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EC number: 217-915-8 | CAS number: 2008-39-1
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study with acceptable restrictions
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 999
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: EPA-Pesticide Assessment Guidelines, Subdivision F, Hazard Evaluation, Human and Domestic Animals, Series 81, 82, and 83, US Department of Commerce, National Technical Information Service PB91-154617, 1991.
- Deviations:
- not specified
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Dimethylammonium 2,4-dichlorophenoxyacetate
- EC Number:
- 217-915-8
- EC Name:
- Dimethylammonium 2,4-dichlorophenoxyacetate
- Cas Number:
- 2008-39-1
- Molecular formula:
- C8H6Cl2O3.C2H7N
- IUPAC Name:
- dimethylammonium 2,4-dichlorophenoxyacetate
- Details on test material:
- - Name of test material (as cited in study report): 2,4-D DMA, 2,4-D dimethylamine salt
- Analytical purity: 66.2% active ingredient
- Source of the test material: Industrial Task Force II on 2,4-D Research Data
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Sprague-Dawley, Frederick, MD, USA
- Diet: commercial diet "Purina certified Laboratory Chow (R) #5002” ad libitum
- Water: ad libitum
- Acclimation period: at least 6 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): approx. 21
- Humidity (%): approx. 50
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- sterile deionized water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
2,4-D DMA was mixed with sterile deionized water - Duration of treatment / exposure:
- single administration of 10 mL/kg body weight of the dosing solution
- Frequency of treatment:
- single application
- Post exposure period:
- 24, 48 and 72 h
Doses / concentrations
- Remarks:
- Doses / Concentrations:
39.7, 132, 397 mg/kg based on the active ingredient
Basis:
nominal in water
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Route of administration: oral (gavage)
- Doses / concentrations: 80 mg/kg
Examinations
- Tissues and cell types examined:
- Bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
Doses were selected based on mortality results in range finding studies (3 mice/group).
Dose levels of 2,4-D DMA were as follows: 265, 530, 794, 1060 and 1324 mg/kg.
A top dose of 397 mg/kg was chosen based on mortality at doses of 530 mg/kg and above.
DETAILS OF SLIDE PREPARATION:
Bone marrow samples were collected at 3 intervals after treatment by removing the adhering soft tissue and epiphyses of both femurs,
and flushing or aspirating the marrow into a centrifuge tube utilizing a volume of foetal calf serum. After centrifugation to pellet the tissue, most of the supernatant was drawn off, the cells were resuspended, and the suspension spread on slides and air-dried.
The slides were then fixed, stained in either May-Gruenwald/Giemsa or Wright-Giemsa. - Evaluation criteria:
- 1000 polychromatic erythrocytes (PCE) were evaluated from each animal for the incidence of micronucleated polychromatic erythrocytes (MN-PCE).
Treatment induced perturbation in bone marrow erythropoiesis was ascertained by determining the relative proportion of PCE to normochromatic
erythrocytes (NCE). - Statistics:
- Analysis of the data was performed using an analysis of variance on the square root arcsine transformation which was performed on the proportion of cells with micronuclei per animals followed by Tukey`s Studentized Range test (HSD) with adjustments for multiple comparison.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
Any other information on results incl. tables
Table 1:Pattern of mortality from range-finding studies of 2,4-D DMA
Dose (mg/kg body weight) |
Sex |
No. of dead animals |
265 |
Male |
0/3 |
Female |
0/3 |
|
530 |
Male |
1/3 |
Female |
0/3 |
|
794 |
Male |
3/3 |
Female |
2/3 |
|
1060 |
Male |
3/3 |
Female |
3/3 |
|
1324 |
Male |
3/3 |
Female |
3/3 |
Treatment (mg/kg)a |
Sex |
24 h sacrifice |
48 h sacrifice |
72 h sacrifice |
|||
% MN-PCEb |
Ratio PCE/ NCEc |
% MN-PCE |
Ratio PCE/ NCE |
% MN-PCE |
Ratio PCE/ NCE |
||
Negative control 10 mL/ kg water |
Male |
0.06 ± 0.04d |
0.45 ± 0.07 |
- |
- |
- |
- |
Female |
0.06 ± 0.06 |
0.84 ± 0.07 |
- |
- |
- |
- |
|
Positive control 80 mg/ kg cyclophosphamide |
Male |
1.48 ± 0.35* |
0.57 ± 0.06 |
- |
- |
- |
- |
Female |
2.12 ± 0.36* |
0.87 ± 0.15 |
- |
- |
- |
- |
|
39.7 |
Male |
0.04 ± 0.02 |
0.51 ± 0.03 |
0.10 ± 0.03 |
0.72 ± 0.05 |
0.12 ± 0.07 |
0.57 ± 0.07 |
Female |
0.02 ± 0.02 |
0.77 ± 0.08 |
0.06 ± 0.06 |
0.73 ± 0.17 |
0.08 ± 0.04 |
0.75 ± 0.13 |
|
132 |
Male |
0.06 ± 0.04 |
0.47 ± 0.08 |
0.12 ± 0.05 |
0.62 ± 0.12 |
0.06 ± 0.06 |
0.79 ± 0.17 |
Female |
0.08 ± 0.06 |
0.08 ± 0.13 |
0 |
0.66 ± 0.12 |
0.04 ± 0.04 |
0.70 ± 0.08 |
|
397 |
Male |
0.12 ± 0.06 |
0.33 ± 0.05 |
0.02 ± 0.02 |
0.55 ± 0.06 |
0.18 ± 0.06 |
0.48 ± 0.03 |
Female |
0.04 ± 0.02 |
0.75 ± 0.10 |
0.06 ± 0.04 |
0.47 ± 0.09 |
0.08 ± 0.04 |
0.38 ± 0.13 |
There was no significant increase in the frequency of micronucleated polychromatic erythrocytes.
- = not done
* = significantly greater than the corresponding vehicle control, p < 0.05
a = based on active ingredient content
b = Percent micronucleated cells based on the total polychromatic cells present in the scored optic field.
c = Ratio of polychromatic (PCE) to normochromatic cells (NCE), based upon the number of NCE in the optical fields containing 1000 PCE.
d = data are means and standard deviations
No increase in the incidence of micro-nucleated polychromatic erythrocytes in any sex or at any time point in the treated mice was observed. Therefore no clastogenic potential could be detected in this test
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
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