Calibration of laboratory derived indices for non-target arthropod risk assessment with field data for plant protection products

被引:1
|
作者
Bakker, Frank [1 ]
Aldershof, Saskia [2 ]
Braaker, Sonja [3 ]
Dinter, Axel [4 ]
Elston, Charlotte [5 ]
Kroder, Stefan [6 ]
Mayer, Christoph-Julian [7 ]
Pilling, Ed [8 ]
Neumann, Paul [9 ]
机构
[1] Bakker Consultant, Lieu Dit Pichoy, F-32250 Fources, France
[2] Biores & Evaluat, Clusiusweg 3, NL-9751 PN Haren, Netherlands
[3] BASF SAS, 21 Chemin Sauvegarde, F-69130 Ecully, France
[4] FMC Agr Solut, Westhafenpl 1, D-60327 Frankfurt, Germany
[5] Syngenta, Jealotts Hill Int Res Stn, Bracknell RG42 6EY, Berks, England
[6] Adama Deutschland GmbH, Edmund Rumpler Str 6, D-51149 Cologne, Germany
[7] BASF SE Agrarzentrum Limburgerhof, Speyerer Str 2, D-67117 Limburgerhof, Rheinland Pfalz, Germany
[8] Corteva Agrisci, 3B Pk Sq,Milton Pk, Abingdon OX14 4RN, Oxon, England
[9] Bayer AG, Crop Sci, Monheim, Germany
关键词
Insects; Risk assessment; Pesticides; Hazard Quotient; Protection goals; PESTICIDE TESTING PROGRAM; WORKING-GROUP PESTICIDES; DIFFERENCE; NOEC;
D O I
10.1016/j.ecoenv.2022.113427
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The Hazard Quotient (HQ) compares field application rate to intrinsic toxicity assessed with sensitive indicator species. As a hazard indicator for risk assessment, the HQ must be calibrated against measured effects under field conditions. Because protection goals may be context specific, we analyse how choice of acceptance criteria affects setting of the HQ and calibrate HQ for various scenarios under the strict condition that no false negative conclusions may be reached. We use Non-Target Arthropod toxicity data from laboratory studies on inert (Tier 1) and on natural substrates (Tier 2) and calibrate the HQ using application rates and arthropod abundance counts from field studies in orchards, arable fields, and hay meadows in 34 locations in Western Europe. With 21 formulations (17 active substances) tested in mostly multi-rate field studies, our reference data base has 120/121 values at Tier 1/Tier 2, respectively. We use the Proportion of Affected Taxa and Duration of Effect to jointly define acceptance criteria, starting with No Observed Effects. Absence of field effects is correctly predicted with HQ < 1.3 at Tier 1 and HQ < 0.48 at Tier 2, but these settings result in a high proportion of false positive outcomes. Increasing accepted duration of effect from 0 to 4 to 8 weeks results in HQ-threshold changes from 1.3 to 6.4 to 250 for Tier 1 studies and from 0.48 to 1.1 to 5.7 for Tier 2 studies. This coincides with a clear decrease in false positive outcomes. Recovery within a year is correctly concluded for 73% of the products passing the corresponding Tier 1 HQ < 2600 and for 92% of products at Tier 2 (HQ < 230). Our analysis shows that the calibration is appropriate for a broad geographical range, for in-field and off-field situations and for phytophagous and non-phytophagous species alike.
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页数:11
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