(Also known as: phosphinothricin ; glufosinate ion; AE F035956; HOE 39866)
SUMMARY Hazard alerts
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 |
|---|---|---|---|
|   | Ecotoxicity Low alert: Bees acute contact ecotoxicity: Low; Bees acute oral ecotoxicity: Low Warning: Significant data are missing |
Human health High alert: Reproduction/development effects; Neurotoxicant |
| Description | A herbicide, usually used as the ammonium salt, for total vegetation control and to control a wide range of weeds and grasses |
|---|
| Example pests controlled | Annual broadleaved weeds including nightshade, lamb's quarters, ragweed, velvetleaf, wild mustard; Annual grasses including Barnyardgrass, bristly foxtail, witchgrass |
| Example applications | Oilseed rape; Potatoes; Maize; Soybean; Non-cropped areas |
| Efficacy & activity | - |
| GB COPR regulatory status | Not approved |
|---|
| Date COPR inclusion expires | Not applicable |
| GB LERAP status | No UK approval for use as a plant protection agent |
| EC Regulation 1107/2009 status | Not approved | |||||||
|---|---|---|---|---|---|---|---|---|
| Dossier rapporteur/co-rapporteur | Germany/France | |||||||
| Date EC 1107/2009 inclusion expires | Not applicable | |||||||
| EU Candidate for substitution (CfS) | Not applicable | |||||||
| Listed in EU database | Yes | |||||||
| Approved for use (✓) under EC 1107/2009 in the following EU Member States |
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| Approved for use (✓) under EC 1107/2009 by Mutual Recognition of Authorisation and/or national regulations in the following EEA countries |
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| Also used in | - |
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| Isomerism | Glufosinate exhibits stereoisomerism due to the presence of a chiral carbon atom at the C-2 position, which is bonded to four distinct groups: an amino group, a carboxyl group, a hydrogen atom, and the hydroxymethylphosphinylbutyl side chain. This tetrahedral chirality results in enantiomerism, producing two isomers, designated as (R)- and (S)-glufosinate (also known as L- and D-glufosinate, respectively). The (S)-enantiomer (L-glufosinate, glufosinate-P) is significantly more active as a herbicide, however, commercial formulations are typically racemic. |
|---|
| Chemical formula | C5H12NO4P |
| Canonical SMILES | CP(=O)(CCC(C(=O)O)N)O |
| Isomeric SMILES | - |
| International Chemical Identifier key (InChIKey) | IAJOBQBIJHVGMQ-UHFFFAOYSA-N |
| International Chemical Identifier (InChI) | InChI=1S/C5H12NO4P/c1-11(9,10)3-2-4(6)5(7)8/h4H,2-3,6H2,1H3,(H,7,8)(H,9,10) |
| 2D structure diagram/image available? | Yes |
Cambridge Crystallographic Data Centre diagrams
| Common Name | Relationship | Link |
|---|---|---|
| glufosinate | - |
| Pesticide type | Herbicide | |
|---|---|---|
| Substance groups | Organophosphate herbicide | |
| Minimum active substance purity | - | |
| Known relevant impurities | - | |
| Substance origin | Synthetic | |
| Mode of action | Non-selective, contact with some systemic action. Glutamine synthetase inhibitor: accumulates ammonium ions, inhibits photosynthesis. | |
| CAS RN | 51276-47-2 | |
| EC number | 257-102-5 | |
| CIPAC number | 437 | |
| US EPA chemical code | - | |
| PubChem CID | 4794 | |
| CLP index number | No data found | |
| Molecular mass | 181.13 | |
| PIN (Preferred Identification Name) | (2RS)-2-amino-4-[hydroxy(methyl)phosphinoyl]butyric acid | |
| IUPAC name | (2RS)-2-amino-4-[hydroxy(methyl)phosphinoyl]butyric acid | |
| CAS name | 2-amino-4-(hydroxymethylphosphinyl)butanoic acid | |
| Global Governance status: Listed (✓) under |
|
|
| Relevant Environmental Water Quality Standards | - | |
| Forever chemical | - | |
| Highly Hazardous Pesticide (HHP) | Type I | Yes [ C4 Criterion 4: Pesticide active ingredients that meet the criteria of reproductive toxicity Categories 1A and 1B of the Globally Harmonized System on Classification and Labelling of Chemicals (GHS) (those with a CLP classification of H360) ] |
| Type II | Yes [ R04 Rule 4: Pesticide active ingredients that meet the criteria of reproductive toxicity Categories 1A and 1B of the Globally Harmonized System on Classification and Labelling of Chemicals (GHS) (those with a CLP classification of H360) ] |
|
| Other status information | - | |
| Herbicide Resistance Class (HRAC MoA class) | H | |
| Herbicide Resistance Class (WSSA MoA class) | 10 | |
| Insecticide Resistance Class (IRAC MoA class) | Not applicable | |
| Fungicide Resistance Class (FRAC MOA class) | Not applicable | |
| Examples of recorded resistance | - | |
| Physical state | Solid | |
| Related substances & organisms | ||
| Property | Value |
|---|
| Availability status | Current |
| Introduction & key dates | 1984, first introduced in Japan |
| Example manufacturers & suppliers of products using this active now or historically |
|
| Example products using this active |
|
| Formulation and application details | Usually applied as the ammonium variant formulated as a water soluble concentrate |
| Commercial production | Glufosinate is commercially produced through microbial fermentation using genetically engineered Streptomyces species, followed by chemical purification and salt formation. The process begins with the cultivation of Streptomyces hygroscopicus or related strains that biosynthesise glufosinate as a secondary metabolite. Fermentation is carried out under controlled conditions in large bioreactors, where the organism produces the active compound over several days. After fermentation, the broth is filtered and the glufosinate is extracted and purified using ion-exchange chromatography and crystallisation. |
| Impact on climate of production and use | - |
ENVIRONMENTAL FATE
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|---|
| Solubility - In water at 20 °C at pH 7 (mg l−1) | - | - | - |
| Solubility - In organic solvents at 20 °C (mg l−1) | - | - | - |
| Melting point (°C) | 230 | V3 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) 3 = Unverified data of known source |
- |
| Boiling point (°C) | - | - | - |
| Degradation point (°C) | - | - | - |
| Flashpoint (°C) | - | - | - |
| Octanol-water partition coefficient at pH 7, 20 °C | P | 1.10 X 10-04 | Calculated | - |
| Log P | -3.96 | 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) | - | - | - |
| Dissociation constant pKa) at 25 °C | 2 | L2 L = Pesticide manuals and hard copy reference books / other sources 2 = Unverified data of unknown source |
- |
| Strong acid, pKa(2)= 2.0; pKa(3)=9.8 | ||
| 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) | - | - | - |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| General biodegradability | - |
| Soil degradation (days) (aerobic) | DT50 (typical) | - | - | - |
| DT50 (lab at 20 °C) | - | - | - |
| DT50 (field) | - | - | - |
| DT90 (lab at 20 °C) | - | - | - |
| DT90 (field) | - | - | - |
| DT50 modelling endpoint | - | - | - |
| Note | - |
| 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. |
| Decay in stored produce DT50 | - |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| Linear | Kd (mL g−1) | - | - | - |
| Koc (mL g−1) | - |
| Notes and range | - |
| Freundlich | Kf (mL g−1) | - | - | - |
| Kfoc (mL g−1) | - |
| 1/n | - |
| Notes and range | - |
| pH sensitivity | - |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| GUS leaching potential index | - | - | - |
| SCI-GROW groundwater index (μg l−1) for a 1 kg ha−1 or 1 l ha−1 application rate | Value | Cannot be calculated | - | - |
| Note | - |
| Potential for particle bound transport index | - | - | - |
| Potential for loss via drain flow | - | - | - |
| Photochemical oxidative DT50 (hrs) as indicator of long-range air transport risk | - | - | - |
| Bio-concentration factor | BCF (l kg−1) | Low risk | Q3 Q = Miscellaneous data from online sources Based on LogP < 33 = Unverified data of known source |
Low risk |
| CT50 (days) | - | - | Known metabolites
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|---|
| Mammals - Acute oral LD50 (mg kg−1) | 1625 | 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 ) Rat4 = Verified data |
Moderate |
| Mammals - Short term dietary NOEL | (mg kg−1) | - | - | - |
| (ppm diet) | - | - |
| Mammals - Chronic 21d NOAEL (mg kg−1 bw d−1) | - | - | - |
| Birds - Acute LD50 (mg kg−1) | - | - | - |
| Birds - Short term dietary (LC50/LD50) | - | - | - |
| Birds - Chronic 21d NOEL (mg kg−1 bw d−1) | - | - | - |
| Earthworms - Acute 14 day LC50 (mg kg−1 dw soil) | - | - | - |
| Earthworms - Chronic NOEC, reproduction (mg kg−1 dw soil) | - | - | - |
| Soil micro-organisms | - | - | - |
| Collembola | Acute LC50 (mg kg−1) | - | - | - |
| Chronic NOEC (mg kg−1) | - | - | - |
| Non-target plants | Vegetative vigour ER50 (g ha−1) | - | - | - |
| Seedling emergence ER50 (g ha−1) | - | - | - |
| Honeybees (Apis spp.) | Contact acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | > 345 | 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 ) as ammonium variant4 = Verified data |
Low |
| Oral acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | > 600 | 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 ) as ammonium variant4 = Verified data |
Low |
| Unknown mode acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | - | - | - |
| Chronic | - | - | - |
| Notes | - | |
| Bumblebees (Bombus spp.) | Contact acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | - | - | - |
| - | ||
| Oral acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | - | - | - |
| - | ||
| Mason bees (Osmia spp.) | Contact acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | - | - | - |
| Oral acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | - | - | - |
| Other bee species (1) | Acute LD50 (worst case from 24, 48 and 72 hour values - μg insect−1) | - | - | - |
| Mode of exposure | - | |
| Other bee species (2) | Acute LD50 (worst case from 24, 48 and 72 hour values - μg insect−1) | - | - | - |
| Mode of exposure | - | |
| Beneficial insects (Ladybirds) | - | - | - |
| Beneficial insects (Lacewings) | - | - | - |
| Beneficial insects (Parasitic wasps) | - | - | - |
| Beneficial insects (Predatory mites) | - | - | - |
| Beneficial insects (Ground beetles) | - | - | - |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| Temperate Freshwater Fish - Acute 96 hour LC50 (mg l−1) | - | - | - |
| Temperate Freshwater Fish - Chronic 21 day NOEC (mg l−1) | - | - | - |
| Tropical Freshwater Fish - Acute 96 hour LC50 (mg l−1) | - | - | - |
| Temperate Freshwater Aquatic invertebrates - Acute 48 hour EC50 (mg l−1) | - | - | - |
| Temperate Freshwater Aquatic invertebrates - Chronic 21 day NOEC (mg l−1) | - | - | - |
| Tropical Freshwater Aquatic invertebrates - Acute 48 hour EC50 (mg l−1) | - | - | - |
| Aquatic crustaceans - Acute 96 hour LC50 (mg l−1) | - | - | - |
| Sediment dwelling organisms - Acute 96 hour LC50 (mg l−1) | - | - | - |
| Sediment dwelling organisms - Chronic 28 day NOEC, static, water (mg l−1) | - | - | - |
| Sediment dwelling organisms - Chronic 28 day NOEC, sediment (mg kg−1) | - | - | - |
| Aquatic Plants (free-floating, fonds growth, fresh) - 7 day (mg l−1) | - | - | - |
| Aquatic plants (rooted, growth rate, fresh) - 14 day (mg l−1) | - | - | - |
| Algae - Acute (growth rate, fresh; mg l−1) | - | - | - |
| Algae - Chronic (growth rate, fresh; mg l−1) | - | - | - |
| Mesocosm study data | NOEAEC mg l−1 | - | - | - | NOEAEC mg l−1 | - | - | - |
| Marine bivalves | - | - | - |
HUMAN HEALTH AND PROTECTION
General
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| Threshold of Toxicological Concern (Cramer Class) | High (class III) | - | - |
| Mammals - Acute oral LD50 (mg kg−1) | 1625 | 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 ) Rat4 = Verified data |
Moderate |
| Mammals - Dermal LD50 (mg kg−1 body weight) | - | - | - |
| Mammals - Inhalation LC50 (mg l−1) | - | - | - |
| Other Mammal toxicity endpoints | - | - | - |
| ADI - Acceptable Daily Intake (mg kg−1 bw day−1) | 0.021 | 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 |
- |
| ARfD - Acute Reference Dose (mg kg−1 bw day−1) | 0.021 | 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 |
- |
| AAOEL - Acute Acceptable Operator Exposure Level (mg kg−1 bw day−1) | - | - | - |
| AOEL - Acceptable Operator Exposure Level - Systemic (mg kg−1 bw day−1) | 0.0021 | 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 |
- |
| Dermal penetration studies (%) | - | - | - |
| Dangerous Substances Directive 76/464 | List I | - | - |
| Exposure Routes | Public | - |
| Occupational | Risk of exposure acceptable under label recommendations for use for personal protection clothing and equipment |
| MRLs | European | EU MRL pesticide database  |
| Great Britain | GB MRL Register  |
| Notes | - |
| Drinking Water Standards | - | - | - |
| Drinking Water MAC (μg l−1) | - | - | - |
| Mammalian dose elimination route and rate | - | - | - |
| Specific human health issues (hazard-based) |
|
|
|---|---|---|
| General human health issues | No further information available | |
| Property | Value and interpretation |
|---|
| General | IMDG Transport Hazard Class 6.1 |
| CLP classification 2013 | Health: H302, H312, H332, H360FD, H373 |
| WHO Classification | II (Moderately hazardous) |
| UN Number | UN2783 |
| Waste disposal & packaging | - |
| Shelf-life, storage, stability and reactivity | - |
TRANSLATIONS
| Language | Name |
|---|
| English | glufosinate |
| French | glufosinate |
| German | Glufosinat |
| Danish | glufosinat |
| Italian | glufosinate |
| Spanish | glufosinato |
| Greek | - |
| Polish | glufosynat |
| Swedish | glufosinat |
| Hungarian | glufozinat |
| Dutch | glufosinaat |
| Norwegian | - |
Record last updated:
13/11/2025
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