Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP)

Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks. Ausführliche Beschreibung

Gespeichert in:

Autor*in:	EFSA Panel of the Plant Protection Products and their Residues (PPR) [verfasserIn] Antonio Hernandez‐Jerez [verfasserIn] Paulien Adriaanse [verfasserIn] Annette Aldrich [verfasserIn] Philippe Berny [verfasserIn] Tamara Coja [verfasserIn] Sabine Duquesne [verfasserIn] Andreas Focks [verfasserIn] Marinovich Marina [verfasserIn] Maurice Millet [verfasserIn] Olavi Pelkonen [verfasserIn] Aaldrik Tiktak [verfasserIn] Christopher Topping [verfasserIn] Anneli Widenfalk [verfasserIn] Martin Wilks [verfasserIn] Gerrit Wolterink [verfasserIn] Arnaud Conrad [verfasserIn] Silvia Pieper [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2021

Schlagwörter:	groundwater modelling monitoring non‐target organisms soil surface water

Übergeordnetes Werk:	In: EFSA Journal - Wiley, 2018, 19(2021), 3, Seite n/a-n/a
Übergeordnetes Werk:	volume:19 ; year:2021 ; number:3 ; pages:n/a-n/a

Links:	Link aufrufen Link aufrufen Link aufrufen Journal toc

DOI / URN:	10.2903/j.efsa.2021.6498

Katalog-ID:	DOAJ049207288

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520			\|a Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks.
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653		0	\|a Chemical technology
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700	0		\|a Paulien Adriaanse \|e verfasserin \|4 aut
700	0		\|a Annette Aldrich \|e verfasserin \|4 aut
700	0		\|a Philippe Berny \|e verfasserin \|4 aut
700	0		\|a Tamara Coja \|e verfasserin \|4 aut
700	0		\|a Sabine Duquesne \|e verfasserin \|4 aut
700	0		\|a Andreas Focks \|e verfasserin \|4 aut
700	0		\|a Marinovich Marina \|e verfasserin \|4 aut
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700	0		\|a Christopher Topping \|e verfasserin \|4 aut
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700	0		\|a Martin Wilks \|e verfasserin \|4 aut
700	0		\|a Gerrit Wolterink \|e verfasserin \|4 aut
700	0		\|a Arnaud Conrad \|e verfasserin \|4 aut
700	0		\|a Silvia Pieper \|e verfasserin \|4 aut
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allfields	10.2903/j.efsa.2021.6498 doi (DE-627)DOAJ049207288 (DE-599)DOAJc6205ace5be147fd9589ed99441a11c8 DE-627 ger DE-627 rakwb eng TX341-641 TP1-1185 EFSA Panel of the Plant Protection Products and their Residues (PPR) verfasserin aut Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP) 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks. groundwater modelling monitoring non‐target organisms soil surface water Nutrition. Foods and food supply Chemical technology Antonio Hernandez‐Jerez verfasserin aut Paulien Adriaanse verfasserin aut Annette Aldrich verfasserin aut Philippe Berny verfasserin aut Tamara Coja verfasserin aut Sabine Duquesne verfasserin aut Andreas Focks verfasserin aut Marinovich Marina verfasserin aut Maurice Millet verfasserin aut Olavi Pelkonen verfasserin aut Aaldrik Tiktak verfasserin aut Christopher Topping verfasserin aut Anneli Widenfalk verfasserin aut Martin Wilks verfasserin aut Gerrit Wolterink verfasserin aut Arnaud Conrad verfasserin aut Silvia Pieper verfasserin aut In EFSA Journal Wiley, 2018 19(2021), 3, Seite n/a-n/a (DE-627)618834982 (DE-600)2540248-1 18314732 nnns volume:19 year:2021 number:3 pages:n/a-n/a https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/article/c6205ace5be147fd9589ed99441a11c8 kostenfrei https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/toc/1831-4732 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_235 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 19 2021 3 n/a-n/a
spelling	10.2903/j.efsa.2021.6498 doi (DE-627)DOAJ049207288 (DE-599)DOAJc6205ace5be147fd9589ed99441a11c8 DE-627 ger DE-627 rakwb eng TX341-641 TP1-1185 EFSA Panel of the Plant Protection Products and their Residues (PPR) verfasserin aut Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP) 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks. groundwater modelling monitoring non‐target organisms soil surface water Nutrition. Foods and food supply Chemical technology Antonio Hernandez‐Jerez verfasserin aut Paulien Adriaanse verfasserin aut Annette Aldrich verfasserin aut Philippe Berny verfasserin aut Tamara Coja verfasserin aut Sabine Duquesne verfasserin aut Andreas Focks verfasserin aut Marinovich Marina verfasserin aut Maurice Millet verfasserin aut Olavi Pelkonen verfasserin aut Aaldrik Tiktak verfasserin aut Christopher Topping verfasserin aut Anneli Widenfalk verfasserin aut Martin Wilks verfasserin aut Gerrit Wolterink verfasserin aut Arnaud Conrad verfasserin aut Silvia Pieper verfasserin aut In EFSA Journal Wiley, 2018 19(2021), 3, Seite n/a-n/a (DE-627)618834982 (DE-600)2540248-1 18314732 nnns volume:19 year:2021 number:3 pages:n/a-n/a https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/article/c6205ace5be147fd9589ed99441a11c8 kostenfrei https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/toc/1831-4732 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_235 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 19 2021 3 n/a-n/a
allfields_unstemmed	10.2903/j.efsa.2021.6498 doi (DE-627)DOAJ049207288 (DE-599)DOAJc6205ace5be147fd9589ed99441a11c8 DE-627 ger DE-627 rakwb eng TX341-641 TP1-1185 EFSA Panel of the Plant Protection Products and their Residues (PPR) verfasserin aut Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP) 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks. groundwater modelling monitoring non‐target organisms soil surface water Nutrition. Foods and food supply Chemical technology Antonio Hernandez‐Jerez verfasserin aut Paulien Adriaanse verfasserin aut Annette Aldrich verfasserin aut Philippe Berny verfasserin aut Tamara Coja verfasserin aut Sabine Duquesne verfasserin aut Andreas Focks verfasserin aut Marinovich Marina verfasserin aut Maurice Millet verfasserin aut Olavi Pelkonen verfasserin aut Aaldrik Tiktak verfasserin aut Christopher Topping verfasserin aut Anneli Widenfalk verfasserin aut Martin Wilks verfasserin aut Gerrit Wolterink verfasserin aut Arnaud Conrad verfasserin aut Silvia Pieper verfasserin aut In EFSA Journal Wiley, 2018 19(2021), 3, Seite n/a-n/a (DE-627)618834982 (DE-600)2540248-1 18314732 nnns volume:19 year:2021 number:3 pages:n/a-n/a https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/article/c6205ace5be147fd9589ed99441a11c8 kostenfrei https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/toc/1831-4732 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_235 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 19 2021 3 n/a-n/a
allfieldsGer	10.2903/j.efsa.2021.6498 doi (DE-627)DOAJ049207288 (DE-599)DOAJc6205ace5be147fd9589ed99441a11c8 DE-627 ger DE-627 rakwb eng TX341-641 TP1-1185 EFSA Panel of the Plant Protection Products and their Residues (PPR) verfasserin aut Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP) 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks. groundwater modelling monitoring non‐target organisms soil surface water Nutrition. Foods and food supply Chemical technology Antonio Hernandez‐Jerez verfasserin aut Paulien Adriaanse verfasserin aut Annette Aldrich verfasserin aut Philippe Berny verfasserin aut Tamara Coja verfasserin aut Sabine Duquesne verfasserin aut Andreas Focks verfasserin aut Marinovich Marina verfasserin aut Maurice Millet verfasserin aut Olavi Pelkonen verfasserin aut Aaldrik Tiktak verfasserin aut Christopher Topping verfasserin aut Anneli Widenfalk verfasserin aut Martin Wilks verfasserin aut Gerrit Wolterink verfasserin aut Arnaud Conrad verfasserin aut Silvia Pieper verfasserin aut In EFSA Journal Wiley, 2018 19(2021), 3, Seite n/a-n/a (DE-627)618834982 (DE-600)2540248-1 18314732 nnns volume:19 year:2021 number:3 pages:n/a-n/a https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/article/c6205ace5be147fd9589ed99441a11c8 kostenfrei https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/toc/1831-4732 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_235 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 19 2021 3 n/a-n/a
allfieldsSound	10.2903/j.efsa.2021.6498 doi (DE-627)DOAJ049207288 (DE-599)DOAJc6205ace5be147fd9589ed99441a11c8 DE-627 ger DE-627 rakwb eng TX341-641 TP1-1185 EFSA Panel of the Plant Protection Products and their Residues (PPR) verfasserin aut Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP) 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks. groundwater modelling monitoring non‐target organisms soil surface water Nutrition. Foods and food supply Chemical technology Antonio Hernandez‐Jerez verfasserin aut Paulien Adriaanse verfasserin aut Annette Aldrich verfasserin aut Philippe Berny verfasserin aut Tamara Coja verfasserin aut Sabine Duquesne verfasserin aut Andreas Focks verfasserin aut Marinovich Marina verfasserin aut Maurice Millet verfasserin aut Olavi Pelkonen verfasserin aut Aaldrik Tiktak verfasserin aut Christopher Topping verfasserin aut Anneli Widenfalk verfasserin aut Martin Wilks verfasserin aut Gerrit Wolterink verfasserin aut Arnaud Conrad verfasserin aut Silvia Pieper verfasserin aut In EFSA Journal Wiley, 2018 19(2021), 3, Seite n/a-n/a (DE-627)618834982 (DE-600)2540248-1 18314732 nnns volume:19 year:2021 number:3 pages:n/a-n/a https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/article/c6205ace5be147fd9589ed99441a11c8 kostenfrei https://doi.org/10.2903/j.efsa.2021.6498 kostenfrei https://doaj.org/toc/1831-4732 Journal toc kostenfrei GBV_USEFLAG_A SYSFLAG_A GBV_DOAJ GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_95 GBV_ILN_105 GBV_ILN_110 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_235 GBV_ILN_285 GBV_ILN_293 GBV_ILN_602 GBV_ILN_636 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2106 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2232 GBV_ILN_2470 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4700 AR 19 2021 3 n/a-n/a
language	English
source	In EFSA Journal 19(2021), 3, Seite n/a-n/a volume:19 year:2021 number:3 pages:n/a-n/a
sourceStr	In EFSA Journal 19(2021), 3, Seite n/a-n/a volume:19 year:2021 number:3 pages:n/a-n/a
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institution	findex.gbv.de
topic_facet	groundwater modelling monitoring non‐target organisms soil surface water Nutrition. Foods and food supply Chemical technology
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container_title	EFSA Journal
authorswithroles_txt_mv	EFSA Panel of the Plant Protection Products and their Residues (PPR) @@aut@@ Antonio Hernandez‐Jerez @@aut@@ Paulien Adriaanse @@aut@@ Annette Aldrich @@aut@@ Philippe Berny @@aut@@ Tamara Coja @@aut@@ Sabine Duquesne @@aut@@ Andreas Focks @@aut@@ Marinovich Marina @@aut@@ Maurice Millet @@aut@@ Olavi Pelkonen @@aut@@ Aaldrik Tiktak @@aut@@ Christopher Topping @@aut@@ Anneli Widenfalk @@aut@@ Martin Wilks @@aut@@ Gerrit Wolterink @@aut@@ Arnaud Conrad @@aut@@ Silvia Pieper @@aut@@
publishDateDaySort_date	2021-01-01T00:00:00Z
hierarchy_top_id	618834982
id	DOAJ049207288
language_de	englisch
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Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. 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author	EFSA Panel of the Plant Protection Products and their Residues (PPR)
spellingShingle	EFSA Panel of the Plant Protection Products and their Residues (PPR) misc TX341-641 misc TP1-1185 misc groundwater misc modelling misc monitoring misc non‐target organisms misc soil misc surface water misc Nutrition. Foods and food supply misc Chemical technology Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP)
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topic_title	TX341-641 TP1-1185 Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP) groundwater modelling monitoring non‐target organisms soil surface water
topic	misc TX341-641 misc TP1-1185 misc groundwater misc modelling misc monitoring misc non‐target organisms misc soil misc surface water misc Nutrition. Foods and food supply misc Chemical technology
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title_auth	Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP)
abstract	Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks.
abstractGer	Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks.
abstract_unstemmed	Abstract The European Commission asked the European Food Safety Authority (EFSA) to prepare a statement on a framework for the environmental risk assessment (ERA) of transition metals (e.g. iron and copper) used as active substances in plant protection products (PPPs). Non‐degradability, essentiality and specific conditions affecting fate and behaviour as well as their toxicity are distinctive characteristics possibly not covered in current guidance for PPPs. The proposed risk assessment framework starts with a preliminary phase, in which monitoring data on transition metals in relevant environmental compartments are provided. They deliver the metal natural background and anthropogenic residue levels to be considered in the exposure calculations. A first assessment step is then performed assuming fully bioavailable residues. Should the first step fail, refined ERA can, in principle, consider bioavailability issues; however, non‐equilibrium conditions need to be taken into account. Simple models that are fit for purpose should be employed in order to avoid unnecessary complexity. Exposure models and scenarios would need to be adapted to address environmental processes and parameters relevant to the fate and behaviour of transition metals in water, sediment and soils (e.g. speciation). All developments should follow current EFSA guidance documents. If refined approaches have been used in the risk assessment of PPPs containing metals, post‐registration monitoring and controlled long‐term studies should be conducted and assessed. Utilisation of the same transition metal in other PPPs or for other uses will lead to accumulation in environmental compartments acting as sinks. In general, it has to be considered that the prospective risk assessment of metal‐containing PPPs can only cover a defined period as there are limitations in the long‐term hazard assessment due to issues of non‐degradability. It is therefore recommended to consider these aspects in any risk management decisions and to align the ERA with the goals of other overarching legislative frameworks.
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title_short	Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP)
url	https://doi.org/10.2903/j.efsa.2021.6498 https://doaj.org/article/c6205ace5be147fd9589ed99441a11c8 https://doaj.org/toc/1831-4732
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author2	Antonio Hernandez‐Jerez Paulien Adriaanse Annette Aldrich Philippe Berny Tamara Coja Sabine Duquesne Andreas Focks Marinovich Marina Maurice Millet Olavi Pelkonen Aaldrik Tiktak Christopher Topping Anneli Widenfalk Martin Wilks Gerrit Wolterink Arnaud Conrad Silvia Pieper
author2Str	Antonio Hernandez‐Jerez Paulien Adriaanse Annette Aldrich Philippe Berny Tamara Coja Sabine Duquesne Andreas Focks Marinovich Marina Maurice Millet Olavi Pelkonen Aaldrik Tiktak Christopher Topping Anneli Widenfalk Martin Wilks Gerrit Wolterink Arnaud Conrad Silvia Pieper
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doi_str	10.2903/j.efsa.2021.6498
callnumber-a	TX341-641
up_date	2024-07-03T22:03:53.979Z
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score	7.398587

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Statement of the PPR Panel on a framework for conducting the environmental exposure and risk assessment for transition metals when used as active substances in plant protection products (PPP)

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