Dimethachlor (Ref: CGA 17020)

Dimethachlor (Ref: CGA 17020)	Last updated: 14/01/2021
(Also known as: dimethachlore)

GENERAL INFORMATION

Description

A herbicide used pre-emergence to control most annual grasses and broad-leaved weeds

Example pests controlled

Loose silky-bent; Meadow grass; Brome; Slender foxtail; Common chickweed; Red dead-nettle; Mayweed

Example applications

Winter oilseed rape; Soybeans; Sugarbeet

Efficacy & activity

Availability status

Current

Introduction & key dates

1977

UK regulatory status

UK COPR regulatory status

Approved

Date COPR inclusion expires

31/12/2024

UK LERAP status

Crop over 5m - See Authorisation for Crop LERAP Details

EC Regulation 1107/2009 (repealing 91/414)

EC Regulation 1107/2009 status

Approved

Dossier rapporteur/co-rapporteur

Hungary/Austria

Date EC 1107/2009 inclusion expires

31/12/2021

EU Candidate for substitution (CfS)

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
✓			✓		✓		✓	✓

Also used in

Chemical structure

Isomerism

Chemical formula

C₁₃H₁₈ClNO₂

Canonical SMILES

CC1=C(C(=CC=C1)C)N(CCOC)C(=O)CCl

Isomeric SMILES

No data

International Chemical Identifier key (InChIKey)

SCCDDNKJYDZXMM-UHFFFAOYSA-N

International Chemical Identifier (InChI)

InChI=1S/C13H18ClNO2/c1-10-5-4-6-11(2)13(10)15(7-8-17-3)12(16)9-14/h4-6H,7-9H2,1-3H3

2D structure diagram/image available?

Yes

General status

Pesticide type

Herbicide

Substance group

Chloroacetamide

Minimum active substance purity

Known relevant impurities

Substance origin

Synthetic

Mode of action

Selective, absorbed by new shoots of seedlings and roots. Inhibition of VLCFA (inhibition of cell division)

CAS RN

50563-36-5

EC number

256-625-6

CIPAC number

688

US EPA chemical code

PubChem CID

39722

Molecular mass

255.74

PIN (Preferred Identification Name)

2-chloro-N-(2,6-dimethylphenyl)-N-(2-methoxyethyl)acetamide

IUPAC name

2-chloro-N-(2-methoxyethyl)acet-2',6'-xylidide

CAS name

2-chloro-N-(2,6-dimethylphenyl)-N-(2-methoxyethyl)acetamide

Other status information

Relevant Environmental Water Quality Standards

Herbicide Resistance Classification (HRAC)

Herbicide Resistance Classification (WSSA)

Insecticide Resistance Classification (IRAC)

Not applicable

Fungicide Resistance Classification (FRAC)

Not applicable

Examples of recorded resistance

Physical state

Colourless crystals

Formulations

Property

Value

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

Teridox 500Ec

Example products using this active

Ciba-Geigy

Formulation and application details

Usually supplied as an emulsifiable concentrate

ENVIRONMENTAL FATE

Property

Value

Source; quality score; and other information

Interpretation

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

2300

High

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

500000

Methanol

500000

Acetone

42000

Hexane

440000

Octanol

Melting point (°C)

46.3

Boiling point (°C)

Decomposes before boiling

Degradation point (°C)

300

Flashpoint (°C)

Not expected to self ignite; Not highly flammable

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

1.48 X 10⁰²

Calculated

Log P

2.17

Low

Bulk density (g ml⁻¹)

1.23

Dissociation constant pKa) at 25 °C

Not applicable

No dissociation

Vapour pressure at 20 °C (mPa)

0.64

Low volatility

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

1.70 X 10^-04

Non-volatile

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

Neutral solution: 215nm = 14461, 265nm = 486
Acidic solution: 215nm = 14768, 265nm = 572
Basic solution: 215nm = 9576, 265nm = 469

Surface tension (mN m⁻¹)

57.2-66.1

at 20°C 0.19-1.9g l⁻¹

Degradation

Property

Value

Source; quality score; and other information

Interpretation

General biodegradability

Soil degradation (days) (aerobic)

DT₅₀ (typical)

Non-persistent

DT₅₀ (lab at 20 °C)

6.5

Non-persistent

DT₅₀ (field)

3.2

Non-persistent

DT₉₀ (lab at 20 °C)

27.8

Non-persistent

DT₉₀ (field)

10.5

DT₅₀ modelling endpoint

Note

EU dossier lab studies DT₅₀ range 2.3 (silt loam) - 15.6 (loamy sand) days, DT₉₀ range 11-65.9 days

Dissipation rate RL₅₀ on plant matrix

Value

Note

Dissipation rate RL₅₀ on and in plant matrix

Value

Note

Aqueous photolysis DT₅₀ (days) at pH 7

Value

Stable

Note

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

Value

200

Persistent

Note

Stable pH 1 to pH 9, DT₅₀ 9.3 days at pH 13 up to 50 °C

Water-sediment DT₅₀ (days)

14.1

Fast

Water phase only DT₅₀ (days)

Moderately fast

Soil adsorption and mobility

Property

Value

Source; quality score; and other information

Interpretation

Linear

K_d

K_oc

Notes and range

Freundlich

K_f

4.20

Mobile

K_foc

¹/_n

0.91

Notes and range

EU dossier kf range 0.32-18.4, K_foc range 29.7-128 mL g⁻¹, ¹/_n range 0.760-0.939, Soils=10

pH sensitivity

Fate indices

Property

Value

Source; quality score; and other information

Interpretation

GUS leaching potential index

1.09

Calculated

Low leachability

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

Value

2.50 X 10^-03

Calculated

Note

Potential for particle bound transport index

Low

Calculated

Potential for loss via drain flow

Mobile

Calculated

Key metabolites

Metabolite

Formation medium

Estimated maximum occurrence fraction

1107/2009 relevancy

N-(2,6-dimethylphenyl)-N-(2-methoxyethyl)oxalamic acid (Ref: CGA 50266)

Soil

0.355

Major fraction, Relevant

((2,6-dimethylphenyl)-2-methoxyethyl)carbamoyl)methanesulfonic acid sodium salt (Ref: CGA 354742)

Soil

0.158

Major fraction, Relevant

Other known metabolites

Metabolite name and reference

Aliases

Formation medium / Rate

Estimated maximum occurrence fraction

Metabolising enzymes

3-{2-[(2,6-dimethyl-phenyl)-(2-hy-droxyacetyl)amino]ethylsulfanyl}-2-hydroxypropionic acid (Ref: SYN 528702)
Note: Risk to groundwater

Soil (Aerobic)

(2,6-dimethylphenylcarbamoyl)-methanesulfonic acid sodium salt (Ref: CGA 369873)
Note: Detected in lysimeter leachate; Risk to groundwater

Soil (Aerobic); Groundwater

[(2,6-dimethylphenyl)-(2-sulfo-acetyl)amino]acetic acid sodium salt (Ref: CGA 373464)
Note: Detected in lysimeter leachate; Risk to groundwater

Soil (Aerobic)

2-[(2-hydroxyacetyl)-(2-methoxy-ethyl)amino]-3-methylbenzoic acid (Ref: SYN 530561)
Note: Detected in lysimeter leachate; Risk to groundwater

Soil (Aerobic)

N-carboxymethyl-N-(2,6-dimethyl-phenyl)oxalamic acid (Ref: CGA 102935)
Note: Risk to groundwater

Soil (Aerobic)

N-(2,6-dimethylphenyl)-N-(2-methoxyethyl)acetamide (Ref: CGA 42443)

Soil (Anaerobic); Water/sediment

IMPURITY

2,6-dimethylaniline (Ref: CGA 72649)

Not applicable

ECOTOXICOLOGY

Property

Value

Source; quality score; and other information

Interpretation

Bio-concentration factor

BCF (l kg⁻¹)

Estimated

Low potential

CT₅₀ (days)

Not available

Mammals - Acute oral LD₅₀ (mg kg⁻¹)

1600

Rat

Moderate

Mammals - Short term dietary NOEL

(mg kg⁻¹)

> 12

Rat 2 year

High

(ppm diet)

> 300

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

267

Rat Reproductive NOAEL

Low

Birds - Acute LD₅₀ (mg kg⁻¹)

524

Coturnix japonica

Moderate

Birds - Short term dietary (LC₅₀/LD₅₀)

> 1470 mg kg bw⁻¹ day⁻¹

Coturnix japonica

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

102

Coturnix japonica (females acid) NOEL

Moderate

Fish - Acute 96 hour LC₅₀ (mg l⁻¹)

3.9

Oncorhynchus mykiss

Moderate

Fish - Chronic 21 day NOEC (mg l⁻¹)

0.85

Oncorhynchus mykiss

Moderate

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

Daphnia magna

Moderate

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

2.3

Daphnia magna

Moderate

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)

4.0

Chironomus riparius

Moderate

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

25.0

Chironomus riparius

Moderate

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

0.035

Lemna gibba

Moderate

Non-target plants

> 1500

Echinochloa crusgalli
Vegetative vigour, ER₅₀
as g ha⁻¹

> 1500

Echinochloa crusgalli
Seedling emergence, ER₅₀
as g ha⁻¹

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

0.0065

Pseudokirchneriella subcapitata

High

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

Honeybees (Apis spp.)

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

> 200

Apis mellifera

Low

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

> 300

Apis mellifera

Low

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

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 pollinators (1)

Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)

Mode of exposure

Other pollinators (2)

Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)

Mode of exposure

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

Eisenia foetida corr

Moderate

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

Other soil macro-organisms

Acute LC₅₀ (mg kg⁻¹)

Chronic NOEC (mg kg⁻¹)

Other arthropod (1)

LR₅₀ g ha⁻¹

48 hour
Aphidius rhopalosiphi adult

% Effect

Other arthropod (2)

LR₅₀ g ha⁻¹

655

7 day
Typhlodromus pyri

% Effect

Soil micro-organisms

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

Dose: 7.5 kg ha⁻¹ 28 days

Mesocosm study data

NOEAEC mg l⁻¹

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)

1600

Rat

Moderate

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

2000

Rat

Mammals - Inhalation LC₅₀ (mg l⁻¹)

> 4.45

Rat 4 hr (nose only)

Other Mammal toxicity endpoints

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

0.1

Rat SF=100

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

0.5

Rat SF=100

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

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

0.1

Dog SF=100

Dermal penetration studies (%)

3.0-10.0

concentration dependent

Dangerous Substances Directive 76/464

Exposure Routes

Public

No unacceptable risks to bystanders identified

Occupational

No unacceptable risks to operators or other workers identified

European MRLs

EU MRL pesticide database

Drinking Water Standards

Drinking Water MAC (μg l⁻¹)

0.1

EU Dir 89/778/EC limit

Health issues

Specific human health issues

Carcinogen

Genotoxic

Endocrine disruptor

; ; ; ;

No data found

Reproduction / development effects

Acetyl cholinesterase inhibitor

Neurotoxicant

Respiratory tract irritant

Skin irritant

Skin sensitiser

Eye irritant

Phototoxicant

No data found

General human health issues

No further information available

Handling issues

Property

Value and interpretation

General

Not explosive or oxidising
IMDG Transport Code is usually 9

CLP classification 2013

Health: H302, H317
Environment: H400, H410

EC Risk Classification

Xn - Harmful: R22, R43
N - Dangerous for the environment: R50, R53

EC Safety Classification

S2, S24, S37, S60, S61

WHO Classification

II (Moderately hazardous)

UN Number

Usualy 3077

Waste disposal & packaging

Packaging Group III (minor danger)

TRANSLATIONS

Language

Name

English

dimethachlor

French

dimethachlore

German

Dimethachlor

Danish

dimethachlor

Italian

dimetaclor

Spanish

dimetacloro

Greek

dimethachlor

Polish

dimetachlor

Swedish

Hungarian

dimetaklor

Dutch

Record last updated:	14/01/2021
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