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55 results for “Pesticide residues”
Figure 1 in Organochlorine pesticide residues in feathers of four bird species from western part of Turkey
Figure 1. Specimen collecting locations from four geographical regions (A: Central Anatolia; B: Aegean; C: Mediterranean; D: Marmara; triangle: common buzzard, square; common kestrel; circle: common blackbird; ring: house sparrow) across Turkey.
Annexes to the EFSA external scientific report "Proposed prospective scenarios for cumulative risk assessment of pesticide residues"
<p>In the context of prospective cumulative risk assessment of pesticides, different options and scenarios for a tiered approach were investigated by means of 15 case studies for the cumulative assessment group associated with an effect on the motor division of the nervous system (CAG-NAM) and 15 case studies for the cumulative assessment group associated with an effect on hypothyroidism (CAG-TCF) (doi:10.2903/sp.efsa.2021.EN-6811). The results of the prospective exposure calculations are reported in the following annexes:</p> <p><strong>Annex A</strong>: Acute exposure calculations - CAG-NAM</p> <p><strong>Annex B</strong>: Chronic exposure calculations - CAG-TCF</p> <p><strong>Annex C</strong>: Results supporting the discussion on prospective acute scenarios - CAG-NAM</p> <p><strong>Annex D</strong>: Results supporting the discussion on prospective chronic scenarios - CAG-TCF</p> <p>The case studies reported above also include fictitious data, which were included for assessing the relevance of the various parameters in these calculations. The results of these case studies do not represent real estimates of exposure or risk, nor do they represent the formal outcome of a risk assessment.</p>
Supplementary digital data for "Widespread contamination of soils and vegetation with Current Use Pesticide residues along altitudinal gradients in a European Alpine valley"
<p>Supplementary digital data for the publication:</p> <p>Widespread contamination of soils and vegetation with Current Use Pesticide residues along altitudinal gradients in a European Alpine valley</p> <p>Data that was no publicly available but is used for Figure 1 - 3 in the manuscript is provided in this repository in addition to the raw data describing the occurrence in plant and soil matrices throughout the Vinschgau valley along the altitudinal transects.</p> <p> </p>
Retrospective cumulative dietary risk assessment of craniofacial alterations by residues of pesticides
<p>EFSA established cumulative assessment groups and conducted retrospective cumulative risk<br> assessments for two types of craniofacial alterations (alterations due to abnormal skeletal<br> development, head soft tissue alterations and brain neural tube defects) for 14 European populations<br> of women in childbearing age. Cumulative acute exposure calculations were performed by probabilistic<br> modelling using monitoring data collected by Member States in 2017, 2018 and 2019. A rigorous<br> uncertainty analysis was performed using expert knowledge elicitation. Considering all sources of<br> uncertainty, their dependencies and differences between populations, it was concluded with varying<br> degrees of certainty that the MOET resulting from cumulative exposure is above 100 for the two types<br> of craniofacial alterations. The threshold for regulatory consideration established by risk managers is<br> therefore not exceeded. Considering the severity of the effects under consideration, it was also<br> assessed whether the MOET is above 500. This was the case with varying levels of certainty for the<br> head soft tissue alterations and brain neural tube defects. However, for the alterations due to<br> abnormal skeletal development, it was found about as likely as not that the MOET is above 500 in<br> most populations. For two populations, it was even found more likely that the MOET is below 500.<br> These results were discussed in the light of the conservatism of the methodological approach.</p> <p>The indicators of craniofacial alterations, input and output data for the exposure assessment are reported in the following annexes:</p> <p>• Annex A – Indicators of craniofacial alterations collected for 85 selected active substances;<br> • Annex B1 – Input data for the exposure assessment of CAG-DACL;<br> • Annex B2 – Input data for the exposure assessment of CAG-DAH;<br> • Annex C1 – Output data for the Tier I exposure assessment of CAG-DAC;<br> • Annex C2 – Output data for the Tier I exposure assessment of CAG-DAH;<br> • Annex D1 – Output data for the Tier II exposure assessment of CAG-DAC;<br> • Annex D2 – Output data for the Tier II exposure assessment of CAG-DAH.</p>
APPENDIX D of the 2022 EU Report on Pesticide Residues
<p>Detailed information on the different control programmes, full list of samples exceeding the MRLs anonymised by sample code, analytical scope from the official laboratories reporting to EFSA data on pesticide residues, the HBGV and PF used in the risk assessment.</p> <p><br>Detailed information on deterministic and probabilistic risk assessment results.</p>
Figure 2 in Detection of enteropathogens and research of pesticide residues in Lactuca sativa from traditional and agroecological fairs
Figure 2. Difenoconazole calibration curve.
Italian results from the monitoring of pesticide residues in food
<p>This dataset contains the analytical results of pesticide residues measured in the food products analysed by the national competent authorities. Pesticide residues resulting from the use of plant protection products on crops that are used for food or feed production may pose a risk factor for public health. For this reason, a comprehensive legislative framework has been established in the European Union (EU), which defines rules for the approval of active substances used in plant protection products, the use of plant protection products and for pesticide residues in food. In order to ensure a high level of consumer protection, legal limits, so called “maximum residue levels” or briefly “MRLs”, are established in Regulation (EC) No 396/2005. EU-harmonised MRLs are set for all pesticides covering all types of food products. A default MRL of 0.01 mg/kg is applicable for pesticides not explicitly mentioned in the MRL legislation. Regulation (EC) No 396/2005 imposes on Member States the obligation to carry out controls to ensure that food placed on the market is compliant with the legal limits.</p> <p>A sample is considered <strong>free of quantifiable residues</strong> if the analytes were not present in concentrations at or above the limit of quantification (LOQ). The LOQ is the smallest concentration of an analyte that can be quantified with the analytical method used to analyse the sample. It is commonly defined as the minimum concentration of the analyte in the test sample that can be determined with acceptable precision and accuracy.</p> <p>If a sample <strong>contains quantifiable residues</strong> but within the legally permitted limit (maximum residue level, MRL), it is described as a sample with quantified residue levels within the legal limits (below or at the MRL)</p> <p>A sample is considered <strong>non-compliant</strong> with the legal limit (MRL), if the measured residue concentrations clearly exceed the legal limits, taking into account the measurement uncertainty. It is current practice that the uncertainty of the analytical measurement is taken into account before legal or administrative sanctions are imposed on food business operators for infringement of the MRL legislation.</p> <p> </p> <p><strong>REPORTING AUTHORITIES CONTRIBUTING TO EACH DATA COLLECTION:</strong></p> <p>MOPER_2023 - Ministry of Health</p> <p>MOPER_2022 - Ministry of Health</p> <p>MOPER_2021 - Ministry of Health</p> <p>MOPER_2020 - Ministry of Health</p> <p>MOPER_2019 - Ministry of Health</p> <p>MOPER_2018 - Ministry of Health</p> <p>MOPER_2017 - Ministry of Health</p> <p>MOPER_2016 - Ministry of Health</p> <p>MOPER_2015 - Ministry of Health</p> <p>MOPER_2014 - Ministry of Health</p> <p>MOPER_2013 - Ministry of Health</p> <p>MOPER_2012 - Ministry of Health</p> <p>MOPER_2011 - Ministry of Health</p> <p> </p> <p><strong>We are seeking feedback on our open data please complete the survey at the link below:<br>https://ec.europa.eu/eusurvey/runner/9344dfa0-f384-cb72-65f6-6c187a6d0f14</strong></p>
Milkweed plants bought at nurseries may expose monarch caterpillars to harmful pesticide residues
<p>The decline of monarch butterflies in both the eastern and western United States has garnered widespread public interest. Planting milkweeds, their larval host plants, has been promoted as one action individuals can take, but little is known with respect to potential pesticide contamination of store-bought milkweeds. In this study, we collected leaf samples from 235 milkweed plants purchased at 33 retail nurseries across the US to screen for pesticides. Across all samples, we detected 61 different pesticides with an average of 12.2 (±5.0) compounds per plant. While only 9 of these compounds have been experimentally tested on monarch caterpillars, 38 % of samples contained a pesticide above a concentration shown to have a sub-lethal effect for monarchs. We detected only a modest predictive ability of retailer size and milkweed species, and plants with labels advertising their value for wildlife did not have fewer pesticides at concentrations known to have a negative effect on monarchs. These results demonstrate the extensiveness of pesticide exposure within nursery milkweeds and the potential impacts on monarchs and other insects exposed to store-bought plants.</p>
Annexes on the 2021 EU report on pesticide residues
<p>Detailed information on the different control programmes, full list of samples exceeding the MRLs anonymised by sample code, analytical scope from the official laboratories reporting to EFSA data on pesticide residues, the HBGV and PF used in the risk assessment.</p> <p>Detailed information on deterministic and probabilistic risk assessment results.</p>
Milkweed plants bought at nurseries may expose monarch caterpillars to harmful pesticide residues
Open the record for dataset details and reuse information.
Supplementary digital data for Exposure of Insects to Current Use Pesticide Residues in Soil and Vegetation along Spatial and Temporal Distribution in Agricultural Sites
Open the record for dataset details and reuse information.
Dissipation of selected pesticide residues in grapes by using ozone enriched atmosphere
<p>Research article</p>
Pesticide residue monitoring in South Tyrol (Italy)
<ul> <li>Pesticide residue monitoring programm in South Tyrol (Province Bolzano, Italy)</li> <li>The programm is organized and conducted by the Department of Public Health, Servizio Igiene e Sanità<br> Pubblica—Azienda Sanitaria dell’Alto Adige, Bolzano, Italy</li> <li>Further despription and data available at: <ul> <li>https://www.sabes.it/gesundheitsvorsorge/umweltmedizin.asp</li> <li>https://umwelt.provinz.bz.it/pestizide-suedtirol.asp</li> </ul> </li> <li>Residue concentrations of grass samples per sampling site and sampling date can be found in the file "Pesticide_monitoring_SouthTyrol_2018_2021.csv "</li> <li>Available period: 2018 to 2021</li> <li>All sampling sites were public sites</li> <li>Names of active agents are in Italian</li> <li>Residue concentartions are given in "mg kg<sup>-1</sup>"</li> <li>"n.d." means "not detected"</li> <li>Lower limit of quantification (LOQ) was by default 0.01 mg kg<sup>-1</sup></li> <li>GPS coordinates of the sampling sites are can be found in thefile "Coordinates_sampling_sites.csv"</li> </ul>
Figure 1 in Detection of enteropathogens and research of pesticide residues in Lactuca sativa from traditional and agroecological fairs
Figure 1. Deltamethrin calibration curve.
Supplementary material to: Demonstration of a tool to assess cumulative risks from combined exposure to multiple pesticide residues in fruits and vegetables
<p>Supplementary material to: Kruisselbrink, J.W., van der Voet, H., van Lenthe, M.S., de Boer, W.J., Bakker, R. (2023). Demonstration of a tool to assess cumulative risks from combined exposure to multiple pesticide residues in fruits and vegetables. Wageningen University & Research Biometris report 48.01.23. https://doi.org/10.18174/584369. Catalogues and secondary data for the cumulative risk calculations.</p>
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