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EC number: 940-725-8 | CAS number: -
- 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:
- fertility, other
- Remarks:
- based on test type (migrated information)
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 1991
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable well-documented study report which meets basic scientific principles.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 415 [One-Generation Reproduction Toxicity Study (before 9 October 2017)]
- Principles of method if other than guideline:
- Male rats were given 0, 750, 1500 or 3000 mg/kg neat JP-8 daily by gavage for 70 days prior to mating with naive females to assess fertility and sperm parameters.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- JP-8 jet fuel
- IUPAC Name:
- JP-8 jet fuel
- Reference substance name:
- Kerosine (petroleum)
- EC Number:
- 232-366-4
- EC Name:
- Kerosine (petroleum)
- Cas Number:
- 8008-20-6
- IUPAC Name:
- 8008-20-6
- Details on test material:
- The JP-8 jet fuel was supplied by the U.S. Air Force (AFRL Propulsion Directorate, Wright- Patterson AFB, OH). The fuel met the requirements of Military Specification MIL-T-83133A. JP-8 was administered by gavage without a vehicle (neat). Control animals were dosed with 1.0 mL distilled water under the same conditions as test groups. Volumes to be administered each day were calculated from the individual daily body weights and the density of the test material (0.81 g/mL).
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Labs, Kingston, NY
- Weight at study initiation: (P) Males: 180 to 220 g
- Diet (e.g. ad libitum): Formula 5008, Ralston Purina, St. Louis, MO, ad libitum
- Water (e.g. ad libitum):ad libitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21-25
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- JP-8 was administered by gavage without a vehicle (neat). Control animals were dosed with 1.0 mL distilled water under the same conditions as test groups. Volumes to be administered each day were calculated from the individual daily body weights and the density of the test material (0.81 g/mL).
- Details on mating procedure:
- In order to stagger delivery dates, male rats were paired with more than one female rat between 70 and 90 days of dosing with JP-8. Male rats were gavaged during cohabitation and returned to individual cages after successful mating. Exposure was continued until the rats were euthanized by carbon dioxide overdose at 90 days
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 90 days
- Frequency of treatment:
- daily; 7 days/ week
- Details on study schedule:
- The rats were given 0 (control), 750, 1500 or 3000 mg/kg JP-8 daily by gavage for 70 days prior to mating with naive females. Male rats were cohabitated with one female at a time. In order to stagger delivery dates, male rats were paired with more than one female rat between 70 and 90 days of dosing with JP-8. Male rats were gavaged during cohabitation and returned to individual cages after successful mating.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0 (control), 750, 1500 or 3000 mg/kg
Basis:
actual ingested
- No. of animals per sex per dose:
- 20 males
- Control animals:
- yes, sham-exposed
- Positive control:
- none
Examinations
- Parental animals: Observations and examinations:
- body weight and mortality
- Oestrous cyclicity (parental animals):
- not examined
- Sperm parameters (parental animals):
- The epididymides were collected from each male rat at necropsy. The epididymides were then minced in phosphate buffered saline with bovine serum albumin; the resulting sperm suspension was videotaped in a Petroff Hauserr chamber. Determinations were made from the videotape using the CellSoft Automated Semen Analyzer (CRYO Resources, Ltd., New York, NY). Motility parameters measured by the CellSoft Analyzer were: sperm concentration, motile sperm concentration, percent motility, velocity, linearity, maximum amplitude of lateral head displacement (ALH), mean ALH and beat/cross frequency. The CellSoft Analyzer also measured the following parameters: mean radius, number of circular cells, percent circular cells/motile cells and percent circular cells/all cells.
- Litter observations:
- not examined
- Postmortem examinations (parental animals):
- not examined
- Postmortem examinations (offspring):
- not examined
- Statistics:
- Statistical Analyses for General Toxicity Data
Adult body weights, organ weights and urine metabolites were analyzed by an ANOVA with multiple comparisons. Clinical chemistry results, hematology values, urinalysis data and severity of pathological changes were compared using an ANOVA. The level of significance was accepted at p<0.05 unless stated otherwise.
Statistical Analyses for Reproductive Measures
A one-factor (dose) or two-factor (dose and pup sex) analysis of variance (ANOVA) was performed for continuous variables. Error terms used were either dam(dose) or pup sex and dam(dose). One-way ANOVA was used with gestation lengths, sperm parameters and litter sizes while two-way was used for pup weights. Post-hoc paired comparisons of dose used two-tailed t-tests with pooled error.
For categorical variables, a Chi-square test of proportions was used to determine differences among the doses. Chi-square tests were used for pregnancy rates and percent viability. Posthoc paired comparison for the viability parameter was performed with Fisher's Exact test. The level of significance was accepted at p<0.05 unless stated otherwise. - Reproductive indices:
- Unexposed females mated with dosed males were allowed to give birth in order to determine gestation length. Successful mating (gestation day 0) was determined by presence of copulatory plug or sperm in a vaginal contents smear. Pregnancy rate (%) and gestation duration (days) were recorded for all dams. All rats were euthanized by carbon dioxide overdose.
- Offspring viability indices:
- not examined
Results and discussion
Results: P0 (first parental generation)
General toxicity (P0)
- Clinical signs:
- no effects observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Organ weight findings including organ / body weight ratios:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Other effects:
- not examined
Reproductive function / performance (P0)
- Reproductive function: oestrous cycle:
- not examined
Details on results (P0)
Gestation parameters for unexposed females mated with treated males are shown below (Table 1). Pregnancy rates and gestation lengths were not adversely affected by paternal gavage exposure to JP-8. These parameters were not significantly different between dose groups. As a whole, these dams had low pregnancy rates, including the controls.
Epididymal sperm samples from males exposed by gavage to 0, 750, 1500 and 3000 mg/kg/day JP-8 for 90 days were evaluated using the CellSoft Automated Semen Analyzer. Table 2 contains sperm values for each dose group. The number of male rats per group ranged from 20 to 23. Outliers were removed after rigorous statistical analysis and were not related to dose. Significant differences were not found under any condition of analysis.
Effect levels (P0)
- Dose descriptor:
- NOAEL
- Remarks:
- fertility
- Effect level:
- >= 3 000 mg/kg bw/day (actual dose received)
- Sex:
- male
Results: F1 generation
General toxicity (F1)
- Clinical signs:
- not examined
- Mortality / viability:
- not examined
- Body weight and weight changes:
- not examined
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- not examined
- Histopathological findings:
- not examined
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
TABLE 1. GESTATION PARAMETERS OF UNEXPOSED DAMS MATED TO MALE RATS
Dose Group | Number of Dams | Pregnancy Rate | Gestation Length |
mg/kg/day | (n) | (%) | mean (+/- SE) |
0 | 36 | 47 | 21.24 (0.26) |
750 | 38 | 39 | 21.07 (0.18) |
1500 | 42 | 57 | 21.08 (0.15) |
3000 | 32 | 53 | 21.41 (0.12) |
TABLE 2. SPERM PARAMETERS (MEAN ± SE) IN MALE RATS EXPOSED
Parameter | 0 mg/kg/day | 750 mg/kg/day | 1500 mg/kg/day | 3000 mg/kg/day |
(n=21) | (n=21) | (n=23) | (n=20) | |
Percent Motile | 25.06 +/- 2.07 | 29.60 +/- 2.26 | 25.10 +/- 1.59 | 24.60 +/- 2.01 |
Conc. Motile (million/mL) | 0.21 +/- 0.02 | 0.19+/- 0.02 | 0.20 +/- 0.02 | 0.16 +/- 0.02 |
Mean Velocity (um/s) | 112.21 +/- 4.14 | 122.59 +/- 5.64 | 117.85 +/- 5.09 | 117.04 +/- 4.84 |
Mean Linearity | 3.74 +/- 0.14 | 3.70 +/- 0.21 | 4.27 +/- 0.16 | 4.04 +/- 0.21 |
Max ALH (um) | 4.04 +/- 0.19 | 4.28 +/- 0.24 | 4.06 +/- 0.15 | 4.00 +/- 0.19 |
Mean ALH (um) | 3.44 +/- 0.15 | 3.64 +/- 0.18 | 3.47+ 0.1 | 3.41 +/- 0.14 |
Beat/Cross Frequency Hz (1/s) | 10.42 +/- 0.28 | 10.34 +/- 0.23 | 10.86 +/- 0.19 | 10.70 +/- 0.27 |
Avg Radius (um) | 16.04 +/- 1.19 | 15.67 +/- 0.92 | 15.93 +/- 1.22 | 13.79 +/- 0.93 |
Circular % of Motile | 14.18 +/- 1.43 | 13.96 +/- 1.72 | 17.26 +/- 1.86 | 16.38 +/- 2.3 |
Circular % of All Cells | 3.87 +/- 0.63 | 4.33 +/- 0.71 | 4.23 +/- 0.5 | 4.30 +/- 0.72 |
Applicant's summary and conclusion
- Conclusions:
- The NOAEL >=3000 mg/kg/day for male rat fertility.
- Executive summary:
Male rats were given 0, 750, 1500 or 3000 mg/kg neat JP-8 daily by gavage for 70 days prior to mating with naive females to assess fertility and sperm parameters. Males were allowed to mate while continuing to receive treatment. Aside from a decrement in male body weight, no clinical signs were observed. There were no statistical differences noted in any reproductive parameter measured. The reproductive NOAEL >= 3000 mg/kg/day for male rats.
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