounted injectors. Secondly, in the lower particulate emitting engines the particulates have a relatively high VOC fraction that may decrease the value when using the Particulate Measurement Protocol (PMP) mass measurement method. The PMP method also typically returns a lower mass value than the current method. Further developments of these engines may allow power particulate levels to be achieved.

DIESEL EMISSIONS CONTROL

  EIC welcomes the RIA's conclusions in favour of stringent controls on PM emissions but additionally believes that low diesel NOx emissions are achievable.

  Certification data suggests that small and medium diesel vehicles can, today, meet a NOx emission value of around 150mg/km, at a competitive CO2 level. Further developments in injection technology, some Homogeneous Charge Compression Ignition (HCCI) operation and trade-off associated with fitment of a particulate filter indicate NOx emissions approaching 100mg/km are not unreasonable for a number of vehicle types by 2010. This leaves only a small requirement for post combustion emission control through hydrocarbon SCR, NOx traps, urea Selective Catalytic Reduction (SCR) or some other form of NOx emission control to meet a 80mg/km NOx emission. While these technologies are currently in the development stage, this low level of conversion will be available by 2010 if development is encouraged and at a low risk if the system fails. Also, if NOx sensors are fitted, emission control malfunctions will be easily detected. Then by 2015 technology will have been developed with operating experience enabling robust systems to be used to decrease diesel NOx emissions further through post combustion emission control, perhaps enabling further benefits in fuel economy through engine calibration. With this in mind we feel the case for NOx abatement is understated and the difficulties overestimated. EIC members also feel that the use of catalytic after-treatment for emissions control would result in additional benefits by ironing out the real-world variability in the diesel NOx emissions clearly illustrated when testing current diesels on the artemis, as compared with the current MVEG test cycle.

Annex 2

DRIVING RESOURCE EFFICIENCY

1.  INTRODUCTION

1.1  The Policy Background

  In May 1999, the UK Government published A better quality of life, a strategy for sustainable development for the UK. This set the aim of meeting four objectives at the same time:

    —  social progress which recognises the needs of everyone;

    —  effective protection of the environment;

    —  prudent use of natural resources; and

    —  maintenance of high and stable levels of economic growth and employment.

  Key to any hope of reconciling these objectives is major improvements in the efficiency with which we use resources.

  There are initiatives at global, EU and UK level to improve the efficiency of resource use. At a global level the World Summit for Sustainable Development (WSSD) held in Johannesburg in 2002 agreed that countries should start work on sustainable consumption and production strategies.

  At an EU level eco-efficiency is seen as an important key part of the EU's core Lisbon strategy and the Dutch Presidency has led the start of an initiative on a "Clean Clever Competitive Europe" to promote eco-efficient innovations.

  In the UK the Government published in September 2003 "Changing Patterns: UK Government Framework for Sustainable Consumption and Production".

  Whatever the terminology, there is clearly widespread agreement on the objective—we must gain more economic benefit from less environmental/resource input.

1.2  The Environmental Industries Commission (EIC)

  EIC was launched in 1995 to give the environmental technology and services industry a strong and effective voice with Government.

  With some 240 Member companies EIC has grown to be the largest trade association in Europe for the environmental technology and services industry. It enjoys the support of leading politicians from all three major parties, industrialists, trade union leaders, environmentalists and academics.

  EIC Members in the environmental consultancy sector led the way in the 1990s on pioneering projects on waste minimisation. This started with the famous Aire Calder project which concluded that when a polluting company expertly examines its process efficiency "the financial case for adopting a philosophy of waste minimisation is so overwhelming that companies should need little further encouragement to save money and the environment".

2.  OPPORTUNITY FOR RESOURCE EFFICIENCY

  There is a great deal of evidence of the opportunities for resource efficiency—and the benefits it can bring to businesses. Just a few examples include:

  In 1998 the book "Factor Four: Doubling Wealth, Halving Resource Use" detailed many case studies of businesses cutting the amount of resources they used whilst increasing profits.

  In the UK the Government funded Envirowise best practice progamme has helped business save £800 million through resource efficiency.

  And in April 2003 a study from the Environment Agency "The Benefits of Greener Business" concluded that £2-£3 billion is lost each year by manufactured industry in wasted natural resources—equivalent to about 7 per cent of total manufacturing industry profit.

3.  GOVERNMENT INITIATIVES TO DRIVE RESOURCE EFFICIENCY

  There are already a number of legislative and fiscal drivers towards resource efficiency.

    —  Integrated Pollution Prevention and Control Directive.

    —  Packing Regulations.

    —  Producer responsibility requirements including packaging; WEEE, RoHS, ELVs.

    —  Landfill Tax (which increases the cost of waste).

There are also a number of Government-funded programmes attempting to drive resource-efficiency, many funded by the revenue raised from the Landfill Tax, for example:

    —  WRAP Waste Minimisation initiatives, with a focus on real nappies, home composting and retailer innovation in packaging and other goods and services.

    —  The National Resource and Waste Forum, Household Waste Prevention Toolkit for Local Action.

    —  Envirowise extended services for SMEs and support for regional business programmes, made possible through £12 million of Defra funding for 2005.

    —  Carbon Trust activities, including ActionEnergy support for business, climate change agreements and tax breaks (ECAs).

    —  The Constructing Excellence programme for the construction sector.

    —  The Market Transformation Programme initiative on product improvements and other product policy activities within Defra (eg ACCPE) and the Environment Agency.

However it is clear that improvements in resource efficiency are much slower than required to tackle challenges such as climate change and the every growing amounts of waste produced by society.

  For example the Government's "Changing Patterns" report concluded that "In terms of energy required and waste produced, the UK is significantly less efficient than some of its key trading partners".

4.  AN AGENDA FOR DRIVING RESOURCE EFFICIENCY

  Making progress on this huge agenda requires not just one or two policies but a wide ranging strategy. As noted above there are many existing Government policies and initiatives in this area.

However progress is slow and there is an urgent need for an acceleration of these policies.

4.1  Indicators

  In order to be able to monitor the success of policy measures we need to be able to measure resource efficiency.

  In 2001 the Prime Minister's Strategy Unit (then called Performance and Innovation Unit) produced a report on "Resource Productivity: Making More with Less" which called for indicators and indicative targets on resource productivity.

Alongside the "Changing Patterns" report the Government produced a consultation on indicators on sustainable consumption and production.

  However there is still no framework for measuring progress towards resource efficiency.

  Once such a framework is in place it is then possible to set targets for resource efficiency. EIC considers these would be more meaningful if done on a sectoral basis, rather than an overall target for the economy.

RECOMMENDATIONS: THE GOVERNMENT SHOULD PUT IN PLACE A FRAMEWORK OF INDICATORS ON RESOURCE EFFICIENCY, INCLUDING INDICATORS FOR EACH INDUSTRIAL SECTOR.

  The Government should introduce sectoral targets for resource efficiency to give industry clarity as to the ends Government wishes to achieve.

4.2  IPPC Directive

  The EU IPPC regime puts obligations on regulated installations to use Best Available Techniques to minimise the environmental impacts of their process—this includes resource efficiency. By 2007 it will apply to some 5,000 installations in England and Wales.

A recent review by the EA of IPPC as a driver for resource efficiency measures recommended increasing the emphasis on resource efficiency in the licensing and inspection processes, through better staff training and improved guidance.

RECOMMENDATIONS: THE GOVERNMENT SHOULD ASK THE EUROPEAN COMMISSION TO INSURE THE IPPC BEST AVAILABLE TECHNIQUE REFERENCE DOCUMENTS (BREFS) DRAWN UP IN SEVILLE BENCHMARK RESOURCE USE FOR EACH REGULATED SECTOR.

  The Government should require the Environment Agency to put a high priority on resource efficiency under IPPC—and to publish a regular report on the resource efficiency gains achieved.

4.3  EMAS

  When the EU Eco-Management and Audit Scheme was first proposed MEPs called for a mandatory scheme which would have required companies to do eco-audits which would have identified resource efficiency opportunities. The voluntary scheme actually put in place has achieved very limited take up across the EU and improvements in resource efficiency have been patchy.

  The current Dutch Government focus on eco-efficiency provides an opportunity to look again at mandatory mechanisms for pushing resource efficiency out beyond a relatively few business leaders.

RECOMMENDATION: THE UK SHOULD PRESS THE EU TO LOOK AGAIN AT WAYS OF REQUIRING LARGER COMPANIES TO DO AUDITS OF THEIR RESOURCE USE. ONE POSSIBLE WAY OF STARTING THIS WOULD BE TO PUT GREATER FOCUS ON RESOURCE PRODUCTIVITY UNDER THE IPPC DIRECTIVE.

4.4  OPERATING AND FINANCIAL REVIEW

  New changes to company law will require the largest public companies to publish an Operating and Financial Review.

  Currently the draft Regulations leave this up to companies to decide if environmental issues are significant to the company and, should, therefore, be reported on.

RECOMMENDATION: THE GOVERNMENT SHOULD REQUIRE REPORTING ON ENVIRONMENTAL ISSUES IN THE OPERATING AND FINANCIAL REVIEW AND INCLUDE RESOURCE EFFICIENCY AS ONE OF THE AREAS THAT MUST BE REPORTED ON.

4.5  Landfill Tax

  The scheduled increases in Landfill Tax are forcing companies to give increasing priority to waste reduction measures by increasing the cost of waste disposal. The Landfill Tax is set to increase by at least £3/tonne/year until it reaches £35/tonne. A faster rate of increase would be a more powerful driver for waste reduction as well as for the development and deployment of technologies that divert waste from landfill. It would also raise more revenue to recycle into schemes to encourage and support resource efficiency.

RECOMMENDATION: THE GOVERNMENT SHOULD INCREASE THE LANDFILL TAX BY £5 A TONNE A YEAR UNTIL IT REACHES £35 A TONNE (WHEN THE IMPACT OF THE RATE SHOULD BE REVIEWED).

4.6  SUPPORT AND ADVICE

  The Government funded Envirowise programme has already had considerable success in promoting resource efficiency. The scheme is an important complement to the stick approach of regulation and fiscal measures. The Government has recently announced an increase in funding as part of the recycling of Landfill Tax receipts. However to penetrate more than a small proportion of business the programme needs expanding further.

RECOMMENDATION: THE GOVERNMENT SHOULD USE THE RECEIPTS FROM A FASTER INCREASE IN THE LANDFILL DIRECTIVE TO INCREASE FUNDING TO ENVIROWISE.

4.7  TAX INCENTIVES

  The Enhanced Capital Allowance (ECA) Scheme to incentivise energy efficient technology has now been running for some time. EIC was instrumental in promoting the introduction of fiscal incentives for companies purchasing environmental technologies.

  The Government has widened the scheme to water saving technologies and has announced it will consult on extending to waste minimisation and recycling technologies.

  While the scheme has had some success, there are several problem areas: the incentive amounts, in monetary terms, to only about 7% of the cost of the product, which can be significantly higher than less efficient models. The chain of authority in purchasing decisions can by long and convoluted, and the procurement decision maker can be some distance from the person claiming tax credits. As it is based on a tax break, the ECA scheme holds no incentive for non-tax paying bodies, particularly the public sector, which is a major purchaser of energy-using equipment.

RECOMMENDATIONS: THE GOVERNMENT SHOULD INCREASE THE ALLOWANCE FOR THE MOST ENVIRONMENTAL PRODUCTS TO 150%. THIS WILL UNDOUBTEDLY STIMULATE END USERS MUCH MORE TO INSIST ON ECA LISTED EQUIPMENT BEING USED.

The Government should provide an Inland Revenue certificate to accompany sales of ECA registered equipment to be sent to the building owner in order to address the problem of information being transferred along the sales chain by simplifying the documentation required.

  The Government should incorporate a requirement to use the ECA registered equipment (where relevant) into public procurement policies.

4.8  ENERGY EFFICIENCY POLICY

  A key Government scheme to encourage energy efficiency is the Climate Change Levy and the associated Climate Change Agreements (CCAs) which set sector-by-sector targets for energy efficiency gains. EIC welcomed the announcement that the Agreements will be extended to other energy intensive sectors. However our Members consider the levels at which they are set is too weak.

  The new EU Emissions Trading Scheme also has potential to drive energy efficiency. In this context it is extremely disappointing to see the weak National Allocation Plan which the UK is proposing.

RECOMMENDATIONS: THE GOVERNMENT SHOULD TIGHTEN CCAS TO PROVIDE A REAL DRIVER TOWARDS ENERGY EFFICIENCY

  The Government should abandon efforts to submit a weakened National Allocation Plan to the European Commission.

4.9  INNOVATION POLICY

  Government puts significant levels of support into innovation by business—for example through the Technology Strategy. This gives it leverage to encourage innovation in resource efficiency.

RECOMMENDATION: THE GOVERNMENT SHOULD REQUIRE ALL PROJECTS APPLYING FOR SUPPORT UNDER ITS TECHNOLOGY STRATEGY TO DEMONSTRATE A CONTRIBUTION TO RESOURCE EFFICIENCY AND USE THIS AS PART OF ITS SELECTION CRITERIA.

4.10  PUBLIC PROCUREMENT

  A wide range of Government and stakeholder reports have set out the huge potential of public procurement to play a leading role in sustainable development in general and resource efficiency in particular.

  Government policy has responded slowly to this challenge. However in 2003 the Government published the "Report and Recommendations of the Sustainable Procurement Group" and followed this with a revised "Joint Note on Environmental Issues in Purchasing" and a list of "Quick Wins" issued by the Office of Government Commerce (OGC). There has also been a handbook developed by the European Commission to clarify EU rules in this area.

  EIC, therefore, considers most of the required policy is in place. However the problem is with implementation which is still very patchy.

  In particular our Members report that equipment purchased in PFI projects is still overwhelming specified on least capital cost rather than whole life costing.

RECOMMENDATION: THE GOVERNMENT NEEDS TO GIVE POLITICAL MOMENTUM TO INTEGRATING RESOURCE EFFICIENCY CONSIDERATIONS INTO PUBLIC PROCUREMENT.

  The Government should urgently undertake an audit of energy efficiency in recent PFI projects and issue clear instructions that all PFI projects must meet high resource efficiency standards in the future.

February 2005





 
previous page contents next page

House of Commons home page Parliament home page House of Lords home page search page enquiries index

© Parliamentary copyright 2005
Prepared 13 April 2005