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EC number: 201-044-5 | CAS number: 77-62-3
- 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
Acute Toxicity: oral
Administrative data
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- July 28 - August 17, 1993
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study performed in accordance with OECD & EU test guidelines in compliance with GLP and reported with a GLP certificate.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- not specified
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.1 (Acute Toxicity (Oral))
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- standard acute method
- Limit test:
- yes
Test material
- Reference substance name:
- 2,2'-methylenebis[6-(1-methylcyclohexyl)-p-cresol]
- EC Number:
- 201-044-5
- EC Name:
- 2,2'-methylenebis[6-(1-methylcyclohexyl)-p-cresol]
- Cas Number:
- 77-62-3
- Molecular formula:
- C29H40O2
- IUPAC Name:
- 2-{[2-hydroxy-5-methyl-3-(1-methylcyclohexyl)phenyl]methyl}-4-methyl-6-(1-methylcyclohexyl)phenol
- Test material form:
- other: solid
- Details on test material:
- Name: Mutterlaugenrükstand
Batch No.: Fil-1248
Chemical name: not specified by the sponsor
Physical state: brownish sticky solid substance
Density: 1.04 g/ml
Identification: labelled, where appropriate, with name of test article, batch no., name of sponsor, project no., date of receipt, storage conditions, handling precautions and expiry date
Storage: ambient
Stability: not specified by the sponsor
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Species: rat
Strain: Bor: WISW (SPF Cpb)
Source: Fa. Winkelmann, Versuchstierzucht GmbH & Co. KG, Gartenstr.27, 33178 Borchen
Date of receipt: July 14, 1993 (range finding); July 21, 1993 (main test)
Acclimatization period: 14 days (range finding); 13 days (main test)
Animal selection: random
Animal identification: with colored markings; cage labelled with dosage, sex, date of study initiation, project no.
Weight range at study initiation: m: 196 - 225 g, f: 158 - 187 g
Husbandry
Housing: collective housing up to a maximum of 5 animals per cage (Makrolon® type II)
Illumination: artificial lighting (120 lux) from 7.00 a.m. - 7.00 p.m.
Temperature: 22 ± 3°C
Relative humidity: 30 - 70 %
Measurement: with thermohygrometer twice daily
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- polyethylene glycol
- Details on oral exposure:
- Solvent/vehicle: polyethylene glycol 400 (PEG 400)
Batch: 110. 297833690
The test article was administered as a 20% solution in PEG 400 in a volume of 10 ml/kg. The dissolution of the test substance was performed by stirring and mild warming. - Doses:
- Single does 2000 mg/kg bw
- No. of animals per sex per dose:
- 2 females for range finding study
10 animals in the main study (5 males & 5 females) - Control animals:
- no
- Details on study design:
- Pre-experimental procedure
Prior to study initiation, the animals were acclimatized to laboratory conditions for 14 days (range finding) and 13 days (main test). Only healthy animals were used in the test.
The animals were fasted from 16 h before until 3 - 4 h after administration of the test article.
Administration of the test article
A single oral administration of the test article was performed by gavage using a stomach tube.
Range finding
A preliminary range finding test with a dose of 2000 mg/kg body weight was conducted using two female rats.
Main study
Clinical observations
In each animal a number of clinical-toxicological signs were evaluated according to a modified Irwin-Screening procedure (Screening Methods in Pharmacology, R. A. Turner, 1965, p. 26). Any change from the normal condition was noted (increase or decrease) and the degree of severity of any clinical symptoms was assessed. The animals were examined at the following post-treatment intervals: 10 min, 1 h, 2 h, 6 h, 24 h, and thereafter once daily up to day 14.
Body weights
Body weights were recorded immediately before treatment (day 0) and on days 7 and
14 p.a. (termination).
Necropsy
The animals were sacrificed by CO2 asphyxiation after 14 days and gross pathological examinations were subsequently performed. - Statistics:
- None specified in the study report.
Results and discussion
- Preliminary study:
- There were no death in the preliminary study.
Effect levels
- Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- No animals died during the course of the main study.
- Clinical signs:
- No abnormal clinical signs were observed apart from a slight diarrhoea in 9 animals at 6h post administration. The situation resolved itself within 24h.
- Body weight:
- Weight gains were normal in all animals.
- Gross pathology:
- Gross pathological examinations at 14 days p. a. (terminal necropsy) revealed no test article-dependent findings. The macroscopic change that was observed was attributable to minor variations which can occur spontaneously in rats of ths strain and age.
- Other findings:
- No further findings reported in the study.
Any other information on results incl. tables
INDIVIDUAL DOSE AND PRE-TERMINAL DEATHS – RANGE FINDING
Test article: Mutterlaugenrückstand Project No.: 10-04-0063/00-93
Species: Rat Animal no.: 6 + 7
Sex: f
Anim. No. |
Sex |
Dose (mg/kg) |
Volume (ml) |
Pre-terminal deaths |
|||||||||||||
24h |
48h |
Days p.a. |
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3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
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6 |
F |
2000 |
1.7 |
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7 |
F |
2000 |
1.9 |
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Open boxes: no pre-terminal deaths
INDIVIDUAL DOSE AND PRE-TERMINAL DEATHS – MAIN STUDY
Test article: Mutterlaugenrückstand Project No.: 10-04-0063/00-93
Species: Rat Animal no.: 1 - 10
Sex: m, f
Anim. No. |
Sex |
Dose (mg/kg) |
Volume (ml) |
Pre-terminal deaths |
|||||||||||||
24h |
48h |
Days p.a. |
|||||||||||||||
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
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1 |
M |
2000 |
2.1 |
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2 |
M |
2000 |
2.2 |
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3 |
M |
2000 |
2.1 |
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4 |
M |
2000 |
2.0 |
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5 |
M |
2000 |
2.3 |
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6 |
F |
2000 |
1.7 |
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7 |
F |
2000 |
1.9 |
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8 |
F |
2000 |
1.8 |
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9 |
F |
2000 |
1.6 |
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10 |
F |
2000 |
1.7 |
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Open boxes: no pre-terminal deaths
CLINICAL OBSERVATIONS
Test article: Mutterlaugenrückstand Project No.: 10-04-0063/00-93
Species: Rat Sex: m,f
Dose mg/kg |
Observation period p.a. |
Findings |
2000 |
10 min – 2h (10/10) 6h (10/10) 24h – day 14 (10/10) |
No abnormal clinical signs Slight diarrhea in 9 animals No abnormal clinical signs |
Figures in parenthesis indicate number of surviving animals
BODY WEIGHTS – INDIVIDUAL VALUES (g)
Dose: 2000 mg/kg
Anim. No. |
Sex |
Day 0 |
Day 7 p.a. |
Day 14 p.a. |
1 |
M |
205 |
252 |
274 |
2 |
M |
218 |
270 |
288 |
3 |
M |
206 |
252 |
287 |
4 |
M |
196 |
232 |
257 |
5 |
M |
225 |
272 |
304 |
6 |
F |
172 |
191 |
198 |
7 |
F |
187 |
211 |
217 |
8 |
F |
178 |
200 |
211 |
9 |
F |
158 |
176 |
189 |
10 |
F |
168 |
192 |
207 |
BODY-WEIGHTS – MEAN VALUES (g)
Sex |
N |
Day 0 |
Day 7 p.a. |
Day 14 p.a. |
Males |
5 |
210.0 ± 11.5 |
255.6 ± 16.3 |
282.0 ± 17.6 |
Females |
5 |
172.6 ± 10.9 |
194.0 ± 12.9 |
204.4 ± 11.0 |
NECROPSY
Test article: Mutterlaugenrückstand Project No.: 10-04-0063/00-93
Species: Rat Animal no.: 1 - 10
Sex: m, f Dose: 2000 mg/kg
Spontaneous death: ---- n = -
Killed in extremis: ---- n = -
Animal No. |
Specified Findings |
|
|
Terminal sacrifice: 14 days p.a. n = 10
Animal No. |
Specified Findings |
7 1 – 6, 8 – 10 |
Uterus: hydrometra No specific findings |
Applicant's summary and conclusion
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- the basis of the results obtaned after a single oral administration, the LD50 values after 24 h and 14 days were as follows:
male and female > 2000 mg/kg - Executive summary:
The aim of the test was to determine the acute median lethal dose of "Mutterlaugenrückstand". Information derived from this test serves to indicate the existence of possible hazards likely to arise from short-term exposure to the test article by the oral route.
The test was conducted according to the OECD guideline for the testing of chemicals OECD 401 (February 24, 1987) and the EEC directive 92/69ÆEC (July 31, 1992). The study was carried out as described in the corresponding protocol approved by the testing facility and the study sponsor on June 28 and July 1, 1993, respectively. The principles of Good Laboratory Practice for the testing of chemicals as specified by national (BGBL. I, no. 13, § 19 a, March 22, 1990) and international (OECD, Paris, 1982) legislation were followed during the performance of the study.
SUMMARY
The acute oral toxicity of "Mutterlaugenrückstand" was investigated in 5 male and 5 female Wistar rats.
On the basis of the range finding results, the animals were given a single oral administration of "Mutterlaugenrückstand" at a dose of 2000 mg/kg.
Clinical observations were conducted at regular intervals during the 14-day observation period. Body weights were measured at days 0, 7 and 14 p.a. Gross pathological examinations were performed on all animals 14 days p.a.
The following results were obtained:
1. No abnormal clinical signs were observed apart from a slight diarrhea in 9 animals at 6 h p.a.
2. Weight gains were normal in all animals.
3. Gross pathological examinations at 14 days p.a. (terminal necropsy) revealed no test article-dependent findings.
4. On the basis of the results obtained after a single oral administration, the LD50 values after 24 hand 14 days were as follows:
male and female > 2000 mg/kg
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