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.
Physical repellent action based on odour and taste
Substance source
Extracted from a wide range of plants including grapes, neroli, wisteria, oranges and ylang ylang. It is also secreted by the musk glands of foxes and dogs
1985, formal studies as bird repellent undertaken; 1993, registered US EPA
Example manufacturers & suppliers of products using this active now or historically
Bird Shield Repellent Corp
Roth Chemical Company
Lansdowne Aromatics
BSRC
Example products using this active
Formulation and application details
Agricultural products are usually delivered in liquid emulsions or solutions
Commercial production
Methyl anthranilate is commercially produced primarily through petroleum-based chemical processes. The most common method involves the esterification of anthranilic acid with methanol in the presence of an acid catalyst. The process requires large quantities of acid catalysts and the disposal of toxic liquid acids after the reaction. An alternative approach involves microbial production which involves metabolic engineering of microorganisms like Escherichia coli and Corynebacterium glutamicum to produce methyl anthranilate directly from glucose. This process optimizes enzyme expression, increases precursor supply, and enhances cofactor availability, making it a more sustainable and natural method.
Impact on climate of production and use
The estimated GHG emissions from the commercial production of methyl anthranilate varies according to the production method. Petroleum-based synthesis is estimated to emit approximately 3-7 kg CO₂e per kg of product. Emissions from microbial fermentation processes typically range 0.5–2.0 kg CO₂e per kg of product.
ENVIRONMENTAL FATE
Property
Value
Source; quality score; and other information
Interpretation
Solubility - In water at 20 °C at pH 7 (mg l⁻¹)
2850
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source
High
Solubility - In organic solvents at 20 °C (mg l⁻¹)
Octanol-water partition coefficient at pH 7, 20 °C
P
7.59 X 1001
Calculated
-
Log P
1.88
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)
1.17
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source
-
Dissociation constant pKa) at 25 °C
2.23
V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source
-
Strong acid
Vapour pressure at 20 °C (mPa)
-
-
-
Henry's law constant at 25 °C (Pa m³ mol⁻¹)
-
-
-
Volatilisation as max % of applied dose lost
From plant surface
-
-
-
From soil surface
-
-
-
Maximum UV-vis absorption L mol⁻¹ cm⁻¹
-
-
-
Surface tension (mN m⁻¹)
-
-
-
Degradation
Property
Value
Source; quality score; and other information
Interpretation
General biodegradability
-
Soil degradation (days)
DT₅₀ (typical)
-
-
-
DT₅₀ (lab at 20 °C)
-
-
-
DT₅₀ (field)
-
-
-
DT₉₀ (lab at 20 °C)
-
-
-
DT₉₀ (field)
-
-
-
DT₅₀ modelling endpoint
-
-
-
Note
-
Soil mineralisation
Aerobic (at 20 °C)
-
-
-
Anaerobic (at 20 °C)
-
-
Dissipation rate RL₅₀ (days) on plant matrix
Value
-
-
-
Note
-
Dissipation rate RL₅₀ (days) on and in plant matrix
Value
-
-
-
Note
-
Aqueous photolysis DT₅₀ (days) at pH 7
Value
-
-
-
Note
-
Aqueous hydrolysis DT₅₀ (days) at 20 °C and pH 7
Value
-
-
-
Note
-
Water-sediment DT₅₀ (days)
-
-
-
Water phase only DT₅₀ (days)
-
-
-
Sediment phase only DT₅₀ (days)
-
-
-
Air degradation
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.
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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Ecotoxicity
Warning:
Human health
