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Evidence from Oxfordshire County Council
to the Environmental Planning Study


From: David Young, Director of Environmental Services, Oxfordshire County Council, County Hall, Oxford   OX1 1SD
Contact Officer: Chris Cousins, Assistant Director (Land Use Planning)

23 June 2000

The County Council's Environmental Committee considered the attached report on 31 May. The Committee agreed the recommendations in the report, namely that the comments in paragraphs 4-20 and Annex A be forwarded to you as the County Council's views on the study. Yours sincerely

Chris Cousins
Assistant Director
(Land Use Planning)


AGENDA ITEM ENV15

ENVIRONMENTAL COMMITTEE - 31 MAY 2000

Report by the Director of Environmental Services

Introduction

1.      In July 1999 the Royal Commission on Environmental Pollution (RCEP) announced it was to review environmental planning. The aim of its study is to assess whether the various regimes for setting and achieving environmental goals provide an effective, accountable and transparent way of protecting the environment. The scope of the study goes much wider than land use planning (although that aspect is central) and encompasses other planning regimes, such as those covering pollution control, air quality, waste, water, agri-environment and biodiversity.

2.      The Commission is now seeking views on the issues listed in Annex A of this report. It stresses that this list is not necessarily exhaustive, and invites comments on other issues which consultees consider relevant. The Commission does not expect those responding to address all of the issues raised. The closing date for responses is 23 June 2000.

Comments of the Director of Environmental Services

3.      The RCEP study raises many issues which need to be addressed, and is welcome. In general, and in response to the RCEP's request, I have attempted to tailor my comments to the specific questions raised. The question numbers are shown in square brackets. The questions themselves and some detailed responses not covered in the body of the report are at Annex A. However, before proceeding to these questions there are some general points to make.

General Points

4.      First, environmental planning on its own can rarely achieve significant environmental goals. It needs to operate within a supportive public policy framework where, for example, fiscal and regulatory regimes pull in the same direction. Too often in the past central government has expressed admirable objectives, but failed to back them up with the necessary financial and other incentives and penalties. One result of this is that the "planning system" is then accused of failure, when the conditions which would have allowed success were never created in the first place.

5.      A good current example of this looks likely to be the government's enthusiasm for an "urban renaissance", with high density housing of quality design. Research commissioned by the government indicates that the key to achieving such quality high density housing is to devote less space to car parking. This in turn would suggest that car ownership levels in urban areas need to fall, yet there is no sign of government seeking to pursue such a policy, which would undoubtedly need to be preceded by massive investment in alternative modes of transport.

6.      Perhaps a less contentious example is the fact that building new houses on greenfield sites does not attract VAT, whereas refurbishment or conversion of existing buildings does. This has worked against the government's wish to see more development on urban brownfield sites. There are now indications that this is likely to change to some extent, although it may take a fairly substantial change in the tax regime to achieve significant change on the ground. The key point is this: that environmental planning can achieve relatively little if it is having to work against the economic grain.

7.      The second general point is that the flouting of environmental rules needs to be viewed by both legislators and society at large as a far more serious offence than it currently is. That in turn means more effective enforcement powers for regulators, and sentencing which provides a more effective deterrent for offenders. At present, for example, a developer may make millions of pounds from unlawfully dumping waste in the countryside, yet face a fine of only a few thousand pounds for failing to comply with an enforcement notice. (In theory, if the matter goes to Crown Court, the fine can be unlimited, but is very seldom significant, tending to reinforce the point that a change in public attitudes is also required.) And even that will not necessarily secure the removal of the waste. While planning authorities have powers to remove the waste themselves and claim the cost back, that is small comfort if the developer goes bankrupt.

Environmental Sustainability [1]

8.      It is perhaps worth highlighting the question [1e] about the extent to which planning regimes have moved from "predict and provide" to "plan, monitor and manage", not least because of its relevance to the debate over regional planning guidance. It remains unclear as to how exactly the "plan, monitor and manage" approach will work in practice. One prerequisite for the approach to work is that planning authorities must be able to adjust their plans in the light of monitoring. At present, it is relatively straightforward for them to increase land supply. The legislative provision also exists for planning authorities to reduce land supply, including the option to revoke planning permissions. However, in practice, the compensation provisions make this prohibitively expensive, and so there is a sort of ratchet effect, whereby land for development can be released but not clawed back. (This also ties in to the issue of betterment discussed at paragraphs 13 and 14).

Boundaries, Integration versus Co-ordination, Subsidiarity & Democracy [2, 3 & 4]

9.      One of the main problems with the current arrangements for environmental planning is the extent to which they give rise to public confusion. This applies both to geographical and functional boundaries.

10.      For example, the recent local government reorganisation has resulted in additional complexities for the public, developers and others. Thus, for example, Oxfordshire retains a two-tier system of county and districts, while Berkshire has unitary authorities which nonetheless still operate a voluntary arrangement for such things as strategic planning at a county level.

11.      Moreover, successive governments have removed numerous functions from direct central or local government control. This often makes "joined up" government more difficult than when these functions were joined up. The fact that the government appears to be unable to insist that recycled materials from the MOD owned site at Upper Heyford are used in the A43 dualling just a couple of miles away appears to be but one illustration of the problems caused by excessive fragmentation.

12.       The RCEP study asks [3d] about the extent to which speeding up the planning system can be reconciled with effective environmental protection. There is also concern about the extent to which it can be reconciled with the requirements for ever-wider consultation, or with the UK's peculiarly adversarial way of conducting planning inquiries [4f]. These aspects of the UK planning system threaten at times to bring it to a halt.

13.      They also link to another of the RCEP's concerns, "betterment" [3h]. The planning system introduced in 1947 envisaged the increase in land values brought about by the grant of planning permission reverting to the public purse, on the basis that the increase had been brought about by the exercise of public policy. Attempts over the years to introduce and implement such a "betterment tax" have failed. However, an unofficial "tax" already applies in the form of "planning gain". As a tax planning gain is seriously flawed: it is not open or transparent - the rates are not published; it sometimes leads to public suspicion that planning permissions may be being bought and sold; and it is inequitable and regressive, in that the richest parts of the country, with most pressure for development, are those most able to negotiate the contributions justified by the development, while poorer areas often have to forego such necessary contributions to get any development at all.

14.      The sums of money involved are often very large: for example, an acre of agricultural land in central Oxfordshire might fetch £2,000-£3,000; with planning permission for housing it could fetch £800,000. This can encourage developers and landowners to press their case at every stage in the planning process and contribute to the overload on the system. The fact that they frequently employ barristers and numerous consultants presenting information in a complex and inaccessible way (often regardless of whether the information is inherently complex or not) may deter true public involvement in the planning process and make it unnecessarily adversarial.

15.      Taxing betterment openly and fairly and/or requiring a minimum level of contribution from all development would be preferable to the current system of unofficial taxation through planning gain: it should also remove public concerns that planning permissions may be being bought and sold, and free up some of the logjam in the system. It would also help if the automatic right of every objector to appear at local plan inquiries were to be reconsidered. An EIP type process, with the inspector (or panel) charged with ensuring a probing discussion of the issues involved, is one possible alternative, although it can result in lack of precision, leaving issues unresolved.

16.      As for openness, transparency and accountability [4b], there are certain features of local government practice that many would welcome being introduced at national government level. These include: public reports and recommendations from named officers; public timetables for preparing PPGs or RPG similar to the requirement for structure and local plans; a public record of how consultation responses have been handled; and fixed-term elections.

17.      The RCEP asks about the division of responsibilities between the planning and pollution control authorities [3e]. The current arrangements certainly cause confusion at times, and government attempts to clarify the position (e.g. in PPG10 - Planning & Waste Management) have not been particularly successful. As far as waste is concerned, the extent of exemption from waste management licensing raises public worries, as does the general issue of enforcement (see paragraph 7). It might be simpler and clearer for developers if they were to be issued with a single permission covering both planning and pollution control aspects. However, there would still be several bodies involved.

18.      The RCEP asks [3f] whether a satisfactory integration between transport planning and land use planning has been achieved. At the local level, the County Council has tried to direct transport investment in a way that supports its land use strategy, although at times this has proved difficult due to inadequate resources. The Local Transport Plan system also offers the prospect of improved integration of land use and transport planning, although there are still some problems to be ironed out. However, significant problems remain. It can be difficult, if not impossible, for local authorities compulsorily to purchase land for transport infrastructure at existing use values, and they may be held to ransom by landowners. The lack of power for local highway/transport authorities to direct refusal of planning applications on transport grounds causes problems which are likely to increase with the "detrunking" of much of the highway network.

19.      However, decisions on the big investment in transport planning are taken at the national level, and here there is considerable cause for concern. For example, the review of regional planning guidance for the south east (see separate agenda item) provides an opportunity for the government to give a clear lead on how it expects transport investment to support its land use strategy, and vice versa. However, the Secretary of State's proposed changes to the draft RPG fail to do this; instead there is simply a list of already approved road schemes. Such a lack of integration at the national and regional level is likely to undermine many local attempts at better land use/transport integration.

Assessment Approaches [5]

20.      Environmental impact assessment (EIA) is the most widely used assessment approach in the land use planning field. EIA is used in assessing the impact of development proposed in individual planning applications and in looking at potential mitigating measures. EIA is paid for and commissioned by the developer, and in my view this is a key weakness of the system: of the many thousands of EIAs undertaken I am not aware of one that has recommended that the proposed development should not proceed. I think that the developer should continue to pay for EIA where it is required, but should have no control over its commissioning or evaluation. This should be overseen by an independent body; the most straightforward might be the local planning authority.

Financial and Staff Implications

21.      None have been identified as arising directly from this report.

Environmental Implications

22.      The report and RCEP study is concerned with protecting the environment.

Implications for People Living in Poverty

23.      In general people living in poverty suffer disproportionately from the effects of environmental damage. Those with more money can, up to a point, choose to buy themselves a better environment. As a broad point, therefore, improved protection of the environment is likely to be of particular benefit to people living in poverty.

RECOMMENDATIONS

24.      It is recommended that the comments in paragraphs 4 to 20 and Annex A of the report be forwarded to the Royal Commission on Environmental Pollution as the County Council's views on the Commission's study of environmental planning.


ANNEX A

ROYAL COMMISSION STUDY OF ENVIRONMENTAL PLANNING: ISSUES ON WHICH EVIDENCE IS SOUGHT
Question Response
1.     Environmental sustainability

(a)     Has the pursuit of sustainable development as the broad objective of policy had favourable or unfavourable consequences for protection of the environment? To the extent that consequences have been unfavourable, how could that best be remedied?



To an extent it has encouraged people to think more holistically and longer term. However, at times vested interests have tried to hijack the concept, arguing that such things as out of town leisure complexes or shopping centres really represent sustainable development.
(b)    Can environmental objectives always be balanced against other issues or are there environmental imperatives? If so, how are they (or how should they be) determined? At a certain point there are undoubtedly environmental imperatives eg the survival of the planet as a place fit for human habitation. One of the difficulties with identifying the point at which an environmental imperative should take precedence relates to the issue of thresholds. Another relates to politics: ultimately, the weight to be given to environmental and other factors (including environmental imperatives) is a political decision.
(c)    What regulatory approaches are likely to be the most effective and practicable to protect the environment, in both measurable terms, eg. water, soil and air quality, and less tangible aspects, eg. Landscape and amenity? See main report.
(d)     In practice, to what extent does land use planning still embody a presumption in favour of development? Has the legislative change to a plan-led system given land use planning the potential to become a more effective instrument for achieving environmental sustainability? Is any further change necessary, and, if so, what? PPG1 states in the introduction that 'applications for development which are in accordance with the plan shall be allowed unless material considerations indicate otherwise' (paragraph 2). This could be somewhat misleading, and it would be helpful to have the PPG's qualification (found at paragraph 40) that 'applications which are not in accordance with relevant policies in the plan should not be allowed unless material considerations justify granting a planning permission' appeared in the introduction also.
(e)    In practice, how far have planning regimes in general moved from "predict and provide" to "plan, monitor and manage" to avoid environmentally unsustainable outcomes? See main report.
(f)    Do current arrangements for environmental planning sufficiently take into account the cumulative impacts of developments? Almost certainly not. For example, it is difficult if not impossible to seek contributions under C1/97 from small developments to mitigate their environmental impact, yet cumulatively they may be very significant.
(g)     To what extent is effective environmental planning hindered by a lack of resources within central government and local government, statutory agencies and advisory bodies? Have the procedures become too complex for any institution to cope adequately? Lack of resources is certainly a problem - see main report. The procedures are now complex and this is exacerbated by the number of bodies involved, and their differing accountabilities.
(h)     What are the implications of long-term risks, such as those posed by climate change or persistent waste, for environmental planning? Can planning systems become drivers for limiting the extent of damage from unavoidable climate change? The precautionary principle almost certainly needs to be taken far more seriously than it currently is. However, this is currently very difficult since both commercial and political time horizons tend to be fairly short. Planning has an important role in providing a policy framework to limit the extent of damage from climate change, but it is difficult for it to be proactive (for example, in encouraging the development of renewable energy) because it lacks implementation powers.
(i)     To what extent does the achievement of environmental sustainability depend on permitted uses being time limited? Increased time limiting of permitted uses would be helpful.
2.    Boundaries

(a)     To what extent does a mismatch between administrative areas and environmental processes contribute to environmentally sustainable planning, for instance in river catchments or along coastlines? What should be done about it?

No further comment.
(b)     What problems arise from different plans being produced and implemented for overlapping geographical areas? Public confusion, and sometimes inconsistency of implementation.
(c)    Should the land use planning system be responsible for helping to deliver policy targets in other areas such as transport, energy, water provision, flood protection, climate change and nature conservation? Yes, but only where it also has powers to influence the outcome - see main report.
(d)    How might geographical information systems (GIS) contribute to environmental planning in both the short and long term? What problems are associated with data accessibility and quality, and how might they be addressed? Through improvement to both the quality of and ease of access to information.
(e)    Does the lack of control over certain activities, such as forestry and agriculture, prejudice the achievement of environmental goals? If so, what would be the effect of introducing such controls? Farming and forestry activity can have a considerable impact on certain environmental goals, such as protecting and enhancing biodiversity. Some controls would be beneficial but would need to be set and applied sensibly.
3.    Integration or co-ordination?

(a)     Does the current system need "fixing"? What gaps, unnecessary duplication and conflicts exist in present arrangements for environmental planning?



There is a multiplicity of different plans, produced at different levels by different authorities. Some of these plans are statutory (eg. structure plans, local plans), some are voluntary: and of these only some stand a good chance of being implemented. Some plans (eg. the Local Environment Agency Action Plans or LEAPS) sit somewhat uneasily with the statutory development plan system, and at times it can be difficult to be certain of their scope and purpose. A simplification of the present system would be helpful.
(b)    Is there in practice a hierarchy in the formulation of different types of environmental plans? Would there be advantages in establishing a clearer hierarchy? As a).
(c)    Should the process of environmental planning be further rationalised, eg. as in New Zealand? Or would better co-ordination be sufficient to ensure an efficient and effective system? -
(d)    Are present arrangements for environmental planning efficient and cost-effective? Can the wish to speed up the land use planning process be reconciled with effective environmental protection? See main report.
(e)    Are the mandates and procedures of the pollution control bodies appropriate to their environmental planning responsibilities? Are these responsibilities appropriate? Is it practical to have parallel decisions on land use planning and pollution control? See main report.
(f)    Has a satisfactory integration of transport planning and land use planning been achieved? If not, what more needs to be done? See main report.
(g)    To what extent could economic instruments, non-statutory procedures, or informal arrangements complement environmental planning regulation, and how effective would they be at providing environmentally sustainable solutions? Would there be implications for openness, transparency and accountability? See main report.
(h)    One possible economic instrument could be a "betterment tax" aiming to increase public ownership of development gain. Is such a tax feasible and desirable? Might there be some way of linking the rate of tax to environmental impact? See main report.
(i)    Does the adoption of sustainability as the focus of policy intensify disagreements about the boundary between public and private development rights and obligations? To what extent does the current system enable such issues to be resolved? To some extent, yes. The wider implications of this question are discussed in the main report.
4.    Subsidiarity and democracy

(a)     Is the current balance between elected leadership, expert assessment and public participation in environmental planning decisions appropriate?



Main report discusses expert assessment and public participation. Environmental planning is bound to involve political decisions. Expert advice should be available to decision makers in an accessible and open way.
(b)    How do we ensure that all levels of decision-making processes are sufficiently open, transparent and accountable to gain public acceptance? What are the best ways to reflect the range of public opinion whilst maintaining an appropriate procedural timetable? When should local public opinion be overridden in the interest of a broader common goal? See main report.
(c)    What should be the relationship between international, national, regional and local goals? Should environmental planning take place at the lowest level consistent with the common good (the principle of subsidiarity)? How far do current arrangements depart from that principle? See main report. In general environmental planning should take place at the lowest level consistent with the common good - although this can be hard to define. However, some decisions need to be taken at a higher level in order to avoid decision making paralysis. For example, a large part of the government's reason in deciding that mineral and waste development should be county matters was that if such developments were determined at a lower level, few, if any, necessary permissions would be granted.
(d)    Are new regional planning arrangements, or other measures such as strengthening the strategic planning role of local government, needed to ensure greater coherence between national and local planning regimes? If so, what should these be and how should they be made accountable? The current regional planning arrangements are in a state of transition and some confusion. National government has not provided a clear framework within which inter-regional issues (such as the "N-S divide") or issues of national policy (eg air travel and airports) can be addressed. Regional government in England in its current form lacks direct democratic accountability. Measures to strengthen the strategic planning role of local government could be a way of addressing the 'democratic deficit' that currently exists.
(e)    To what extent do the principles of the environmental planning regimes in England, Scotland, Wales and Northern Ireland need to differ from each other? What are the specific drivers for these differences? -
(f)    Does the present form of planning inquiry offer the best way of resolving disputes? Should it be extended to permit a third party right of appeal? If so, should such rights be restricted to prevent abuse? See main report. One possibility would be to restrict the scope for developers to appeal. In principle, under a plan-led system the wide scope for appeal to the Secretary of State threatens to undermine both that system and the principle of subsidiarity. The right of developers to seek redress through the courts if a local planning authority had erred in law would remain.

Some commentators think that the Human Rights Act makes the introduction of a third party right of appeal inevitable. If this is the case, then very serious thought will have to be given to ways of ensuring that the planning system doesn't grind to a halt.

(g)    Would environmental tribunals or courts enhance public confidence in the land use planning appeals process? If so, would they impose significant extra costs and delays? -
5.    Assessment approaches

(a)    What are the most appropriate appraisal methodologies for use in drawing up environmental plans and assessing the environmental impact of plans prepared for other purposes? Do appraisal methodologies applied to individual cases provide sufficient information about their implications for the achievement of wider environmental goals?



Environmental appraisal of plans is still developing. Again, this tends to be an area where local government practice is more open than that of central government: there is, for example, no routine environmental appraisal of central government planning policy guidance. In general, the higher the level of plan, the more difficult it is to be specific about the likely implications.
(b)    Could increased use of such methodologies dovetail effectively with the efficient operation of environmental planning systems? How widely applicable should environmental appraisal be? What level of detail is appropriate for the various plan types? Who should be responsible for: i) undertaking environmental appraisal, and ii) judging its quality? See main report.
(c)    What would be the value of increased use of other assessment tools, eg. sustainability appraisal, environmental capital, environmental footprint, environmental space, and health impact assessment? -
(d)    Are there good examples of comparisons between the actual environmental, social and economic effects predicted when a case was being considered and what the actual effects were? In addition, is there evidence of the effectiveness of pre-development migration and compensation agreements at avoiding unsustainable outcomes? -
(e)    How adequate is the knowledge base, including the location and availability of expertise, provision of training for practitioners, and the accessibility and quality of data? How far are any of these elements in the knowledge base constrained by the lack of resources or suitable institutions, and, if appropriate, how could that be remedied? -

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