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EC number: 229-347-8 | CAS number: 6484-52-2
- 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
- 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- no data
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Remarks:
- Well documented literature. The study has been performed in line with OECD and/or EC guidelines but with a substance analogue and the data are read across.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 006
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 453 (Combined Chronic Toxicity / Carcinogenicity Studies)
- Principles of method if other than guideline:
- In this study, the chronic toxicity (52-week oral feeding) and carcinogenicity (104-week oral feeding) was investigated.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Ammonium sulphate
- EC Number:
- 231-984-1
- EC Name:
- Ammonium sulphate
- Cas Number:
- 7783-20-2
- Molecular formula:
- H3N.1/2H2O4S
- IUPAC Name:
- diammonium sulfate
- Details on test material:
- - Name of test material (as cited in study report): Ammonium sulfate
No further data
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Yoneyama Kagaku Kogyo (Osaka Japan)
- Age at study initiation: 5 weeks
- Housing: three or four rats per plastic cage
- Diet: ad libitum
- Water: Tap water ad libitum
- Acclimation period: 1 week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 24 ± 1 °C
- Humidity (%): 55 ± 5 %
- Air changes (per hr): 18
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Recapture rates for ammonium sulfate from the admixed diet at each concentration level were confirmed to be 95.4-98.7%.
- Duration of treatment / exposure:
- 52 and 104 weeks
- Frequency of treatment:
- continuously in the diet
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
42, 256, 1527 mg/kg bw/day (males); 48, 284, 1490 mg/kg bw/d (females
Basis:
other: actual ingested, 52-week chronic toxicity study
- Remarks:
- Doses / Concentrations:
0.1, 0.6, 3.0% in the diet
Basis:
other: nominal in diet, 52-week chronic toxicity study
- Remarks:
- Doses / Concentrations:
564.1, 1288.2 mg/kg bw/d (males); 649.9, 1371.4 mg/kg bw/d (females)
Basis:
other: actual ingested, 2-year carcinogenicity study
- Remarks:
- Doses / Concentrations:
1.5, 3 % in the diet
Basis:
other: nominal in diet 2-year carcinogenicity study
- No. of animals per sex per dose:
- Chronic toxicity study: 10/sex
Carcinogenicity study: 50/sex - Control animals:
- yes, plain diet
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
BODY WEIGHT: Yes
- Time schedule for examinations: every 2 weeks until week 10 and every 5 weeks thereafter.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
OPHTHALMOSCOPIC EXAMINATION: No data
HAEMATOLOGY: Yes
- Time schedule for collection of blood: 52 weeks
- Anaesthetic used for blood collection: Yes: ether
- Animals fasted: Yes: overnight
- How many animals: 10
- Parameters checked: red blood cell count (RBC), hemoglobin concentration (Hb), hematocrit (Ht), mean corpuscular volume (MCV), mean corpuscular hemoglobin (MCH), mean corpuscular hemoglobin concentration (MCHC), platelet count (Plt) and white blood cell count (WBC). Differential leukocyte counts and the reticulocyte count (Ebl).
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: 52 weeks
- Animals fasted: Yes: overnight
- How many animals: 10
- Parameters checked: total protein (TP), albumin (Alb), albumin/globulin ratio (AIG), total bilirubin (T-bil), total cholesterol (T-Cho), triglyceride (TG), blood urea nitrogen (BUN), creatinine (Cre), calcium (Ca), inorganic phosphorus (IP), sodium (Na), potassium (K), chloride Cl), aspartate transaminase (AsT), alanine transaminase (AlT), alkaline phosphatase (ALP) and gamma-glutamyl transpeptidase (gamma-GTP)
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes
Brain, lungs, heart, spleen, liver, adrenals, kidneys and testes were weighed. As for adrenals, kidneys and testes, weights of each side were separately recorded and the total of both sides was used for calculation of group mean and SD values.
In addition to these organs, the nasal cavity, trachea, aorta, pituitary, thyroids, parathyroids, salivary glands, tongue, esophagus, stomach, duodenum, jejunum, ileum, caecum, colon, rectum, pancreas, urinary bladder, epididymides, prostate, seminal vesicles, ovaries, uterus, vagina, mammary glands, skin, mesenteric and submandibular lymph nodes, thymus, sternum, femur including bone marrow, sciatic nerve, trigeminal nerve, spinal cord (cervical, thoracic and lumber cords), eye, Harderian gland and thigh muscle. All organs and tissues in the control and 3.0% group animals were histopathologically examined. Additionally, macroscopically abnormal sites in the 0.1% and 0.6% group animals in the chronic study and all organs and tissues of the 1.5% animals in the carcinogenicity study were also histopathologically examined. - Statistics:
- Variance in data for body weights, hematology, serum biochemistry and organ weights were checked for homogeneity by Bartlett test. When the data were homogeneous, one-way analysis of variance (ANOVA) was used. In the heterogeneous cases, the Kruskal-Wallis test was applied. When statistically significant differences were indicated, Dunnett's multiple test was employed for comparison between control and treated groups. Final survival rates and the incidences of tumor and non-neoplastic lesions were compared with the Fisher's exact probability test or the Mann-Whitney's U-test.
Results and discussion
Results of examinations
- Details on results:
- CLINICAL SIGNS AND MORTALITY
In the chronic toxicity study, no mortality was found in any groups throughout the treatment period.
In the carcinogenicity study, the survival rate of control, 1.5% and 3.0% groups were 88%, 78% and 76%, respectively, for males, and 76%, 80% and 80%, respectively, for females, and no significant differences were observed among the groups.
BODY WEIGHT AND WEIGHT GAIN
No test substance-related change in the body weights was found.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
A tendency for increase of food intake in the male 3.0% group in the chronic toxicity study was noted.
HAEMATOLOGY
No significant variation was found.
CLINICAL CHEMISTRY
No dose related alteration was found.
ORGAN WEIGHTS
Absolute and relative kidney weights were increased or showed a tendency for increase at 3.0% in both sexes in the chronic toxicity study. Absolute spleen weights were decreased and relative liver weights were increased in the 3.0% male dose group. No dose-related changes were found in the other organs.
GROSS PATHOLOGY
There were no obvious macroscopic findings in any group in either the chronic toxicity or carcinogenicity studies, except for massive, nodular or focal lesions suggesting neoplastic change in the carcinogenicity study.
HISTOPATHOLOGY:
In the carcinogenicity study, non-neoplastic and neoplastic lesions were noted in the control and treatment groups, with no significant inter-group difference in their incidences or severity.
Effect levels
open allclose all
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 256 mg/kg bw/day (actual dose received)
- Sex:
- male
- Basis for effect level:
- other: 0.6% in the diet; Absolute and relative kidney weights were increased at the high dose level for both sexes. Absolute spleen weights were decreased and relative liver weights were increased in high dose males.
- Dose descriptor:
- NOAEL
- Effect level:
- 284 mg/kg bw/day (actual dose received)
- Sex:
- female
- Basis for effect level:
- other: 0.6% in the diet: Absolute and relative kidney weights were increased at the high dose level for both sexes.
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Organ weight of male rats fed diet containing ammonium sulfate for 52 weeks (Chronic toxicity study).
control | 0.1% | 0.6% | 3.0% | |
Body weight (g) | 410.9 ± 12.3 | 428.6 ± 17.6 | 416.7 ± 23.7 | 400.5 ± 15.1 |
Brain (g) | 2.04 ± 0.05 | 2.03 ± 0.07 | 2.05 ± 0.05 | 2.04 ± 0.05 |
Lungs (g) | 1.20 ± 0.09 | 1.23 ± 0.21 | 1.16 ± 0.07 | 1.13 ± 0.06 |
Heart (g) | 1.09 ± 0.08 | 1.10 ± 0.07 | 1.08 ± 0.05 | 1.08 ± 0.07 |
Spleen (g) | 0.73 ± 0.05 | 0.72 ± 0.04 | 0.83 ± 0.36 | 0.68 ± 0.04 * |
Liver (g) | 9.62 ± 0.58 | 9.92 ± 0.73 | 10.26 ± 0.63 | 10.0 ± 0.85 |
Adrenals (g) | 0.03 ± 0.01 | 0.04 ± 0.01 | 0.04 ± 0.00 | 0.04 ± 0.00 |
Kidneys (g) | 2.35 ± 0.25 | 2.32 ± 0.11 | 2.42 ± 0.11 | 2.51 ± 0.11 * |
Testes (g) | 3.38 ± 0.17 | 3.27 ± 0.11 | 3.25 ± 0.25 | 3.29 ± 0.14 |
Organ weight of female rats fed diet containing ammonium sulfate for 52 weeks (Chronic toxicity study).
control | 0.1% | 0.6% | 3.0% | |
Body weight (g) | 207.4 ± 13.49 | 220.3 ± 8.68 | 219.2 ± 13.62 | 212.7 ± 24.39 |
Brain (g) | 1.86 ± 0.04 | 1.83 ± 0.04 | 1.83 ± 0.05 | 1.82 ± 0.05 |
Lungs (g) | 0.82 ± 0.06 | 0.79 ± 0.10 | 0.83 ± 0.12 | 0.79 ± 0.05 |
Heart (g) | 0.65 ± 0.05 | 0.67 ± 0.05 | 0.70 ± 0.03 | 0.67 ± 0.05 |
Spleen (g) | 0.44 ± 0.04 | 0.44 ± 0.02 | 0.45 ± 0.03 | 0.45 ± 0.07 |
Liver (g) | 4.44 ± 0.26 | 4.66 ± 0.35 | 4.69 ± 0.40 | 4.89 ± 0.42 |
Adrenals (g) | 0.04 ± 0.00 | 0.04 ± 0.01 | 0.04 ± 0.01 | 0.04 ± 0.01 |
Kidneys (g) | 1.25 ± 0.07 | 1.35 ± 0.08 * | 1.35 ± 0.09 | 1.39 ± 0.08 ** |
* Significantly different from the control at p<0.05. **Significantly different from the control at p<0.01.
Applicant's summary and conclusion
- Executive summary:
In the subchronic part of the study, groups of 10 rats/sex were fed a diet containing the test substance (purity not given) at concentrations of 0, 0.1, 0.6, or 3% for 1 year. These concentrations corresponded to average daily intakes of 0, 42, 256, and 1527 mg/kg bw/d for males and 0, 48, 284, and 1490 mg/kg bw/d for females, respectively. For investigation of the carcinogenic potential, groups of 50 rats/sex were fed a diet containing the test substance (purity not given) at concentrations of 0, 1.5, or 3% for 2 years. These concentrations corresponded to average daily intakes of 0, 564.1, and 1288.2 mg/kg bw/d for males and 0, 649.9, and 1371.4 mg/kg bw/d for females respectively.
Absolute and relative kidney weights were increased at the high dose level for both sexes. Absolute spleen weights were decreased and relative liver weights were increased in high dose males. No macroscopic changes were recorded by gross pathology, except for massive nodular or focal lesions suggesting neoplastic changes. At histopathological examination, non-neoplastic and neoplastic lesions were noted in the control and treatment groups, with no significant inter-group difference in their incidences or severity.
The authors concluded that the no observed adverse effect level of ammonium sulfate was the 0.6% diet, which is equivalent to 256 and 284 mg/kg bw/d in males and females, respectively, and the compound is noncarcinogenic under the conditions of the study.
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