Table 81.
Possible management measures useful to mitigate the risk for amphibians and reptiles exposed to PPP after their intended uses in agricultural landscapes. Measures, implementation strategies, pros and cons are listed. Measures with higher probability of being implemented in the near future are highlighted in grey
Objective | Mitigation measure | Motivation | Practical implementation | Advantages | Constraints | Chances for implementation (higher impact and probability of success are highlighted) | No. |
---|---|---|---|---|---|---|---|
Specific provisions to lower the exposure of amphibians and reptiles to PPP | Maintain/create higher quality habitat for amphibians and reptiles. For amphibians, this could include buffer strips around breeding ponds, wet spots and forest edges partly used as terrestrial habitat. For reptiles, this may include hedgerows, stone walls, etc. that are protected from spraying | Statutory (CAP)/personal commitment of farmers | Cross compliance for the set up and management of ecological focus areas (EFA) under CAP – minimum ecological status of EFA need to be updated. A literature review (or further research) may be needed to quantify the effectiveness of these measures | Wide application in EU; optimal management of EFA as habitat for amphibians and reptiles is likely possible | Loss of productive land possible and correspondent loss of income. Land share requested by cross compliance is min. 5%. Minimum ecological status of EFA need to be updated in order to support amphibian and reptile populations | Implemented in current CAP schemes. ‘Farmers with arable land exceeding 15 ha must ensure that at least 5% of their land is an ecological focus area with a view to safeguarding and improving biodiversity on farms. Ecological focus areas may include, for example, fallow land, landscape features, afforested areas, terraces, hedges/wooded strips or nitrogen fixing crops such as clover and alfalfa which help to improve soil organic matter. Hedges, trees, ponds, ditches, terraces, stone walls and other landscape features are important habitats for birds and other species and help protect biodiversity, including pollinators.a’ However, not all ‘greening’ measures are likely to support biodiversity and specifically amphibians and reptiles. Update of CAP after 2020 should ensure minimum quality standards for ecological focus areas | 1a |
Voluntary | Voluntary participation supported by agro‐environmental schemes. A literature review (or further research) may be needed to quantify the effectiveness of these measures | Providing terrestrial habitats targeted to support amphibians and reptiles | Possibly participation by farmers already interested in lowering environmental impact. Low subsidies and market constraints might hamper further developments | The application of agri‐environment programmes has been compulsory for Member States in the framework of their rural development plans, whereas they remain optional for farmers. Higher financial support would increase farmers’ participation. Further improvement will depend on the CAP developments after 2020 | 1b | ||
Convert arable land into grassland | Voluntary | Voluntary participation supported by agro‐environmental schemes | Very low or even no plant protection product application, no soil disturbance | High expenses for funding; recultivation after 5 years | The application of agri‐environment programmes has been compulsory for Member States in the framework of their rural development plans, whereas they remain optional for farmers. Higher financial support would increase farmers’ participation. Further improvement will depend on the CAP developments after 2020 | 1c | |
Decide to waive locally the application of PPP in hot spots of amphibian and reptile presence | Voluntary | Technically possible, local support through authorities needed | No ‘loss’ of arable land | Weed infestation on fertile soils: possible lower yield with poorer quality, dedicated management with possible technical problems | Little chances of implementation due to considerable disadvantages and constraints | 1d | |
Implement monitoring and shift time of PPP application to minimise coincidence with amphibian migration | Voluntary/provided by administration | Extensive monitoring of amphibian presence is needed to determine when PPP application timing should be altered | Less exposure of amphibians in‐field during main migration periods | Only applicable at the local scale, not translatable to other locations due to differences in amphibian phenology, time shift may benefit one population but may impact others too (‘trade‐off’), not applicable to reptiles inhabiting the field | Implementation possible; but very specific knowledge on amphibians is to be provided to farmers on site. Research and funding is needed to establish appropriate monitoring schemes. Research is needed to develop suitable models. Patchy distributed information on local presence and movements of amphibian species is already available | 1e | |
Reduce PPP input in non‐target areas occurring via spray drift and run‐off | Statutory | Already widely implemented in PPP management (buffer strips, vegetated buffer strips and drift reducing nozzles) | Accepted risk mitigation at EU level | None | High, legally binding risk mitigation measures | 1f | |
Measures to reduce risk of amphibians and reptiles to plant protection products by lowering toxicity | Replace PPP with expected high toxic impact by less toxic products | Voluntary | Causes higher management effort in farms, but principally applicable | Less temporal coincidence of toxic product applications with migrating amphibian populations; less toxic effects | Replacement may lead to ‘trade offs’ due to higher toxicity for other organism groups | Further scientific investigations on exposure, uptake rate and toxicity of PPP for terrestrial stages of amphibians and reptiles is required. Risk assessment scheme apt at identifying (active substances in) PPP with high toxic potential is needed. Assessment methodologies to identify alternatives for ‘candidates for substitution’ need to further developed | 2a |
General provisions to lower the amount/discourage the use of PPP in agricultural landscape | Increase organic farming shares | Changed consumer behaviour, personal commitment of farmers, political goals | Personal commitment of farmers/supporting schemes | No synthetic plant protection products applied; sustainable land use configuration and management | There is only partly and/or temporarily awareness in European consumers with currently limited impact on conversion from conventional agricultural to organic farming | Although constantly increasing in market share, it is not expected that organic farming will be increased to a minimum quota by political will in the short range. The Rural Development Programme (2014–2020) supports the conversion to organic farming. Cross compliance under CAP is automatically achieved by organic farmers without changes of management practicesb | 3a |
Implement additional taxes on plant protection products | Economic advantages | Toxicity of PPP to amphibians and reptiles can be incorporated into the index for taxation calculation | PPP might be used as last measure if other appropriate and less expensive cultivation measures including crop rotations fail | High uncertainty regarding the degree of implementation due to personal farmer's choices Possible unexpected market movements, less planning security for involved industrial sector | Currently, implemented in some European Member Statesc based on flat taxes, taxes on sold PPP volume or on expected environmental impact. Currently, no political signs indicating a short‐ or a medium‐term implementation in other Member States or an agreed European schemes. | 3b | |
Apply integrated farming scheme (IF) including integrated pest management (IPM) | Currently statutory (CAP; Sustainable Use Directived) | Cross compliance | Can substantially lower the PPP input in agricultural landscapes | Initially cost and training intensive, substantial production changes might be necessary; failing in cross compliance difficult to control by administration? | Applying the principle of IPM is requested by EU policy. Increasing trend on the practical application of IPM. Medium term higher implementation to be expected | 3c | |
Voluntary/personal commitment of farmers | Voluntary participation supported by agro‐environmental schemes | Farmers are trained and practise IPM consequently | Possibly participation by farmers already interested in lowering environmental impact. Low subsidies and market constraints might hamper further developments. | The application of agri‐environment programmes has been compulsory for Member States in the framework of their rural development plans, whereas they remain optional for farmers. Higher financial support would increase farmers’ participation. Success will depend on the CAP developments after 2020 | 3d |
CAP: Common Agricultural Policy; PPP: plant protection product; IPM: Integrated Pest Management.
PAN Europe: overview on pesticide taxation scheme in Europe https://drive.google.com/drive/folders/0BznMpGKv0fAzYkxOTUp0Z3BOOWc
Directive 2009/128/EC.