(Also known as: Bordo mix; tricalcium tetracoppper sulphate)
SUMMARY
Bordeaux mixture is a copper sulfate/lime complex fungicide which also has some bactericide properties. It has a low aqueous solubility and is not volatile. It is not persistent in soil systems but can be stable in water. It is moderately toxic to most fauna and flora. Its mammalian oral toxicity is low but it is a probable eye 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 |
|---|---|---|---|
|   | Ecotoxicity Moderate alert: Birds acute ecotoxicity: Moderate; Fish acute ecotoxicity: Moderate; Daphnia acute ecotoxicity: Moderate; Daphnia chronic ecotoxicity: Moderate; Bees acute contact ecotoxicity: Moderate; Bees acute oral ecotoxicity: Moderate; Earthworms acute ecotoxicity: Moderate |
Human health Low alert Warning: Significant data are missing |
| Description | A copper sulfate/lime complex fungicide which also has some bactericide properties |
|---|
| Example pests controlled | Downy mildew; Damping-off; Powdery mildew: Fire blight; Leaf curl; Blackspot |
| Example applications | Vines; Fruit including apples, pears, olives, peaches, nectarines; Walnuts; ornamentals including roses; Non-agricultural situations including domestic gardons and allotments |
| Efficacy & activity | Copper based products have been shown to be affective against many fungal pathogens in field trials. |
| GB COPR regulatory status | Approved |
|---|
| Date COPR inclusion expires | 31/12/2027 |
| GB LERAP status | No data |
| EC Regulation 1107/2009 status | Approved | |||||||
|---|---|---|---|---|---|---|---|---|
| Dossier rapporteur/co-rapporteur | France/Germany | |||||||
| Date EC 1107/2009 inclusion expires | 31/12/2025 | |||||||
| EU Candidate for substitution (CfS) | Yes - two 'Persistent-Bioaccumulative-Toxic' criteria | |||||||
| Listed in EU database | Yes | |||||||
| Approved for use (✓) under EC 1107/2009 in the following EU Member States |
|
|||||||
| Approved for use (✓) under EC 1107/2009 by Mutual Recognition of Authorisation and/or national regulations in the following EEA countries |
|
| Also used in | Iran; Morocco |
|---|
| Isomerism | None |
|---|
| Chemical formula | CuO2H2 + CaSO4 |
| Canonical SMILES | - |
| Isomeric SMILES | - |
| International Chemical Identifier key (InChIKey) | - |
| International Chemical Identifier (InChI) | - |
| 2D structure diagram/image available? | Yes |
| Pesticide type | Fungicide; Other substance | |
|---|---|---|
| Other bioactivity & uses | Bactericide | |
| Substance groups | Inorganic compound | |
| Minimum active substance purity | >257 g kg−1 total copper | |
| Known relevant impurities | EU 2018 dossier: May contain heavy metals including Pb, Cd, As, Ni, CO, Sb & Hg | |
| Substance origin | Semi-synthetic; Mixture | |
| Mode of action | Contact and protectant. Prevents fungal spore germination. | |
| CAS RN | 8011-63-0 | |
| Alternative/old CAS RN | 1333-22-8 | |
| EC number | 616-932-1 | |
| CIPAC number | 44.604 | |
| US EPA chemical code | - | |
| PubChem CID | - | |
| CLP index number | 029-022-00-9 | |
| Molecular mass | 860.5 | |
| PIN (Preferred Identification Name) | - | |
| IUPAC name | mix, with or without stabilising agents, of calcium hydroxide and copper(II) sulphate | |
| CAS name | bordeaux mixture | |
| Global Governance status: Listed (✓) under |
|
|
| Relevant Environmental Water Quality Standards | - | |
| Forever chemical | - | |
| Highly Hazardous Pesticide (HHP) | Type I | - |
| Type II | Yes [ 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 | - | |
| Herbicide Resistance Class (HRAC MoA class) | Not applicable | |
| Herbicide Resistance Class (WSSA MoA class) | Not applicable | |
| Insecticide Resistance Class (IRAC MoA class) | Not applicable | |
| Fungicide Resistance Class (FRAC MOA class) | M01 | |
| Examples of recorded resistance | - | |
| Physical state | Blue-green fine powder which is a mixture of naturally occurring inorganic substances | |
| Related substances & organisms | ||
| Property | Value |
|---|
| Availability status | Current |
| Introduction & key dates | 1885, introduced |
| Example manufacturers & suppliers of products using this active now or historically |
|
| Example products using this active |
|
| Formulation and application details | Often supplied as a soluble concentrate but also available as concentrated suspensions, wettable dispersible granules and wettable powders. |
| Commercial production | Bordeaux mixture is commercially produced by combining copper(II) sulphate and hydrated lime (calcium hydroxide) in water. This reaction creates a suspension of copper hydroxide and calcium sulphate. The process involves dissolving copper sulphate in water, slaking quicklime with water to create a lime slurry, and then carefully mixing the two solutions. |
| Impact on climate of production and use | Data on GHG emissions for the commercial production of Bordeaux mixture will vary significantly depending on the processes involved. Manica, a leading producer of Bordeaux mixture, has conducted a detailed carbon footprint and concluded that less than 1 kg of CO2e per kg of finished product is emitted. This includes emissions from raw materials, transportation, production, and packaging. Notably, however, the company uses regenerated copper sourced 100% from Itay, which significantly reduces the environmental cost. |
ENVIRONMENTAL FATE
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|---|
| Solubility - In water at 20 °C at pH 7 (mg l−1) | 2.2 | 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 ) 4 = Verified data |
Low |
| Solubility - In organic solvents at 20 °C (mg l−1) | 9.6 | 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 ) Toluene5 = Verified data used for regulatory purposes |
- |
| 9.8 | 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 ) Dichloromethane5 = Verified data used for regulatory purposes |
- |
| 9.8 | 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 ) n-Hexane5 = Verified data used for regulatory purposes |
- |
| 8.8 | 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 ) Acetone5 = Verified data used for regulatory purposes |
- |
| Melting point (°C) | 400 | 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 ) 4 = Verified data |
- |
| Boiling point (°C) | Decomposes before boiling | 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) | 110 | 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 |
- |
| Flashpoint (°C) | - | - | - |
| Octanol-water partition coefficient at pH 7, 20 °C | P | 2.75 X 1000 | Calculated | - |
| Log P | 0.44 | 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 ) 3 = Unverified data of known source |
Low |
| Fat solubility of residues | Solubility | - | - | - |
| Data type | - | - | - |
| Density (g ml−1) | - | - | - |
| 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) | 3.40 X 10-10 | V2 V = ChemID Online Databases; Chemspider; PubChem. (ChemID ) at 25 °C2 = Unverified data of unknown source |
Low volatility |
| 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 | Acidic soln: 205nm=5923, 250nm=3119, 800nm=70, 290nm=520, 295nm=398 | 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) | 68.9 | 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 |
- |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| General biodegradability | Not biodegradable |
| Soil degradation (days) (aerobic) | DT50 (typical) | 10000 | A2 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 ) 2 = Unverified data of unknown source |
Very persistent |
| DT50 (lab at 20 °C) | - | - | - |
| DT50 (field) | - | - | - |
| DT90 (lab at 20 °C) | - | - | - |
| DT90 (field) | - | - | - |
| DT50 modelling endpoint | - | - | - |
| Note | EU 2018 dossier: No degradation expected |
| 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 | Stable | 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 |
Stable |
| Note | - |
| Aqueous hydrolysis DT50 (days) at 20 °C and pH 7 | Value | Stable | 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 |
Stable |
| 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 | 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 metabolites
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|---|
| Mammals - Acute oral LD50 (mg kg−1) | > 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 |
Low |
| 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) | > 616 | 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 as copper5 = Verified data used for regulatory purposes |
Moderate |
| Birds - Short term dietary (LC50/LD50) | > 334.1 mg CU kg bw−1 day−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) | - | - | - |
| Earthworms - Acute 14 day LC50 (mg kg−1 dw soil) | > 195.5 | 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 ) 5 = Verified data used for regulatory purposes |
Moderate |
| Earthworms - Chronic NOEC, reproduction (mg kg−1 dw soil) | - | - | - |
| Soil micro-organisms | 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: 20 kg Cu/ha; 28 Day |
- |
| 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) | > 25.2 | 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 ) Apis mellifera5 = Verified data used for regulatory purposes |
Moderate |
| Oral acute LD50 (worst case from 24, 48 and 72 hour values - μg bee−1) | > 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 ) Apis mellifera5 = Verified data used for regulatory purposes |
Moderate |
| 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) as Mortality LR50 g Cu/ha, Std lab test | > 14700 | 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 ) Aphidius rhopalosiphi5 = Verified data used for regulatory purposes |
Low |
| Beneficial insects (Predatory mites) as Mortality LR50 g Cu/ha, Std lab test | > 13200 | 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 ) Typhlodromus pyri5 = Verified data used for regulatory purposes |
Low |
| Beneficial insects (Ground beetles) | - | - | - |
| Property | Value | Source; quality score; and other information | Interpretation |
|---|---|
| Temperate Freshwater Fish - Acute 96 hour LC50 (mg l−1) | 21.39 | 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 |
Moderate |
| Temperate Freshwater Fish - Chronic 21 day NOEC (mg l−1) | 22.5 | 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 ) Oncorhynchus mykiss5 = Verified data used for regulatory purposes |
Low |
| Tropical Freshwater Fish - Acute 96 hour LC50 (mg l−1) | - | - | - |
| Temperate Freshwater Aquatic invertebrates - Acute 48 hour EC50 (mg l−1) | 1.87 | 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) | 0.02 | 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 |
| 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) (EC50) | 0.145 | F1 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 ) Lemna minor1 = Estimated data with little or no verification |
Moderate |
| Aquatic plants (rooted, growth rate, fresh) - 14 day (mg l−1) | - | - | - |
| Algae - Acute (growth rate, fresh; mg l−1) (72 hr ErC50, Static) | 0.041 | 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) | - | - | - |
| 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) | Not applicable | - | - |
| Mammals - Acute oral LD50 (mg kg−1) | > 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 |
Low |
| Mammals - Dermal LD50 (mg kg−1 body weight) | > 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 |
- |
| Mammals - Inhalation LC50 (mg l−1) | 1.97 | 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 (whole body)5 = Verified data used for regulatory purposes |
- |
| Other Mammal toxicity endpoints | - | - | - |
| ADI - Acceptable Daily Intake (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 |
- |
| ARfD - Acute Reference Dose (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 |
- |
| 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) | 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 |
- |
| Dermal penetration studies (%) | 1-9 | 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 ) concentration dependent5 = Verified data used for regulatory purposes |
- |
| Dangerous Substances Directive 76/464 | List II | - | - |
| Exposure Routes | Public | Negligible risk to bystanders for proposed uses |
| Occupational | Acceptable risk to operators and workers for proposed uses with PPE/PPC |
| MRLs | European | EU MRL pesticide database  |
| Great Britain | GB MRL Register  |
| Notes | - |
| Drinking Water Standards | - | - | - |
| Drinking Water MAC (μg l−1) | 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 ) EU Dir 89/778/EC limit as Cu5 = Verified data used for regulatory purposes |
- |
| 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 | Not explosive or oxidising Not expected to auto-ignite; Not highly flammable |
| CLP classification 2013 | Health: H318, H332 |
| WHO Classification | II (Moderately hazardous) |
| UN Number | - |
| Waste disposal & packaging | - |
| Shelf-life, storage, stability and reactivity | - |
TRANSLATIONS
| Language | Name |
|---|
| English | Bordeaux mixture |
| French | Bouillie bordelaise |
| German | Bordeauxbrühe |
| Danish | bordeauxvæske |
| Italian | poltiglia bordolese |
| Spanish | cobre de sulfato tribeisico |
| Greek | - |
| Polish | mieszanina Bordeaux |
| Swedish | - |
| Hungarian | Bordeau |
| Dutch | - |
| Norwegian | - |
Record last updated:
23/10/2025
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