Epoxiconazole (Ref: BAS 480F)

Epoxiconazole (Ref: BAS 480F)	Last updated: 17/07/2024
(Also known as: epoxyconazole)

SUMMARY

Epoxiconazole is a broad-spectrum fungicide. It has a low aqueous solubility and is relatively volatile. It may persist in both soil and water systems. It is not highly toxic to mammals and is not expected to bioaccumulate. Epoxiconazole is moderately toxic to birds, honeybees, earthworms and most aquatic organisms.

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
Environmental fate Moderate alert: Moderately persistent; GUS: Transition state; Drainflow: Slightly mobile; Potential for particle bound transport: Medium	Ecotoxicity High alert: Birds chronic ecotoxicity: High	Human health High alert: Mammals chronic toxicity: High; Endocrine disrupter; Reproduction/development effects

GENERAL INFORMATION

Description

A broad-spectrum fungicide for control of diseases caused by Ascomycetes, Basidiomycetes and Deuteromycetes

Example pests controlled

Black & yellow Sigatoka, Coffee rust; Septoria leaf blotch; Stem rust

Example applications

Sugarbeet; Cereals including wheat, barley, rye, oats and triticale; Coffee; Bananas

Efficacy & activity

Wheat/Eyespot=Low; Wheat/Mildew=Low; Wheat/Septoria=Moderate; Wheat/Rust=High; Wheat/Ear blight=Low; Barley/Rhynchosporium=Low; Barley/Mildew=Low; Barley/Rust=Moderate; Barley/Net blotch=Low; Barley/Ramularia=Low

Availability status

Current

Introduction & key dates

1993, first registered

GB regulatory status

GB COPR regulatory status

Phasing out

Date COPR inclusion expires

Not applicable

GB LERAP status

Cat A

EC Regulation 1107/2009 (repealing 91/414)

EC Regulation 1107/2009 status

Not approved

Dossier rapporteur/co-rapporteur

Poland

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

ATAustria	BEBelgium	BGBulgaria	CYCyprus	CZCzech Republic	DEGermany	DKDenmark	EEEstonia	ELGreece
✓	✓	✓		✓	✓	✓	✓	✓
ESSpain	FIFinland	FRFrance	HRCroatia	HUHungary	IEIreland	ITItaly	LTLithuania	LULuxembourg
✓		✓	✓	✓	✓	✓	✓	✓
LVLatvia	MTMalta	NLNetherlands	PLPoland	PTPortugal	RORomania	SESweden	SISlovenia	SKSlovakia
✓		✓	✓	✓	✓		✓	✓

Approved for use (✓) under EC 1107/2009 by Mutual Recognition of Authorisation and/or national regulations in the following EEA countries

ISIceland	NONorway

Additional information

Also used in

Australia

Chemical structure

Isomerism

A molecule with 2 chiral centres resulting in four stereoisomers

Chemical formula

C₁₇H₁₃ClFN₃O

Canonical SMILES

C1=CC=C(C(=C1)C2C(O2)(CN3C=NC=N3)C4=CC=C(C=C4)F)Cl

Isomeric SMILES

No data

International Chemical Identifier key (InChIKey)

FEVYAAHIKWPJNV-TYDMEHBZSA-N

International Chemical Identifier (InChI)

InChI=1S/C17H13ClFN3O/c18-15-4-2-1-3-14(15)16-17(23-16,9-22-11-20-10-21-22)12-5-7-13(19)8-6-12/h1-8,10-11,16H,9H2/t16-,17-/m1/s1

2D structure diagram/image available?

Yes

General status

Pesticide type

Fungicide

Substance groups

Triazole fungicide; Conazole fungicide

Minimum active substance purity

920 g kg⁻¹

Known relevant impurities

EU dossier - None declared

Substance origin

Synthetic

Mode of action

Preventative and curative action. Sterol biosynthesis inhibitor.

CAS RN

135319-73-2

Alternative/old CAS RN

106325-08-0

EC number

406-850-2

CIPAC number

609

US EPA chemical code

123909

PubChem CID

3317081

CLP index number

No data found

Molecular mass

329.76

PIN (Preferred Identification Name)

rac-1-{[(2R,3S)-3-(2-chlorophenyl)-2-(4-fluorophenyl)oxiran-2-yl]methyl}-1H-1,2,4-triazole

IUPAC name

(2RS,3SR)-1-[3-(2-chlorophenyl)-2,3-epoxy-2-(4-fluorophenyl)propyl]-1H-1,2,4-triazole

CAS name

rel-1-(((2R,3S)-3-(2-chlorophenyl)-2-(4-fluorophenyl)oxiranyl)methyl)-1H-1,2,4-triazole

Other status information

Relevant Environmental Water Quality Standards

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)

Examples of recorded resistance

Physical state

White to off-white coloured solid

Formulations

Property

Value

Example manufacturers & suppliers of products using this active now or historically

AgriGuard
BASF
Bayer Environ
Landgold
Standon
BOC Sciences
Titan Ag Pty Ltd

Example products using this active

Epic
Opus
Splice
Swing Gold
Tango super
Venture
Titan Epoxiconazole 500SC

Formulation and application details

Often supplied as a soluble concentrate which is mixed with water and applied as a spray

ENVIRONMENTAL FATE

Property

Value

Source; quality score; and other information

Interpretation

Solubility - In water at 20 °C (mg l⁻¹)

7.1

Low

Solubility - In organic solvents at 20 °C (mg l⁻¹)

100000

Ethyl acetate

140000

Acetone

28800

Ethanol

40000

Toluene

Melting point (°C)

136.2

Boiling point (°C)

310

Degradation point (°C)

310

Flashpoint (°C)

Octanol-water partition coefficient at pH 7, 20 °C

2.00 X 10⁰³

Calculated

Log P

3.3

High

Fat solubility of residues

Solubility

Soluble

Data type

Regulatory data - observed in metabolism and farm animal feeding studies

Density (g ml⁻¹)

1.38

Dissociation constant pKa) at 25 °C

Not applicable

No dissociation

Vapour pressure at 20 °C (mPa)

3.5 X 10^-04

Low volatility

Henry's law constant at 25 °C (Pa m³ mol⁻¹)

1.649 X 10^-05

Non-volatile

Volatilisation as max % of applied dose lost

From plant surface

24 hr

Volatilisation is not considered critical for air pollution

From soil surface

24 hr

Volatilisation is not considered critical for air pollution

Maximum UV-vis absorption L mol⁻¹ cm⁻¹

204nm = 32000, 263nm = 390; No absorption above 290nm

Surface tension (mN m⁻¹)

72.9

at 20°C 6.4mg l⁻¹

Degradation

Property

Value

Source; quality score; and other information

Interpretation

General biodegradability

Not readily biodegradable

Soil degradation (days) (aerobic)

DT₅₀ (typical)

353.5

Persistent

DT₅₀ (lab at 20 °C)

353.5

Persistent

DT₅₀ (field)

97.7

Moderately persistent

DT₉₀ (lab at 20 °C)

1000

Very persistent

DT₉₀ (field)

2960

DT₅₀ modelling endpoint

Note

EU 2019 dossier lab studies DT₅₀ (normalised) range 127.1-1000 days, DT₉₀ (measured) > 1000 days, Soils=20. Field studies DT₅₀ (measured) range 0.75-247.8 days, DT₉₀ (measured) range 183.7->10,000 days, Soils=12; Other studies: lab DT₅₀ range 224-2236 days, field range 52-226 days

Dissipation rate RL₅₀ (days) on plant matrix

Value

Note

Dissipation rate RL₅₀ (days) on and in plant matrix

Value

11.8

Note

Published literature RL₅₀ range 3.1-26.5 days, 5 field crops, various matrices, n=5

Aqueous photolysis DT₅₀ (days) at pH 7

Value

Stable

Note

Aqueous hydrolysis DT₅₀ (days) at 20 °C and pH 7

Value

Stable

Note

Stable pH 5 to pH 9 at 25 °C, some hydrolysis at elevated temperatures

Water-sediment DT₅₀ (days)

103.6

Slow

Water phase only DT₅₀ (days)

1000

(default)

Stable

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

Soil adsorption and mobility

Property

Value

Source; quality score; and other information

Interpretation

Linear

K_d (mL g⁻¹)

K_oc (mL g⁻¹)

Notes and range

Freundlich

K_f (mL g⁻¹)

12.2

Slightly mobile

K_foc (mL g⁻¹)

894

¹/_n

0.86

Notes and range

EU 2019 dossier K_f range 8.24-17.8 mL g⁻¹, K_foc range 702-1962 mL g⁻¹, ¹/_n range 0.83900.882, Soils=5

pH sensitivity

Fate indices

Property

Value

Source; quality score; and other information

Interpretation

GUS leaching potential index

2.09

Calculated

Transition state

SCI-GROW groundwater index (μg l⁻¹) for a 1 kg ha⁻¹ or 1 l ha⁻¹ application rate

Value

9.22 X 10^-02

Calculated

Note

Potential for particle bound transport index

Medium

Calculated

Potential for loss via drain flow

Slightly mobile

Calculated

Photochemical oxidative DT₅₀ (hrs) as indicator of long-range air transport risk

43.92

Calculated using the Atkinson method. Assumed 0.5E+06 OH/cm³, 24 hr

Below the level of concern for long-range air transport

Bio-concentration factor

BCF (l kg⁻¹)

Whole fish

Low potential

CT₅₀ (days)

0.8

Known soil metabolites

Metabolite

Major/Minor fraction

$Click here for further information on Major/Minor fraction$

Estimated maximum occurrence fraction

Notes

1,2,4-triazole (Ref: CGA 71019)

Minor fraction

0.066

1-(2-chlorophenyl)-2-(4-fluorophenyl)-1-hydroxy-3-(1H-1,2,4-triazol-1-yl)propane (Ref: BF480-alcohol)

1-[(2Z)-3-(2-chlorophenyl)-2-(4-fluorophenyl)-2 propenyl]-1H-1,2,4-triazole (Ref: BF480-entriazole)

Known groundwater metabolites

None

Other known metabolites

Metabolite name and reference

Aliases

Formation medium / Rate

Estimated maximum occurrence fraction

triazole alanine

Plant

1H-1,2,4-triazol-1-ylacetic acid (Ref: CGA 142856)

TAA

Plant

triazoly hydroxyl propionic acid (Ref: 480M50)

THPA

Plant

triazole acetic acid

Plant

1-[(2Z)-3-(2-chlorophenyl)-2-(4-fluorophenyl)-2 propenyl]-1H-1,2,4-triazole (Ref: BF480-entriazole)

Surface wtaer; Sediment

ECOTOXICOLOGY

Terrestrial ecotoxicology

Property

Value

Source; quality score; and other information

Interpretation

Mammals - Acute oral LD₅₀ (mg kg⁻¹)

3160

Rat

Low

Mammals - Short term dietary NOEL

(mg kg⁻¹)

7.5

Rat

High

(ppm diet)

Mammals - Chronic 21d NOAEL (mg kg⁻¹ bw d⁻¹)

2.3

Rat Reproductive NOAEL

High

Birds - Acute LD₅₀ (mg kg⁻¹)

> 2000

Colinus virginianus

Low

Birds - Short term dietary (LC₅₀/LD₅₀)

> 907 mg kg bw⁻¹ day⁻¹

Colinus virginianus

Birds - Chronic 21d NOEL (mg kg⁻¹ bw d⁻¹)

0.91

Colinus virginianus NOAEL

High

Earthworms - Acute 14 day LC₅₀ (mg kg⁻¹)

> 500

Eisenia foetida corr

Moderate

Earthworms - Chronic NOEC, reproduction (mg kg⁻¹)

>= 3.24

Eisenia foetida corr

Moderate

Soil micro-organisms

Nitrogen mineralisation: No significant adverse effect
Carbon mineralisation: No significant adverse effect

28 Day

Collembola

Acute LC₅₀ (mg kg⁻¹)

Chronic NOEC (mg kg⁻¹)

0.495

Folsomia candida corr

Non-target plants

Honeybees (Apis spp.)

Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

> 100

Apis mellifera

Low

Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

> 83

Apis mellifera

Moderate

Unknown mode acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

Chronic as 10-day LDD₅₀ µg bee⁻¹ day⁻¹

45.5

Notes

Bumblebees (Bombus spp.)

Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

> 200

Bombus terrestris

Low

Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)

> 165.5

Bombus terrestris

Low

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) as Mortality LR₅₀ g ha⁻¹

> 373.5

Chrysoperla carnea

Beneficial insects (Parasitic wasps) as Mortality LR₅₀ g ha⁻¹ 48 hr

297.14

Aphidius rhopalosiphi

Beneficial insects (Predatory mites) as Mortality LR₅₀ g ha⁻¹ 7 day

4.73

Typhlodromus pyri

Beneficial insects (Ground beetles)

Aquatic ecotoxicology

Property

Value

Source; quality score; and other information

Interpretation

Temperate Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)

> 0.92

Oncorhynchus mykiss

Moderate

Temperate Freshwater Fish - Chronic 21 day NOEC (mg l⁻¹)

0.01

Oncorhynchus mykiss 28 day

Moderate

Tropical Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)

Temperate Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)

> 3.13

Daphnia magna

Moderate

Temperate Freshwater Aquatic invertebrates - Chronic 21 day NOEC (mg l⁻¹)

0.63

Daphnia magna

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)

0.0625

Chironomus riparius Emergence

High

Sediment dwelling organisms - Chronic 28 day NOEC, static, water (mg l⁻¹)

>= 0.00625

Chironomus riparius

High

Sediment dwelling organisms - Chronic 28 day NOEC, sediment (mg kg⁻¹)

0.03

Chironomus riparius Dry sediment

High

Aquatic plants - Acute 7 day EC₅₀, biomass (mg l⁻¹)

0.014

Lemna gibba

Moderate

Algae - Acute 72 hour EC₅₀, growth (mg l⁻¹)

> 10.69

Pseudokirchneriella subcapitata

Low

Algae - Chronic 96 hour NOEC, growth (mg l⁻¹)

0.0078

Pseudokirchneriella subcapitata

Moderate

Mesocosm study data

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)

3160

Rat

Low

Mammals - Dermal LD₅₀ (mg kg⁻¹ body weight)

2000

Rat

Mammals - Inhalation LC₅₀ (mg l⁻¹)

> 5.3

Rat 4 hr (nose only)

Other Mammal toxicity endpoints

ADI - Acceptable Daily Intake (mg kg⁻¹ bw day⁻¹)

0.008

Mouse SF=100

ARfD - Acute Reference Dose (mg kg⁻¹ bw day⁻¹)

0.023

Rat SF=100

AAOEL - Acute Acceptable Operator Exposure Level (mg kg⁻¹ bw day⁻¹)

0.011

Rat SF=200

AOEL - Acceptable Operator Exposure Level - Systemic (mg kg⁻¹ bw day⁻¹)

0.008

Rat SF=100

Dermal penetration studies (%)

2-36

concentration dependent

Dangerous Substances Directive 76/464

List II

Exposure Routes

Public

Acceptable risk for proposed uses

Occupational

Acceptable risk for proposed uses

MRLs

European

EU MRL pesticide database

Great Britain

GB MRL Register

Notes

GB MRL expected to deviate from the EU MRL in mid-2023

Drinking Water Standards

Drinking Water MAC (μg l⁻¹)

Mammalian dose elimination route and rate

Extensively metabolised and eliminated within 186 hr, ~17% via urine and ~78% via faeces.

Health issues

Specific human health issues

Carcinogen

Genotoxic

Endocrine disruptor

; ; ; ;

Reproduction / development effects

Acetyl cholinesterase inhibitor

Neurotoxicant

Respiratory tract irritant

Skin irritant

Skin sensitiser

Eye irritant

Phototoxicant

General human health issues

Possible liver toxicant
US EPA - likely to be a human carcinogen; CLP data - suspected carcinogen
Endocrine issues - Inhibition of aromatase activity, decrease of estrogen production

Handling issues

Property

Value and interpretation

General

Not explosive or oxidising
IMDG Transport Hazard Class 9
Not explected to auto-ignite, Not highly flammable

CLP classification 2013

Health: H351, H360Ddf
Environment: H411

WHO Classification

Not listed (Not listed)

UN Number

UN3077

Waste disposal & packaging

Packaging Group III (minor danger)

Shelf-life, storage, stability and reactivity

Chemically stable under standard ambient conditions. Limited shelf-life

TRANSLATIONS

Language

Name

English

epoxiconazole

French

epoxiconazole

German

Epoxiconazol

Danish

epoxiconazol

Italian

epossiconazolo

Spanish

epoxiconazol

Greek

epoxiconazole

Polish

epoksykonazol

Swedish

Hungarian

epoxikonazol

Dutch

epoxiconazool

Norwegian

Record last updated:	17/07/2024
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