Select Committee on Environment, Food and Rural Affairs Written Evidence


Supplementary memorandum submitted by PAN UK (Z 41)

  PAN UK would like to submit the following further information, in response to the questions asked during the evidence session on 8 February 2005.

1.  PESTICIDE TAX

1.1  Administration costs and Hypothecation

  There are a large number of reports and publications relating to the use of a pesticide tax. The most comprehensive of these is the Ecotec report to the DETR.[14] In none of these documents are we aware of any information relating to the cost of implementation and therefore cannot respond further to the suggestion that the high cost of administering a pesticide tax will make such a tax unjustifiable.

  PAN UK would like to point out, however the following:

    —  There is currently a levy on pesticide sales to cover a number of costs, including monitoring of wildlife incidents, pesticide usage and pesticide residues. This is set at a much lower level than most proposed taxes and yet is seen as cost effective.

    —  Taxes, both flat-rate and banded, are implemented in other countries and revenues are raised successfully. There also appears to be no difficulty in hypothecation of these taxes. A brief report outlining these schemes was prepared by PAN-UK for Friends of the Earth and a copy will be provided for your information.

  We would suggest that any problems that are envisaged with either successfully hypothecating the tax or with unreasonably high administration costs should be addressed to the Treasury.

  There has been some suggestion that, using the principle of "the polluter pays", it could be appropriate to hypothecate the tax to pay for the removal of pesticides from drinking water. While this sounds reasonable and logical, we would not support this unless it could be ensured that farmers themselves do not shoulder this burden. There would be a danger that the resulting reduction in farm incomes would lead to a greater reluctance to move towards potentially more risky strategies such as non-chemical alternatives or lowered doses. Farmers would thus be locked into a high-pesticide-use strategy. We would support hypothecation only for the development and promotion of reductions in pesticide inputs and non-chemical alternatives.

1.2  Design of a Banded Tax

  During the evidence session on 8 February, I suggested that we could send some details of tax banding schemes. I have found it difficult to identify the necessary information within a reasonable time frame—PAN itself has not developed such a scheme, but has worked on this with other organisations. Since the option of a tax is suggested in the consultation on the National Strategy for Pesticides, this will be an appropriate opportunity for a fuller discussion about possible taxation schemes.

  A brief outline of some of the proposed/existing schemes are outlined below:

  A number of studies have addressed this issue and there are therefore a several "off the shelf" options. In particular, banded taxes have already been implemented in Norway. A review of some tax banding options is contained in the Ecotec report, and other organisations have more recently undertaken studies on classifying pesticide hazards—eg the Environment Agency in 2003 proposed a ranking method for chemicals based on their direct environmental effect; work undertaken by the RSPB and PAN-UK built on this and took into account the indirect effects; The Co-op, in conjunction with a number of organisations including PAN-UK, is developing a system for classifying pesticides by the hazard they present. PAN-UK is not in a position to supply details of these schemes, but more detailed information may be available from the relevant organisations.

  Some of the above schemes are based solely on hazards, others attempt to take into account the way they are used by included some level of risk assessment. Since there are a wide range of pesticide impacts which could be included in the banding system, and risk assessment is far from straightforward, PAN is concerned that an attempt to include them all and to satisfy all the relevant stakeholders, could lead to an immensely complicated, and ultimately unworkable scheme. We recognise that the more complicated the tax becomes, the greater the administration costs are likely to be. This may be a valid reason for keeping to a relatively simple scheme, such as a flat rate tax that is supported by PAN Europe.

  It is important that whether a flat-rate or banding system is employed, some attempt to account for the differences in application rate between pesticides is required. A simple tax per kg will discriminate against high volume products even when these may have lower levels of impacts than low volume products and an ad valorem tax may be most appropriate. A discussion of the likely effects of some of the different tax options is given in the Ecotec report.

  Whatever scheme is employed, it is likely that some anomalies will be generated whereby the tax system encourages moves towards less desirable pesticides. There will be a need for good monitoring of pesticide usage and regular reviews of the banding system to ensure that these anomalies are eliminated quickly.

  Evidence from the countries that currently have a pesticide tax show that a tax does not, on its own, appear to result in a large reduction in pesticide usage, although as part of a package of measures to reduce pesticides it has been successful.

  In summary, PAN UK would support:

    —  A fully hypothecated pesticide tax.

    —  A relatively simple scheme that can be applied at the earliest opportunity.

    —  The revenue raised to be used for providing independent, free advice to farmers on how to reduce their dependence on pesticides and for research and development into non-chemical pest control methods.

2.  CURRENT VI TARGETS

  2.1  Three of the main VI targets (Crop Protection Management Plans, Sprayer testing and National Register of Spray Operators) relate only to the "means" of achieving a reduction in impact, rather than the end itself. We believe that there is likely to be a relatively poor correlation between these targets and reduced environmental impact, even if the targets were met in full.

  2.2  The targets are largely only quantitative and there seems to be no element of "quality".

  2.2.1  One example that has already been outlined is that of Crop Protection Management Plans—the VI only monitors how many are completed, not the levels that are being achieved—a "poor" plan still counts towards the target.

  2.2.2  A second example is NRoSO and the need to accrue CPD points. Firstly, spray operators have three years to accrue 30 points, so in principle, few people will need to have any points at all at the moment. It is important to have targets for points awarded as well as the number of spray operators registered. Secondly, points are available for activities that many spray operators will already be doing—subscribing to farming journals, attending shows and events—and so the VI should really be monitoring increases in points obtained. Thirdly, personal experience of giving talks at events where CPD points are awarded suggests that, in some cases at least, (i) speakers are given no brief of what to say; (ii) those allocating points to the event have no knowledge of what is going to be said and (iii) there is no feedback to speakers afterwards.

  2.3  Current targets are aimed only at reaching the most professional and environmentally aware farmers and so they should be relatively easy to meet. There appears to be no strategy for reaching the rest.

  2.4  Targets should be based on environmental impact, and include terrestrial as well as water contamination. It may be difficult and expensive to monitor environmental impacts, but it needs to be done. If further research is needed to establish the best methodology, then this should be done as a matter of urgency.

  2.5  A target of pesticide use reduction should be relatively easy to measure and we would be much more confident of a correlation with environmental impacts than the existing targets. But, we need to ensure it is measured sensibly—kg sold is declining anyway as pesticides become more concentrated in their effect so this would not be helpful, and won't take account of moves to less hazardous pesticides which should also be encouraged.

3.  OTHER ISSUES

  3.1  A significant amount of training and information is currently in the hands of the Ag Chem manufacturers and distributors who rely on selling pesticides to make their profits. We will never get a real emphasis on use reduction until this is provided by wholly independent organisations.

  3.2  Research has not been well targeted:

    —  The issues of the relationship between pesticides and biodiversity and how to measure biodiversity impacts have not been addressed. The SAFFIE project is largely aimed at crop and field margin management techniques to offset the effects of pesticides, rather than directly reducing pesticide impacts.

    —  The VI has not taken the opportunity to contribute to the development of non-chemical alternatives or other techniques for reducing use.

    —  There is a real danger that full advantage will not be taken of the research funded through the VI unless the Ag Chem industry have a commitment to following it up in some way—eg there is a clear need in one of the projects (Spray behaviour at reduced application volumes) for individual companies to extend the work to their own products. There is little sign of this happening, and little evidence that agrochemical manufacturers are aware of the opportunities that this project has highlighted.

  3.3  The VI has put most responsibility for reducing the environmental impacts of pesticides onto farmers. They Agrochemical Industry has offered little in terms of supporting lower doses or a commitment to developing less hazardous products.

  3.4  The CPA in their evidence said (in response to Q4)—"we will never ask people to use more than absolutely necessary" and yet shortly afterwards, evidence from representatives of distributors (response to Q57, Ms Doonan and Ms Bend) were saying that in practice, rates lower than those recommended by the manufacturer were often used and that there is a "misunderstanding that pesticides are regularly used at the label rate". This potential for reducing doses should be taken full advantage of—and the necessary information should be freely available to all pesticide users, not just customers of particular companies or members of particular organisations.

  3.5  There are a wide range of routes of exposure to pesticides for the public and therefore, while not originally a driver for the VI, it could now be extended to take account of health as well as environmental impacts. A recent PAN UK report[15]reviews the issues relating to exposure of the public and a copy will be provided for your information.

4.  PAN UK RECOMMENDATIONS

  4.1  A National Pesticide Strategy to provide a complete framework for all pesticide-related issues, implemented by a body that has a much wider remit than the current PSD, and is effectively a "pest management directorate"

  4.2  Some elements should be taken out of the VI and made mandatory—this is the only way to reach 100% of spray operators—in particular sprayer testing and spray operator training. These must apply to all non-domestic pesticide users, not just those in agriculture. Steps should be taken to ensure that these elements are not box-ticking exercises, and that there is some independent assessment of quality.

  4.3  We believe that voluntary action is likely to be needed to implement the National Pesticide Strategy. This could be achieved through a revised and extended VI, and should include:

    —  A Pesticide Use Reduction programme.

    —  Monitoring of pesticide usage.

    —  Advice to farmers that is free and independent.

    —  Targeted action on the most hazardous pesticides and substitution of less hazardous ones.

    —  Specific action against those pesticides causing particular problems, such as those regularly turning up in water.

    —  Improvements in information to farmers about how to minimise pesticide impacts.

    —  More R&D into non-chemical controls and reduced pesticide usage.

    —  Monitoring of a wide range of environmental impacts.

    —  Additional action to monitor and reduce potential public exposure.

  The costs of these measures could be met through a Pesticide Tax.

PAN UK

March 2005





14   Design of a tax or charge scheme for pesticides Ecotec report for DETR, March 1999. Back

15   Alison Craig, December 2004, People's Pesticide Exposures, PAN UK. Back


 
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