Select Committee on Environmental Audit Minutes of Evidence


Supplementary memorandum from The Royal Society for the Protection of Birds (RSPB)

Response to specific questions from the Environmental Audit Committee following RSPB'S Oral Evidence Session, 26 May 2004

  The RSPB is Europe's largest wildlife charity with over 1 million members. We manage one of the largest conservation estates in the UK with more than 180 nature reserves, covering more than 100,000 hectares.

  The RSPB is the UK member of the BirdLife International Partnership, a global alliance of independent national conservation organisations working in more than 100 countries worldwide. The BirdLife International Partnership strives to conserve birds, their habitats and global biodiversity, working with people towards sustainability in the use of natural resources.

  The RSPB's policy and advocacy work covers a wide range of issues including climate change, energy, education for sustainable development, marine issues, water trade and agriculture. The RSPB also provides financial and technical support to BirdLife partners in Eastern Europe, Africa and Asia and supports community based projects to help deliver local benefits from sustainable natural resource management. The RSPB were actively engaged with the World Summit on Sustainable Development (WSSD) and are now working to ensure sustainable development is central to policy, decision making and action at all levels.

INTRODUCTION

  The RSPB is grateful for the opportunity to submit supplementary comments to its written and oral evidence. We will answer the questions in the order in which they have been posed.

1.   You stress the need to work safely within ecological limits as the bottom line. In the case of greenhouse gas emissions and global warming, the concept of an environmental limit has become widely understood and accepted. How well developed is this concept in other areas?[6]

  Regrettably, we fear that, while the concept is reasonably well developed in other areas, such as biodiversity loss, and is intuitively reasonably easy to grasp, the gravity of its implications has not yet swayed public opinion, or led to meaningful policy change. For example, in 2002, in preparation for the Johannesburg World Summit on Sustainable Development, the RSPB and Cambridge University convened a panel of internationally renowned ecologists and economists to assess progress on conserving ecosystems since the Rio Earth Summit in 1992. The results of that analysis, published in the journal Science, revealed that the total economic value of global ecosystems (wild nature) was at least 20 trillion dollars. The study further suggested that, on average globally, over one percent of undegraded ecosystems was being converted to human each year, incurring an economic loss equivalent to a permanent, accumulating loss of an additional $250 billion each and every year into the future. This was due to the loss of irreplaceable ecosystem services provided by nature (eg climate regulation, nutrient cycling, flood defence, water cycling, etc). Conversely, an expenditure of only $40-50 billion per year on conservation could yield economic benefits of around $4-5 trillion—a benefit cost ratio of 100:1. Regrettably, however, rather than investing in conservation at even a fraction of this level, the global policy community invests in (perverse) subsidies (through trade, agriculture, fisheries, energy, etc) of $1-2 trillion a year that encourage unsustainable conversion of wild nature. Some of the economists involved in the study were concerned that we had seriously underestimated the true value of wild nature, and underplayed the gravity of its continuing loss, by calculating total values on the basis of average costs of loss, not the marginal costs that would increase rapidly as surviving wild nature diminished.

With regard to plan proliferation, you refer in your memorandum (paragraph 3.6) to the tensions and contradictions of various strategies. Can you give some examples?

  Some examples of tensions and contradictions can be found within strategies, others between them. For example, within the UK strategy itself, there is a clear tension between the objectives of "high . . . levels of economic growth" and "effective protection of the environment" (see below). Most tensions, though, occur between strategies. For example, while it is commendable that the DTI has adopted a sustainable development strategy, that strategy, which emphasises carbon reduction and resource productivity, is not wholly consonant with the departmental strategy, which emphasises growth and enterprise. Nor is it clear that two strategies should be necessary; ideally, the departmental strategy would be sustainable. In a similar vein, early drafts of the Innovation Review made scant reference to the DTI sustainable development strategy, even though its purpose, to promote innovation, is closely linked to resource productivity. A similar type of tension is evident at an EU level between the Lisbon Strategy and the (Gothenburg) Sustainable Development Strategy. Even though the latter has now been subsumed into the former, the thrust of the two is quite different, and the amalgamation has largely been at the expense of the principles of sustainability.

  In other instances, there is less a tension and more a simple diffusion and blurring of objectives between strategies. For example, within the sixth environmental action plan of the EU, there are four priority areas: tackling climate change; nature and biodiversity-protecting a unique resource; environment and health; sustainable use of natural resources; and management of wastes. The EU Sustainable Development Strategy contains a similar, but crucially different, set of priorities: Climate change; Transport; Public health; and Management of natural resources, including biodiversity. It is not so much that the plan and strategy should not contain different priorities so much as the fact that they contain quite similar priorities expressed quite differently. To complicate matters further, the sixth environmental action plan itself requires the development of a further seven thematic strategies, on: soil; pesticides; marine; waste recycling; management of natural resources; urban environment; air quality. Even more confusing, the so-called Cardiff process called upon all formations of the Council to produce sector-specific strategies for integrating environmental concerns into economic policy. Partly as a result of this kind of plan proliferation, in which plans are rarely cross-referenced, none of these initiatives has so far delivered real change and some, such as the Cardiff process, and even the EU Sustainable Development strategy, appear to have ground to a halt.

Do you think the UK Sustainable Development Strategy should simply provide an overarching statement of aims and principles, or should it drive progress more actively?

  The strategy should at the very least provide a statement of aims and principles. But it could go further, in particular by committing to particular policy measures to internalise external costs in particular sectors, through: regulation and standard-setting; taxation; damage liability; capped levels of tradable permits, and so on. Internalising external costs, combined with a programme of public awareness-raising, would do more than anything else actually to change behaviour.

If the latter, would you welcome the inclusion of specific topic areas (eg waste, energy) and associated targets?

  A greater degree of specificity about priority issues, targets for them, and policy mechanisms to be used to achieve them would be very helpful. However, without a considerably longer period of consultation, and in order to avoid a very large and complex strategy indeed, it might be preferable to commit in the strategy to certain priority issues, but to propose developing targets for those issues, and the policy mechanisms to achieve them, subsequently. The strategy, however, should make a firm commitment to making such targets firm, rather than aspirational, and to developing them in a fixed period of time.

What implications would such a focus on specific areas have for other topic-specific strategies (eg the waste strategy) and for the strategies of devolved administrations?

  As indicated above, it would be possible to identify priority issues, and to commit to producing issue-specific targets within fixed time frames, without duplicating or making redundant existing or future issue-specific strategies. On the contrary, issue-specific strategies would become the vehicles whereby priorities identified in the strategy would be taken forward. The principal change from current practice would be that the (sustainable development) strategy would make a clear commitment to producing firm issue-specific targets on firm timescales; and the issue-specific strategies would be created or revised (in the timescale specified) to include a much higher degree of specificity than is currently the case both about the target(s) to be achieved and the policies to achieve them. Assuming the sustainable development strategy were reviewed periodically, it would be possible at that time to revisit priorities, and consider whether they needed new targets, or replacing with emerging priorities.

Do you have any specific suggestions for ways to reduce plan proliferation and ensure consistency across different strategies?

  Reducing plan proliferation and ensuring consistency are two different objectives, though each would be made easier by achieving the other. By and large the number of plans could be reduced by considering areas and ways in which plans currently overlap or duplicate each other, thereby introducing the possibility of contradiction or confusion. Where overlap currently occurs, plans could either be revised in such a way that their purpose is more clearly differentiated from that of parallel plans, or they could be eliminated or amalgamated. For example, there is plenty of room for the relationship between the Lisbon and Cardiff processes, the EU Sustainable Development Strategy, and the Sixth Environmental Action Plan to be rationalised in this way. If such rationalisation does occur, however, it will be crucial to avoid economic considerations prevailing even more completely than they already do over environmental and social ones. It is this concern that, on balance, makes retention of a separation between HMG departmental strategies and departmental sustainable development strategies advisable at least for the foreseeable future. Where such separation is retained, however, there should be a much greater degree of cross-referencing among strategies, and active efforts to ensure that their content, especially their objectives, are consistent and mutually compatible.

Do you think that changing the way sustainable development is defined in the strategy (in terms of overall definition, key objectives, and principles) would make the slightest difference in practice to the way Government departments implement policies?

  Although it would take time for any substantial changes to become fully internalised in the culture and practice of Government, we do believe that an orientation in the definition of sustainable development away from economic growth and towards quality of life or well-being would bring about change. Nor is it inconceivable that some such change might be both rapid and significant. For example, had the Department for Transport taken on the Public Service Agreement target that is currently shared between DTI and DEFRA to reduce carbon dioxide by 20% by 2010, it would have been much more (politically) difficult for the DfT to have published an aviation white paper that paid so little attention to managing and reducing demand for air travel. A white paper emphasising demand management would have been a significant improvement.

Apart from your suggestion for a marine indicator, are there any other measures you would like to see included in the indicators to reflect the extent to which the UK is currently unsustainable?

  The only other change to the basket of headline indicators that should be considered is the removal of GDP and GDP per capita. Not only is it far from clear that high levels of economic growth are compatible with sustainable development, but it is far from clear that GDP is a complete measure of economic growth. Moreover, to a much greater extent than most of the other headline indicators, it is a complex, heavily weighted composite indicator, with very little transparency about its underlying assumptions. This is not to suggest that GDP should be abandoned for all purposes. It clearly has an important role to play in helping to determine monetary and economic policy. But a strong argument can be made that it is not suitable as an indicator of sustainable development.

Is the Government adequately addressing the issue of sustainable consumption (as opposed to production), and to what extent will the next Strategy be undermined because of the failure to make more progress on this agenda?

  It appears to be true for many sectors and activities that cost-reducing efficiency gains yield lower prices and increased demand that offset, or more than offset, initial efficiency gains. As a result, overall consumption increases. It is also true that, while the UK is to be commended for having developed a strategy for sustainable production and consumption, the strategy neither acknowledges nor addresses the magnitude of the problem of consumption or its paradoxical relationship with productivity. Indeed, by preferring indicators that focus on relative (to levels of production) rather than absolute reductions of resource use, it arguably masks the problem.

  That having been said, the question of how to reduce absolute levels of consumption is probably the most challenging we face. Certainly, there can be a business incentive to improve productivity, and to produce services rather than goods (so long as the environmental consequences of manufacturing are not simply displaced, or even exacerbated, by exporting them overseas). It is certainly possible to incentivise the move to service provision financially, by fundamental environmental tax reform. Nevertheless, there will still be pressure to consume. For in a free market economy, where success is defined by economic growth achieved through advertising, trade and commerce, there is little incentive for commercial entities or Governments actually to discourage consumption. Profit in the private sector and tax revenue in the public sector would fall. So, unless the rate of efficiency gain outstrips the rate of consumption, resource use will increase.

  Nevertheless, a combination of pricing signals that fully reflect external costs, combined with a large-scale effort to raise public awareness and change consumer values, would, over time, and especially if undertaken globally, take us in the right direction, particularly if price and value messages are reinforced by real world evidence (for example extreme weather events) of the consequences of profligate consumption.

Was the potential conflict between sustainable consumption and consumerism fully appreciated when this initiative was agreed at the WSSD?

  In two senses, it was appreciated. Just as there is an intuitive understanding of the concept of ecological limits among policy makers and the public, there is an intuitive grasp of the conflict between consumerism and sustainable consumption. But, like ecological limits, the conflict tends to remain an abstraction, rather than a reality, so long as the limits have not yet been reached. For some constituencies at the WSSD, however, especially environmental and social interests on the one hand, and business interests on the other, the potential conflict was more tangible. Given that the conflict was tangible, and that the stakes are so high, the fact that agreement was reached at all suggests perhaps that there is little commitment actually to implement it.

Are there any machinery of Government changes you would like to see in order to reflect better key priorities in any future Sustainable Development strategy?

  The publication of the Treasury assessment of departmental spending bids against sustainability criteria and PSA targets would be helpful.

In particular, do you think that overall responsibility for Sustainable Development should remain with DEFRA, or would it-and the SDU-be better placed elsewhere (eg Cabinet Office)?

  The keys to effective mobilisation and coordination of sustainable development, including an effective SD unit, are adequate resources, clear objectives, and the ability (and location) to take an overview across Government. Wherever responsibility and the unit are located, they must be given clear political authority from the highest levels, with clear signals and structures for all departments to contribute. In that context, a sustainable development network, similar to the group that formed in the run up to Johannesburg, and similar to the new sustainable energy policy network (SEPN), but run from DEFRA by the SDU, might be helpful, with named participants from prescribed agencies and departments taking part.

During the fuel duty protests of 2000, what action did the RSPB take to make the case for maintaining the fuel duty escalator?

  For years and months before the fuel duty protests, the RSPB had been publicly supportive of the fuel duty escalator and had supported it in formal communications with Government. When the protests occurred, the RSPB took action both directly with policymakers, and through the media. Specifically, with respect to policymakers, along with several other environmental NGOs, we submitted (different) letters to both the Prime Minister and the Chancellor, supporting the escalator, and requesting a meeting with Mr Brown.

  With respect to the media, we made strenuous efforts to gain coverage for our perspective but, without previous environmental justification for the escalator from Government, or overt commitment to hypothecate fuel duty revenues to sustainable transport spending, and without an environmental justification for the escalator from Government at the time of the protests, environmental groups found it very difficult to capture press attention. For example, the RSPB organised a letter to the press from a group of environmental NGOs, but the letter was not published by the Times or the Guardian, only by the Independent. We also arranged a joint NGO press conference in Brighton at the start of the Labour Party conference, which was preceded and followed by press releases announcing the conference and reporting its results. However, only one or two representatives from the national media attended the conference, and none reported the event. We did gain coverage in the Independent subsequently.

  All that having been said, it is probably the case that, just as the Government could have been more explicitly supportive of the reasons for the escalator, the RSPB could have anticipated better the likely opposition to it, and have prepared a more comprehensive response, including alerting our membership to the issue, and requesting their support. In that context, when protests appeared possible again recently we did write to some of our members, explaining the environmental reasons for fuel duty, and asking for their support in requesting the Government to honour its commitment to raise fuel duty by 1.9p/litre in September.

July 2004





6   Please see a further explanation on this issue on Ev 170-171 Back


 
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