Select Committee on Environment, Food and Rural Affairs Sixth Special Report


The Present State Of Waters In England And Wales

4. We readily acknowledge the improvements in oxygen status that have been achieved in the rivers of England and Wales in recent decades and the return of key indicator species such as salmon to many of our river systems. We are aware, however, that this has been achieved largely through investment in improving the quality of effluent discharged from major sewage treatment works and to a lesser extent the reduction in industrial pollution resulting from shrinkage in the manufacturing sector and the better management of animal wastes on farm holdings - sources of pollution which are relatively easy to identify and, with technological advances, to treat. We are far less sanguine about the wider picture (paragraph 29).

The Government welcomes the Committee's acknowledgement that much has been achieved to improve river water quality, principally through massive water industry investment. Diffuse sources of pollution are now proportionately much more significant - the Government's plans to address agricultural sources of diffuse pollution are dealt with in the Government's response to recommendation 10.

The rationale for the approach written into the Water Framework Directive of monitoring elements such as fish, invertebrates and algae is that they each respond to different pressures. Such broad monitoring is more likely to pick up the impact of more significant pressures requiring control and mitigation measures.

The Biological GQA remains the best national classification system for ecological quality. Macro-invertebrates do respond to a variety of pressures including organic pollution and toxic metals, however it is recognized that this system is not designed to detect the impacts of, for example, nutrient pressures.

Methods have been developed using macrophytes and diatoms to assess the impact of nutrients and nutrient control measures in rivers. These methods (Mean Trophic Rank and Trophic Diatom Index) have mainly been applied by the Environment Agency to determine the impacts of waste water treatment works discharges for the purposes of the EC Urban Waste Water Treatment Directive. However this approach is concerned primarily with the impact of relatively large point sources of nutrients, especially phosphorus. As the Water Framework Directive is concerned with the impact of all pressures, both point and diffuse, the Environment Agency is working with Scottish Environment Protection Agency to develop operational tools to enable the prediction of the expected (reference condition) macrophyte or diatom community at any river or lake site, an assessment of ecological status based on the observed macrophyte community (expressed in terms of quantitative deviation from the reference condition), and a diagnosis of the anthropogenic pressures affecting the observed community.

5. We are very concerned about the eutrophication of British waters, especially in Sites of Special Scientific Interest (SSSIs) (paragraph 32).

The eutrophication process is complex, affected by a range of factors, and measuring its extent in particular waters can be technically difficult. As part of the overall response to the Water Framework Directive, improved reference-based methodologies will have to be developed. Research is in hand to formulate the new tools that will be required. Notwithstanding these issues, the risks and undesirable effects of eutrophication are acknowledged as a significant concern. The Government is in the process of implementing a range of management measures, particularly the Urban Waste Water Treatment, Nitrate and Habitats Directives and (for marine waters) an OSPAR strategy in this area. In addition, the Environment Agency published a strategy on eutrophication in 2000, implementation of which is part of the Agency's "Making It Happen" initiative.

It is important to bear in mind that phosphorus concentrations in rivers have significantly reduced since 1990, although there is no similar trend as yet for nitrates. Nutrients from point sources are increasingly coming under control through the implementation of the Urban Waste Water Treatment and Habitats Directives. With regard to diffuse nutrient pollution, the Nitrates Directive, with recently extended UK designations, is now being implemented to reduce nitrogen pollution and may also help further to reduce phosphorus pollution. The potential need for additional measures on diffuse agricultural nutrient pollution is being looked at in the current Government review (see responses to recommendations 7 - 10).

Regarding SSSIs, some riverine sites are already designated as Sensitive Areas (Eutrophic) under the Urban Waste Water Treatment Directive. There are currently 109 Sensitive Areas (Eutrophic) in England which are reviewed every four years. The Environment Agency is also introducing phosphorus standards for riverine Special Areas of Conservation (all of which are SSSIs) under the Habitats Directive. These standards will drive action under the periodic review of water price limits. The potential to extend those standards to all SSSI rivers will be considered.

The Environment Agency is working with partners to take forward Habitat Action Plans under the UK Biodiversity Action Plan which includes addressing key threats to chalk rivers, mesotrophic lakes and eutrophic standing waters - with priorities for protective action generally being sites of high conservation status. This is incorporated in a holistic approach to the improvement of biodiversity in the aquatic and wetland environment under the biodiversity strategy for England.

6. It will be necessary to integrate the response to the Water Framework Directive with domestic flood control and planning policies. And if the assessment of water quality is to go beyond current measures a wider range of pollutants and sources of pollution will have to be taken into account (paragraph 34).

The Directive does not cover flooding or land use planning explicitly, but both can have implications for environmental water quality. Defra is pursuing integration with the land use planning system in two main ways:

§  by ensuring that national and regional land use planning guidance properly reflects new water priorities - for example the guidance on planning and pollution control. There is a regular programme for revising this guidance to reflect new considerations such as the Water Framework Directive;

§  through applying the existing system of controls on water pollution, including the need to consult the Environment Agency on certain categories of development applications, and the powers which the Agency already has to control discharges and abstraction (the latter being subject to amendment in the Water Bill).

6.2 The implications for flood management in England and Wales are currently being assessed with the Environment Agency, recognizing that many flood defence measures play a significant role in protection of the public and property. We are also taking part in a European working group to develop best practice guidance on flood prevention and mitigation.

6.3 A review of project appraisal guidance is likely to be required to ensure that all flood defence projects are consistent with the application of the Directive, building on current approaches that are already being developed through shoreline management planning and catchment flood management plans which will, themselves, form building blocks in the river basin management plan process.

Defra already actively encourages a wide range of approaches to flood control and encourages consideration of options that include managed realignment of defences to create more sustainable and environmentally acceptable solutions as well as the creation of flood storage areas on agricultural, amenity and other suitable land.

Diffuse Pollution and Agriculture

7. It has been estimated that nitrogen loading on British waters is nearly three times higher now than it was in the first half of the last century, and that phosphorus loading is more than twice as high now as it was then (paragraph 46).

The Government takes the view that considerably more needs to be done to tackle nutrient pollution, from both agricultural and non-agricultural sources. The extension of the area of nitrate vulnerable zones from 8% of the agricultural area of England to 55% and the associated action programme measures will go some way towards reducing agricultural nitrogen loads. As point sources increasingly come under control diffuse pollution inputs will become more evident (see recommendations 8-10).

Phosphorus is one of the principal pollutants arising from diffuse agricultural sources and the Government's strategic review of diffuse water pollution from agriculture (DWPA) is looking at cost-effective measures to tackle this, and other nutrient related pollution issues. Measures adopted now to tackle phosphorus will take some time to have an impact in the water course, because of the need to both reduce the amount of phosphorus in reservoirs such as soil and sediment and restore ecosystems, which may involve processes such as species reintroduction and biomanipulation.

8. The extent of the diffuse pollution problem in the water bodies of England and Wales is symptomatic of the intensity with which we use the landscape (paragraph 47).

The intensity of land use is clearly an important factor in assessing and understanding diffuse pollution loads to water courses. However, particularly in some vulnerable catchments, the problem could be mitigated by the promotion and better targeting of existing good practice measures in agriculture and elsewhere. See recommendations 7 and 9-10 for DWPA.

9. Limiting diffuse pollution will be a costly and expensive undertaking, and will impact on an agricultural industry which is already under severe pressure. It is likely to require changes in agricultural practice - perhaps even to the direction and ethos of the CAP. As such it is emblematic of the significance and wide-ranging impact of the Water Framework Directive (paragraph 47).

Any changes in agricultural practice proposed in order to implement the Water Framework Directive will clearly have to be proportionate and cost-effective if they are to be successful in reducing diffuse pollution inputs. The Department's review referred to above is examining a wide range of potential policy instruments, including regulation, voluntary and advisory measures as well as economic instruments, and will aim to choose the most appropriate and cost-effective measures, tailored to suit local circumstances. What is appropriate in one river basin district will not necessarily be appropriate in another. The Directive's RIA is currently being updated but any measures adopted will adhere to the general principles set out in annex A to the Sustainable Food and Farming Strategy - Facing the Future, published in December 2002.

The European Commission published its formal proposals on Reform of the CAP - 'A Long Term Perspective for Sustainable Agriculture' on 22 January 2003. The Government supports the Commission's proposals, the central element of which is to decouple agricultural production from subsidy. If agreed, this would bring farmers closer to the market, delivering economic, environmental and international benefits. The Government supports the Greek Presidency in its aim of reaching agreement in June 2003.

10. The Government should now clarify the timetable for completion of the strategic review of diffuse pollution from agriculture. We trust that the review will consult as widely as possible about the scale of the problem, and the strategies and resources needed to bring this most intractable of pollution sources under control. Given the likely impact that dealing with diffuse pollution will have on the agriculture industry we recommend that the review assess carefully the financial implications of the Directive for the agricultural industry to ensure that the costs of implementation for this sector are proportionate in respect of its present ability to pay (paragraph 48).

Following a discussion paper[1] published in June 2002 a further discussion document was published 30 April 2003. By the end of 2003-04 we will have developed an Action Plan which will include specific policy instruments on which we will have consulted formally.

The purpose of the review is to identify the most cost-effective approaches for reducing this pollution, and so the costs of different options and the principles of sustainable development will be considered in formulating proposals for consultation. The choice of policy instruments will have an effect on the distribution of the costs of reducing diffuse water pollution from agriculture and the potential impacts on all stakeholders will be carefully considered as part of the policy development process. Full consultation with stakeholders is being conducted as part of the process.

11. We urge the Environment Agency and others to be more aware of the status of lakes and ponds (paragraph 51).

Lakes are a water body category under the Directive, so their status will be assessed according to the requirements of the Directive.

In considering which lakes should be considered, the Directive provides a minimum area cut off value of greater than 50 hectares. This would in effect mean that many small but important standing waters might not be considered. To overcome this the Agency and the UKTAG are proposing a series of significance tests for smaller water bodies, such as conservation value, to justify their inclusion.

For lakes and ponds that do not fall within these either of these criteria, it is expected that the measures taken to protect other surface water bodies will provide protection for small lakes and ponds within the same catchment.


1   'Initial Thinking on the Problem and Solutions' Back


 
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