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EC number: 905-287-4 | CAS number: 1638758-52-7
- 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

Toxicity to reproduction
Administrative data
- Endpoint:
- screening for reproductive / developmental toxicity
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- weight of evidence
- Justification for type of information:
- The reproductive toxicity of the individual (o-, m- and p-) cresol isomers has been investigated in three separate two-generation toxicity studies. No effects on fertility were seen in any study at the high dose level of 450 mg/kg bw/d. General toxicity (increased mortality and in clinical signs including hypoactivity, ataxia, twitches, tremors, prostration, gasping, rapid respiration and perioral wetness) were observed at dose levels of 175 and 450 mg/kg bw/d, resulting parental NOAELs of 30 mg/kg bw/d. Reduced pup weight and viability were seen at the highest (and parentally toxic) dose level of 450 mg/kg bw/d, leading to NOAEL values of 175 mg/kg bw/d. OECD 422 screening studies available for xylenol (mixed isomers) and ethylphenol (mixed isomers) both report and absence of effects on fertility and reproductive NOAEL values of 245 mg/kg bw/d. The Category substances therefore consistently demonstrate a lack of reproductive toxicity. Read-across is therefore proposed to the study with xylenol as the closest structural analogue among the Category members.
Developmental toxicity studies in the rat are available for the individual (o-, m- and p-) cresol isomers. Each study identified significant maternal toxicity (mortality, clinical signs, bodyweight deficits) at the high dose level of 450 mg/kg bw/d, resulting in maternal NOAELs of 175 mg/kg bw/d for each isomer. Slight fetotoxicity was observed at 450 mg/kg bw/d for o-cresol (one visceral variation: dilated lateral ventricles of the brain) and for p-cresol (reduced foetal weight, reduced skeletal ossification). There were no foetal effects with m-cresol at any dose level.
Data source
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Reaction mass of 2,4-xylenol and 2,5-xylenol
- EC Number:
- 905-287-4
- Cas Number:
- 1638758-52-7
- Molecular formula:
- (CH3)2C6H3OH
- IUPAC Name:
- Reaction mass of 2,4-xylenol and 2,5-xylenol
- Test material form:
- solid: bulk
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on mating procedure:
- Male and female rats were pair 1:1 and cohabited for a maximum of 14 days. Female rats with spermatozoa observed in a msear of the vaginal conents and/or a copulatory plug in situ were considered to at GD 0 and then individually housed.
- Analytical verification of doses or concentrations:
- yes
- Duration of treatment / exposure:
- Minimum of 28 days (14 days of dosing prior to cohabitation).
- Frequency of treatment:
- Once daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:Basis:analytical conc.30, 100, 300 mg/kg/day
- No. of animals per sex per dose:
- 10 male and 10 females/group
Results and discussion
Results: P0 (first parental generation)
Effect levels (P0)
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- ca. 100 mg/kg bw/day
- Based on:
- other:
- Sex:
- male/female
- Basis for effect level:
- other: Due to clinical observations (urine-stained fur, increased kidney, liver and ovarian relative weight).
- Dose descriptor:
- NOAEL
- Remarks:
- Reproductive
- Effect level:
- >= 245 mg/kg bw (total dose)
- Based on:
- other:
- Sex:
- male/female
- Basis for effect level:
- other: Whilst a reduced mating frequency was observed, this was within the laboratory's historical control range, therefore not considered biologically relevant.
Results: F1 generation
Effect levels (F1)
- Key result
- Dose descriptor:
- NOAEL
- Generation:
- F1
- Effect level:
- > 245 mg/kg bw/day
- Based on:
- other:
- Sex:
- female
- Basis for effect level:
- clinical signs
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
All rats survived the treatment. In males, urine stained fur was observed at the 245 mg/kg/day level. Body weight gain and food consumption were unaffected by treatment. Mating frequency was reduced at the 245 mg/kg/day level. Neurotoxicity was not observed during the study and there were no treatment related effects observed at gross necropsy or histopathologically. Urine staining of the fur was observed in females at the 245 mg/kg/day level. F1 animals showed no treatment related clinical or necropsy signs. Haematology, clinical pathology and FOB parameters were unaffected.
Relative weights of the kidney, liver and ovaries were observed to be increased in the 245 mg/kg/day treatment group,
Decreased mating and fertility indices were reported at the highest dose level (245 mg/kg bw) in the combined repeated dose toxicity and reproduction/developmental toxicity screening test. The number of female rats that mated was reduced from 100% in the control group (10/10) to 80% at 245 mg/kg bw (8/10) but the difference was not significantly different. The historical control value was reported as 97.6% over the period 1992-2002 but as no range was given this figure was of limited value. Following a request to Argus addition all historical control data were provided on 19 April 2010. The information provided showed fertility data for individual years from 1992 to 1997 giving the range as well as the mean values and these are shown in Table 1.
Table 1: Fertility index for studies conducted in Crl:CD(SD) Rats
Year |
Average |
Minimum |
Maximum |
No of studies |
1992 |
94.1 |
80.0 |
100.0 |
4 |
1993 |
89.5 |
80.0 |
100.0 |
9 |
1994 |
90.5 |
66.7 |
100.0 |
17 |
1995 |
93.8 |
89.7 |
100.0 |
5 |
1996 |
93.1 |
84.0 |
100.0 |
13 |
1997 |
91.7 |
71.4 |
100.0 |
23 |
1992 - 1997 |
91.7 |
66.7 |
100.0 |
71 |
It is clear from the historical control data that fertility in the mixed xylenols study was within the historical control range in several years during the period from 1992-1997 which corresponds to the time when the mixed xylenols study was conducted.
As the reduced fertility at 245 mg/kg bw was not statistically significant and was within the historical control range, this effect is considered not to be related to treatment and the NOAEL for reproductive effects in this study should be ≥ 245 mg/kg bw.
Applicant's summary and conclusion
- Conclusions:
- The test substance mixed xylenol isomers was administered to rats by oral gavage at 0, 30, 100 and 245 mg/kg/day. The general toxicological No Observable Adverse Effect Level was shown to be 100 mg/kg/day. The SD determined that the reproductive NOAEL was found to be 100 mg/kg/day due to reduced mating at 245 mg/kg/day, however following request of the historical control data from the laboratory, the reduction in mating frequency to 80% was within the laboratory's historical vehicle control data for this period. Therefore the reproductive NOAEL is considered to be 245 mg/kg/day
- Executive summary:
The above results are suitable to be used for read across for Reaction mass of 2,4-xylenol and 2,5-xylenol, due to the category being based on structural similarity and comparable physicochemical properties, leading to similar (eco)toxicological properties.
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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