3-(2,4,6-trimethylphenyl)pentanedioic acid (Ref: R173642) |
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Last updated: 11/04/2021
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(Not known by any other names) |
The following 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.
Environmental fate |
Ecotoxicity |
Human health |
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Chemical transformation product |
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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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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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Metabolite |
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Soil, Groundwater |
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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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Not applicable |
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- |
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250.3 |
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- |
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- |
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3-(2,4,6-trimethylphenyl)pentanedioic acid |
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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 |
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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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16 |
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Non-persistent |
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16 |
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Non-persistent |
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- |
- |
- |
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237 |
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Persistent |
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- |
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- |
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EU dossier lab studies DT₅₀ range 7.0-86.1 days, DT₉₀ range 40.1-816 days |
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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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1.6 |
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Moderately mobile |
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108 |
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EU dossier Kd range 0.08-4.9 mL g⁻¹, Koc range 4.3-250 mL g⁻¹, Soils=5 |
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1.18 |
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Moderately mobile |
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83 |
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0.87 |
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EU dossier Kf range 0.05-3.5 ml/g, Kfoc range 3.0-210 mL g⁻¹, 1/n range 0.75-0.97, Soils=5 |
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Adsorption inversely related to soil pH |
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2.51 |
Calculated |
Transition state |
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1.04 X 10-01 |
Calculated |
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None
Terrestrial ecotoxicology |
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- |
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> 1000 |
Eisenia foetida |
Low |
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- |
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Nitrogen mineralisation: No significant adverse effect Carbon mineralisation: No significant adverse effect |
Dose: 0.39 mg kg⁻¹ |
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> 120 |
Oncorhynchus mykiss |
Low |
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- |
- |
- |
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- |
- |
- |
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85 |
Daphnia magna |
Moderate |
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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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99 |
Lemna gibba |
Low |
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- |
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- |
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HUMAN HEALTH AND PROTECTION |
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EU MRL pesticide database |
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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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3-(2,4,6-trimethylphenyl)pentanedioic acid |
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- |
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Record last updated: |
11/04/2021 |
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 |