| 8a-hydroxyavermectin B1a (Ref: NOA 448112) |

Last updated: 18/09/2025
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(Not known by any other names) |
The following Pesticide Hazard Tricolour (PHT) alerts are based on the data in the tables below. An absence of an alert does not imply the substance has no implications for human health, biodiversity or the environment but just that we do not have the data to form a judgement. The alerts for Highly Hazardous Pesticides (HHPs) are based on applying the FAO/WHO (Type 1) and the PAN (Type II) criteria to PPDB data. Further details on the HHP indicators are given in the tables below. Neither the PHT nor the HHP hazard alerts take account of usage patterns or exposure, thus they do not represent risk.
| PHT: Environmental fate |
PHT: Ecotoxicity |
PHT: Human health |
Highly Hazardous Pesticide |
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Chemical transformation product |
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- |
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- |
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Not applicable |
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Not applicable |
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Not applicable |
| EC Regulation 1107/2009 (repealing 91/414) |
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Not applicable |
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Not applicable |
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Not applicable |
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Not applicable |
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No |
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ATAustria |
BEBelgium |
BGBulgaria |
CYCyprus |
CZCzech Republic |
DEGermany |
DKDenmark |
EEEstonia |
ELGreece |
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ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
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LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
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ISIceland |
NONorway |
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8a-hydroxyavermectin B1a exhibits complex stereoisomerism, primarily due to its multiple chiral centres and conjugated double bonds within its large macrocyclic lactone structure. The molecule contains over a dozen stereocentres, each contributing to a specific three-dimensional configuration that defines its biological activity. It also includes conjugated diene systems, which can theoretically allow for geometric (E/Z) isomerism, although the natural product is biosynthesised with a fixed configuration. |
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C₄₈H₇₂O₁₅ |
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CCC(C)C1C(C=CC2(O1)CC3CC(O2)CC=C(C(C(C=CC=C4C(OC5C4(C(CC(C5O)C)C(=O)O3)O)O)C)OC6CC(C(C(O6)C)OC7CC(C(C(O7)C)O)OC)OC)C)C |
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CC[C@H](C)[C@@H]1[C@H](C=C[C@@]2(O1)C[C@@H]3C[C@H](O2)C/C=C(/[C@H]([C@H](/C=C/C=C/4\C(OC5[C@@]4([C@@H](CC(C5O)C)C(=O)O3)O)O)C)OC6C[C@@H]([C@H]([C@@H](O6)C)OC7C[C@@H]([C@H]([C@@H](O7)C)O)OC)OC)\C)C |
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QTRXVXOQSMGGHD-UTSCHBFWSA-N |
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InChI=1S/C48H72O15/c1-11-24(2)42-27(5)17-18-47(63-42)23-32-20-31(62-47)16-15-26(4)41(59-38-22-36(55-10)43(30(8)57-38)60-37-21-35(54-9)40(50)29(7)56-37)25(3)13-12-14-33-45(51)61-44-39(49)28(6)19-34(46(52)58-32)48(33,44)53/h12-15,17-19,24-25,27,29-32,34-45,49-51,53H,11,16,20-23H2,1-10H3/b13-12+,26-15+,33-14+/t24-,25-,27-,29-,30-,31?,32-,34-,35-,36-,37-,38-,39+,40-,41-,42+,43-,44+,45?,47+,48+/m0/s1 |
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No |
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Metabolite |
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Soil |
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Unclassified substance |
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- |
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- |
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Synthetic |
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Not applicable |
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- |
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- |
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- |
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- |
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- |
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- |
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- |
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- |
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- |
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- |
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889.09 |
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(1'R,2R,3S,4'S,6S,8'R,10'E,12'S,13'S,14'E,16'Z,24'S)-2-[(2S)-butan-2-yl]-18',21',24'-trihydroxy-12'-[(4S,5S,6S)-5-[(4S,5S,6S)-5-hydroxy-4-methoxy-6-methyloxan-2-yl]oxy-4-methoxy-6-methyloxan-2-yl]oxy-3,11',13',22'-tetramethylspiro[2,3-dihydropyran-6,6'-3,7,19-trioxatetracyclo[15.6.1.14,8.020,24]pentacosa-10,14,16-triene]-2'-one |
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(1'R,2R,3S,4'S,6S,8'R,10'E,12'S,13'S,14'E,16'Z,24'S)-2-[(2S)-butan-2-yl]-18',21',24'-trihydroxy-12'-[(4S,5S,6S)-5-[(4S,5S,6S)-5-hydroxy-4-methoxy-6-methyloxan-2-yl]oxy-4-methoxy-6-methyloxan-2-yl]oxy-3,11',13',22'-tetramethylspiro[2,3-dihydropyran-6,6'-3,7,19-trioxatetracyclo[15.6.1.14,8.020,24]pentacosa-10,14,16-triene]-2'-one |
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8a-hydroxyavermectin B1a |
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| UK Poisons List Order 1972 |
Rotterdam Convention |
Montreal Protocol |
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| Stockholm Convention |
OSPAR |
EU Water Framework Directive |
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- |
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- |
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- |
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Yes [ R09 Rule 9: Pesticide active ingredients that have demonstrated a high aquatic toxicity (where acute ecotoxicity for fish, invertebrates or algae =< 0.1 mg l⁻¹) ] |
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- |
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Not applicable |
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Not applicable |
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Not applicable |
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Not applicable |
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- |
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- |
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Not applicable |
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Not applicable |
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- |
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- |
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- |
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- |
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13.8 |
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Moderate |
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- |
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- |
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| - |
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0.0037 |
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Low volatility |
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- |
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32.1 |
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Moderately persistent |
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32.1 |
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Moderately persistent |
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- |
- |
- |
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136.3 |
- |
Persistent |
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- |
- |
- |
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35.7 |
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- |
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EU 2019 dossier lab studies DT₅₀ (normalised) range 16.9-81.7 days, DT₉₀ (measured) range 56.0-272 days, Soils=11 |
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- |
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45.0 |
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Moderately fast |
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26.9 |
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Slow |
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- |
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- |
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As this parameter is not normally measured directly, a surrogate measure is used: ‘Photochemical oxidative DT₅₀’. Where data is available, this can be found in the Fate Indices section below. |
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| Soil adsorption and mobility |
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- |
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- |
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- |
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41.0 |
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Slightly mobile |
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1943 |
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0.871 |
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EU dossier Kf range 15.9-78.9 mL g⁻¹, Kfoc range 1098-3104 mL g⁻¹, 1/n range 0.796-0.961, Soils=3 |
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- |
None
| Terrestrial ecotoxicology |
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1.5 |
R3 R = Peer reviewed scientific publications 3 = Unverified data of known source Rat |
High |
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- |
- |
- |
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- |
- |
- |
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> 100 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Anas platyrhynchos |
Moderate |
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- |
- |
- |
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- |
- |
- |
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161 |
Eisenia foetida corr |
Moderate |
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- |
- |
- |
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Nitrogen mineralisation: No significant adverse effect Carbon mineralisation: No significant adverse effect |
Dose: 0.66 mg kg⁻¹ 28 Day |
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- |
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- |
- |
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- |
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0.504 |
Oncorhynchus mykiss |
Moderate |
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0.00052 |
Oncorhynchus mykiss |
High |
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- |
- |
- |
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0.0016 |
Daphnia magna |
High |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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0.003 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Chironomus riparius |
High |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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> 6.1 |
Raphidocelis subcapitata |
Moderate |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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| Regulatory Threshold Levels (RTLs) |
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Note: These RTLs have been calculated using the regulatory approach used in the European Union and based on ecotoxocity values in the PPDB.
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0.15 |
Worst case of acute and chronic mammals |
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10 |
Worst case of acute and chronic birds |
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32.2 |
Worst case of acute and chronic earthworms |
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No data |
No data for non-target plants vegetative vigour and seedling emergence |
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No data |
No data for contact and oral honeybees |
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No data |
No data for parasitic wasps and predatory mites |
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5.2E-05 |
Worst case of temperate acute and chronic fish |
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1.6E-05 |
Worst case of temperate acute and chronic aquatic invertebrates |
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0.61 |
Worst case of free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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- |
- |
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1.5 |
R3 R = Peer reviewed scientific publications 3 = Unverified data of known source Rat |
High |
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- |
- |
- |
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- |
- |
- |
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- |
- |
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- |
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- |
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- |
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- |
- |
- |
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| Carcinogen |
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Endocrine disruptor |
| No data found |
A0 A = Chromosome aberration (EFSA database) 0 = No data ; B0 B = DNA damage/repair (EFSA database) 0 = No data ; C0 C = Gene mutation (EFSA database) 0 = No data ; D0 D = Genome mutation (EFSA database) 0 = No data ; E0 E = Unspecified genotoxicity type (miscellaneous data source) 0 = No data |
No data found |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
| No data found |
No data found |
No data found |
| Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
| No data found |
No data found |
No data found |
| Eye irritant |
Phototoxicant |
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| No data found |
No data found |
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No further information available |
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No information available |
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- |
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Not listed (Not listed) |
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8a-hydroxyavermectin B1a |
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| Record last updated: |
18/09/2025 |
| Contact: |
aeru@herts.ac.uk |
| Please cite as: |
Lewis, K.A., Tzilivakis, J., Warner, D. and Green, A. (2016) An international database for pesticide risk assessments and management. Human and Ecological Risk Assessment: An International Journal, 22(4), 1050-1064. DOI: 10.1080/10807039.2015.1133242 |
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