Doc 23112 10 January 2014 ECPA position paper on Commission impact assessment on criteria for endocrine disruptors Summary Shortly the European Commission will initiate an impact assessment (IA) on the policy options for the criteria for endocrine disruptors (EDs). This paper makes a number of suggestions which we believe would support a robust impact assessment. The paper suggests that: The scope of the IA should include all sectors to which the final ED criteria will be applied (i.e. it should include pesticides, biocides and REACH). The impacts on each chemical sector should be assessed separately and individually and not be aggregated together. The IA should be sufficiently detailed to provide a meaningful assessment (i.e. including sufficiently detailed to an agronomic level) upon which to compare policy options and to make robust policy decisions. All existing information on the impacts of the cut-off criteria in Regulation 1107/2009 as well as those around the revisions to Directive 91/414, should be used as input. The following policy options (scenarios) should be assessed (1) baseline scenario – interim criteria, (2) DG Environment proposal for the ED criteria, (3) hazard characterisation scenario, (4) risk assessment scenario. Both intended and unintended impacts of the above policy options should be assessed for the following: agronomic impacts, impacts on human health and environment, socioeconomic impacts, trade impacts and global competitiveness of European agriculture To provide a credible evaluation, the IA should be adequately resourced and should be undertaken by a group of well experienced and independent experts. Background In June 2013 DG Environment presented to the other Commission services a draft recommendation for the criteria for the identification of endocrine disruptors (ED) intended to be applied to pesticides, biocides, general chemicals and cosmetics. DG Environment and DG Sanco have since been asked to prepare an impact assessment (IA) comparing possible policy options for the criteria. Based on the outcome of the IA, DG Environment and DG Sanco are expected to prepare legislative proposals for the inclusion of the criteria into the regulations for pesticides and biocides respectively. This paper describes ECPA’s suggestions on the elements and information that we believe should be considered by the Commission in preparing and undertaking the IA. The paper uses as a basis the Commission Impact Assessment Guidelines, SEC (2009) 921. Scope and level of analysis ECPA anticipates that the scope of the IA will be constrained by the existing legal obligations and policy decisions (i.e. it is likely to focus on the decision at stake in relation to the development of the ED criteria and not on the previous decision to adopt hazard based criteria for ED). The IA may be limited in scope to pesticides and biocides only or it may be broadened to also consider REACH and cosmetics. ECPA believes that the IA should include all sectors to which the 1 http://ec.europa.eu/governance/impact/commission_guidelines/commission_guidelines_en.htm final ED criteria will be applied, i.e. the scope should include pesticides, biocides and REACH. The impacts on each of these sectors should be assessed separately and individually and not be aggregated together. In relation to the level of the analysis, the IA should be sufficiently detailed to provide a meaningful assessment (i.e. including sufficiently detailed to an agronomic level) upon which to compare policy options and to make robust policy decisions. However, if due to possible time constraints, it is not logistically possible to analyse to a sufficient level of detail across all existing pesticides (and biocides), then alternatives include analysis by chemical class or selecting a representative selection of substances. ECPA would strongly recommend that if the Commission does undertake a substance by substance evaluation on all or a subset of substances, then the results of this assessment should not be published in way that creates a public list of suspected endocrine disruptors. Note: the Commission has the general obligation of ensuring a proportionate depth and scope of analysis linked with the significance of the possible impacts and how politically important the issue is. Gathering information and consulting stakeholders ECPA would encourage the Commission to use existing information on the possible impacts of the cut-off criteria in Regulation 1107/2009 as an input into the IA. These include the previous and current reports prepared by various Member State competent authorities (UK, DK, SE) and the European Parliament around the revisions to Directive 91/414. As well as information relating to the number of substances concerned, existing data on the agronomic, trade and socio-economic impacts should also be included as well as information relating to anticipated health and environmental benefits of policy options. The impact on human health and the environment should be compared by assessing the overall risk associated with the different policy options. The list of reports recommended by ECPA to be considered are included in Attachment 1. In relation to stakeholder consultation, ECPA would support a public consultation period of at least 3 months (via written, web based procedure). We would also support the option of specific meetings with targeted groups. Defining the problem ECPA believes that the impact assessment process offers an opportunity not only to compare the different policy options for the criteria, but also to compare hazard-based versus risk-based policy options. While this is a separate topic in itself, the Commission is required by Regulation 1107/2009 to review the cut-off criteria by the end of 2014. This could be an efficient way to achieve both goals and to ensure a consistent assessment. To that end, ECPA supports the inclusion of a risk assessment scenario as one of the policy options. Defining the policy objective Consistent with relevant existing EU legislation (e.g. Reg 1107/2009), the overall objective for the Commission’s policy should be to ensure a high level of protection for human health and the environment. Within this objective ECPA believes that measures to achieve this should be science and risk-based and proportionate to the risk. Page 2 Defining policy options The Commission is expected to define different policy options on which the IA will be performed (in order to compare the different options). Developing the options does involves consideration of the proportionality principle. ECPA would suggest that the following policy options (scenarios) be evaluated in the IA: (1) baseline scenario – assumes no development of the final ED criteria and the interim criteria apply (C2 and R2, R2 and toxic to ED organs). Note: this baseline scenario applies only to pesticides and biocides; REACH and cosmetics will have a different baseline scenario. (2) DG Environment proposal for the ED criteria – the proposal as prepared during the course of2013. This scenario assumes that pesticide active substances placed in category 1 are not authorised, those in category 2 will undergo risk assessment (i.e. no direct impact on ability to register). (3) Hazard characterisation scenario – as scenario (2) above but includes the elements of hazard characterisation (potency, severity, irreversibility, lead toxicity). Inclusion of these elements in the final ED criteria were supported by some Commission services. (4) Risk assessment scenario – to assess the historical situation of managing EDs and to compare the policy options above across different sectors. Currently there is inconsistency between pesticides, biocides and REACH with regards to the regulation of endocrine disruptors; some incorporate elements of risk assessment (REACH), while others are purely hazard based (pesticides, biocides). This scenario would also be useful in relation to a comparison with the approach employed in other regions of the world (e.g. US), as the EU impact assessment guidelines explicitly mention considering international standards when conducting an impact assessment. In addition, this scenario would represent the situation prior to the adoption of Reg 1107/2009 and the inclusion of the hazard based cut-off criteria. ECPA also believes that as a second step the IA should evaluate the benefits and disadvantages of a categorisation scheme in order to consider whether it is needed and if it provides any significant improvements for the protection of human health and the environment. Assessing economic, social and environmental impacts We understand that the Commission is expected to assess the likely economic, social and environmental impacts, both intended and unintended for each policy option. The analysis should provide information on the impacts of the options as net changes as a basis for comparing them both against one other and against the ‘no policy change’/baseline scenario. ECPA believes that the following specific factors and indicators should be evaluated in the IA: - agronomic impacts such as: crop yields resistance management availability of affordable and effective crop protection alternatives - impacts on human health (including consideration of food safety) such as: occurrence of mycotoxins, availability of a balanced diet - impacts on environment such as: availability of effective alternatives, Page 3 ILUC considerations, CO2 emissions, biodiversity - socio-economic impacts , including consideration of food supply chain, such as : food supply index (imports vs exports) farm revenue rural development market value of pesticide/biocides prices of products/food costs employment (including downstream sectors) GDP impact on innovation - trade impacts: trade balance, international and within the EU . - global competitiveness of European agriculture Consideration should be given to both intended and unintended impacts and not only to impacts within the EU but also internationally (e.g. trade). Within the factors mentioned above, the IA should also consider the consequences occurring as a result of substances being replaced by others (e.g. possible unintended impacts of substance substitution and/or the ability to find alternative substances). The impacts should be assessed within each different piece of concerned legislation (pesticides, biocides as well as REACH and cosmetics). In making this analysis the Commission will need to take into account the differences in regulatory consequences of being considered as an endocrine disruptor between the sectorial legislation. For example, both pesticides and biocides have hazard based cut-off criteria (REACH and cosmetics do not), however the derogation clauses from these cut-offs are different between these two regulations. The Commission should also take into account those substances which may already be captured by the other cut-off criteria (e.g. CMR). Comparing options The results of the impact assessment across the different policy options are expected to be evaluated considering the criteria of effectiveness, efficiency and coherence. A summary overview of all the positive and negative economic, social and environmental impacts for the options analysed is expected to be prepared together with a ranking of the options. A cost-benefit analysis should also be part of this analysis. Resourcing In order to provide a credible and meaningful evaluation, ECPA appreciates that significant resources will be required. As discussed above, it should be undertaken in sufficient detail, but given the magnitude of the work, we believe that the services of an external expert would be helpful. A group of experienced and independent experts would be helpful, not only to gather the necessary information but also to undertake the IA itself. Page 4 Attachment 1 – list of reports recommended to be used as input to the IA Note: the documents below relate predominately to pesticides only. Further information from the other chemical sectors will be needed. Document ECPA report potential impact of current draft proposal for the endocrine disruption criteria – March 2013 ADAS report on role of azoles in wheat and potatoes Comments (or doc.no.) 22658 ADAS-JKI report on role of azoles in OSR 22205 Nomisma report on role of azoles in wheat production 21928 Teagasc ED impact assessment 23203 PSD impact assessment of cut-off criteria – May 2008 22838 Trinity Dublin and IfA Giessen on availability of azoles 22206 Horta study on role of azoles in Italian wheat production 21531 20986 All Member State Competent Authorities impact assessments on ED (HSE/CRD, BfR, BfR/CRD, DK, FR, ……) Impact assessment on Revision Dir 91/414– Graham Brookes 15100 Nomisma study Revision Dir 91/414 (socio-economic) 17306-17308 Health Impact study EP on Revision Dir 91/414 All Member State Competent Authorities IAs on revision of Dir 91/414 (, ES, FR – Arvalis, UK – potato council, Cranfield study etc…) Member State Competent Authorities IA on Revision Dir 91/414 (NL – Wageningen) MS IA – HGCA UK All work linked to ‘loss of products’ during Revision Dir 91/414 Global agricultural trends and their impact on European Union 17608 agriculture (Humboldt-University) Healthy nutrition and healthy lifestyle- the contribution of plant protection products. WRc impact assessment on ED substances 23115 FERA report on agronomic and economic impact of ED criteria Page 5 23116