SUMMARY
In accordance with Article 6 of Regulation (EC) No 396/2005, BASF SE submitted two separate applications to the competent national authority in Spain and Ireland (evaluating Member States, EMSs) to modify the existing maximum residue levels (MRLs) for the active substance (a.s.) fluxapyroxad in kaki/Japanese persimmons and cultivated fungi, respectively.
The first application for an MRL in cultivated mushrooms, alongside the dossier containing the supporting data in IUCLID format, was submitted through the European Food Safety Authority (EFSA) Central Submission System on 23 September 2022. The appointed EMS Ireland assessed the dossier and declared its admissibility on 19 December 2022. The second application for an MRL in kaki/Japanese persimmons, alongside the dossier containing the supporting data in IUCLID format, was submitted through the EFSA Central Submission System on 16 January 2023 and the appointed EMS Spain declared its admissibility on 15 February 2023. Subsequently, following the implementation of the EFSA's confidentiality decision, the non-confidential versions of the dossiers were published by EFSA, and a public consultation was launched on each dossier. The consultation aimed to consult stakeholders and the public on the scientific data, studies and other information part of, or supporting, the submitted application, in order to identify whether other relevant scientific data or studies are available. The two consultations run from 7 June 2023 to 25 July 2023. Neither additional data nor comments were submitted in the framework of these consultations.
At the end of the commenting period, each EMS proceeded drafting the evaluation report, in accordance with Article 8 of Regulation (EC) No 396/2005. Both evaluation reports were submitted to the European Commission and forwarded to EFSA on 5 December 2023 and 11 January 2024 for the application on MRLs in cultivated mushrooms and MRLs in kaki/Japanese persimmons, respectively.
To accommodate for the intended use of fluxapyroxad, the EMS Ireland proposed to raise the existing MRL for cultivated fungi from the limit of quantification (LOQ) of 0.01 to 0.3 mg/kg. The EMS Spain proposed to raise the existing MRL for kaki/Japanese persimmons from the LOQ of 0.01 to 0.2 mg/kg.
EFSA assessed the applications and evaluation reports as required by Article 10 of the MRL regulation. EFSA identified points that needed further clarification for both applications and requested that the EMSs to address them. The applicant provided the requested information for each application in an updated IUCLID dossier. The additional information was duly considered by the EMSs in Ireland and Spain, who submitted a revised evaluation report to EFSA on 8 February 2024 and 7 March 2024, respectively. These updated reports replaced the previously submitted evaluation reports. For efficiency, the assessment was merged into a single reasoned opinion.
Based on the conclusions derived by EFSA in the framework of Directive 91/414/EEC, the data evaluated under previous MRL assessments, and the additional data provided by each EMS in the framework of the two applications, the following conclusions are derived.
The metabolism of fluxapyroxad following foliar applications was investigated in crops belonging to the groups of fruit crops, cereals/grass and pulses/oilseeds and following seed treatment in cereals. The metabolism of fluxapyroxad in rotational crops was investigated in root/tuber, leafy and cereal crops after bare soil applications. Studies investigating the effect of processing on the nature of fluxapyroxad (hydrolysis studies) demonstrated that the a.s. is stable.
Based on the metabolic pattern identified in metabolism studies, hydrolysis studies and the toxicological relevance of metabolites, the residue definitions for plant products were proposed as ‘fluxapyroxad’ for enforcement and risk assessment. These residue definitions are applicable to primary crops, rotational crops and processed products.
EFSA concluded that for the commodities assessed in these applications, the metabolism of fluxapyroxad in primary crops and the possible degradation in processed products have been sufficiently addressed and that the previously derived residue definitions are applicable. As the proposed uses of fluxapyroxad are on kaki/Japanese persimmons belonging to the group of permanent crops, and on mushrooms cultivated indoor in substrates, investigations of residues in rotational crops are not required in the framework of the current applications.
A sufficiently validated analytical method based on high performance liquid chromatography with tandem mass spectrometry (HPLC-MS/MS) is available to quantify residues of fluxapyroxad in the commodities assessed in these applications according to the enforcement residue definition. The method enables quantification of residues at or above 0.01 mg/kg (LOQ) in the commodities assessed (high water content matrices). The extraction efficiency of the enforcement method available (coded L0137/01) has been proven in high water content commodities.
The available residue trials are sufficient to derive an MRL proposal of 0.2 mg/kg for kaki/Japanese persimmons by extrapolation from residue trials on apples, and to derive an MRL proposal of 0.3 mg/kg for cultivated mushrooms based on the proposed Good Agricultural Practices (GAP).
Specific studies investigating the magnitude of fluxapyroxad residues in processed commodities are not required, as the individual total theoretical maximum daily intake is expected to be below the trigger value of 10% of the ADI.
Residues of fluxapyroxad in commodities of animal origin were not assessed since the commodities under consideration in these MRL applications are normally not fed to livestock.
The toxicological profile of fluxapyroxad was assessed in the framework of the EU pesticides peer review under Directive 91/414/EEC, and the data were sufficient to derive an acceptable daily intake (ADI) of 0.02 mg/kg body weight (bw) per day and an acute reference dose (ARfD) of 0.25 mg/kg bw. The metabolite (M700F008), which is included in the residue definition for risk assessment in products of animal origin, was concluded to be of similar toxicity as the parent a.s.
The consumer risk assessment was performed with revision 3.1 of the EFSA Pesticide Residues Intake Model (PRIMo). The short-term exposure assessment was performed only for the commodities assessed in the present MRL applications and did not exceed the ARfD for any of the crops assessed.
In the framework of the MRL review, a comprehensive long-term exposure assessment was performed, taking into account the existing uses at the EU level and the Codex MRLs (CXLs) that were implemented in the MRL legislation. EFSA updated the chronic risk assessment conducted in the framework of the MRL review with the median residue (STMR) values, derived in support of an MRL application submitted after the MRL review for certain root crops and coffee beans, the STMR values in support of CXLs assessed by EFSA after the MRL review and implemented in the EU MRL legislation and the STMR values derived from the residue trials submitted with the present MRL applications. The crops on which no uses or supported safe CXLs were reported in the MRL review and subsequently published EFSA outputs were excluded from the exposure calculation. The estimated long-term dietary intake accounted for a maximum of 73% of the ADI (NL toddler diet).
EFSA concluded that the proposed uses of fluxapyroxad on kaki/Japanese persimmons and cultivated mushrooms will not result in a consumer exposure exceeding the toxicological reference values and therefore are unlikely to pose a risk to consumers' health. The long-term consumer risk assessment is indicative, pending the submission of the confirmatory data requested under the MRL review.
EFSA proposes to amend the existing MRLs as reported in the summary table below.
Full details of all end points and the consumer risk assessment can be found in Appendices B–D.
Codea | Commodity | Existing EU MRL (mg/kg) | Proposed EU MRL (mg/kg) | Comment/justification |
Enforcement residue definition: FluxapyroxadF | ||||
0161060 | Kaki/Japanese persimmons | 0.01* | 0.2 | The submitted data are sufficient to derive an MRL proposal for the intended SEU use by extrapolation from residue trials on apples. Risk for consumers unlikely |
0280010 | Cultivated fungi | 0.01* | 0.3 | The submitted data are sufficient to derive an MRL proposal for the intended indoor EU use. Risk for consumers unlikely |
ASSESSMENT
The European Food Safety Authority (EFSA) received two separate applications to modify the existing maximum residue levels (MRLs) for fluxapyroxad in kaki/Japanese persimmons and in cultivated fungi. The detailed description of the intended uses of fluxapyroxad, which are the basis for the current MRL applications, is reported in Appendix A.
Fluxapyroxad is the International Organisation for Standardisation common name for 3-(difluoromethyl)-1-methyl-N-(3′,4′,5′-trifluoro[1,1′-biphenyl]-2-yl)-1H-pyrazole-4-carboxamide (IUPAC). The chemical structures of the a.s. and its main metabolites are reported in Appendix E.
Fluxapyroxad1 was evaluated in the framework of Directive 91/414/EEC2 with the United Kingdom designated as rapporteur Member State (RMS) for the representative uses as a foliar treatment on cereals. The draft assessment report (DAR) prepared by the RMS has been peer reviewed by EFSA (EFSA, 2012). Fluxapyroxad was approved3 for the use as fungicide on 1 January 2013.
The EU MRLs for fluxapyroxad are established in Annex II of Regulation (EC) No 396/2005.4 The review of existing MRLs according to Article 12 of Regulation (EC) No 396/2005 (MRL review) has been performed (EFSA, 2020a) and the proposed modifications have been implemented in the MRL legislation. Subsequently, EFSA has issued another reasoned opinion on the modification of MRLs for fluxapyroxad (EFSA, 2020b) which was not yet considering the MRL review outcome. The proposals from this reasoned opinion have been considered in recent MRL regulation.5 Certain Codex maximum residue limits (CXLs) have been taken over in the EU MRL legislation (FAO, 2013, 2015, 2018, 2020).
In accordance with Article 6 of Regulation (EC) No 396/2005 and following the provisions set by the ‘Transparency Regulation’ (EU) 2019/13816, the applicant BASF SE submitted two separate applications to the competent national authority in Ireland and Spain (evaluating Member States, EMSs) to modify the existing MRLs for the active substance (a.s.) fluxapyroxad in cultivated fungi and kaki/Japanese persimmons, respectively.
The first application for an MRL in cultivated mushrooms, alongside the dossier containing the supporting data in IUCLID format, was submitted through the EFSA Central Submission System on 23 September 2022. The appointed EMS Ireland assessed the dossier and declared its admissibility on 19 December 2022. The second application for an MRL in kaki/Japanese persimmons, alongside the dossier containing the supporting data in IUCLID format, was submitted through the EFSA Central Submission System on 16 January 2023 and the appointed EMS Spain declared its admissibility on 15 February 2023. Subsequently, following the implementation of the EFSA's confidentiality decision, the non-confidential versions of the dossiers were published by EFSA, and a public consultation was launched on each dossier. The consultation aimed to consult stakeholders and the public on the scientific data, studies and other information part of, or supporting, the submitted application, in order to identify whether other relevant scientific data or studies are available. The two consultations run from 7 June 2023 to 25 July 2023. No additional data nor comments were submitted in the framework of these consultations.
At the end of the commenting period, each EMS proceeded drafting the evaluation report, in accordance with Article 8 of Regulation (EC) No 396/2005. Both evaluation reports were submitted to the European Commission and forwarded to EFSA on 5 December 2023 and on 11 January2024 for the application on MRLs in cultivated mushrooms and MRLs in kaki/Japanese persimmons, respectively.
EFSA assessed the applications and evaluation reports as required by Article 10 of the MRL regulation. For efficiency, the assessment was merged in a single reasoned opinion.
EFSA identified points which needed further clarification for both applications and requested the EMSs to address them. The applicant provided the requested information for each application in an updated IUCLID dossier. The additional information was duly considered by the EMSs Ireland and Spain who submitted a revised evaluation report to EFSA on 8 February 2024 and 7 March 2024, respectively. These updated reports replaced the previously submitted evaluation reports.
EFSA based its assessment on the evaluation report submitted by each EMS (Ireland, 2023; Spain, 2023), the DAR and its final addendum prepared under Council Directive 91/414/EEC (United Kingdom, 2011a, 2011b), the Commission review report on fluxapyroxad (European Commission, 2012), the conclusion on the peer review of the pesticide risk assessment of the a.s. fluxapyroxad (EFSA, 2012), as well as the conclusions from previous EFSA opinions on fluxapyroxad (EFSA, 2011, 2015, 2016a, 2017, 2020b), including the reasoned opinion on the MRL review according to Article 12 of Regulation No 396/2005 (EFSA, 2020a), and the Scientific reports in support to the preparation of an EU position for the Codex Committee on Pesticide Residues (CCPR) meetings (EFSA, 2013, 2016b, 2019b, 2021).
For these applications, the data requirements established in Regulation (EU) No 544/20117 and the guidance documents applicable at the date of submission of the IUCLID application are applicable (European Commission, 1997a, 1997b, 1997c, 1997d, 1997e, 1997f, 1997g, 2010, 2020, 2021, 2022; OECD, 2011). The assessment is performed in accordance with the legal provisions of the Uniform Principles for the Evaluation and the Authorisation of Plant Protection Products adopted by Commission Regulation (EU) No 546/2011.8
It is noted that kaki/Japanese persimmons is a melliferous crop and the use of fluxapyroxad described in the current application is expected during the flowering period, however, further data is not required according to the data requirements applicable for the assessment of the submitted application.
It is noted that the EU pesticides peer review of the renewal of approval of the a.s. fluxapyroxad in accordance with Regulation (EC) No 1107/2009 is to be initiated in the near future and therefore the conclusions reported in this reasoned opinion might need to be reconsidered in the light of the outcome of the peer review.
A selected list of end points of the studies assessed by EFSA in the framework of these MRL applications including the end points of relevant studies assessed previously, is presented in Appendix B.
The evaluation reports submitted by the EMSs (Ireland, 2023; Spain, 2023) and the exposure calculations using the EFSA Pesticide Residues Intake Model (PRIMo) are considered as supporting documents to this reasoned opinion and, thus, are made publicly available as background documents to this reasoned opinion.9
RESIDUES IN PLANTS
Nature of residues and methods of analysis in plants
Nature of residues in primary crops
The metabolism of fluxapyroxad after foliar applications was investigated in fruits (tomatoes), pulses/oilseeds (soybean) and cereals/grasses (wheat) crop groups in the framework of the EU pesticides peer review (EFSA, 2012). Additionally, the metabolism study on cereal (wheat) seed treatment was submitted and evaluated in the context of the previous MRL application (EFSA, 2015). These studies have been re-evaluated during the MRL review for fluxapyroxad (EFSA, 2020a).
After foliar applications, fluxapyroxad was the main component of the total radioactive residues (TRR) in tomatoes, wheat and soyabeans plant parts, except in seeds, where the metabolism showed to be more extensive. In tomatoes and wheat following the foliar treatment, parent compound represented 54% of the TRR up to more than 90% TRR, while in soyabean seeds it was determined to be 7% up to 21% TRR, and the two major metabolites M700F002 and M700F048 were identified as 33.5% and 20% TRR, respectively (EFSA, 2012). The metabolic pathway of fluxapyroxad was similar in cereals following foliar application and after seed treatment (EFSA, 2015, 2020a).
Considering that the metabolism of fluxapyroxad was found to be similar in three different crop groups, the results of these studies can be extended to all crop categories (European Commission, 1997a). For the intended uses of fluxapyroxad on kaki/Japanese persimmons and cultivated mushrooms, which belong to the fruits crop group, the metabolic behaviour in primary crops is sufficiently addressed.
Nature of residues in rotational crops
Fluxapyroxad is not proposed to be used on crops that can be grown in rotation.
For kaki/Japanese persimmons (permanent crop) and cultivated fungi (grown in substrate) assessed in these applications, no information is required (EFSA, 2023; European Commission, 1997c).
The Guidance on the assessment of pesticide residues in rotational crops published by EFSA in 2023 specifies that rotational crop studies shall not be required for uses of plant protection products in cultivated fungi, where rotations on the same substrate are not part of the normal agricultural practices (EFSA, 2023). EFSA is proposing to take into consideration this explanation, even though the Guidance per se is not yet applicable.
Nevertheless, studies on the nature of residues in rotation crop are available and are reported in Appendix B of this reasoned opinion for completeness.
Nature of residues in processed commodities
The effect of processing on the nature of fluxapyroxad was investigated in the framework of the EU pesticides peer review (EFSA, 2012) in studies performed under standard hydrolysis conditions.
These studies showed that fluxapyroxad is hydrolytically stable under standard processing conditions such as pasteurisation, baking, brewing and boiling and sterilisation (EFSA, 2012). This conclusion was confirmed in the framework of the MRL review (EFSA, 2020a).
EFSA concluded that the nature of residues of the a.s. under standard hydrolysis conditions is sufficiently addressed, and further studies are not required for the intended uses.
Analytical methods for enforcement purposes in plant commodities
The analytical method for the determination of residues of fluxapyroxad in plant commodities was assessed in the context of the EU pesticides peer review and the MRL review (EFSA, 2012, 2020a). The high performance liquid chromatography with tandem mass spectrometry (HPLC-MS/MS) method (L0137/01) and its independent laboratory validation (ILV) are sufficiently validated for the determination of the residues of fluxapyroxad in high water, high acid, high oil content and dry matrices. The method allows quantifying residues at or above the LOQ of 0.01 mg/kg. The LOQ of 0.01 mg/kg is achievable in all four main plant matrices by using the Quick, Easy, Cheap, Effective, Rugged and Safe (QuEChERS) multi-residue method in routine analyses (EFSA, 2020a).
As reported in the MRL review, according to the EU Reference Laboratories, fluxapyroxad can be monitored by the above-mentioned method in high water and high acid content commodities with a lower LOQ of 0.002 mg/kg and in dry and high oil content commodities with an LOQ of 0.005 mg/kg, and in honey with an LOQ of 0.005 mg/kg (EFSA, 2020a).
EFSA concludes that sufficiently validated analytical method is available for enforcing the proposed MRLs for fluxapyroxad in kaki/Japanese persimmons and cultivated fungi.
The extraction efficiency of the analytical method for enforcement of fluxapyroxad in high water content commodities is sufficiently demonstrated as the extraction procedure of the enforcement method based on the solvent system (i.e. methanol/water, 1/1 v/v single extraction) was cross-validated using radiolabelled sample material from the fluxapyroxad metabolism study in tomatoes (three-step extraction with methanol/water followed by two-step extraction with water) (Ireland, 2023; Spain, 2023). Overall, EFSA notes that the extraction efficiency of the analytical method applied for enforcement is proven in high water content commodities, as indicated according to the requirements of the extraction efficiency Guidance, SANTE 2017/10632 (European Commission, 2022).
Storage stability of residues in plants
The storage stability of fluxapyroxad residues in plants stored under frozen conditions was investigated in the framework of the EU pesticides peer review (EFSA, 2012). The storage stability of fluxapyroxad was demonstrated for a period of 24 months at −20°C in all plant matrices and processed products.
EFSA concludes that sufficiently validated storage stability studies are available to support the use of fluxapyroxad in cultivated mushrooms and kaki (high water content commodities).
Proposed residue definitions
Based on the metabolic pattern identified in metabolism studies and the results of hydrolysis studies, the toxicological relevance of metabolites, the following residue definitions were proposed in the EU pesticides peer review and the MRL review (EFSA, 2012, 2020a):
- Residue definition for enforcement: Fluxapyroxad
- Residue definition for risk assessment: Fluxapyroxad
The residue definitions apply to primary crops, rotational crops and processed products (EFSA, 2012, 2020a).
The residue definition for enforcement set in Regulation (EC) No 396/2005 is identical to the above-mentioned residue definition.
Taking into account the proposed uses assessed in these applications, EFSA concluded that these residue definitions are appropriate and no further information is required.
Magnitude of residues in plants
Magnitude of residues in primary crops
Kaki/Japanese persimmons
The applicant proposed to extrapolate residue data from the 8 independent and GAP-compliant trials performed on apples in Southern Europe to kaki/Japanese persimmons (Spain, 2023). Kaki are minor crops and a minimum of four trials is sufficient. This extrapolation is acceptable according to the EU technical guidelines (TG) (European Commission, 2020). It is to be noted that the SEU GAP proposed for use in kaki is identical to the SEU GAP on pome fruits authorised in the EU, and the same residue trials were already assessed by EFSA in the framework of MRL review (EFSA, 2020a). Therefore, the submitted trials are considered valid for extrapolation and are briefly summarised in the below paragraph for completeness.
The eight SEU trials were performed in Italy, Greece and Spain over two seasons, 2010 and 2011. All of the trials were of a decline design. In all residue trials, two applications were made at a single rate equivalent to 75 g a.s./ha and one at a single rate equivalent to 90 g a.s./ha. Thus, within the 25% acceptable tolerance range (European Commission, 2020). The sampling was performed from the treated and the untreated plots on Days 28–29, 34–36 (corresponding to the pre-harvest interval (PHI)) and 41–43 days after the application (Spain, 2023).
Overall, the number of trials performed on apples in Southern Europe is sufficient to derive by extrapolation an MRL proposal of 0.2 mg/kg for the intended use of fluxapyroxad on kaki/Japanese persimmon.
Cultivated fungi
In support of the intended use of cultivated fungi, the applicant submitted four independent GAP-compliant residue trials performed on two mushroom varieties grown in indoor conditions. The trials were conducted in Germany and Northern France during the growing season of 2021.
The mushrooms were cultivated in boxes containing the substrate consisting of an organic compost material, which is being used only once for each batch of cultivation (Ireland, 2023). In the four residue trials, the single application was made at the rate of ±25% of 6 kg a.s./ha (within acceptable deviation, European Commission, 2020), 5–7 days after cover-up. Subsequently, the samples from treated mushroom caps with stems were collected at the PHI of 7 and 10 days in the first study and at the PHI of 9 and 11 days in the second study.
The residue levels in mushrooms ranged between 0.052 mg/kg and 0.093 mg/kg. No residues of fluxapyroxad at or above the LOQ of the analytical method of fluxapyroxad were found in any of the untreated specimens.
Overall, the number of trials is sufficient to derive an MRL proposal of 0.3 mg/kg for the intended use of fluxapyroxad on mushrooms.
It is noted that the residues of fluxapyroxad in mushrooms are considerably higher at a PHI of 9 as compared to a PHI of 11 (fast decline in short time). It is nevertheless concluded that residues of fluxapyroxad in mushrooms will not occur above the MRL of 0.3 mg/kg because mushrooms must be harvested according to the intended use pattern at the PHI of 10 or later.
The residue data from the supervised residue trials in primary crops are summarised in Appendix B.1.2.1. Before analyses, the samples from the residue trials on mushrooms were stored under conditions for which the integrity had been demonstrated (Ireland, 2023). Samples from the submitted residue trials on apples were previously concluded to be valid (EFSA, 2020a).
The method (L0137/01) used for the analysis of residues of fluxapyroxad in kaki/Japanese persimmons and cultivated fungi is based on HPLC-MS/MS and enables quantification of residues at or above the LOQ of 0.01 mg/kg in the commodities assessed. According to the EMS, the method used to analyse samples for fluxapyroxad residues was sufficiently validated and fit for purpose (Ireland, 2023; Spain, 2023). Since the method is the same as the monitoring analytical method, the extraction efficiency can be considered proven (see Section 1.1.4).
Magnitude of residues in rotational crops
Since kaki/Japanese persimmon and mushrooms are not expected to be grown in rotation (see Section 1.1.2), rotational crops studies are not deemed relevant for this application.
It is noted that, the EMS Ireland calculated the potential transfer of residues of fluxapyroxad (total amount of a.s. in the field) if mushrooms are treated according to the intended GAP in case the substrate is then used for fertilisation (Ireland, 2023). As the assessment of the fertiliser uses is not in the remit of Regulation (EC) No 396/2005, EFSA is not verifying the assessment of calculation provided in this Reasoned opinion.
Magnitude of residues in processed commodities
Specific studies to assess the magnitude of fluxapyroxad residues in processed commodities were not submitted and are not required according to Regulation (EC) No 544/2011, considering that the contribution of residues in the commodities under consideration (kaki and cultivated mushrooms) to the overall dietary exposure is expected to be individually below 10% of the ADI for any European consumer diet group (European Commission, 1997d).
Proposed
The available data are considered sufficient to derive an MRL proposal of 0.2 mg/kg and MRL proposal of 0.3 mg/kg, as well as risk assessment values for the intended SEU use on kaki/Japanese persimmon and indoor use on cultivated fungi, respectively (see Appendix B.1.2.1). In Section 3 EFSA assessed whether residues on these commodities resulting from the intended uses are likely to pose a consumer health risk.
RESIDUES IN LIVESTOCK
As the commodities under consideration are not normally fed to livestock, the nature and magnitude of fluxapyroxad residues in livestock are not assessed in the framework of both applications.
CONSUMER RISK ASSESSMENT
EFSA performed a dietary risk assessment using revision 3.1 of the EFSA PRIMo (EFSA, 2018, 2019). This exposure assessment model contains food consumption data for different sub-groups of the EU population and allows the acute and chronic exposure assessment to be performed in accordance with the internationally agreed methodology for pesticide residues (FAO, 2016).
For the products of animal origin, the calculation is based on the STMR values and highest residue levels (HR values) derived according to the residue definition for enforcement (FAO, 2013), multiplied by the relevant conversion factors (CFrisk) derived by EFSA from ruminant and poultry feeding studies to accommodate for the risk assessment residue definition (EFSA, 2011, 2020a).
The toxicological reference values for fluxapyroxad used in the risk assessment (i.e. ADI of 0.02 mg/kg bw per day and ARfD of 0.25 mg/kg bw values) were derived in the framework of the EU pesticides peer review (European Commission, 2012). The metabolite (M700F008), which is included in the residue definition for risk assessment in products of animal origin, was concluded to be of similar toxicity as the parent a.s.
Short-term (acute) dietary risk assessment
The short-term exposure assessment was performed in accordance with the internationally agreed methodology and focused on the commodities assessed in these applications (FAO, 2016). The calculations were based on the HR (expressed according to the residue definition for risk assessment) derived from supervised field trials, and the complete list of input values can be found in Appendix D.1. The short-term exposure did not exceed the ARfD for any of the commodities assessed in these applications.
Long-term (chronic) dietary risk assessment
In the framework of the MRL review, a comprehensive long-term exposure assessment was performed, taking into account the existing uses at EU level (EFSA, 2020a). EFSA updated the chronic risk assessment conducted in the framework of the MRL review with the STMR values derived from the residue trials submitted in support of an MRL application submitted after the MRL review (EFSA, 2020b), the STMR values from residue trials submitted in support of CXLs assessed by EFSA and implemented in the EU MRL legislation (FAO, 2013, 2015, 2018, 202010) and the STMR values from the residue trials submitted with the present MRL applications. The calculation was refined for bananas with residue observed in the pulp and for melons, pumpkins and watermelons with the peeling factor of 0.38 to take into account the edible portion of these commodities. Since residues from rotational crop field studies could contribute to exposure assessment, they were also considered in the calculations for the existing EU uses, when appropriate (more detail can be found in Appendix B.1.2.2.(c) of ‘Summary of residues data from the combined primary uses and rotational crops’ EFSA, 2020a). The input values used in the exposure calculations are summarised in Appendix D.1.
Exceedances of the ADI are not indicated for any of the consumer diet groups. The highest estimated long-term dietary exposure is reported for the NL toddler diet, representing up to 73% of the ADI of fluxapyroxad. The contribution of residues expected in kaki/Japanese persimmons and cultivated fungi to the overall long-term exposure accounted for 0.003% and 0.09% of the ADI, respectively (see Appendix B.3).
The contribution of residues expected in the commodities assessed in these applications to the overall long-term exposure is presented in more detail in Appendix B.3. EFSA concluded that the long-term intake of residues of fluxapyroxad resulting from the existing and the intended uses is unlikely to present a risk to consumer health. The long-term consumer risk assessment is indicative, pending the submission of the confirmatory data requested under the MRL review.
It is noted that the EU pesticides peer review of the renewal of approval of the a.s. fluxapyroxad in accordance with Regulation (EC) No 1107/2009 is to be initiated in the near future, and therefore the conclusions reported in this reasoned opinion might need to be reconsidered in the light of the outcome of the peer review.
For further details on the exposure calculations, a screenshot of the Report sheet of the PRIMo is presented in Appendix C.
CONCLUSION AND RECOMMENDATIONS
The data submitted in support of these MRL applications were found to be sufficient to derive a MRL proposal of 0.2 mg/kg for kaki/Japanese persimmons by extrapolation from residue trials on apples and a MRL proposal of 0.3 mg/kg for cultivated mushrooms.
EFSA concluded that the proposed uses of fluxapyroxad on kaki/Japanese persimmons (SEU use) and cultivated mushrooms (indoor use) will not result in a consumer exposure exceeding the toxicological reference values and therefore are unlikely to pose a risk to consumers' health. The long-term consumer risk assessment is indicative, pending the submission of the confirmatory data requested under the MRL review.
The MRL recommendations are summarised in Appendix B.4.
- a.s.
- active substance
- ADI
- acceptable daily intake
- ARfD
- acute reference dose
- BBCH
- growth stages of mono- and dicotyledonous plants
- bw
- body weight
- CCPR
- Codex Committee on Pesticide Residues
- CF
- conversion factor for enforcement to risk assessment residue definition
- CIPAC
- Collaborative International Pesticide Analytical Council
- CXL
- Codex maximum residue limit
- DALA
- days after last application
- DAR
- draft assessment report
- DAT
- days after treatment
- EMS
- evaluating Member State
- FAO
- Food and Agriculture Organization of the United Nations
- GAP
- Good Agricultural Practice
- HPLC
- high performance liquid chromatography
- HPLC-MS
- high performance liquid chromatography with mass spectrometry
- HPLC-MS/MS
- high performance liquid chromatography with tandem mass spectrometry
- HR
- highest residue
- IEDI
- international estimated daily intake
- IESTI
- international estimated short-term intake
- ILV
- independent laboratory validation
- IUPAC
- International Union of Pure and Applied Chemistry
- JMPR
- Joint FAO/WHO Meeting on Pesticide Residues
- LOQ
- limit of quantification
- MRL
- maximum residue level
- MS
- Member States
- NEU
- northern European Union
- OECD
- Organisation for Economic Co-operation and Development
- PBI
- plant-back interval
- PHI
- pre-harvest interval
- PRIMo
- (EFSA) Pesticide Residues Intake Model
- QuEChERS
- Quick, Easy, Cheap, Effective, Rugged and Safe (analytical method)
- RAC
- raw agricultural commodity
- RMS
- rapporteur Member State
- SC
- suspension concentrate
- SEU
- southern European Union
- STMR
- supervised trials median residue
- TRR
- total radioactive residue
- WHO
- World Health Organization
ABBREVIATIONS
ACKNOWLEDGEMENTS
EFSA wishes to thank: Stathis Anagnos, Mavriou Galini, Matteo Lazzari and Elena Taglianini for the support provided to this scientific output.
CONFLICT OF INTEREST
If you wish to access the declaration of interests of any expert contributing to an EFSA scientific assessment, please contact
REQUESTOR
European Commission
QUESTION NUMBERS
EFSA-Q-2023-00108; EFSA- Q-2022-00877
COPYRIGHT FOR NON-EFSA CONTENT
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APPENDIX A - Summary of intended GAP triggering the amendment of existing EU MRLs
Crop and/or situation | NEU, SEU, MS or country | F G or I (a) | Pests or Group of pests controlled | Preparation | Application | Application rate per treatment | PHI (days)d | Remarks | |||||||
Type b | Conc. a.s. (g/L) | Method kind | Range of growth stages & seasonc | Number min-max | Interval between application (days) min–max | kg a.s./hL min-max | Water (L/ha) min-max | Rate min-max | Unit | ||||||
Kaki/Japanese persimmons | SEU | F |
Alternaria spp. Mycosphaerella nawae |
SC | 300 | Foliar spray | 53–81 | 1–3 | 7 | 0.006–0.045 | 200–1500 | 0.09 | kg a.i./ha | 35 |
Spain (2023) Max. annual a.s.: 270 g/ha |
Cultivated fungi | EU | I |
Verticillium fungicola (VERTFU) Dactylium dendroïdes (DACYDE) |
SC | 300 | Spraying | 2–9 days after cover-up | 1 | – | 0.4 | 1500 | 6.0 | kg a.i./ha | 10 |
Ireland (2023) Cultivated in substrate |
APPENDIX B - List of end points
Residues in plants
Nature of residues and analytical methods for enforcement purposes in plant commodities
Metabolism studies, analytical methods and residue definitions in plants
Primary crops (available studies) | Crop groups | Crops | Applications | Sampling | Comment/Source |
Fruit crops | Tomato | Foliar, 3 × 100 g a.s./ha, interval 7 days | 3 DALA | Radiolabelled fluxapyroxad: aniline and pyrazole rings (EFSA, 2012) | |
Cereals/grass | Wheat | Foliar, 2 × 125 g a. s./ha, BBCH 30–35, 69 | 36 DAT, 4, 34–35 DALA | Radiolabelled fluxapyroxad: aniline and pyrazole rings (EFSA, 2012) | |
Seed treatment, 1 × 75 g a.s/100 kg (equivalent to 135 g a.s./ha) | 93, 112, 161 DAT | Radiolabelled fluxapyroxad: aniline and pyrazole rings (EFSA, 2015) | |||
Pulses/oilseeds | Soyabean | Foliar, 3 × 60 g a. s./ha, BBCH 16–17, 51–59, 71–75 | 0 DAT, 34 DALA | Radiolabelled fluxapyroxad: aniline and pyrazole rings (EFSA, 2012) | |
Rotational crops (available studies) | Crop groups | Crop(s) | Application(s) | PBI (DAT) | Comment/Source |
Root/tuber crops | White radish | Bare soil, 1 × 250 g a.s./ha | 30, 120/149, 365 | Studies with radiolabelled fluxapyroxad: aniline and pyrazole rings (EFSA, 2012) | |
Leafy crops | Spinach | Bare soil, 1 × 250 g a.s./ha | 30, 120/149, 365 | ||
Cereal (small grain) | Wheat | Bare soil, 1 × 250 g a.s./ha | 30, 120/149, 365 | ||
Processed commodities (hydrolysis study) | Conditions | Stable? | Comment/Source | ||
Pasteurisation (20 min, 90°C, pH 4) | Yes | EFSA (2012) | |||
Baking, brewing and boiling (60 min, 100°C, pH 5) | Yes | EFSA (2012) | |||
Sterilisation (20 min, 120°C, pH 6) | Yes | EFSA (2012) |
Stability of residues in plants
Plant products (available studies) | Category | Commodity | T (°C) | Stability period | Compounds covered | Comment/Source | |
Value | Unit | ||||||
High water content | Apple, tomato, potato | −20 | 24 | Months | Fluxapyroxad | EFSA (2012) | |
High oil content | Soybean, avocado | −20 | 24 | Months | Fluxapyroxad | EFSA (2012) | |
High protein content | Dried pea | −20 | 24 | Months | Fluxapyroxad | EFSA (2012) | |
High acid content | Grape, Lemon | –20 | 24 | Months | Fluxapyroxad | EFSA (2012) | |
Dry/High starch | Cereal grain | –20 | 24 | Months | Fluxapyroxad | EFSA (2012) |
Magnitude of residues in plants
Summary of residues data from the supervised residue trials
Commodity | Regiona | Residue levels observed in the supervised residue trials (mg/kg) | Comments/Source | Calculated MRL (mg/kg) | HRb (mg/kg) | STMRc (mg/kg) | CFd |
Kaki/Japanese persimmons | SEU | 0.012; 0.024; 0.028; 0.031; 0.047; 0.050; 0.067; 0.10 |
Residue trials on apples compliant with GAP on kaki already assessed by EFSA (EFSA, 2020a) Extrapolation to kaki/Japanese persimmons possible |
0.2 | 0.10 | 0.039 | n.a. |
Cultivated fungi | EU | 0.052, 0.066, 0.08, 0.093 | Residue trials on cultivated fungi compliant with GAP | 0.3 | 0.093 | 0.073 | n.a. |
Residues in rotational crops
Processing factors
No processing studies were submitted in the framework of the present MRL applications.
Residues in livestock
Not relevant.
Consumer risk assessment
Recommended MRLs
Codea | Commodity | Existing EU MRL (mg/kg) | Proposed EU MRL (mg/kg) | Comment/justification |
Enforcement residue definition: FluxapyroxadF | ||||
0161060 | Kaki/Japanese persimmons | 0.01* | 0.2 | The submitted data are sufficient to derive an MRL proposal for the intended SEU use by extrapolation from residue trials on apples. Risk for consumers unlikely |
0280010 | Cultivated fungi | 0.01* | 0.3 | The submitted data are sufficient to derive an MRL proposal for the intended indoor EU use. Risk for consumers unlikely |
APPENDIX C - Pesticide Residue Intake Model (PRIMo)
APPENDIX D - Input values for the exposure calculations
Consumer risk assessment
Commodity | Existing/Proposed MRL (mg/kg) | Source | Chronic risk assessment | Acute risk assessment | ||
Input valuea (mg/kg) | Comment | Input valuea (mg/kg) | Commentb | |||
Risk assessment residue definition: FluxapyroxadF | ||||||
Grapefruits | 0.6 | FAO (2020) | 0.15 | STMR-RAC | 0.27 | HR-RAC |
Oranges | 1.5 | FAO (2020) | 0.395 | STMR-RAC | 0.59 | HR-RAC |
Lemons | 1 | FAO (2020) | 0.38 | STMR-RAC | 0.46 | HR-RAC |
Limes | 1 | FAO (2020) | 0.38 | STMR-RAC | 0.46 | HR-RAC |
Mandarins | 1 | FAO (2020) | 0.38 | STMR-RAC | 0.46 | HR-RAC |
Almonds | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Brazil nuts | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Cashew nuts | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Chestnuts | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Coconuts | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Hazelnuts/cobnuts | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Macadamia | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Pecans | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Pine nut kernels | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Pistachios | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Walnuts | 0.04 | FAO (2015) | 0.01 | STMR-RAC | 0.03 | HR-RAC |
Other tree nuts | 0.04 | FAO (2015) | 0.01 | STMR-RAC | ||
Apples | 0.9 | FAO (2013) | 0.3 | STMR-RAC | 0.47 | HR-RAC |
Pears | 0.9 | FAO (2013) | 0.3 | STMR-RAC | 0.47 | HR-RAC |
Quinces | 0.9 | FAO (2013) | 0.3 | STMR-RAC | 0.47 | HR-RAC |
Medlar | 0.9 | FAO (2013) | 0.3 | STMR-RAC | 0.47 | HR-RAC |
Loquats/Japanese medlars | 0.9 | FAO (2013) | 0.3 | STMR-RAC | 0.47 | HR-RAC |
Other pome fruit | 0.9 | FAO (2013) | 0.3 | STMR-RAC | ||
Apricots | 1.5 | FAO (2015) | 0.44 | STMR-RAC | 0.63 | HR-RAC |
Cherries (sweet) | 3 | EFSA (2020a) | 0.555 | STMR-RAC | 1.86 | HR-RAC |
Peaches | 1.5 | EFSA (2020a) | 0.44 | STMR-RAC | 0.63 | HR-RAC |
Plums | 1.5 | EFSA (2020a) | 0.435 | STMR-RAC | 0.95 | HR-RAC |
Table grapes | 3 | FAO (2015) | 0.47 | STMR-RAC | 1.4 | HR-RAC |
Wine grapes | 3 | FAO (2015) | 0.47 | STMR-RAC | 1.4 | HR-RAC |
Strawberries | 4 | EFSA (2020a) | 0.815 | STMR-RAC | 2.34 | HR-RAC |
Blueberries | 7 | EFSA (2020a) | 2.39 | STMR-RAC | 3.77 | HR-RAC |
Kumquats | 1 | FAO (2020) | 0.38 | STMR-RAC | 0.46 | HR-RAC |
Kaki/Japanese persimmons | 0.2 | Intended use | 0.039 | STMR-RAC | 0.1 | HR-RAC |
Bananas | 3 | FAO (2015) | 0.55 | STMR-RAC pulp | 0.1 | HR-RAC pulp |
Mangoes | 0.7 | EFSA (2020a) | 0.18 | STMR-RAC | 0.37 | HR-RAC |
Papayas | 1 | FAO (2018) | 0.054 | STMR-RAC | 0.51 | HR-RAC |
Potatoesd | 0.3 | EFSA (2020a) | 0.09 | STMR-RAC | 0.12 | HR-RAC |
Cassava roots/maniocd | 0.2 | EFSA (2020a) | 0.2 | MRL | 0.08 | HR-RAC |
Sweet potatoesd | 0.2 | EFSA (2020a) | 0.03 | STMR-RAC | 0.08 | HR-RAC |
Yamsd | 0.2 | EFSA (2020a) | 0.03 | STMR-RAC | 0.08 | HR-RAC |
Arrowrootsd | 0.2 | EFSA (2020a) | 0.03 | STMR-RAC | 0.08 | HR-RAC |
Other tropical root and tuber vegetablesd | 0.2 | EFSA (2020a) | 0.03 | STMR-RAC | ||
Beetrootsd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Carrotsd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Celeriacs/turnip rooted celeriesd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Horseradishesd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Jerusalem artichokesd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Parsnipsd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Parsley roots/Hamburg roots parsleyd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Radishesd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Salsifiesd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Swedes/rutabagasd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Turnipsd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | 0.5 | HR-RAC |
Other root and tuber vegetablesd | 0.9 | EFSA (2020b) | 0.085 | STMR-RAC | ||
Garlicd | 0.2 | EFSA (2020a) | 0.03 | STMR-RAC | 0.08 | HR-RAC |
Onionsd | 0.2 | EFSA (2020a) | 0.03 | STMR-RAC | 0.08 | HR-RAC |
Shallotsd | 0.2 | EFSA (2020a) | 0.03 | STMR-RAC | 0.08 | HR-RAC |
Spring onions/green onions and Welsh onionsd | 0.7 | EFSA (2020a) | 0.185 | STMR-RAC | 0.42 | HR-RAC |
Tomatoes | 0.6 | FAO (2013) | 0.07 | STMR-RAC | 0.44 | HR-RAC |
Sweet peppers/bell peppers | 0.6 | FAO (2013) | 0.07 | STMR-RAC | 0.44 | HR-RAC |
Aubergines/egg plants | 0.6 | FAO (2013) | 0.07 | STMR-RAC | 0.44 | HR-RAC |
Okra/lady's fingers | 0.6 | FAO (2013) | 0.07 | STMR-RAC | 0.44 | HR-RAC |
Other solanacea | 0.6 | FAO (2013) | 0.07 | STMR-RAC | ||
Cucumbers | 0.2 | EFSA (2020a) | 0.05 | STMR-RAC | 0.11 | HR-RAC |
Gherkins | 0.2 | EFSA (2020a) | 0.05 | STMR-RAC | 0.11 | HR-RAC |
Courgettes | 0.2 | EFSA (2020a) | 0.05 | STMR-RAC | 0.11 | HR-RAC |
Other cucurbits–edible peel | 0.2 | EFSA (2020a) | 0.05 | STMR-RAC | ||
Melons | 0.15 | EFSA (2020a) | 0.017 | STMR-RAC*PeF | 0.027 | HR-RAC*PeF |
Pumpkins | 0.15 | EFSA (2020a) | 0.017 | STMR-RAC*PeF | 0.027 | HR-RAC*PeF |
Watermelons | 0.15 | EFSA (2020a) | 0.017 | STMR-RAC*PeF | 0.027 | HR-RAC*PeF |
Other cucurbits–inedible peel | 0.15 | EFSA (2020a) | 0.0171 | STMR-RAC*PeF | ||
Sweet corn | 0.15 | EFSA (2020a) | 0.01 | STMR-RAC | 0.09 | HR-RAC |
Broccolid | 2 | EFSA (2020a) | 0.28 | STMR-RAC | 1.27 | HR-RAC |
Cauliflowersd | 0.2 | EFSA (2020a) | 0.07 | STMR-RAC | 0.14 | HR-RAC |
Brussels sproutsd | 0.4 | EFSA (2020a) | 0.05 | STMR-RAC | 0.14 | HR-RAC |
Head cabbagesd | 0.5 | EFSA (2020a) | 0.01 | STMR-RAC | 0.27 | HR-RAC |
Chinese cabbages/pe-tsaid | 4 | EFSA (2020a) | 0.895 | STMR-RAC | 1.9 | HR-RAC |
Kalesd | 0.15 | EFSA (2020a) | 0.01 | STMR-RAC | 0.06 | HR-RAC |
Kohlrabiesd | 0.15 | EFSA (2020a) | 0.01 | STMR-RAC | 0.06 | HR-RAC |
Lamb's lettuce/corn saladsd | 4 | EFSA (2020a) | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Lettucesd | 4 | EFSA (2020a) | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Escaroles/broad-leaved endivesd | 4 | EFSA (2020a) | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Cress and other sprouts and shootsd | 4 | Reg. (EU) 2018/685 | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Land cressd | 4 | Reg. (EU) 2018/685 | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Roman rocket/rucolad | 4 | EFSA (2020a) | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Red mustardsd | 4 | Reg. (EU) 2018/685 | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Baby leaf crops (including brassica species)d | 4 | Reg. (EU) 2018/685 | 0.245 | STMR-RAC | 1.8 | HR-RAC |
Other lettuce and other salad plantsd,f | 4 | Reg. (EU) 2018/685 | 0.245 | STMR-RAC | ||
Spinachesd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Purslanesd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Chards/beet leavesd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Witloofs/Belgian endivesd | 6 | EFSA (2020a) | 1.95 | STMR-RAC | 2.5 | HR-RAC |
Chervild | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Chivesd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Celery leaves | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Parsleyd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Saged | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Rosemaryd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Thymed | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Basil and edible flowersd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Laurel/bay leavesd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Tarragond | 3 | EFSA (2020a) | 0.055 | STMR-RAC | 1.44 | HR-RAC |
Other herbsd | 3 | EFSA (2020a) | 0.055 | STMR-RAC | ||
Beans (with pods) | 2 | FAO (2013) | 0.65 | STMR-RAC | 0.74 | HR-RAC |
Beans (without pods) | 0.09 | FAO (2013) | 0.03 | STMR-RAC | 0.04 | HR-RAC |
Peas (with pods) | 2 | FAO (2013) | 0.65 | STMR-RAC | 0.74 | HR-RAC |
Peas (without pods)e | 0.3 | Reg. (EU) 2021/644 | 0.3 | MRL | 0.3 | MRL |
Cardoonsd | 9 | EFSA (2020a) | 1.675 | STMR-RAC | 5.15 | HR-RAC |
Celeriesd | 9 | EFSA (2020a) | 1.675 | STMR-RAC | 5.15 | HR-RAC |
Florence fennelsd | 9 | EFSA (2020a) | 1.675 | STMR-RAC | 5.15 | HR-RAC |
Globe artichokesd | 0.4 | EFSA (2020a) | 0.08 | STMR-RAC | 0.19 | HR-RAC |
Leeksd | 0.7 | EFSA (2020a) | 0.185 | STMR-RAC | 0.42 | HR-RAC |
Rhubarbsd | 9 | EFSA (2020a) | 1.675 | STMR-RAC | 5.15 | HR-RAC |
Cultivated fungi | 0.3 | Intended use | 0.073 | STMR-RAC | 0.093 | HR-RAC |
Beansd | 0.3 | FAO (2013) | 0.04 | STMR-RAC | 0.04 | STMR-RAC |
Lentilsd | 0.4 | EFSA (2020a) | 0.04 | STMR-RAC | 0.04 | STMR-RAC |
Peasd | 0.4 | EFSA (2020a) | 0.04 | STMR-RAC | 0.04 | STMR-RAC |
Lupins/lupini beansd | 0.2 | EFSA (2020a) | 0.01 | STMR-RAC | 0.01 | STMR-RAC |
Linseeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Peanuts/groundnuts | 0.01 | EFSA (2020a) | 0.01 | STMR-RAC | 0.01 | STMR-RAC |
Poppy seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Sesame seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Sunflower seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Rapeseeds/canola seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Soyabeans | 0.15 | EFSA (2020a) | 0.01 | STMR-RAC | 0.01 | STMR-RAC |
Mustard seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Cotton seeds | 0.5 | FAO (2018) | 0.08 | STMR-RAC | 0.08 | STMR-RAC |
Pumpkin seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Safflower seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Borage seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Gold of pleasure seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Hemp seeds | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Castor beans | 0.9 | EFSA (2020a) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Oil palm fruits | 0.8 | FAO (2013) | 0.09 | STMR-RAC | 0.09 | STMR-RAC |
Kapok | 0.8 | FAO (2013) | 0.09 | STMR-RAC | 0.81 | HR-RAC |
Barleyd | 3 | EFSA (2020a) | 0.54 | STMR-RAC | 0.54 | STMR-RAC |
Maize/cornd | 0.01 | EFSA (2020a) | 0.01 | STMR-RAC | 0.01 | STMR-RAC |
Oatd | 3 | EFSA (2020a) | 0.54 | STMR-RAC | 0.54 | STMR-RAC |
Riced | 5 | EFSA (2020a) | 0.865 | STMR-RAC | 0.865 | STMR-RAC |
Ryed | 0.4 | EFSA (2020a) | 0.115 | STMR-RAC | 0.115 | STMR-RAC |
Sorghumd | 0.8 | EFSA (2020a) | 0.19 | STMR-RAC | 0.19 | STMR-RAC |
Wheatd | 0.4 | EFSA (2020a) | 0.115 | STMR-RAC | 0.115 | STMR-RAC |
Coffee beans | 0.2 | EFSA (2020b) | 0.03 | STMR-RAC | 0.03 | STMR-RAC |
Strawberry leavesd | 30 | EFSA (2020a) | 0.55 | STMR-RAC | 14.4 | HR-RAC |
Rooibosd | 30 | EFSA (2020a) | 0.55 | STMR-RAC | 14.4 | HR-RAC |
Mate/matéd | 30 | EFSA (2020a) | 0.55 | STMR-RAC | 14.4 | HR-RAC |
Other herbal infusions (dried leaves)d | 30 | EFSA (2020a) | 0.55 | STMR-RAC | ||
Valerian rootd | 2 | EFSA (2020a) | 0.32 | STMR-RAC | 1.04 | HR-RAC |
Ginseng rootd | 2 | EFSA (2020a) | 0.32 | STMR-RAC | 1.04 | HR-RAC |
Other herbal infusions (dried roots)d | 2 | EFSA (2020a) | 0.32 | STMR-RAC | ||
Sugar beet rootsd | 0.4 | EFSA (2020a) | 0.12 | STMR-RAC | 0.15 | HR-RAC |
Sugar canesd | 3 | EFSA (2020a) | 0.26 | STMR-RAC | 1.34 | HR-RAC |
Chicory rootsd | 0.3 | EFSA (2020a) | 0.07 | STMR-RAC | 0.21 | HR-RAC |
Swine: Muscle/meatc | 0.015 | FAO (2013) | 0.026 | STMR-RAC*CF | 0.062 | HR-RAC*CF |
Swine: Fat tissue | 0.2 | FAO (2013) | 0.048 | STMR-RAC*CF | 0.180 | HR-RAC*CF |
Swine: Liver | 0.1 | FAO (2013) | 0.083 | STMR-RAC*CF | 0.310 | HR-RAC*CF |
Swine: Kidney | 0.1 | FAO (2013) | 0.082 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Swine: Edible offal (other than liver and kidney) | 0.2 | Reg. (EU) 2021/644 | 0.048 | STMR-RAC*CF | 0.180 | HR-RAC*CF |
Bovine: Muscle/meatc | 0.015 | EFSA (2020a), FAO (2013) | 0.025 | STMR-RAC*CF | 0.062 | HR-RAC*CF |
Bovine: Fat tissue | 0.2 | EFSA (2020a), FAO (2013) | 0.047 | STMR-RAC*CF | 0.18 | HR-RAC*CF |
Bovine: Liver | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Bovine: Kidney | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Bovine: Edible offal (other than liver and kidney) | 0.2 | Reg. (EU) 2021/644 | 0.048 | STMR-RAC*CF | 0.180 | HR-RAC*CF |
Sheep: Muscle/meatc | 0.015 | EFSA (2020a), FAO (2013) | 0.025 | STMR-RAC*CF | 0.062 | HR-RAC*CF |
Sheep: Fat tissue | 0.2 | EFSA (2020a), FAO (2013) | 0.047 | STMR-RAC*CF | 0.18 | HR-RAC*CF |
Sheep: Liver | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Sheep: Kidney | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Sheep: Edible offal (other than liver and kidney) | 0.2 | Reg. (EU) 2021/644 | 0.047 | STMR-RAC*CF | 0.181 | HR-RAC*CF |
Goat: Muscle/meatc | 0.015 | EFSA (2020a), FAO (2013) | 0.025 | STMR-RAC*CF | 0.062 | HR-RAC*CF |
Goat: Fat tissue | 0.2 | EFSA (2020a), FAO (2013) | 0.047 | STMR-RAC*CF | 0.18 | HR-RAC*CF |
Goat: Liver | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Goat: Kidney | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Goat: Edible offal (other than liver and kidney) | 0.2 | Reg. (EU) 2021/644 | 0.047 | STMR-RAC*CF | 0.181 | HR-RAC*CF |
Equine: Muscle/meatc | 0.015 | EFSA (2020a), FAO (2013) | 0.025 | STMR-RAC*CF | 0.062 | HR-RAC*CF |
Equine: Fat tissue | 0.2 | EFSA (2020a), FAO (2013) | 0.047 | STMR-RAC*CF | 0.18 | HR-RAC*CF |
Equine: Liver | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Equine: Kidney | 0.1 | EFSA (2020a), FAO (2013) | 0.081 | STMR-RAC*CF | 0.31 | HR-RAC*CF |
Poultry: Muscle/meatc | 0.02 | EFSA (2020a), FAO (2013) | 0.04 | STMR-RAC*CF | 0.048 | HR-RAC*CF |
Poultry: Fat tissue | 0.05 | EFSA (2020a), FAO (2013) | 0.022 | STMR-RAC*CF | 0.05 | HR-RAC*CF |
Poultry: Liver | 0.02 | EFSA (2020a), FAO (2013) | 0.022 | STMR-RAC*CF | 0.034 | HR-RAC*CF |
Poultry: Edible offal (other than liver and kidney) | 0.05 | Reg. (EU) 2021/644 | 0.022 | STMR-RAC*CF | 0.05 | HR-RAC*CF |
Other farmed animals: Muscle/meatc | 0.015 | EFSA (2020a), FAO (2013) | 0.2 | MRL | 0.052 | MRL |
Other farmed animals: Fat tissue | 0.2 | EFSA (2020a), FAO (2013) | 0.2 | MRL | 0.2 | MRL |
Other farmed animals: Liver | 0.1 | EFSA (2020a), FAO (2013) | 0.1 | MRL | 0.1 | MRL |
Other farmed animals: Kidney | 0.1 | EFSA (2020a), FAO (2013) | 0.1 | MRL | 0.1 | MRL |
Other farmed animals: Edible offal (other than liver and kidney) | 0.2 | Reg.(EU) 2021/644 | 0.2 | MRL | 0.2 | MRL |
Milk: Cattle | 0.02 | FAO (2013) | 0.004 | STMR-RAC*CF | 0.004 | STMR-RAC*CF |
Milk: Sheep | 0.02 | FAO (2013) | 0.004 | STMR-RAC*CF | 0.004 | STMR-RAC*CF |
Milk: Goat | 0.02 | FAO (2013) | 0.004 | STMR-RAC*CF | 0.004 | STMR-RAC*CF |
Milk: Horse | 0.02 | FAO (2013) | 0.004 | STMR-RAC*CF | 0.004 | STMR-RAC*CF |
Milk: Others | 0.02 | FAO (2013) | 0.004 | STMR-RAC*CF | 0.004 | STMR-RAC*CF |
Eggs: Chicken | 0.02 | FAO (2013) | 0.008 | STMR-RAC*CF | 0.023 | HR-RAC*CF |
Eggs: Duck | 0.02 | FAO (2013) | 0.008 | STMR-RAC*CF | 0.023 | HR-RAC*CF |
Eggs: Goose | 0.02 | FAO (2013) | 0.008 | STMR-RAC*CF | 0.023 | HR-RAC*CF |
Eggs: Quail | 0.02 | FAO (2013) | 0.008 | STMR-RAC*CF | 0.023 | HR-RAC*CF |
Eggs: Others | 0.02 | FAO (2013) | 0.008 | STMR-RAC*CF |
APPENDIX E - Used compound codes
Code/trivial namea | IUPAC name/SMILES notation/InChiKeyb | Structural formulac |
Fluxapyroxad | 3-(difluoromethyl)-1-methyl-N-(3′,4′,5′-trifluoro[1,1′-biphenyl]-2-yl)-1H-pyrazole-4-carboxamide |
|
FC(F)c1nn(C)cc1C(=O)Nc1ccccc1c1cc(F)c(F)c(F)c1 | ||
SXSGXWCSHSVPGB-UHFFFAOYSA-N | ||
M700F002 | 3-(difluoromethyl)-1H-pyrazole-4-carboxylic acid |
|
OC(=O)c1c[NH]nc1C(F)F | ||
IGQNDARULCASRN-UHFFFAOYSA-N | ||
M700F008 | 3-(difluoromethyl)-N-(3′,4′,5′-trifluorobiphenyl-2-yl)-1H-pyrazole-4-carboxamide |
|
O=C(Nc1ccccc1c1cc(F)c(F)c(F)c1)c1c[NH]nc1C(F)F | ||
SYGSBKQBCWBROS-UHFFFAOYSA-N | ||
M700F048 | 3-(difluoromethyl)-1-(b-D-glucopyranosyloxy)-N-(3′,4′,5′-trifluorobiphenyl-2-yl)-1H-pyrazole-4-carboxamide (One example of several possible glycoside structures) |
|
Fc1cc(cc(F)c1F)c1ccccc1NC(=O)c1cn(nc1C(F)F)O[C@@H]1O[C@H](CO)[C@@H](O)[C@H](O)[C@H]1O | ||
KVTPNMBJCLTHFA-GWUZYQLFSA-N |
EFSA (European Food Safety Authority). (2011). Reasoned opinion on the setting of new MRLs for fluxapyroxad (BAS 700 F) in various commodities of plant and animal origin. EFSA Journal, 9(6), 2196. https://doi.org/10.2903/j.efsa.2011.2196
EFSA (European Food Safety Authority). (2012). Conclusion on the peer review of the pesticide risk assessment of the active substance fluxapyroxad (BAS 700 F). EFSA Journal, 10(1), 2522. https://doi.org/10.2903/j.efsa.2012.2522
EFSA (European Food Safety Authority). (2013). Scientific support for preparing an EU position for the 45th session of the codex committee on pesticide residues (CCPR). EFSA Journal, 11(7), 3312. https://doi.org/10.2903/j.efsa.2013.3312
EFSA (European Food Safety Authority). (2015). Reasoned opinion on the modification of the existing MRLs for fluxapyroxad in grapes and potatoes. EFSA Journal, 13(9), 4223. https://doi.org/10.2903/j.efsa.2015.4223
EFSA (European Food Safety Authority). (2016a). Reasoned opinion on setting of import tolerances for fluxapyroxad in various crops. EFSA Journal, 14(3), 4404. https://doi.org/10.2903/j.efsa.2016.4404
EFSA (European Food Safety Authority). (2016b). Scientific report of EFSA on scientific support for preparing an EU position in the 48th session of the codex committee on pesticide residues (CCPR). EFSA Journal, 14(8), 4571. https://doi.org/10.2903/j.efsa.2016.4571
EFSA (European Food Safety Authority), Brancato, A., Brocca, D., De Lentdecker, C., Erdos, Z., Ferreira, L., Greco, L., Janossy, J., Jarrah, S., Kardassi, D., Leuschner, R., Lythgo, C., Medina, P., Miron, I., Molnar, T., Nougadere, A., Pedersen, R., Reich, H., Sacchi, A., … Villamar‐Bouza, L. (2017). Reasoned opinion on the modification of the existing maximum residue levels for fluxapyroxad in various crops. EFSA Journal, 15(9), 4975. https://doi.org/10.2903/j.efsa.2017.4975
EFSA (European Food Safety Authority), Brancato, A., Brocca, D., Ferreira, L., Greco, L., Jarrah, S., Leuschner, R., Medina, P., Miron, I., Nougadere, A., Pedersen, R., Reich, H., Santos, M., Stanek, A., Tarazona, J., Theobald, A., & Villamar‐Bouza, L. (2018). Guidance on use of EFSA pesticide residue intake model (EFSA PRIMo revision 3). EFSA Journal, 16(1), 5147. https://doi.org/10.2903/j.efsa.2018.5147
EFSA (European Food Safety Authority), Anastassiadou, M., Brancato, A., Carrasco Cabrera, L., Ferreira, L., Greco, L., Jarrah, S., Kazocina, A., Leuschner, R., Magrans, J. O., Miron, I., Pedersen, R., Raczyk, M., Reich, H., Ruocco, S., Sacchi, A., Santos, M., Stanek, A., Tarazona, J., … Verani, A. (2019a). Pesticide residue intake model‐ EFSA PRIMo revision 3.1 (update of EFSA PRIMo revision 3). EFSA Supporting Publication, 16(3), EN‐1605. https://doi.org/10.2903/sp.efsa.2019.EN‐1605
EFSA (European Food Safety Authority). (2019b). Scientific report on scientific support for preparing an EU position in the 51st session of the codex committee on pesticide residues (CCPR). EFSA Journal, 17(7), 5797. https://doi.org/10.2903/j.efsa.2019.5797
EFSA (European Food Safety Authority), Anastassiadou, M., Bernasconi, G., Brancato, A., Carrasco Cabrera, L., Greco, L., Jarrah, S., Kazocina, A., Leuschner, R., Magrans, J. O., Miron, I., Nave, S., Pedersen, R., Reich, H., Rojas, A., Sacchi, A., Santos, M., Stanek, A., Theobald, A., … Verani, A. (2020a). Reasoned opinion on the review of the existing maximum residue levels for fluxapyroxad according to Article 12 of regulation (EC) No 396/2005. EFSA Journal, 18(1), 5984. https://doi.org/10.2903/j.efsa.2020.5984
EFSA (European Food Safety Authority), Anastassiadou, M., Bernasconi, G., Brancato, A., Carrasco Cabrera, L., Greco, L., Jarrah, S., Kazocina, A., Leuschner, R., Magrans, J. O., Miron, I., Nave, S., Pedersen, R., Reich, H., Rojas, A., Sacchi, A., Santos, M., Stanek, A., Theobald, A., … Verani, A. (2020b). Reasoned opinion on the setting of import tolerances for fluxapyroxad in certain root crops and coffee beans. EFSA Journal, 18(1), 5950. https://doi.org/10.2903/j.efsa.2020.5950
EFSA (European Food Safety Authority). (2021). Scientific support for preparing an EU position for the 52nd session of the codex committee on pesticide residues (CCPR). EFSA Journal, 19(8), 6766. https://doi.org/10.2903/j.efsa.2021.6766
EFSA (European Food Safety Authority), Greco, L., Janossy, J., Jarrah, S., Kazocina, A., Magrans, J. O., & Reich, H. (2023). Guidance on the assessment of pesticide residues in rotational crops. EFSA Journal, 21(11), 8225. https://doi.org/10.2903/j.efsa.2023.8225
European Commission. (1997a). Appendix A. Metabolism and distribution in plants. 7028/IV/95‐rev., 22 July 1996.
European Commission. (1997b). Appendix B. General recommendations for the design, preparation and realization of residue trials. Annex 2. Classification of (minor) crops not listed in the Appendix of Council Directive 90/642/EEC. 7029/VI/95‐rev. 6, 22 July 1997.
European Commission. (1997c). Appendix C. Testing of plant protection products in rotational crops. 7524/VI/95‐rev. 2, 22 July 1997.
European Commission. (1997d). Appendix E. Processing studies. 7035/VI/95‐rev. 5, 22 July 1997.
European Commission. (1997e). Appendix F. Metabolism and distribution in domestic animals. 7030/VI/95‐rev. 3, 22 July 1997.
European Commission. (1997f). Appendix H. Storage stability of residue samples. 7032/VI/95‐rev. 5, 22 July 1997.
European Commission. (1997g). Appendix I. Calculation of maximum residue level and safety intervals.7039/VI/95 22 July 1997. As amended by the document: classes to be used for the setting of EU pesticide maximum residue levels (MRLs). SANCO 10634/2010, finalised in the Standing Committee on the Food Chain and Animal Health at its meeting of 23–24 March 2010.
European Commission. (2010). Classes to be used for the setting of EU pesticide Maximum Residue Levels (MRLs). SANCO 10634/2010‐rev. 0, Finalised in the Standing Committee on the Food Chain and Animal Health at its meeting of 23–24 March 2010.
European Commission. (2012). Review report for the active substance fluxapyroxad. Finalised in the Standing Committee on the Food Chain and Animal Health at its meeting on 1 June 2012 in view of the approval of fluxapyroxad as active substance in accordance with Regulation (EC) No 1107/2009. SANCO/10692/2012 Rev2, 25 March 2021, 8 pp.
European Commission. (2020). Technical guidelines on data requirements for setting maximum residue levels, comparability of residue trials and extrapolation on residue data on products from plant and animal origin. SANTE/2019/12752, 23 November 2020.
European Commission. (2021). Guidance Document on Pesticide Analytical Methods for Risk Assessment and Post‐approval Control and Monitoring Purposes. SANTE/2020/12830, Rev.1 24. February 2021.
European Commission. (2022). Technical Guideline on the Evaluation of Extraction Efficiency of Residue Analytical Methods. SANTE 2017/10632, Rev. 4, 23 February 2022.
FAO (Food and Agriculture Organization of the United Nations). (2013). Fluxapyroxad. In: Pesticide residues in food – 2012. Report of the Joint Meeting of the FAO Panel of Experts on Pesticide Residues in Food and the Environment and the WHO Expert Group on Pesticide Residues. FAO Plant Production and Protection Paper 215. 51 pp.
FAO (Food and Agriculture Organization of the United Nations). (2015). Fluxapyroxad. In: Pesticide residues in food – 2015. Report of the Joint Meeting of the FAO Panel of Experts on Pesticide Residues in Food and the Environment and the WHO Expert Group on Pesticide Residues. FAO Plant Production and Protection Paper 223. 647 pp.
FAO (Food and Agriculture Organization of the United Nations). (2016). Submission and evaluation of pesticide residues data for the estimation of Maximum Residue Levels in food and feed. Pesticide Residues. 3rd Ed. FAO Plant Production and Protection Paper 225, 298 pp.
FAO (Food and Agriculture Organization of the United Nations). (2018). Fluxapyroxad. In: Pesticide residues in food – 2018. Report of the Joint Meeting of the FAO Panel of Experts on Pesticide Residues in Food and the Environment and the WHO Expert Group on Pesticide Residues. FAO Plant Production and Protection Paper 234. 668 pp.
FAO (Food and Agriculture Organization of the United Nations). (2020). Fluxapyroxad. In: Pesticide residues in food −2019. Report of the Joint Meeting of the FAO Panel of Experts on Pesticide Residues in Food and the Environment and the WHO Expert Group on Pesticide Residues. FAO Plant Production and Protection Paper. 680 pp.
Ireland. (2023). Evaluation report on the modification of MRLs for fluxapyroxad in mushrooms. November 2023, revised in February 2024, 57 pp. www.efsa.europa.eu
OECD (Organisation for Economic Co‐operation and Development). (2011). OECD MRL calculator: Spreadsheet for single data set and spreadsheet for multiple data set, 2 march 2011. In: Pesticide Publications/Publications on Pesticide Residues. http://www.oecd.org
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Abstract
In accordance with Article 6 of Regulation (EC) No 396/2005, the applicant BASF SE submitted two requests to the competent national authority in Spain and Ireland to modify the existing maximum residue levels (MRLs) for the active substance fluxapyroxad in kaki/Japanese persimmons and in cultivated fungi, respectively. The data submitted in support of the requests were found to be sufficient to derive MRL proposals for kaki/Japanese persimmons and cultivated fungi. Adequate analytical methods for enforcement are available to control the residues of fluxapyroxad on the commodities under consideration at the validated LOQ of 0.01 mg/kg. Based on the risk assessment results, EFSA concluded that the short‐term and long‐term intake of residues resulting from the use of fluxapyroxad, according to the reported agricultural practices, is unlikely to present a risk to consumer health. The long‐term consumer risk assessment is indicative, pending the submission of the confirmatory data requested under the MRL review.
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