Aminomethylphosphonic acid |
Last updated: 14/11/2024 |
(Also known as: AMPA; phosphaglycine) |
SUMMARY |
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 |
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Chemical transformation product | |
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Not applicable | |
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Not applicable |
GB regulatory status |
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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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Additional information |
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Chemical structure |
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- | |
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CH₆NO₃P | |
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C(N)P(=O)(O)O | |
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No data | |
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MGRVRXRGTBOSHW-UHFFFAOYSA-N | |
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InChI=1S/CH6NO3P/c2-1-6(3,4)5/h1-2H2,(H2,3,4,5) | |
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Yes |
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Common Name | Relationship | Link |
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aminomethylphosphonic acid | - |
General status |
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Metabolite | |
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Soil, Sediment, Surface water, 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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1066-51-9 | |
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- | |
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- | |
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Not applicable | |
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- | |
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111.04 | |
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aminomethylphosphonic acid | |
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aminomethylphosphonic acid | |
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1-aminomethylphosphonic acid | |
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Potential groundwater contaminant | |
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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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- |
Can be a metabolite of: |
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glyphosate | Soil | 0.488 | Major fraction | |||||
glyphosate | Groundwater | - | Not relevant | |||||
glyphosate-sesquisodium | Soil | 0.469 | Major fraction | |||||
glyphosate-sesquisodium | Groundwater | - | Relevant | |||||
glyphosate-diammonium | Soil | 0.469 | Major fraction | |||||
glyphosate-diammonium | Groundwater | - | Relevant | |||||
glyphosate-dimethylammonium | Soil | 0.469 | Major fraction | |||||
glyphosate-sodium | Soil | - | Major fraction | |||||
glyphosate-sodium | Groundwater | - | Relevant | |||||
glyphosate-isopropylamine | Groundwater | - | Relevant | |||||
glyphosate-monopotassium | Soil | 0.469 | Major fraction | |||||
glyphosate-dimethylammonium | Groundwater | - | Relevant | |||||
glyphosate-monoammonium | Soil | 0.469 | Major fraction | |||||
glyphosate-monoammonium | Groundwater | - | Relevant | |||||
glyphosate-monopotassium | Groundwater | - | Relevant | |||||
glyphosate-isopropylamine | Soil | 0.469 | Major fraction | |||||
glyphosate-trimesium | Soil | 0.154 | Major fraction | |||||
glyphosate-trimesium | Groundwater | - | Relevant |
Formulations |
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1466561 | R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
High | ||||||||
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- | - | - | ||||||||
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- | - | - | ||||||||
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- | - | - | ||||||||
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2.34 X 10-02 | Calculated | - | |||||||
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-1.63 | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
Low | ||||||||
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- | - | - | |||||||
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- | - | - | ||||||||
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1.64 | Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
- | ||||||||
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- | - | - | ||||||||
- | |||||||||||
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- | - | - | ||||||||
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0.16 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
Moderately volatile | ||||||||
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- | - | - |
Degradation |
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- | ||||||||||
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114 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
Persistent | |||||||
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114 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
Persistent | ||||||||
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419.0 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
Very persistent | ||||||||
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169 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
Persistent | ||||||||
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1000 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
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EU dossier 2023 Lab studies DT₅₀ (normalised) range 6.4-378.4 days, DT₉₀ range 13.4-588 days, Soils=9; Field studies (EFSA 2015) DT₅₀ range 283.6-633.1 days, DT₉₀ range 942.3 - >1000 days, Soils =5 | ||||||||||
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132.0 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
Slow | ||||||||
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5.47 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
Moderately fast | ||||||||
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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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- | R3 R = Peer reviewed scientific publications 3 = Unverified data of known source |
Slightly mobile | |||||||
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2002 | ||||||||||
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29.8 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
Slightly mobile | |||||||
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2541 | ||||||||||
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0.76 | ||||||||||
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EU dossier 2023 Kf range 15.7-53.9 mL g⁻¹, Kfoc range 1160-5650 mL g⁻¹, 1/n range 0.707-0.875, Soils =8 | ||||||||||
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Fate indices |
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1.56 | Calculated | Low leachability | ||||||||||||||||||||||||||
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4.55 X 10-02 | Calculated | - | |||||||||||||||||||||||||
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High | Calculated | - | ||||||||||||||||||||||||||
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Slightly mobile | Calculated | - | ||||||||||||||||||||||||||
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Known metabolites |
None
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Terrestrial ecotoxicology |
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> 5000 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Rat5 = Verified data used for regulatory purposes |
Low | ||||||||
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> 2250 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Colinus virginianus5 = Verified data used for regulatory purposes |
Low | ||||||||
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> 1000 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Eisenia foetida5 = Verified data used for regulatory purposes |
Low | ||||||||
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28.12 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Eisenia foetida5 = Verified data used for regulatory purposes |
Moderate | ||||||||
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Nitrogen mineralisation: No significant adverse effect Carbon mineralisation: No significant adverse effect |
A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes Dose: 120 kg ha⁻¹ 28 Day |
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315 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Folsomia candida5 = Verified data used for regulatory purposes |
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Aquatic ecotoxicology |
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> 100 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Oncorhynchus mykiss5 = Verified data used for regulatory purposes |
Low | ||||||||
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> 100 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Daphnia magna5 = Verified data used for regulatory purposes |
Low | ||||||||
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15 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Daphnia magna5 = Verified data used for regulatory purposes |
Low | ||||||||
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12 | A4 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Lemna gibba4 = Verified data |
Low | ||||||||
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191 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Pseudokirchneriella subcapitata5 = Verified data used for regulatory purposes |
Low | ||||||||
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> 100 | F4 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 ) Crassostrea gigas Larva4 = Verified data |
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General |
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High (class III) | - | - | ||||||||
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> 5000 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Rat5 = Verified data used for regulatory purposes |
Low | ||||||||
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2000 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) Rat5 = Verified data used for regulatory purposes |
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0.1 | A5 A = EU regulatory and evaluation data as published by EC, EFSA (RAR, DAR & Conclusion dossiers), EMA (e.g. EU Annex III PIC DGD) (EU - Pesticides database; EFSA Scientific Publications ) 5 = Verified data used for regulatory purposes |
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Health issues |
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Probable liver and kidney toxicant |
Handling issues |
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No information available | |||
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Not listed (Not listed) | |||
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aminomethylphosphonic acid | ||
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kwas aminometylofosfonowy | ||
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Record last updated: | 14/11/2024 |
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 |