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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 281-638-9 | CAS number: 84000-82-8
- 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:
- short-term repeated dose toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- Data is from peer reviewed publication
Data source
Reference
- Reference Type:
- publication
- Title:
- Hydrocarbon Nephropathy In Male Rats: Identification Of The Nephrotoxic Components Of Unleaded Gasoline
- Author:
- Clive A. Halder, Charles E. Holdsworth, Beverly Y. Cockrell And Vincent J. Piccirillo
- Year:
- 1 985
- Bibliographic source:
- Toxicology and Industrial Health, Vol. 1, No. 3, 67-87, 1985
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Refer below principle
- Principles of method if other than guideline:
- 28 days repeated dose oral toxicity study was performed to determine the toxic nature of light catalytic reformed naphtha
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Naphtha (petroleum), light catalytic reformed
- Molecular formula:
- C24H48
- IUPAC Name:
- Naphtha (petroleum), light catalytic reformed
- Details on test material:
- - Name of test material: Light catalytic reformed naphtha
- Molecular formula: C24H48
- Molecular weight: Unspecified
- Substance type: Organic
- Physical state: No data
- Impurities (identity and concentrations): No data
Constituent 1
- Specific details on test material used for the study:
- - Name of test material: Light catalytic reformed naphtha
- Molecular formula: C24H48
- Molecular weight: Unspecified
- Substance type: Organic
- Physical state: No data
- Impurities (identity and concentrations): No data
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Details on species / strain selection:
- No data
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Kingston, New York
- Age at study initiation: 11 weeks approx..
- Weight at study initiation:
- Fasting period before study:
- Housing: The animals were individually housed in suspended polycarbonate cages both during study and for a 2-wk quarantine period. Following the quarantine period, the rats were randomly assigned by weight to groups of 10 each.
- Diet (e.g. ad libitum): Ad libitum
- Water (e.g. ad libitum): Ad libitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22.2 – 23.8 ˚C
- Humidity (%): 40-80%
- Air changes (per hr):
- Photoperiod (hrs dark / hrs light): 12-h light/ dark cycle
IN-LIFE DATES: From: To: No data
Administration / exposure
- Route of administration:
- oral: gavage
- Details on route of administration:
- No data
- Vehicle:
- not specified
- Details on oral exposure:
- No data
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- No data
- Duration of treatment / exposure:
- 28 days
- Frequency of treatment:
- 5 d/week
Doses / concentrations
- Remarks:
- 0, 500 or 2000 mg/Kg/day
- No. of animals per sex per dose:
- Total:
0 mg/Kg /day: 10 male rats
500 mg/Kg /day: 10 male rats
2000 mg/Kg /day: No detailed data
Positive control: 10 male rats - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: The selection of the dosage levels was based on a single pilot study using unleaded gasoline; pilot studies were not conducted on each test material to assay for toxicity. From the pilot study, a 28-d maximum tolerated dose of 2.0 g/ kg/ d was established. Also, the 0.5 g/ kg/ d dose level was selected because it was effective, yet was not lethal. In each case, the test material was administered neat. Dosages for each animal were calculated based upon body weights taken prior to dosing on day I, and the appropriate dosing volume for each test material was determined using its specific gravity.
- Rationale for animal assignment (if not random): The rats were randomly assigned by weight to groups of 10 each
- Rationale for selecting satellite groups: No data
- Post-exposure recovery period in satellite groups:
- Section schedule rationale (if not random): No data - Positive control:
- Yes, Unleaded gasoline blend was used at positive control
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily
- Cage side observations checked in table [No.?] were included. Mortality and Morbidity
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Twice daily
BODY WEIGHT: Yes
- Time schedule for examinations: prior to dosing on day 1 and at the time of the scheduled sacrifices only
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): No data
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No data
- Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No data
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No data
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No data
- Time schedule for examinations: No data
OPHTHALMOSCOPIC EXAMINATION: No data
- Time schedule for examinations: No data
- Dose groups that were examined: No data
HAEMATOLOGY: No data
- Time schedule for collection of blood: No data
- Anaesthetic used for blood collection: No data
- Animals fasted: No data
- How many animals: No data
- Parameters checked in table [No.?] were examined. No data
CLINICAL CHEMISTRY: No data
- Time schedule for collection of blood: No data
- Animals fasted: No data
- How many animals: No data
- Parameters checked in table [No.?] were examined. No data
URINALYSIS: No data
- Time schedule for collection of urine: No data
- Metabolism cages used for collection of urine: No data
- Animals fasted: No data
- Parameters checked in table [No.?] were examined. No data
NEUROBEHAVIOURAL EXAMINATION: No data
- Time schedule for examinations: No data
- Dose groups that were examined: No data
- Battery of functions tested: sensory activity / grip strength / motor activity / other: No data
OTHER: No data - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, gross pathology was performed on all animals which were found dead or moribund. The kidneys for these animals were weighed and were
fixed for histopathologic evaluation; however, the weights were not included in the tabulations of the means for each group. On the day immediately following the 20th dose, the remaining study animals were sacrificed, without prior fasting, using an overdose of sodium pentobarbital, and necropsied. At necropsy, only the kidneys
were removed, trimmed free of perirenal fat and connective tissue, and weighed
HISTOPATHOLOGY: Yes, kidneys were sliced longitudinally and fixed by immersion in 10% neutral buffered formalin. All other tissues were discarded after gross examination.
The processed kidneys were embedded in paraffin and sectioned. Two sections were made from each kidney. One section was stained with hematoxylin and eosin and was used to examine for foci of regenerative epithelium in the renal cortex, as well as for foci of intratubular cast formation located between the inner and outer stripe of the renal medulla. The second section was stained with Mallory-Heidenhain stain to assess the degree of hyaline droplet (phagolysosome) accumulation within the epithelial cells of the proximal convoluted tubules.
The severity of the nephrotoxic responses was evaluated using a grading system that was found to be consistent and reproducible.
The changes were graded on a scale of 1 to 4 based on severity or number of pathologic foci, as applicable. The scores for each lesion type were combined and then multiplied by 10. The kidney lesions from animals that died on or before day 14 of exposure were scored, but these scores were not included in the tabulations of the means for each group. - Other examinations:
- No data
- Statistics:
- Mean and standard deviation calculations were made on body weight, kidney weight and kidney pathology data. The body and kidney weight data were compared statistically to the appropriate saline control group using a Student’s t-Test (Snedecor and Cochran, 1980). The means of the kidney lesion scores were compared to that of the appropriate saline control group using the Mann-Whitney U Test (Hays, 1981). Statistical significance was assigned to a probability of <5%.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- The test chemical doses were well tolerated but lethargy was the most prominent signs.
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- The mean terminal body weights for all high-dose treatment group was significantly reduced than the respective saline control group
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Description (incidence and severity):
- Mean kidney weights gave no indication of nephrotoxicity
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- The most common pathologic findings were confined to the kidneys and stomachs. The kidney lesions generally consisted of discoloration and mottling, and may have been due to postmortem changes since they were mainly observed in the animals that died prematurely.
- Neuropathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- The unleaded gasoline, tested as a positive reference material, produced a strong nephrotoxic response
The light catalytic-reformed naphtha induced a very weak nephrotoxic response. - Histopathological findings: neoplastic:
- not specified
- Other effects:
- not specified
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 500 other: mg/Kg/day
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: No adverse effects were noted at the mentioned dose level
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Table: Summary of Body weights, Kidney effects and mortality
Test chemical |
Dose (mg/Kg/day) |
Initial body weight (g) |
Terminal body weight (g) |
Nephropathy score |
Kidney weight (g) |
Mortality (%) |
Saline (negative control) |
2000 |
163±16 |
211±23 |
27±5 |
1.72±0.15 |
0 |
Reference unleaded gasoline |
500 |
162±14 |
201±21 |
84±13* |
1.77±0.15 |
0 |
2000 |
163±12 |
183±25S- |
83±21* |
1.73±0.20 |
0 |
|
Light catalytic reformed naphtha |
500 |
162±12 |
197±17 |
33±5 |
1.70±0.14 |
0 |
2000 |
167±16 |
176±16S- |
39±9* |
1.70±0.18 |
20 |
* Significantly elevated kidnet scores relative to saline control. P≤0.05 Mann Whitney U test
S- Significantly lower relative to saline control p≤0.05, Student’s t-test
Applicant's summary and conclusion
- Conclusions:
- The No Observed Adverse Effect Level (NOAEL) for light catalytic reformed naphtha is considered to be 500 mg/Kg/day during 28 days study conducted using male Fischer 344 rats.
- Executive summary:
28 days repeated dose oral toxicity study was performed to determine the toxic nature oflight catalytic reformed naphtha. The study was performed using using male Fischer 344 rats at dose levels of 0 (saline), 500 or 2000 mg/Kg/day for 28 days. The animals were doses daily for 5days/week. During the study period, the animals were observed for clinical signs, mortality, morbidity, body weight and organ weight changes, gross and histo-pathology.The test chemical doses were well tolerated but lethargy was the most prominent signs. The mean terminal body weights for all high-dose treatment group (2000 mg/Kg/day) was significantly reduced than the respective saline control group. Mean kidney weights gave no indication of nephrotoxicity. The most common pathologic findings were confined to the kidneys and stomachs. The kidney lesions generally consisted of discoloration and mottling, and may have been due to postmortem changes since they were mainly observed in the animals that died prematurely. The light catalytic-reformed naphtha induced a very weak nephrotoxic response at 2000 mg/Kg/day dose. Based on the observations made, the No Observed Adverse Effect Level (NOAEL) forlight catalytic reformed naphtha is considered to be 500 mg/Kg/day during 28 days study conducted using male Fischer 344 rats.
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.