SUMMARY
Chloropicrin is a fumigant insecticide and nematicide for use with a wide variety of crops. It is highly soluble in water and is highly volatile but tends not to be persistent in the environment. Chloropicrin demonstrates a moderate to high toxicity to most biodiversity. The main exception is that it is not considered to be a bee toxin. It has a moderate mammalian toxicity and is a potential skin, eye and respiratory tract irritant.
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 |
|---|---|---|---|
Environmental fate High alert: Drainflow: Mobile |
Ecotoxicity High alert: Birds acute ecotoxicity: High; Fish acute ecotoxicity: High; Daphnia chronic ecotoxicity: High |
Human health High alert: Mammals chronic toxicity: High |
| Description | A preplant soil fumigant used to control soil borne fungi, diseases and nematodes |
|---|
| Example pests controlled | Caterpillars; Aphids; Scale insects; Spidermites; Whiteflies; Nematodes |
| Example applications | Strawberries; Peppers; Onions; Curcubits; Tobacco; Tomatoes; Ornamentals; Nursery stock; Tree crops, Olives |
| Efficacy & activity | Published evidence is limited but use has been extensive. |
| 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 | Not applicable | |||||||
| 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 |
|
| Also used in | USA; Australia; Morocco |
|---|
| Isomerism | None |
|---|
| Chemical formula | CCl3NO2 |
| Canonical SMILES | C([N+](=O)[O-])(Cl)(Cl)Cl |
| Isomeric SMILES | - |
| International Chemical Identifier key (InChIKey) | LFHISGNCFUNFFM-UHFFFAOYSA-N |
| International Chemical Identifier (InChI) | InChI=1S/CCl3NO2/c2-1(3,4)5(6)7 |
| 2D structure diagram/image available? | Yes |
| Pesticide type | Insecticide; Nematicide | |
|---|---|---|
| Substance groups | Fumigant insecticide; Fumigant nematicide | |
| Minimum active substance purity | 990 g kg−1 | |
| Known relevant impurities | EU dossier - None declared | |
| Substance origin | Synthetic | |
| Mode of action | Via vapour, exact mode of action is multi-site and non-specific | |
| CAS RN | 76-06-2 | |
| EC number | 200-930-9 | |
| CIPAC number | 298 | |
| US EPA chemical code | 081501 | |
| PubChem CID | 6423 | |
| CLP index number | 610-001-00-3 | |
| Molecular mass | 164.37 | |
| PIN (Preferred Identification Name) | trichloro(nitro)methane | |
| IUPAC name | trichloronitromethane | |
| CAS name | trichloronitromethane | |
| Global Governance status: Listed (✓) under |
|
|
| Relevant Environmental Water Quality Standards | - | |
| Forever chemical | - | |
| Highly Hazardous Pesticide (HHP) | Type I | - |
| Type II | Yes [ R01 Rule 1: Pesticide active ingredients that meet the criteria of classes Ia or Ib of the WHO Recommended Classification of Pesticides by Hazard (or those with a CLP classification of H330) ; R09 Rule 9: Pesticide active ingredients that have demonstrated a high aquatic toxicity (where acute ecotoxicity for fish, invertebrates or algae =< 0.1 mg l−1) ] |
|
| Other status information | Potential groundwater contaminant; Marine pollutant; PAN Bad Actor Chemical | |
| Herbicide Resistance Class (HRAC MoA class) | Not applicable | |
| Herbicide Resistance Class (WSSA MoA class) | Not applicable | |
| Insecticide Resistance Class (IRAC MoA class) | 8B | |
| Fungicide Resistance Class (FRAC MOA class) | Not applicable | |
| Examples of recorded resistance | Sitophilus oryzae | |
| Physical state | Colourless liquid | |
| Property | Value |
|---|
| Availability status | Current |
| Introduction & key dates | 1848, first synthesised; 1908, pesticidal activity reported |
| Example manufacturers & suppliers of products using this active now or historically |
|
| Example products using this active |
|
| Formulation and application details | Fumigant. Vapour releasing products that are usually applied with specialised injection equipment or hand-operatated equipment for small areas |
| Commercial production | Chloropicrin is produced commercially through the nitration of chloroform in the presence of nitric acid. In this process, chloroform is reacted with concentrated nitric acid, often with the aid of a catalyst such as sulfuric acid, under controlled temperature and pressure conditions. The reaction introduces a nitro group into the chloroform molecule, resulting in the formation of chloropicrin. This synthesis is highly exothermic and requires careful handling due to the toxic and volatile nature of the reactants and the product. |
| 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) | 2021 | 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 |
High |
| Solubility - In organic solvents at 20 °C (mg l−1) | 500000 | 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 ) Acetone5 = Verified data used for regulatory purposes |
- |
| 500000 | 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 ) Ethanol5 = Verified data used for regulatory purposes |
- |
| 500000 | 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 ) Xylene5 = Verified data used for regulatory purposes |
- |
| 500000 | 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 ) Hexane5 = Verified data used for regulatory purposes |
- |
| Melting point (°C) | Not applicable | Q3 Q = Miscellaneous data from online sources freezes at -70 °C3 = Unverified data of known source |
- |
| Boiling point (°C) | 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 |
- |
| Degradation point (°C) | - | - | - |
| Flashpoint (°C) | - | - | - |
| Octanol-water partition coefficient at pH 7, 20 °C | P | 3.16 X 1002 | Calculated | - |
| Log P | 2.5 | 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 ) at 25 °C5 = Verified data used for regulatory purposes |
Low |
| Fat solubility of residues | Solubility | - | - | - |
| Data type | - | - | - |
| Density (g ml−1) | 1.66 | 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 |
- |
| Dissociation constant pKa) at 25 °C | Not applicable | 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 |
- |
| No dissociation | ||
| Vapour pressure at 20 °C (mPa) | 4.23 X 1006 | 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 |
Highly volatile. If applied directly to plants or soil, drift is a concern & mitigation is advisable |
| Henry's law constant at 25 °C (Pa m3 mol−1) | 3.44 X 1002 | 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 |
Volatile |
| Volatilisation as max % of applied dose lost | From plant surface | - | - | - |
| From soil surface | - | - | - |
| Maximum UV-vis absorption L mol−1 cm−1 | Neutral solution: 203.7nm = 1648, 274nm = 32 Acidic solution: 204.4nm = 1512, 274.2nm = 28 Basic solution: 275nm = 33 |
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 |
- |
| Surface tension (mN m−1) | 71.0 | 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 ) at 20°C5 = Verified data used for regulatory purposes |
- |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| General biodegradability | - |
| Soil degradation (days) (aerobic) | DT50 (typical) | 4.2 | 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 |
Non-persistent |
| DT50 (lab at 20 °C) | 4.2 | 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 |
Non-persistent |
| DT50 (field) | 3.0 | 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 |
Non-persistent |
| DT90 (lab at 20 °C) | 23.3 | 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 |
Non-persistent |
| DT90 (field) | - | - | - |
| DT50 modelling endpoint | - | - | - |
| Note | EU 2017 dossier Lab studies DT50 2.7-21.8 days, DT90 range 2.7-89.3 days, Soils=8; Field study DT50 0.48-5.6 days 2 soils. Other sources: DT50 1.0 day (DW3) |
| 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 | 1.3 | 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 |
| Note | - |
| Aqueous hydrolysis DT50 (days) at 20 °C and pH 7 | Value | Stable | W4 W = French database provided by ARVALIS-Institut du Végétal. Dataset no longer available. 4 = Verified data |
Stable |
| Note | Stable pH 5 to pH 9 |
| 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) | 0.66 | 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 |
Mobile |
| Kfoc (mL g−1) | 60.5 |
| 1/n | 0.91 |
| Notes and range | EU dossier Kf range 0.414-1.15, Kfoc range 24.9-122 mL g−1, 1/n range 0.68-1.08, Soils=4 |
| pH sensitivity | No |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|---|---|
| GUS leaching potential index | 1.06 | Calculated | Low leachability |
| SCI-GROW groundwater index (μg l−1) for a 1 kg ha−1 or 1 l ha−1 application rate | Value | 2.38 X 10-03 | Calculated | - |
| Note | - | ||
| Potential for particle bound transport index | Low | Calculated | - |
| Potential for loss via drain flow | Mobile | Calculated | - |
| Photochemical oxidative DT50 (hrs) as indicator of long-range air transport risk | 1975.2 | 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 ) Calculated using the Atkinson method, 12 hr. EU trigger for long-range transport is DT50 in air <2 days.4 = Verified data |
Substance of concern for long-range air transport |
| Bio-concentration factor | BCF (l kg−1) | Low risk | 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 ) Based on LogP < 35 = Verified data used for regulatory purposes |
Low risk |
| CT50 (days) | - | - | Known soil metabolites|
| Metabolite | Major/Minor fraction | Estimated maximum occurrence fraction | Notes |
|---|
| chloromethane | Minor fraction | - | Anaerobic |
| nitromethane | Minor fraction | 0.03 | Anaerobic |
| chloroform | Minor fraction | - | - |
| dichloronitromethane | Major fraction | 0.174 | - |
| Metabolite | EC SANCO/221/2000 relevancy | ADI (mg kg−1 bodyweight day−1) | WHO drinking water guidance value (μg L−1 day−1) |
|---|
| dichloronitromethane | Relevant | - | - |
| Metabolite name and reference | Aliases | Formation medium / Rate | Estimated maximum occurrence fraction |
|---|---|---|---|
| dichloro(methyl)hydroxylamine | - | Soil leachate | - |
ECOTOXICOLOGY
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|---|
| Mammals - Acute oral LD50 (mg kg−1) | 250 | 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 |
Moderate |
| Mammals - Short term dietary NOEL | (mg kg−1) | 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 ) Rat5 = Verified data used for regulatory purposes |
High |
| (ppm diet) | - | - |
| Mammals - Chronic 21d NOAEL (mg kg−1 bw d−1) | > 2.71 | 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 ) Rat Reproductive NOAEL5 = Verified data used for regulatory purposes |
High |
| Birds - Acute LD50 (mg kg−1) | 62.0 | 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 ) Colinus virginianus5 = Verified data used for regulatory purposes |
High |
| Birds - Short term dietary (LC50/LD50) | 108 mg kg feed−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 ) Colinus virginianus5 = Verified data used for regulatory purposes |
- |
| Birds - Chronic 21d NOEL (mg kg−1 bw d−1) | 10.6 | 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 virginianus NOAEL5 = Verified data used for regulatory purposes |
Moderate |
| Earthworms - Acute 14 day LC50 (mg kg−1 dw soil) | 37.8 | 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 ) Eisenia foetida5 = Verified data used for regulatory purposes |
Moderate |
| Earthworms - Chronic NOEC, reproduction (mg kg−1 dw soil) | - | - | - |
| Soil micro-organisms | Nitrogen mineralisation: Chronic effect [Dose: field rate] Carbon mineralisation: No significant adverse effect [Dose: 5 x field rate] Bacterial populations: 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 |
- |
| 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) | > 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 ) Apis mellifera4 = Verified data |
Low |
| Oral acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | - | - | - |
| Unknown mode acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | > 12.2 | 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 ) Apis mellifera Inhalation4 = Verified data |
Moderate |
| 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) | 0.0048 | 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 |
High |
| 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) | 0.150 | 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 |
Moderate |
| Temperate Freshwater Aquatic invertebrates - Chronic 21 day NOEC (mg l−1) | 0.0025 | 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 |
High |
| Tropical Freshwater Aquatic invertebrates - Acute 48 hour EC50 (mg l−1) | - | - | - |
| Aquatic crustaceans - Acute 96 hour LC50 (mg l−1) | 0.030 | 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 ) Americamysis bahia3 = Unverified data of known source |
High |
| 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) (ErC50, Semi-static) | 0.024 | 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 ) Lemna minor5 = Verified data used for regulatory purposes |
Moderate |
| Aquatic plants (rooted, growth rate, fresh) - 14 day (mg l−1) | - | - | - |
| Algae - Acute (growth rate, fresh; mg l−1) (72 hr ErC50, Static) | 0.16 | 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 ) Raphidocelis subcapitata5 = Verified data used for regulatory purposes |
Moderate |
| Algae - Chronic (growth rate, fresh; mg l−1) (72 hr NOEC, Static) | 0.039 | 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 ) Raphidocelis subcapitata5 = Verified data used for regulatory purposes |
Moderate |
| 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) | 250 | 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 |
Moderate |
| Mammals - Dermal LD50 (mg kg−1 body weight) | - | - | - |
| Mammals - Inhalation LC50 (mg l−1) | 0.044 | 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 ) Rat 4 hr (nose only)5 = Verified data used for regulatory purposes |
- |
| Other Mammal toxicity endpoints | - | - | - |
| ADI - Acceptable Daily Intake (mg kg−1 bw day−1) | 0.001 | 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) | 0.001 | 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) | None allocated | 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 |
- |
| AOEL - Acceptable Operator Exposure Level - Systemic (mg kg−1 bw day−1) | 0.001 | 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 (%) | 100 | A3 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 ) default3 = Unverified data of known source |
- |
| Dangerous Substances Directive 76/464 | - | - | - |
| Exposure Routes | Public | Bystander exposure unlikely based on typical patterns of use Minimal risk of dietary exposure |
| Occupational | Risk of exposure acceptable under label recommendations for use for personal protection clothing and equipment Risk of exposure by inhalation |
| MRLs | European | EU MRL pesticide database  |
| Great Britain | GB MRL Register  |
| Notes | - |
| Drinking Water Standards | - | - | - |
| Drinking Water MAC (μg l−1) | 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 ) EU Dir 89/778/EC limit; Calc MAC=3 μg l−15 = Verified data used for regulatory purposes |
- |
| Mammalian dose elimination route and rate | Extensively metabolised, eliminated mainly via expired air with some loses via urine and faeces | 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 |
- |
| Specific human health issues (hazard-based) |
|
|
|---|---|---|
| General human health issues | Highly toxic | |
| Property | Value and interpretation |
|---|
| General | Not explosive or oxidising IMDG Transport Hazard Class 6.1 Not expected to auto-ignite; Not highly flammable |
| CLP classification 2013 | Health: H302, H330, H335, H315, H319 |
| WHO Classification | Not classified: Fumigant (Not classified: Fumigant) |
| UN Number | UN1580 |
| Waste disposal & packaging | Packaging Group I (great danger) |
| Shelf-life, storage, stability and reactivity | - |
TRANSLATIONS
| Language | Name |
|---|
| English | chloropicrin |
| French | chloropicrine |
| German | Chlorpikrin |
| Danish | chloropicrin |
| Italian | cloropicrina |
| Spanish | cloropicrina |
| Greek | - |
| Polish | chloropikryna |
| Swedish | - |
| Hungarian | - |
| Dutch | chloorpikrine |
| Norwegian | - |
Record last updated:
25/10/2025
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