Diethyltoluamide is an insect repellent. Little data is available regarding its environmental fate. It is moderately toxic to aquatic life. Diethyltoluamide has a moderate mammalian oral toxicity. It is also a neurotoxin and an irritant.
Data alerts
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
Environmental fate Moderate alert: Drainflow: Moderately mobile
Example manufacturers & suppliers of products using this active now or historically
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Example products using this active
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Formulation and application details
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ENVIRONMENTAL FATE
Property
Value
Source; quality score; and other information
Interpretation
Solubility - In water at 20 °C (mg l⁻¹)
912.0
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source
at 25 °C
High
Solubility - In organic solvents at 20 °C (mg l⁻¹)
-
-
-
Melting point (°C)
-45.0
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source
-
Boiling point (°C)
292
E3 E = Manufacturers safety data sheets 3 = Unverified data of known source
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Degradation point (°C)
-
-
-
Flashpoint (°C)
155
E3 E = Manufacturers safety data sheets 3 = Unverified data of known source
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Octanol-water partition coefficient at pH 7, 20 °C
P
1.51 X 1002
Calculated
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Log P
2.18
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source
Low
Fat solubility of residues
Solubility
-
-
-
Data type
-
-
-
Density (g ml⁻¹)
0.985
E3 E = Manufacturers safety data sheets 3 = Unverified data of known source
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Dissociation constant pKa) at 25 °C
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-
-
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Vapour pressure at 20 °C (mPa)
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Henry's law constant at 25 °C (Pa m³ mol⁻¹)
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Maximum UV-vis absorption L mol⁻¹ cm⁻¹
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Surface tension (mN m⁻¹)
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-
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Degradation
Property
Value
Source; quality score; and other information
Interpretation
General biodegradability
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Soil degradation (days) (aerobic)
DT₅₀ (typical)
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-
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DT₅₀ (lab at 20 °C)
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-
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DT₅₀ (field)
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-
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DT₉₀ (lab at 20 °C)
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-
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DT₉₀ (field)
-
-
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DT₅₀ modelling endpoint
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-
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Note
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Dissipation rate RL₅₀ on plant matrix
Value
-
-
-
Note
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Dissipation rate RL₅₀ on and in plant matrix
Value
-
-
-
Note
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Aqueous photolysis DT₅₀ (days) at pH 7
Value
-
-
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Note
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Aqueous hydrolysis DT₅₀ (days) at 20 °C and pH 7
Value
-
-
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Note
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Water-sediment DT₅₀ (days)
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-
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Water phase only DT₅₀ (days)
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-
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Soil adsorption and mobility
Property
Value
Source; quality score; and other information
Interpretation
Linear
Kd
-
Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source
Moderately mobile
Koc
277
Notes and range
Estimated
Freundlich
Kf
-
-
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Kfoc
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1/n
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Notes and range
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pH sensitivity
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Fate indices
Property
Value
Source; quality score; and other information
Interpretation
GUS leaching potential index
-
-
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SCI-GROW groundwater index (μg l⁻¹) for a 1 kg ha⁻¹ or 1 l ha⁻¹ application rate
Value
Cannot be calculated
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-
Note
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Potential for particle bound transport index
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-
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Potential for loss via drain flow
-
-
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Bio-concentration factor
BCF (l kg⁻¹)
Low risk
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source
Based on LogP < 3
Low risk
CT₅₀ (days)
-
-
Known metabolites
None
ECOTOXICOLOGY
Terrestrial ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
1950
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source
Rat
Moderate
Mammals - Short term dietary NOEL
(mg kg⁻¹)
-
-
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(ppm diet)
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Mammals - Chronic 21d NOAEL (mg kg⁻¹ bw d⁻¹)
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-
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Birds - Acute LD₅₀ (mg kg⁻¹)
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-
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Birds - Short term dietary (LC₅₀/LD₅₀)
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-
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Birds - Chronic 21d NOEL (mg kg⁻¹ bw d⁻¹)
-
-
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Earthworms - Acute 14 day LC₅₀ (mg kg⁻¹)
-
-
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Earthworms - Chronic NOEC, reproduction (mg kg⁻¹)
-
-
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Soil micro-organisms
-
-
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Collembola
Acute LC₅₀ (mg kg⁻¹)
-
-
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Chronic NOEC (mg kg⁻¹)
-
-
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Non-target plants
-
-
-
-
-
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Honeybees (Apis spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
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-
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Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
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-
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Unknown mode acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
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-
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Chronic
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Bumblebees (Bombus spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
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-
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Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
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Mason bees (Osmia spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
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-
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Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
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Other bee species (1)
Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)
-
-
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Mode of exposure
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Other bee species (2)
Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)
-
-
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Mode of exposure
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Beneficial insects (Ladybirds)
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-
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Beneficial insects (Lacewings)
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Beneficial insects (Parasitic wasps)
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-
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Beneficial insects (Predatory mites)
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-
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Beneficial insects (Ground beetles)
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-
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Aquatic ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Fish - Acute 96 hour LC₅₀ (mg l⁻¹)
71.3
F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) 3 = Unverified data of known source
F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment ) 3 = Unverified data of known source
Daphnia magna
Moderate
Aquatic invertebrates - Chronic 21 day NOEC (mg l⁻¹)
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