Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 811-605-1 | CAS number: 37318-95-9
- 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
Endpoint summary
Administrative data
Description of key information
Oral, rat (read-across OECD 422): NOAEL = 1000 mg/kg bw/day
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Remarks:
- combined repeated dose and reproduction / developmental screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 17 Feb - 07 April 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- adopted: 23 Mar 1996
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- adopted: 29 Jul 2016
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- other: Crl:WI (Han) (outbred, SPF-Quality)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories France, L'Arbresle Cedex, France
- Age at study initiation: approximately 12 weeks
- Weight at study initiation: 277 - 353 g (males) and 183 - 225 g (females)
- Housing: 5 animals of the same sex per cage in Macrolon cages (MIV type). Sterilised sawdust as bedding material (Litalabo, S.P.P.S., Argenteuil, France) and paper as cage-enrichment (Enviro-dri, Wm. Lillico & Son (Wonham Mill Ltd), Surrey, UK) were supplied.
- Diet: pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany), ad libitum
- Water: tap-water, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 ± 3
- Humidity (%): 40-70
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
OTHER
- This species and strain of rat has been recognised as appropriate for general and reproduction toxicity studies. The testing laboratory has general and reproduction/developmental historical data in this species from the same strain and source. This animal model has been proven to be susceptible to the effects of reproductive toxicants. - Route of administration:
- oral: gavage
- Vehicle:
- polyethylene glycol
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
Formulations (w/w) were prepared daily within 6 h prior to dosing and were homogenised to a visually acceptable level.
Adjustment was made for the density of the test substance (0.944), and the specific gravity of the vehicle (1.125).
VEHICLE:
- Justification for use and choice of vehicle (if other than water): Based on trial formulations performed at the testing laboratory.
- Purity: polyethylene glycol 400, specific gravity 1.125 (Merck, Darmstadt, Germany)
DOSE VOLUME:
5 mL/kg bw - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Chemical analyses of formulations were conducted once during the study to assess accuracy, homogeneity and stability. Samples of formulations were analysed for homogeneity (highest and lowest concentration) and accuracy of preparation (all concentrations). Stability in vehicle over 6 h at room temperature was also determined (highest and lowest concentration).
The accuracy of preparation was considered acceptable if the mean measured concentrations were 85-115% for suspensions. Homogeneity was demonstrated if the coefficient of variation was ≤10%. Formulations were considered stable if the relative difference before and after storage was maximally 10%.
The concentrations analysed in the formulations of Group 2, Group 3 and Group 4 were in agreement with target concentrations (i.e. mean accuracies between 85% and 115%). The formulations of Group 2 and Group 4 were homogeneous (i.e. coefficient of variation ≤ 10%) and formulations at the entire range were stable when stored at room temperature for at least 6 h. - Duration of treatment / exposure:
- 28 days
- Frequency of treatment:
- once daily, 7 days/week
- Dose / conc.:
- 100 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 300 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 10 males and 5 females (main study)
5 males and 5 females (recovery group) - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: based on the results of a 10-day dose range finding study.
- Post-exposure recovery period in satellite groups: 14 days - Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: at least twice daily.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: once prior to start of treatment and at weekly intervals this was also performed outside the home cage in a standard arena. Arena observations were conducted during the treatment phase only. Arena observations were not performed when the animals were mating, or housed individually. The time of onset, degree and duration was recorded. All symptoms were recorded and graded according to fixed scales:
Maximum grade 1: grade 0 = absent, grade 1 = present
Maximum grade 3 or 4: grade 1 = slight, grade 2 = moderate, grade 3 = severe, grade 4 = very severe
BODY WEIGHT: Yes
Males and females were weighed on the first day of exposure and weekly thereafter. Mated Repro females were weighed on Days 0, 4, 7, 11, 14, 17 and 20 post-coitum, and during lactation on Days 1 and 4.
FOOD CONSUMPTION: Yes
Weekly, for males and females. Food consumption was not recorded during the mating period (except for males). Food consumption of mated Repro females was measured on Days 0, 4, 7, 11, 14, 17 and 20 post-coitum and on Days 1 and 4 of lactation.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No
Subjective appraisal was maintained during the study, but no quantitative investigation was introduced as no effect was suspected.
HAEMATOLOGY: Yes
- Time schedule for collection of blood: prior to scheduled post mortem examination
- Anaesthetic used for blood collection: Yes (iso-flurane)
- Animals fasted: Yes
- How many animals: Blood samples were collected from the first 5 Main males (randomly selected at allocation), all Recovery animals and the 5 Main females from each group. In addition to blood collection prior to necropsy, blood samples were collected from the Recovery animals at the end of treatment.
- Parameters checked: White blood cells, Differential leucocyte count, neutrophils, lymphocytes, monocytes, eosinophils, basophils, Red blood cells, Reticulocytes, Red blood cell distribution width, Haemoglobin, Haematocrit, Mean corpuscular volume, Mean corpuscular haemoglobin, Mean corpuscular haemoglobin concentration, Platelets, Prothrombin time, Activated Partial thromboplastin time.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: prior to scheduled post mortem examination
- Anaesthetic used for blood collection: Yes (iso-flurane)
- Animals fasted: Yes, overnight
- How many animals: Blood samples were collected from the first 5 Main males (randomly selected at allocation), all Recovery animals and the 5 Main females from each group. In addition to blood collection prior to necropsy, blood samples were collected from the Recovery animals at the end of treatment.
- Parameters checked: ALAT, ASAT, ALP, Total Protein, Albumin, Total Bilirubin, Urea, Creatinine, Glucose, Cholesterol, Sodium, Potassium, Chloride, Calcium, Inorganic Phosphate, Bile acids.
NEUROBEHAVIOURAL EXAMINATION: Yes
The following tests were performed on the first Main males (randomly selected at allocation), all Recovery animals and the 5 Main females from each group:
- hearing ability, pupillary reflex, static righting reflex and grip strength (score 0 = normal/present, score 1 = abnormal/absent).
- motor activity test (recording period: 1-hour for individual animals, using a computerized monitoring system; Pearson Technical Services, Suffolk, Great Britain).
During the motor activity test, animals were caged individually. The assigned animals were tested during week 4 of treatment (all before blood sampling). Since no treatment-related findings were noted, the functional observation tests and motor activity measurements were not extended to all animals at the end of the recovery phase.
ORGAN WEIGHTS:
The following organ weights and terminal body weight were recorded from the following animals on the scheduled day of necropsy:
- From the first 5 Main males (randomly selected at allocation), the 5 Main females and all
Recovery animals per group: Adrenal glands, Brain, Epididymides, Heart, Kidneys, Liver, Spleen, Testes, Thymus, Ovaries, Uterus (including cervix), Prostate, Seminal vesicles including coagulating glands, Thyroid including parathyroid.
- From all remaining males: Epididymides, Testes
Since no toxicologically relevant effect was noted on organ weights of Main females, no organ weights were collected from Repro females. - Sacrifice and pathology:
- DAY OF NERCROPSY:
- Main animals: Following completion of a minimum of 28 days of dose administration.
- Recovery animals: Following completion of a minimum of 28 days of dose administration and a recovery period of 14 days.
One animal was euthanised in extremis.
GROSS PATHOLOGY: Yes
All animals were subjected to macroscopic examination of the cranial, thoracic and abdominal tissues and organs, with special attention being paid to the reproductive organs. Descriptions of all macroscopic abnormalities were recorded.
HISTOPATHOLOGY: Yes
From the first 5 Main animals/sex/group, all Recovery animals, the selected Repro females/group (with live offspring) and animal no.117 that was killed in extremis (Tissues/organs mentioned in parentheses were not examined by the pathologist, since no signs of toxicity were noted at macroscopic examination):
Adrenal glands, (Aorta), Brain (cerebellum, mid-brain, cortex), Caecum, Cervix, Clitoral gland, Colon, Duodenum, Epididymides, Eyes (including optic nerve and Harderian gland), Female mammary gland area, Femur including joint, Heart, Ileum, Jejunum, Kidneys, (Lacrimal gland, exorbital), (Larynx), Liver, Lung, infused with formalin, Lymph nodes - mandibular, mesenteric, (Nasopharynx), (Oesophagus), Ovaries, (Pancreas), Peyer's patches (jejunum, ileum) if detectable, Pituitary gland, Preputial gland, Prostate gland, Rectum, (Salivary glands - mandibular, sublingual), Sciatic nerve, Seminal vesicles including coagulating gland, Skeletal muscle, (Skin), Spinal cord -cervical, midthoracic, lumbar, Spleen, Sternum with bone marrow, Stomach, Testes1, Thymus, Thyroid including parathyroid (if detectable), (Tongue), Trachea, Urinary bladder, Uterus, Vagina, All gross lesions.
From all remaining animals and females which failed to deliver: Cervix, Clitoral gland, Coagulation gland, Epididymides, Ovaries, Preputial gland, Prostate gland, Seminal vesicles, Testes, Uterus, Vagina, All gross lesions. - Statistics:
- The following statistical methods were used to analyse the data:
- If the variables could be assumed to follow a normal distribution, the Dunnett-test (many-to-one t-test) based on a pooled variance estimate was applied for the comparison of the treated groups and the control groups for each sex.
- The Steel-test (many-to-one rank test) was applied if the data could not be assumed to follow a normal distribution.
- The Fisher Exact-test was applied to frequency data.
An attempt was made to transform the number of corpora lutea by using 1/x, log x, x² and √x.
However, a normal distribution was not obtained. Therefore, the number of corpora lutea was subjected to the Kruskal-Wallis nonparametric ANOVA test to determine inter-group differences, followed by the Wilcoxon test to compare the treated groups to the control group.
All tests were two-sided and in all cases p < 0.05 was accepted as the lowest level of significance.
Group means were calculated for continuous data and medians were calculated for discrete data (scores) in the summary tables. Test statistics were calculated on the basis of exact values for means and pooled variances. Individual values, means and standard deviations may have been rounded off before printing. Therefore, two groups may display the same printed means for a given parameter, yet display different test statistics values.
No statistical analysis was performed on histopathology findings. - Clinical signs:
- no effects observed
- Description (incidence and severity):
- No clinical signs of toxicity were noted that were attributable to treatment.
- Mortality:
- no mortality observed
- Description (incidence):
- No mortality occurred during the study period that was considered to be related to treatment with the test substance. Female no. 117 (1000 mg/kg bw/day) was killed in extremis on Day 17 post-coitum. Microscopic examination revealed a marked granuloma in the bronchus region containing macrophages surrounding food particles and with central areas of necrosis. These findings were indicative of a gavage accident.
- Body weight and weight changes:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No toxicologically relevant changes in body weights and body weight gain were noted up to 1000 mg/kg bw/day.
Any statistically significant changes in body weight gain observed among males and females during the treatment or recovery period were considered to be of no toxicological relevance since the changes occurred in the absence of a dose-related trend and/or were of a slight and/or temporary nature. These changes consisted of a higher body weight gain for males at 1000 mg/kg bw/day during the recovery phase, a lower body weight gain of Repro females at 1000 mg/kg bw/day on Day 11 of the post coitum period, and a higher body weight gain of Main females at 100 mg/kg bw/day over treatment Days 8-22. - Food consumption and compound intake (if feeding study):
- no effects observed
- Description (incidence and severity):
- Food consumption before or after allowance for body weight was similar between treated and control animals.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No toxicologically relevant changes occurred in haematological parameters of treated rats.
The statistically significant lower prothrombin time in males at 1000 mg/kg bw/day and lower relative lymphocyte counts in females at 300 mg/kg bw/day at the end of treatment were considered to be of no toxicological relevance. These changes were absent at the end of the recovery period, occurred in the absence of a (clear) treatment-related trend and remained within the range considered normal for rats of this age and strain. - Clinical biochemistry findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No toxicologically relevant changes occurred in clinical biochemistry parameters of treated rats.
Any statistically significant changes in clinical biochemistry parameters were considered to be of no toxicological relevance as these occurred in the absence of a (clear) treatment-related trend, remained within the range considered normal for rats of this age and strain and/or were present at the end of the recovery period only. At the end of treatment these changes consisted of lower alanine aminotransferase in males at 300 and 1000 mg/kg bw/day, and higher chloride levels in males at 100 mg/kg bw/day. Changes at 1000 mg/kg bw/day at the end of the recovery phase included lower albumin and higher glucose levels in females, and higher inorganic phosphate levels in males. - Urinalysis findings:
- not examined
- Behaviour (functional findings):
- effects observed, non-treatment-related
- Description (incidence and severity):
- Hearing ability, pupillary reflex, static righting reflex and grip strength were normal in all animals.
The variation in motor activity did not indicate a relation with treatment. Males at 300 mg/kg bw/day had significantly lower high sensor counts. Since the range of high sensor values encountered at 300 mg/kg bw/day was similar to that observed in the control group and no dose-related trend was noted, no toxicological relevance was ascribed to this variation. A notable variation in high sensor counts was recorded for females at 1000 mg/kg bw/day. Since the range of values at this dose was essentially similar to that observed in the control group, it was considered that no toxicologically significant effect on high sensor counts had occurred in females at 1000 mg/kg bw/day. - Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No toxicologically relevant changes were noted in organ weights and organ to body weight ratios.
Any statistically significant changes in organ weights and organ to body weight ratios were considered to be of no toxicological relevance as these occurred in the absence of a (clear) treatment-related trend, remained within the range considered normal for rats of this age and strain and/or were present at the end of the recovery period only. Also, no histopathological correlates were noted to support these changes. These changes consisted of a lower spleen to body weight ratio in males at 1000 mg/kg bw/day at the end of the recovery phase, a higher spleen weight and spleen to body weight ratio in females at 100 mg/kg bw/day and the end of treatment, lower heart weight in females at 1000 mg/kg bw/day, higher heart to body weight ratio in females at 1000 mg/kg bw/day at the end of treatment, lower adrenal weight and/or adrenal to body weight ratio in females at 300 and 1000 mg/kg bw/day at the end of treatment, and a lower ovary and ovary to body weight ratio in females at 1000 mg/kg bw/day at the end of treatment. Other organ weights and organ to body weight ratios among the dose groups were similar to control levels. - Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Macroscopic observations at necropsy did not reveal any toxicologically relevant alterations.
The female at 1000 mg/kg bw/day euthanized in extremis (no. 117) showed a hard, greenish nodule on the right medial lobe of the lung, dark red discolouration of the left ovary, enlarged adrenal glands, reduced size of the thymus, enlargement and greenish discolouration of the bronchial lymph node and pleura grown together with the lungs. A watery-clear cyst was found for a single control Repro female (no. 89). This finding was corroborated with a cyst found in the cervix found upon histopathological examination, which likely contributed to this animal’s suspected infertility.
Other incidental findings among control and treated animals at the end of the treatment and/or recovery period included alopecia, red foci on the thymus, reddish discolouration of the thymus or mesenteric lymph node, pelvic dilation of the kidney, reduced size of the testes, epididymides or seminal vesicles, yellowish hard nodules, a red-brown focus or tan discolouration of the clitoral glands, and fluid in the uterus. The incidence of these findings remained within the background range of findings that are encountered among rats of this age and strain, and their incidence did not show a dose-related trend. These necropsy findings were therefore considered to be of no toxicological relevance. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- There were no treatment-related microscopic findings.
One control female (no. 89) had a marked cyst present in the cervix which correlated to the macroscopic finding in this animal and likely accounted for the infertility. One male rat at 100 mg/kg bw/day (no. 18) had an extensive bilateral seminiferous tubular atrophy in the testes with a subsequent extensive epididymal oligospermia, which accounted for its infertility. This was considered to be a spontaneous abnormality with no likely relationship to the test item. No other abnormalities were seen in the reproductive organs of the remaining suspected nonfertile animals which could account for their infertility. All microscopic findings recorded were considered to be within the normal range of background pathology encountered in Wistar-Han rats of this age and strain. The assessment of the integrity of the spermatogenetic cycle did not provide any evidence of impaired spermatogenesis. - Histopathological findings: neoplastic:
- no effects observed
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- behaviour (functional findings)
- body weight and weight gain
- clinical biochemistry
- clinical signs
- food consumption and compound intake
- gross pathology
- haematology
- histopathology: non-neoplastic
- organ weights and organ / body weight ratios
- Key result
- Critical effects observed:
- not specified
- Endpoint:
- short-term repeated dose toxicity: oral
- Remarks:
- combined repeated dose and reproduction / developmental screening
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- adopted: 23 Mar 1996
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- Version / remarks:
- adopted: 29 Jul 2016
- Deviations:
- no
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories Japan, Inc., Yokohama, Japan
- Age at study initiation: 10 weeks
- Weight at study initiation: 352-426 g (males; mean: 372 g), 192-249 g (females; mean: 224 g)
- Housing: individual in stainless steel cages
- Diet: ad libtum
- Water: ad libitum
- Acclimation period: 11 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22.1 - 23.2
- Humidity (%): 48 - 61
- Air changes (per hr): more than 10
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS:
The test substance was diluted in appropritate amounts of corn oil for each dose level. Aliquots of the dosing solution corresponding to the amount of daily administration were stored in the dark at 2 - 6 °C. The stability of the dosing solution was 7 days in a refrigerator and 1 day at room temperature. Therefore, the dosing solution was used within 7 days.
VEHICLE
- Justification for use and choice of vehicle (if other than water): the test substance showed low solubility in water.
- Amount of vehicle (if gavage): 5 mL/kg
- Lot/batch no. (if required): V4N3566 - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- No details reported.
- Duration of treatment / exposure:
- males: 42 days (14 days prior to mating and 28 days thereafter)
females: 42-52 days (from 14 days before mating to day 4 of lactation)
satellite males and females: 42 days and 14 days post-exposure observation period - Frequency of treatment:
- once daily, 7 days/week
- Dose / conc.:
- 100 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 300 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 12 females in control and test groups
7 males in control and 1000 mg/kg bw groups
12 males in 100 and 300 mg/kg bw groups
5 animals per sex in satellite control and 1000 mg/kg bw/day groups (in addition to number listed above) - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale:
Two dose range finding studies were performed. 2000 mg/kg bw of test substance was administered for 3 days in male and female rats. No abnormalities were found in general condition and body weight. The second study was performed at dose levels of 0, 330, 100, 300 and 1000 mg/kg bw/day for 14 days. No abnormalities of general condition, body weight, food consumption, hematological findings, blood biochemical findings, gross pathology and organ weight were found. Therefore, 1000 mg/kg bw/day was selected as the highest dose.
- Post-exposure recovery period in satellite groups: 14 days - Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: once prior to the first exposure and weekly thereafter
BODY WEIGHT: Yes
- Time schedule for examinations:
Males: Day 1 (before administration), 7, 14, 21, 28, 35 and 42 (before sacrifice)
Females: Day 1 (before administration), 7, 14, during pregnancy on Day 0, 7 14 and 21, during lactation on Days 0 and 4 (before sacrifice)
Satellite males and females: Day 1 (before administration), 7, 14, 21, 28, 35, 42, 49 (Day 7 of recovery period) and 56 (Day 14 of recovery period, before sacrifice)
FOOD CONSUMPTION:
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: Yes
HAEMATOLOGY: Yes
- Time schedule for collection of blood: one day after last application
- Anaesthetic used for blood collection: Yes (ether)
- Animals fasted: Yes
- How many animals: 5 per group
- Parameters checked: RBC, Hemoglobin, Hematocrit, MCV, MCH, MCHC, Platelets, Reticulocytes, PT, APTT, WBC, Differential leukocytes: Lymphocytes, Neutrophils, Eosinophils, Basophils, Monocytes
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: one day after last application
- Animals fasted: Yes
- How many animals: 5 per group
- Parameters checked: AST, ALT, ALP, γ-GTP, T-protein, Albumin, A/G, T-bilirubin, BUN, Creatinine, Glucose, T-cholesterol, Triglyceride, Na, K, Cl, Ca, P, LDH, choline esterase
URINALYSIS: Yes (males)
- Time schedule for collection of urine: Day 37 during administration period or Day 9 during recovery period
- Metabolism cages used for collection of urine: Yes
- Animals fasted: Yes
- Parameters checked: Colour, cloudiness, water consumed, volume, specific gravity, Na, K, pH, Protein, Glucose, Ketone body, Bilirubin, Occult blood, Urobilinogen, Epithelial cells, Erythrocytes, Leukocytes, Casts, Crystals, Fat
NEUROBEHAVIOURAL EXAMINATION: Yes
- Time schedule for examinations:
Males: on Week 6 of the administration period
Females: on Week 6 of the administration period
Males and females of satellite groups: on Week 6 of the administration period and on Week 2 of the recovery period
- Dose groups that were examined: all
- Battery of functions tested: hearing reaction, eye sight reaction, sense of touch reaction, pain reaction, pupil reflex, pinna reflex, ipsilateral flexor reaction, eyelid reflex, righting reflex - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
Body surface, mucous membranes and internal organs
HISTOPATHOLOGY: Yes
Brain, pituitary, thyroid, thymus, lung trachea (after liquid immersion fixation), stomach, intestines, heart, liver, spleen, kidney, adrenal gland, bladder, testis, epididymis, prostate, seminal vesicles, ovaries, uterus, spinal cord (cervical, thoracic, lumbar), sciatic nerve, bone marrow (femur), lymph nodes (cervical lymph node, mesenteric lymph nodes), mammary gland, and other gross abnormalities
Spermatogenic cycle (Stage II, III, V, VII, and XII) was also investigated.
SACRIFICE
- Males: on Day 43
- Females: on Day 5 of lactation
- Females (unsuccessful mating): on Day 53
- Females (mated but non-pregnant): on Day 5 after scheduled delivery
- Satellite males and females: on Day 15 of the recovery period - Other examinations:
- Organ weight: brain, liver, kidney, spleen, heart, thymus, thyroid, pituitary, adrenal, testis, sminal vesicle, epididymis
Estrous cycle
Number of ovarian corpora lutea
Number of uterine implantation
Observation of pups - Statistics:
- ANOVA, Barlettm Kruskal-Willis, Dunnett, F test, Studen t-test, Aspin-Welch t-test, Mann-Whitney U-test, Fisher's exact test
- Clinical signs:
- no effects observed
- Description (incidence and severity):
- No abnormalities were observed.
- Mortality:
- no mortality observed
- Description (incidence):
- No mortality was observed.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- No change of body weight and weight gain was observed during the administration period. During the recovery period, a significant increase in body weight was noted in males at 1000 mg/kg bw/day. This was caused by a tendency of the control group animals to lose weight. One male in control group showed a significant decrease in body weight during the recovery period. However, no other abnormalities were observed in this male.
- Food consumption and compound intake (if feeding study):
- effects observed, non-treatment-related
- Description (incidence and severity):
- No change was observed during the administration period in the test groups. A significant increase in food consumption was found in satellite females of the 1000 mg/kg bw/day group on Day 14 of administration. However, it was regarded as an incidental finding since the food consumption of the corresponding control group was relatively small on that day. Therefore, this change was not regarded as a compound-related effect.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No changes were observed. After administration, a significant decrease in APTT was observed in males of the 100 and 300 mg/kg bw/day groups in comparison with control group. However, this change was not regarded as compound-related, because no dose-dependency was observed and this was within reference range.
- Clinical biochemistry findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- A significant decrease in inorganic P was observed in females of the 300 and 1000 mg/kg bw/day groups after administration. However, this change was not regarded as compound-related, since a dose-dependency was not observed and almost all the individual data were within the reference ranges except for one female of 300 mg/kg bw/day.
Choline esterase was increased in females of 1000 mg/kg bw/day after the recovery period but this was within the reference range. This change was not compound-related effect since this change was slightly and no change was observed after the administration period. - Urinalysis findings:
- no effects observed
- Description (incidence and severity):
- No significant changes were found during the administration and recovery periods.
- Behaviour (functional findings):
- no effects observed
- Description (incidence and severity):
- No abnormality was observed for the sensory/reflex function, landing foot, grip strength and motor activity during the administration period. During the recovery period, motor activity increased from 0 to 60 min but not from 0 to 30 min in females dosed 1000 mg/kg bw/day. This effect was not compound-related since the observed change was slight and no change was observed during and after the administration period.
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Description (incidence and severity):
- After the administration period, a significant decrease in the absolute weight of seminal vesicles in males given and a significant decrease in relative weight of spleen in females were observed in the 100 mg/kg bw/day group. However, this change was not compound-related because no abnormalities were found at histopathological examination and there was no dose-dependency.
After the recovery period, a significant decrease in relative weight of pituitary in males of the 1000 mg/kg bw/day group and relative weight of thyroid in females of the 1000 mg/kg group bw/day was observed. Nevertheless, this effect was not compound-related because no abnormality was reported regarding these organs after administration period. - Gross pathological findings:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No test substance-related changes were found. No abnormalities were found in breeding pairs which were not successful at mating and in those which were successful at mating but not pregnant.
After administration period, reddish thymus was noted in one male of the control group and subcutis mass was found in one female of 300 mg/kg by/day group (see also HISTOPATHOLOGY: NEOPLASTIC). After the recovery period, larger spleen and capsular thickening in spleen was found in one male and reddish area in thymus was observed in one female at 1000 mg/kg bw/day. - Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- No test substance-related changes were observed. There were also no changes regarding spermatogenic cycle.
Myocardial degeneration/fibrosis, foam cell accumulation in lung, mineralization in artery in lung, fatty degeneration of hepatocyte, microgranuloma in liver, solitary cyst in kidney, hyaline cast in kidney, lymphocyte infiltration in cortex of kidney, mineralization of cortico-medullary junction in kidney, fibrosis of cortex in kidney and haemorrhage in thymus were observed both in the control and 1000 mg/kg bw/day groups or only in the control group with low incidence. Hyaline droplet of proximal tubular epithelium in kidney was found in all males of the control and 1000 mg/kg bw/day groups. Brown deposit pigment and extramedullary haematopoiesis in spleen were found in all males and females of the control and 1000 mg/kg bw/day groups. However, there were no differences between control and test group. In the 1000 mg/kg bw/group, lymphocyte interstitium infiltration in prostate was found in one male, interstitial focal inflammation in lung and focal necrosis in liver was observed in one female. These changes occur naturally and were not compound-related.
No abnormalities were found in uterus and ovary in the non-pregnant females and the unsuccessful copulation females of the control and 1000 mg/kg bw/day groups, respectively. Degeneration of seminiferous tubules of testis, decrease in sperm and atrophy in prostate was observed in one control male. - Histopathological findings: neoplastic:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Mass on abdomen was found in a female after 40 days of administration in the 300 mg/kg bw/day group. However, this subcutaneous tumour of the mammary gland was a benign fibroadenoma and generated naturally.
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: overall effects
- Key result
- Critical effects observed:
- not specified
Referenceopen allclose all
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- The available information comprises adequate, reliable (Klimisch score 1) and consistent studies from two reference substances with similar structure and intrinsic properties. Read-across is justified based on common precursors and breakdown products of hydrolysis and consistent trends in environmental fate, ecotoxicological and toxicological profile (refer to the endpoint discussion for further details).
The selected study is thus sufficient to fulfil the standard information requirements set out in Annex VIII-IX, 8.6, in accordance with Annex XI, 1.5, of Regulation (EC) No 1907/2006.
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
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Justification for read-across
There are no available data on the repeated dose toxicity of Dodecanoic acid, ester with 1,2,3-propanetriol (CAS 37318-95-9). The assessment was therefore based on studies conducted with analogue substances as part of a read across approach, which is in accordance with Regulation (EC) No. 1907/2006, Annex XI, 1.5. For each specific endpoint the source substance(s) structurally closest to the target substance is/are chosen for read-across, with due regard to the requirements of adequacy and reliability of the available data. Structural similarities and similarities in properties and/or activities of the source and target substance are the basis of read-across. A detailed justification for the analogue read-across approach is provided in the technical dossier (see IUCLID Section 13).
Repeated dose toxicity, oral, subacute
CAS 91052-13-0
The subacute oral toxicity of Glycerides, C8-18 and C18-unsatd. mono- and di-, acetates was investigated in Crl:WI (Han) rats according to OECD guideline 422 and in conformity with GLP (Key, 2010). Dilutions of the test substance in polyethylene glycol were administered once daily to groups of 10 male and 5 female rats at doses of 100, 300 and 1000 mg/kg bw/day for 28 days via gavage. A similar constituted group received the vehicle and served as control. In addition, satellite groups of 5 males and 5 females each for the control and high dose group were used to investigate reversibility of effects during a 14-day post-exposure recovery period. No substance-related mortalities and clinical signs occurred during the whole study period. All parameters assessed at neurobehavioural examination were found to be comparable to controls. Food consumption was similar between treated and control animals and no toxicologically relevant changes in body weights and body weight gain were noted up to 1000 mg/kg bw/day. Any statistically significant changes in clinical biochemistry and haematology parameters were considered to be of no toxicological relevance as these occurred in the absence of a clear treatment-related trend and remained within the range considered normal for rats of this age and strain. Any statistically significant changes in organ weights and organ to body weight ratios were considered to be of no toxicological relevance as these occurred in the absence of a clear treatment-related trend. The organ weight changes were within the range considered normal for rats of this age and strain and/or were present at the end of the recovery period only. In addition, no histopathological changes were noted that would indicate the organ weight changes were adverse effects. At necropsy, all incidental findings remained within the background range of findings that are encountered in rats of this age and strain. Since no dose-related trend was observed, these findings were considered to be of no toxicological relevance. Based on the results of this subacute toxicity study, the NOAEL for Crl:WI rats was considered to be 1000 mg/kg bw/day.
CAS 111-03-5
A GLP-compliant subacute oral toxicity study according to OECD guideline 422 was performed with 2,3-dihydroxypropyl oleate at doses of 100, 300 and 1000 mg/kg bw/day (supporting, 2005). Male and female Sprague Dawley rats (12 per sex and group, except for 1000 mg/kg bw/day: only 7 males) received the test substance in corn oil once daily via gavage. A control group, consisting of 7 males and 12 females, was treated with the vehicle alone. The duration of treatment was 42 days (14 days prior to mating and 28 days thereafter) in males and 42-52 days (from 14 days before mating to day 4 of lactation) in females, respectively. Satellite groups of 5 animals per sex, each for the control and test groups, were used to assess the reversibility of effects during a 14-day post-exposure recovery period. No mortality occurred. No treatment-related clinical signs and no effects on neurobehaviour were observed during the whole study period. No adverse effects on body weight development were observed during the treatment and recovery period. The analysis of clinical, haematological and urinary parameters did not reveal any dose-dependent and/or toxicologically relevant changes in treated animals compared with controls. At 100 mg/kg bw/day, a significant decrease in absolute weight of seminal vesicles in males and a significant decrease in relative weight of spleen in females were observed at necropsy. Since these effects did not follow a dose-dependent relationship and were not accompanied by any histopathological changes in the respective organs, they were not considered to be toxicologically relevant. A decrease in relative weights of pituitary in males and thyroid in females was observed at 1000 mg/kg bw/day at the end of the recovery period. Since no abnormities were reported for these organs after the administration period, they were considered as not test substance -related. No test substance-related changes were found at gross pathology. A low incidence of commonly found microscopic changes was observed, which was evenly distributed between all groups and therefore considered as incidental findings. Although one female showed a subcutaneous tumour of the mammary gland after 40 days exposure to 300 mg/kg bw/day, this benign fibroadenoma was considered to have developed naturally, since no tumours were observed at the higher dose levels. Based on the overall effects observed in this subacute study, a NOAEL of 1000 mg/kg bw/day for male and female Sprague Dawley rats was derived.
Overall conclusion for repeated dose toxicity
Analogue read-across from subacute studies from 2 source substances was applied to assess the potential for the target substance to cause repeated dose toxicity. The NOAEL values for repeated dose toxicity were at or above the currently applied limit dose value of 1000 mg/kg bw/day. No hazard after repeated oral exposure was identified. Therefore, Dodecanoic acid, ester with 1,2,3-propanetriol (CAS 37318-95-9) is not expected to cause long-term toxic effects via the oral route.
Justification for classification or non-classification
According to Article 13 of Regulation (EC) No. 1907/2006 "General Requirements for Generation of Information on Intrinsic Properties of substances", information on intrinsic properties of substances may be generated by means other than tests e.g. from information from structurally related substances (grouping or read-across), provided that conditions set out in Annex XI are met. Annex XI, "General rules for adaptation of this standard testing regime set out in Annexes VII to X” states that “substances whose physicochemical, toxicological and ecotoxicological properties are likely to be similar or follow a regular pattern as a result of structural similarity may be considered as a group, or ‘category’ of substances. This avoids the need to test every substance for every endpoint". Since the analogue concept is applied to Dodecanoic acid, ester with 1,2,3-propanetriol, data will be generated from data for reference source substance(s) to avoid unnecessary animal testing. Additionally, once the analogue read-across concept is applied, substances will be classified and labelled on this basis.
Therefore, based on the analogue read-across approach, the available data on repeated dose toxicity do not meet the classification criteria according to Regulation (EC) 1272/2008, and are therefore conclusive but not sufficient for 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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.