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EC number: 201-174-2 | CAS number: 79-07-2
- 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
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- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
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- Nanomaterial surface chemistry
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- Nanomaterial pour density
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- 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
Endpoint summary
Administrative data
Description of key information
Oral repeated dose toxicity was examined in a key 90-day study and 3 supporting 28- and 90-day studies in rats. Testes, liver, kidney and thyroids were identified as target organs. The overall oral NOAEL was determined to be 10 mg/kg bw/day.
In a key and a supporting dermal repeated dose toxicity study the dermal NOAEL was determined to be 50 mg/kg bw/day.
2 Supporting repeated dose studies with subcutaneous or intravenous administration of Chloroacetamide both resulted in a NOAEL of 10 mg/kg bw/day.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted under GLP and it was done according to valid methods, therefore it is considered relevant, reliable and adequate for classification.
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.27 (Sub-Chronic Oral Toxicity Test: Repeated Dose 90-Day Oral Toxicity Study in Non-Rodents)
- Deviations:
- yes
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
- Deviations:
- yes
- Principles of method if other than guideline:
- No. of animals per group was limited to 10, of which the first 5 were the main group and the next 5 were used for 29-day recovery. This is not considered to impact the study as there is extensive dose response information from other 28- and 90-day toxicity studies.
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Wistar: Hoe: WISKf(SPF71)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Hoechst AG, Hattersheim-Kastengrund (Germany), SPF-Zucht,
- Age at study initiation: Males ca. 4 weeks; females ca. 5 weeks
- Weight at study initiation: Average males 79.8 g; average females 85.4 g
- Housing: Draft mesh cages (Type 3), in groups until 2 animals
- Diet: Rattendiät Altromin 1321 by Altromin GmbH Lage/Lippe (Germany) ad libitum
- Water: Tap water in plastic bottles, ad libitum
- Acclimation period: At least 5 days before study
ENVIRONMENTAL CONDITIONS
Fully airconditioned rooms - Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS: 1kg premix of the 10 fold end concentration was mixed together with 9 kg Altromin 1321 in a ploughshare mixer for 20 minutes. Every mixture was examined analytically for concentration and homogeneity of the test substance.
DIET PREPARATION
- Rate of preparation of diet (frequency): weekly
- Mixing appropriate amounts with (Type of food): Rattendiät Altromin 1321 - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Extraction of the active ingredient from the spiked diet using methanol (Chromasolv R). Concentration and dilution in methanol
(Chromasolv R). Determination of the active ingredient using gaschromatography with a nitrogen selective detector (PND).
(cf report Dr. Thier dd 1984-07-12 / encluded in the study report) - Duration of treatment / exposure:
- 90 days
- Frequency of treatment:
- daily
- Remarks:
- Doses / Concentrations:
0, 2, 10, 50 mg/kg bw/day
Basis:
nominal in diet - No. of animals per sex per dose:
- 10 (of which the first 5 animals were used as the main group, and the next 5 animals for 29-day recovery)
- Control animals:
- yes
- Details on study design:
- - Dose selection rationale: In an earlier 90 days oral repeated dose study doses of 12.5 and 50 mg/kg bw/day were administered. These doses were too high to determine a no effect level. Purpose of this experiment was to determine a no effect level.
- Rationale for selecting satellite groups: first 5 animals of each group were killed at the end of testing; the other 5 were killed after 29 days recovery period.
- Post-exposure recovery period in satellite groups:29 days - Observations and examinations performed and frequency:
- -Monday - Friday 2x daily, on weekends 1x daily: behaviour /health state
-1x weekly: neurological disorders, opacities of eyes, injuries of the mouth's mucous membrane, disturbed toothgrowth
-2x weekly, during acclimation, study and recovery: body weight
-2x weekly during study: feed used; 1x weekly water used
-end of study or end of recovery period: haematological parameters in the blood: Hemoglobin; Erythrocyte count, Leucocyte count, Hematocrit, Reticulocyte count *, Heinz bodies *, Differential Blood Count, Platelet Count, Clotting time (* only in the control group and high dose group)
-after sacrifice: clinical-chemical parameters in the serum: Sodium, Potassium, Inorganic Phosphorus, Uric acid, Bilirubin total, Creatinine, Serum glucose, Urea-N (BUN), Calcium, Chloride, SGOT, SGPT, Alk. Phospatase
-night between 88./89. study day, 16 h urine: urinanalysis (animals unfeed, unwatered): Appearance, Color, Protein, Glucose, Hemoglobin, Bilirubin, pH value, Ascorbic acid, Ketone bodies, Density * (only from high dose and control group), Sediment - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
- Sacrifice by i.p. injection of 50 mg Nembutal / kg bw / de-bleeding by opening the vena cava cranialis
- gross assessment according to Hoechst Sektionsordnung I, Prof. K/G dd 1982-02-04
-relative organ weights (% of bw)
HISTOPATHOLOGY: Yes
- histological assessment of fixated organ or preparations according to Hoechst Sektionsordnung I, Prof. K/G dd 1982-02-04: heart, lungs, liver, kidneys, spleen, stomach, jejunum, colon, bladder, testes, epidiymis, prostate, seminal vesicle, ovaries, uterus,thyroid, pancreas, adrenals, thymus, pituitary gland, brain, eyes with N. opticus, bone marrow (femur marrow) - Other examinations:
- Feed analysis (see Table 1)
- Statistics:
- Statistical evaluation of following measured values, using probability level 0.05:
- body weight at observation times
- body weight gain during intervals
- haematological parameters (except differential blood count)
- clinical chemical parameters
- urinanalysis (pH, density)
- absolute/ relative organ weights
Hoechst evaluation software used according to SOP Dr. Passing, Department of Practical Mathematics. - Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- effects observed, treatment-related
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY: no effects, no mortalities during dosing & recovery period.
BODY WEIGHT AND WEIGHT GAIN: decreased in males & femaels in highest dose from week 2/3 onwards, respectively; reversible in recovery period.
FOOD CONSUMPTION AND COMPOUND INTAKE: decreased in males & females during first 30 days. No effects in recovery period.
FOOD EFFICIENCY: no data
WATER CONSUMPTION: no effects during dosing & recovery period.
OPHTHALMOSCOPIC EXAMINATION: no effects during dosing & recovery period.
HAEMATOLOGY: increased white blood cells at highest dose; reversible in recovery period.
CLINICAL CHEMISTRY: no effects during dosing & recovery period.
URINALYSIS: no effects during dosing & recovery period.
NEUROBEHAVIOUR: no effects during dosing & recovery period.
ORGAN WEIGHTS: male rats, highest dose: reduced testicular weights; still observed in the recovery group - decreased liver weight in females, highest dose; reversible in recovery period however decreased liver weight in males after recovery period.
GROSS PATHOLOGY: male rats, highest dose: smaller testes, reversible in the recovery group
HISTOPATHOLOGY: male rats, highest dose: depression - standstill of spermiogenesis and proliferation of Leydig cells and other interstitial cells in testes; absence of mature & immature sperms instead only loose connective tissue visible in epidydimides; in the recovery group starting to complete regeneration was observed. - Dose descriptor:
- NOAEL
- Effect level:
- 100 mg/kg diet
- Based on:
- test mat.
- Sex:
- male/female
- Dose descriptor:
- NOAEL
- Effect level:
- 10 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Critical effects observed:
- not specified
- Conclusions:
- Chloroacetamide in this 90 day oral repeated dose study in rats caused a decreased body weight gain and increased leucocyte count in the high dose male and female rats. The high dose males had smaller testes, depression- standstill of the spermiogenesis and proliferation of Leydig cells. After a 29 day recovery period, there were signs of beginning or ended regeneration of the testicular tubuli.
The NOAEL for Chloroacetamide in this study was determined to be 10 mg/kg bw/day. - Executive summary:
In a 90 day oral repeated dose study in Wistar rats were given doses of 0, 20, 100 and 500 mg Chloroacetamide test substance/kg feed /day. Each group consisted of 10 male and 10 female animals, of which the first 5 animals of each group, were killed at the end of the 90 day, whereas the other 5 were killed after a 29 day recovery period. In the high dose (500 mg/kg feed) male and female animals showed reduced body weight gain and food consumption and increased leucocytes in both sexes, decreased liver weights in females, and smaller testes, reduced testicular weights, proliferation of Leydig/other interstitial cells and depression - standstill of spermiogenesis in males.Re-onset in the recovery group with partial to complete regeneration of testes was observed in males, therefore this was to be designated as reversible. Further liver weights were reversed in females and slightly decreased in males in the hightest dose recovery groups. The NOAEL was determined to be 100 mg/kg feed, which was reported to correspond with 10 mg/kg bw/day.
Reference
Table 1 Feed analysis
Mixture 1 | (11.01.1984) | Means | |||||
Dose | mg/kg added | days after | mg/kg found | mg/kg in | |||
mg/kg | test subst. | act.ingr. | preparation | Act. Ingr. | Test subst. | feed (real) | |
20 | 20,1 | 20 | 1 | 19 | 19 | ||
20 | 20,1 | 20 | 1 | 14 | 14 | 16,5 | |
100 | 100 | 99,8 | 1 | 92 | 92 | ||
100 | 100 | 99,8 | 1 | 81 | 81 | 86,5 | |
500 | 500 | 499 | 1 | 453 | 454 | ||
500 | 500 | 499 | 1 | 479 | 480 | 467 | |
Mixture 2 | (22.02.1984) | ||||||
Dose | mg/kg added | days after | mg/kg found | mg/kg in | |||
mg/kg | test subst. | act.ingr. | preparation | Act. Ingr. | Test subst. | feed (real) | |
20 | 20 | 19,9 | 1 | 16 | 16 | ||
20 | 20 | 19,9 | 1 | 13 | 13 | 14,5 | |
100 | 100 | 99,7 | 1 | 77 | 77 | ||
100 | 100 | 99,7 | 1 | 78 | 78 | 77,5 | |
500 | 500 | 499 | 1 | 396 | 397 | ||
500 | 500 | 499 | 1 | 381 | 382 | 389,5 | |
Mixture 3 | (24.04.1984) | ||||||
Dose | mg/kg added | days after | mg/kg found | mg/kg in | |||
mg/kg | test subst. | act.ingr. | preparation | Act. Ingr. | Test subst. | feed (real) | |
20 | 20 | 19,9 | 1 | 14 | 14 | ||
20 | 20 | 19,9 | 1 | 14 | 14 | 14 | |
100 | 100 | 99,7 | 1 | 63 | 63 | ||
100 | 100 | 99,7 | 1 | 68 | 68 | 65,5 | |
500 | 500 | 499 | 1 | 362 | 363 | ||
500 | 500 | 499 | 1 | 361 | 362 | 362,5 | |
Overall means | |||||||
Nomimal doses feed | Measured doses feed | ||||||
mg/kg | mg/kg | ||||||
20 | 15,0 | ||||||
100 | 76,5 | ||||||
500 | 406,3 |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 10 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- High (Klimisch 1)
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 3 (not reliable)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted before GLP application and only limited details were available, therefore it is considered less reliable and adequate for classification.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 410 (Repeated Dose Dermal Toxicity: 21/28-Day Study)
- Deviations:
- yes
- Remarks:
- 1 sex only (the impact is considered limited)
- Principles of method if other than guideline:
- Hoechst AG Guideline
- GLP compliance:
- no
- Limit test:
- no
- Species:
- rabbit
- Strain:
- other: Yellow-Silver breed
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Weight at study initiation: average 2.46 kg (1.89-3.14 kg)
- Housing: Individual cages
- Diet: Standard-Futter Altromin K (Altromin GmbH, Lage/Lippe (Germany))
- Water: Tap water - Type of coverage:
- open
- Vehicle:
- water
- Details on exposure:
- Hair depilated in the neck area, on which chloroacetamide was applied as a 40% aqueous solution.
Using a frill of synthetic material, animals were prevented from licking off / orally taking-up the substance - Duration of treatment / exposure:
- 30 days
- Frequency of treatment:
- 1x daily
- Remarks:
- Doses / Concentrations:
0, 25, 50, 100, 200, 400 mg/kg bw/day
Basis:
nominal per unit body weight - Remarks:
- Doses / Concentrations:
0, 0.063, 0.13, 0.25 0.50, 1 mL/kg
Basis:
other: volume/kg body weight - No. of animals per sex per dose:
- 5 females
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- During the study + the 3 day recovery period, animals received a standard diet Altromin K by Altromin GmbH Lage/Lippe
(Germany) as well as tap water. - Observations and examinations performed and frequency:
- Before the study and after its end, blood count and urinanalysis of all animals were done.
- Sacrifice and pathology:
- After the recovery period, all surviving animals were sacrificed by rabbit-punch and de-bleeding. The bodies were dissected and
the organs heart, lung, both kidneys, liver and spleen were histologically examined.
The same procedure was done for animals which had died during the study - except animal 479 of the highest dosage group
which died after the first application. - Clinical signs:
- effects observed, treatment-related
- Dermal irritation:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- liver, heart muscle,Hoechst, 1967) spleen
- Details on results:
- From 100 mg/kg bw/day on, a dose-related weight loss was observed.
At 100 and 200 mg/kg bw/day, dose-related histological changes were observed in the liver and heart (lipid metabolism changes) and spleen (haemosiderin deposition).
Applications of 400 mg/kg bw/day lead to lethality 3/5: 1 animal died after the 1st, 1 after the 2nd and another after the 3rd dosage.
At all dosages, encrustation to induration of the application site was observed. - Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (nominal)
- Based on:
- act. ingr.
- Sex:
- female
- Basis for effect level:
- other: Sytemic NOAEL
- Critical effects observed:
- not specified
- Conclusions:
- In the 25 and 50 mg dose groups there were no systemic effects, whereas at 100, 200 and 400 mg dose groups histological changes in liver, heart muscle and spleen and a dose dependent weight loss were observed . 3 Animals died in the highest dose group. In all dose groups there were local changes of the treated skin area (encrusted to hardened).
- Executive summary:
In a 30 day dermal repeated dose toxicity study in female rabbits, chloroacetamide was tested without coverage (open) in one control and 5 dose groups of each 5 female rabbits at 25, 50, 100, 200 and 400 mg/kg bw /day ( 0.063, 0.13, 1.25, 0.50, 1.00mL/kg bw/day). 3 Days after the end of testing all surviving animals were observed for 3 days. In the 25 and 50 mg dose groups there were no findings. One animal died, but this was not related to the administered substance. In the 100 mg dose group a slight body weight loss was observed during treatment and histological changes in liver, heart muscle and spleen. In the 200 mg dose group similar observations were done with a more significant weight loss. In the 400 mg dose group 3 animals died (1 on day 1, 2 and 3 respectively). Similar changes as in the 100 and 200 mg dose groups in liver, heart muscle and spleen were observed and a significant weight loss. In all dose groups there were local changes of the treated skin area (encrustation to induration).
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 50 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rabbit
- Quality of whole database:
- Limited (Klimisch 3)
Repeated dose toxicity: dermal - local effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study was done with a formulation having a different composition (70% Chloroacetamide; 30% sodium benzoate), however it was considered reliable, adequate and relevant for classification and local DNEL calculation. As there is no clinical biochemistry and only limited histopathology, the study cannot be used for systemic DNELs.
- Principles of method if other than guideline:
- IBR guideline
- GLP compliance:
- no
- Limit test:
- yes
- Species:
- rat
- Strain:
- other: Wistar SPF
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Winkelmann, Paderborn
- Age at study initiation: Adult
- Weight at study initiation: Average ca. 210 g
- Housing: Individual cages
- Diet: Rattenstandardiät (ssniff/Intermast), ad libitum
- Water: Ad libitum
- Acclimation period: 14 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 1°C
- Humidity (%):45-55%
- Photoperiod (hrs dark / hrs light): 12/12 - Type of coverage:
- open
- Vehicle:
- water
- Details on exposure:
- The test substance was dissolved in water, pure or supplied with 1-2 % Lanette R.
Back of animals had been partly shorn.
Using a glass rod, the test solution was applied daily onto the shorn areas. - Duration of treatment / exposure:
- 3 months / 13 weeks
- Frequency of treatment:
- daily
- Remarks:
- Doses / Concentrations:
0, 12.5, 50.0 mg/kg
Basis:
nominal per unit body weight - No. of animals per sex per dose:
- 10
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- Control: Lanette; Group I, 12.5 mg/kg in Lanette 1 %; Group II, 50.0 mg/kg in Lanette 2 %; Group III, 50.0 mg/kg in aqua dest 2 %;
- Observations and examinations performed and frequency:
- clinical symptoms : daily
body weight, weight gains, feed use, feed efficiency, water used : weekly - Sacrifice and pathology:
- section: weights of heart, liver, kidneys, adrenal glands, testicles
histology: testicles - Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Dose descriptor:
- NOAEL
- Effect level:
- 50 mg/kg bw/day (nominal)
- Sex:
- male
- Basis for effect level:
- other: clinical signs; mortality; body weight; food consumption; gross pathology; organ weights; histopathology
- Critical effects observed:
- not specified
- Conclusions:
- The dermal “no-effect” level of CA 24 in male adult rats is 50 mg/kg bw.
- Executive summary:
In a 13 weeks dermal toxicity repeated dose study, Konservierungsmittel CA 24 was applied to the shaved backs of male adult Wistar-rats, at doses of 12.5 and 50.0 mg/kg in Lanette or Aqua dest. Neither test dependent or substance specific changes were observed in the growth parameters and histomorphological examinations. The dermal “no-effect” level of CA 24 in male adult rats is 50 mg/kg bw.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 0.32 mg/cm²
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- High (Klimische 2)
The dermal “no-effect” level of CA 24 in male adult rats is 50 mg/kg bw.Taking into account the 70% Chloroacetamide content and assuming that sodium benzoate was inactive on the skin, 35 mg act./kg bw was considered as local NOAEL. Based on the lower NOAEL, this was considered as key study. Considering a mean body weight of 300 g (based on study data) and a surface area of 325 cm2 (Derelanko, 2008; The Toxicologist's Pocket handbook p29), 10.5 mg was applied on 32.5 cm2 (10% body surface), corresponding to 0.32 mg/cm2.
Additional information
In a key 90 day oral repeated dose study (Hoechst, 1985) 80 Wistar rats (40 males and 40 females) were administered at doses of 0, 20, 100 and 500 mg Chloroacetamide/kg feed /day (equivalent to 0, 2, 10 and 50 mg act.ingr./kg bw/day). In the high dose group, reduced body weight gain/food consumption and increased leucocytes were observed, as well as decreased liver weights in females, and smaller testes, reduced testicular weights, proliferation of Leydig's cells and depression - standstill of spermiogenesis in males. A reduction in testicular and epididymal size was seen. Histopathological examination revealed depression and/or cessation of spermiogenesis as well as moderate proliferation of Leydig’s cells. The epididymis contained neither mature nor immature sperm cells, only cross-linked protein. No other histopathological changes were observed in the males. The females of all dose groups were without histopathological findings. Follicle maturation was found to be normal. In the groups receiving 100 and 20 mg/kg feed ‘approximately 10 and 2 mg/kg body weight/day), no substance-related organ changes were seen. After a 29 -day recovery period, partial to complete regeneration was observed in the testis. The NOAEL was 100 mg/kg feed, corresponding with 10 mg/kg bw/day.
Various supporting oral studies in rats provided
additional dose response and target organ information:
- a 28 days study by oral gavage (Hoechst, 1958) showed increase in
urinary protein; dose dependent macroscopic histological changes in
liver (degenerative changes) and kidneys (changes attributed to
trichloro acetic acid), with NOAEL = 10 mg/kg bw/day;
- a 90 day study with Chloroacetamide in the feed in Sprague-Dawley rats
dosed at 12.5 and 50 mg/kg bw (Leuschner, 1970) showed inhibition of
body weight gain, shaggy fur, enlarged thyroid glands (females), smaller
testes in males, with dose related histological disturbance of
spermatogenesis and seminiferous tubules almost cell-free, with NOAEL <
12.5 mg/kg bw/day.
- a 90 day study with Chloroacetamide in the feed in Sprague-Dawley rats
(Kemper, 1989) also showed decreased body weights and soft/small testes
with impaired spermiogenesis in males dosed at 12.5 and 50 mg/kg feed;
decreased food consumption and histological liver changes (starting
fatty liver degeneration and atrophy) in both sexes at 50 mg/kg;
increased thyroid weights only in females dosed at 50 mg/kg; NOAEL<12.5
mg/kg bw/day.
In a 30 day dermal repeated dose toxicity (Hoechst, 1967) Chloroacetamide was tested without coverage in female rabbits at 25, 50, 100, 200 and 400 mg/kg bw /day (0.063, 0.13, 1.25, 0.50, 1.00 mL/kg bw/day). After the end of testing all surviving animals were observed for 3 days. In the 25 and 50 mg dose groups there were no findings. In the 100 mg/kg dose group a slight body weight loss was observed during treatment and histological changes in liver, heart muscle (lipid metabolism changes) and spleen (haemosiderin deposition). In the 200 mg /kg bw dose group similar observations were done with a more significant weight loss. In the 400 mg dose group 3 animals died (1 on day 1, 2 and 3 respectively). Similar changes as in the 100 and 200 mg/kg bw dose groups in liver, heart muscle and spleen were observed and a significant weight loss. In all dose groups there were local changes of the treated skin area (encrustation to induration). The dermal systemic NOAEL was 50 mg/kg bw/day.
In a 13 weeks dermal toxicity repeated dose study,
Konservierungsmittel CA 24 was applied to the shaved backs of male adult
Wistar-rats, at doses of 12.5 and 50.0 mg/kg in Lanette (1 or 2%) or
Aqua dest (2%). Neither test dependent or substance specific changes
were observed in the growth parameters and histomorphological
examinations. The dermal “no-effect” level of CA 24 in male adult rats
is 50 mg/kg bw.
Taking into account the 70% Chloroacetamide content and assuming that
sodium benzoate was inactive on the skin, 35 mg act.ingr./kg bw was
considered as local NOAEL. Based on the longer duration and the lower
NOAEL, this was considered as key study for local DNEL derivation.
Inhalation is unlikely as vapour pressure is too low and particle size is too high for potential inhalation toxicity. Therefore, inhalation testing is waived.
Two supporting 30 days repeated dose studies (Hoechst, 1967a & b) were available, where chloroacetamide was administered up to doses of 100 mg/kg bw by subcutaneous and intravenous route, respectively. The NOAEL in both studies was 10 mg/kg bw/day, whereas clinical (nervous system) observations and mortality appeared from 25 mg/kg onwards. These studies however were not relevant for classification, so they were disregarded.
Justification for selection of repeated dose toxicity via oral route - systemic effects endpoint:
Key study; the study was conducted under GLP and it was done according to valid methods, therefore it is considered relevant, reliable and adequate for classification.
Justification for selection of repeated dose toxicity dermal - systemic effects endpoint:
Supporting study; the study was conducted before GLP application and only limited details were available, therefore it is considered less reliable and adequate for classification.
Justification for selection of repeated dose toxicity dermal - local effects endpoint:
Key study with longest (90 day) duration; the study was done with a formulation having a different composition (70% Chloroacetamide; 30% sodium benzoate), however it was considered reliable, adequate and relevant for classification and local DNEL calculation.
Repeated dose toxicity: via oral route - systemic effects (target organ) digestive: liver; glandular: thyroids; urogenital: kidneys; urogenital: testes
Repeated dose toxicity: dermal - systemic effects (target organ) cardiovascular / hematological: heart; cardiovascular / hematological: spleen; digestive: liver
Justification for classification or non-classification
Chloroacetamide was classified according the EU labelling regulations Commision Directive 93/21/EEC as HARMFUL with symbol 'Xn' and risk phrase R 25 'HARMFUL IF SWALLOWED'. According to CLP regulation (No. 1272/2008 of 16 December 2008), Category 2 classification is proposed with Signal word 'Warning' and hazard statement H373 'MAY CAUSE DAMAGE TO ORGANS (TESTES, LIVER, KIDNEY) THROUGH PROLONGED OR REPEATED EXPOSURE (ORAL, 28 -90 DAYS)'.
Based on these results and according to the EC Directive (No.93/21/EEC) and CLP (No. 1272/2008 of 16 December 2008),
Chloroacetamide is proposed to be classified for repeated dose STOT Category 2 classification.Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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