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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 240-898-3 | CAS number: 16872-11-0
- 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:
- repeated dose toxicity: oral
- Remarks:
- other: Reproduction / Developmental Toxicity Screening Test
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP-compliant guideline study, available as unpublished report, no restrictions, fully adequate for assessment.
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 007
- Report date:
- 2007
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Guideline 421 (Reproduction / Developmental Toxicity Screening Test)
- GLP compliance:
- yes (incl. QA statement)
- Limit test:
- no
Test material
- Reference substance name:
- Potassium tetrafluoroborate
- EC Number:
- 237-928-2
- EC Name:
- Potassium tetrafluoroborate
- Cas Number:
- 14075-53-7
- IUPAC Name:
- potassium tetrafluoroborate
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
- Details on test material:
- - Name of test material (as cited in study report): potassium tetrafluoroborate
- Physical state: white powder
- Analytical purity: 98.9%
- Lot/batch No.: BWF41213
- Expiration date of the lot/batch: 13 December 2009
- Storage condition of test material: ambient temperature
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland, Sulzfeld, Germany, SPF-bred colony
- Age at study initiation: (P) 8-9 wks
- Weight at study initiation: (P) within 20% of the mean weight for each sex
- Housing: in macrolon cages with wood shavings (Lignocel, Type 3/4) as bedding material and strips of paper (Enviro-dri) as environmental enrichment. During the premating period, the animals were housed in groups of 4/sex. For mating, 1 male and 1 female were housed together. Mated femaleswere housed individually in macrolon cages, which were then placed in another cage rack. After delivery, the cage containing the dam with litter were transferred to another cage rack
- Diet: cereal-based (closed formula) rodent diet (Rat & Mouse No. 3 Breeding Diet, RM3) from a commercial supplier (SDS Special Diets Services, Witham, England), ad libitum
- Water: tap water in polypropylene bottles, cleaned weekly and filled as needed, ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3
- Humidity (%): 30-70
- Air changes (per hr): 10
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Remarks:
- 1% solution in water
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS: The test substance was suspended in 1% CMC. The dosing solutions were prepared weekly and stored at 2-10 ºC. The miscibility of the test substance in vehicle were checked by visual inspection before the start of the study.
VEHICLE
- Concentration in vehicle: 0, 20, 58.2, 175 and 500 mg/mL
- Amount of vehicle: 2 mL/kg bw
- Lot/batch no.: 101K0185
- Purity: 1% solution in water - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Analyses to determine the stability, homogeneity and content of the test substance in the vehicle was conducted, by quantitative determination of the level of potassium tetrafluoroborate by determination of boron using ICP-AES and determination of fluoride using GC-FID with headspace.
- Duration of treatment / exposure:
- Males: during 4 weeks premating period and during the mating period for at least 5 weeks until sacrifice. Females: during a 2-week premating period, during the mating, gestation and lactation period until sacrifice. Animals were not dosed on the day of necropsy.
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
40, 116.5 and 350 mg/kg bw/day (adjusted from 116.5, 350 and 1000 mg/kg bw/day due to body weight loss in high-dose animals)
Basis:
actual ingested
- No. of animals per sex per dose:
- 12/sex/dose
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Rationale for animal assignment: computer randomization proportionally to body weight.
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily in the morning hours by cage-side observations. On working days, all cages were checked again in the afternoon for dead or moribund animals to minimise loss of animals from the study. On Saturdays and Sundays only one check per day was carried out.
BODY WEIGHT: Yes
- Time schedule for examinations: shortly before the time of dosing (randomization) and on the first day of dosing and weekly thereafter during the premating period. In addition, body weights of the male animals were measured on day 3 and 5 of the study. Males were weighed approximately weekly during the mating period until sacrifice. Females were weighed approximately weekly during mating and mated females were weighed on days 0, 7, 14 and 21 during presumed gestation and on day 1 and 4 of lactation. All animals were weighed on the day of sacrifice.
FOOD CONSUMPTION: Yes
Food consumption of male rats was measured approx. weekly, except during the mating period. In addition, food consumption of the male animals was measured on day 3 and 5 of the study, except for male animals of lowest dose group.
Food consumption of female rats was measured weekly during the premating period and during the gestation period from gestation days 0-7, 7-14 and 14-21, and once during the lacation period from day 1 to 4.
WATER CONSUMPTION: Yes
During daily observations, until day 5 of gestation.
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: No
CLINICAL CHEMISTRY: No
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No - Sacrifice and pathology:
- SACRIFICE
- Male animals: all male animals of the 1000 mg/kg bw/day group were sacrified on day 7 of the study after 3 daily dosages and 5 days of recovery. Males from other groups were euthanised after approximately 5 weeks of exposure.
- Maternal animals: sperm-positive females that turned out to be non-pregnant were killed 24-26 days after copulation. Females that became pregnant were sacrificed at day 4 of lactation.
GROSS NECROPSY
Animals were examined grossly for macroscopic changes.
HISTOPATHOLOGY / ORGAN WEIGHTS
Samples of the following organs were preserved: ovaries (after counting of the corpora lutea), uterus (after counting of the implantation sites), testes, epididymides, seminal vehicles, prostate, organs and tissues showing macroscopic abnormalities. - Statistics:
- Clinical findings were evaluated by Fisher's probability test. Body weight, body weight gain, organ weights and food consumption data were subjected to one-way analysis of variance (ANOVA) followed by Dunnett's multiple comparison tests. Histopathological changes were evaluated by Fisher's exact probability test.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY (PARENTAL ANIMALS)
Two female animals of the 350 mg/kg bw/day died during lactation period. Daily clinical observations during the study did not reveal any remarkable findings in animal appearance, general condition or behaviour among the dosing and control groups.
BODY WEIGHT (PARENTAL ANIMALS)
Twelve male animals of the 1000 mg/kg bw/day group lost ca. 10% (30 g) of their initial body weight on day 0 after 3 daily dosages. It was decided, after the consultation with the sponsor, to stop dosing these male animals and to keep these animals in the study without treatment up to day 7, to study the reversibility of this effect. Mean body weight of the animals of day 7 was comparable to their body weight on day 0.
Mean body weight and/or body weight change of the male and female animals of 350 mg/kg bw/day group were statistically significantly decreased during several periods of the study. Mean body weight of the male animals of the 350 mg/kg bw/day group was statistically significantly decreased from day 3 until sacrifice. Mean body weight change of the male animals of this group was statistically significantly decreased between days 0-3, 3-5, 7-14 and 21-28. Mean body weight of the male animals of the 116.5 mg/kg bw/day group was statistically significantly decreased from day 28 until sacrifice. Mean body weight change of the male animals of this group was statistically significantly decreased between days 21-28. No decreased in body weight and body weight change was observed in the male animals of the 40 mg/kg bw/day group. During the premating period, no effect on body weight or body weight change was observed in female animals treated with KBF4. Mean body weight of the female animals of the 350 mg/kg bw/day group was statistically significantly decreased from gestation day 7-21. Mean body weight change of the female animals of this group was statistically significantly decreased from gestation days 7-14. Mean body weight of the female animals of this group was statisitcally significantly decreased on lactation day 1. During the lactation period no effect was observed on mean body weight change of the KBF4-treated females.
FOOD CONSUMPTION (PARENTAL ANIMALS)
Food consumption of the male animals of the 1000 mg KBF4/kg body weight group was statistically significantly decreased (5.45 g/animal/day versus 19.65 g/animal in the control group) from day 0-3. Animals of this group were not longer dosed from day 3 to 7; food consumption of the animals was back to normal or even higher from day 5 to 7. Food consumption of the male animals of the 350 mg KBF4/kg body weight group was statistically significantly decreased during the premating period. Food consumption of the animals of the 116.5 mg KBF4/kg body weight group was comparable to the control group except for the statistical significant difference between dat 7 and 14. Food consumption of the female animals of the 350 mg KBF4/kg body weight group was statistically significantly decreased from day 14-21 of the premating period, during GD 0-14 (g/animal/day) and GD 0-7 (g/kg/day) and day 1-4 of lactation (g/animal/day). One animal of this group did not eat any food from lactation day 1-4. Furthermore, no remarkable differences were observed in the KBF4-treated groups.
ORGAN WEIGHTS (PARENTAL ANIMALS)
Absolute and relative testes and epididymides weights were comparable in all groups.
GROSS PATHOLOGY (PARENTAL ANIMALS)
At scheduled necropsy no treatment-related gross changes were observed.
HISTOPATHOLOGY (PARENTAL ANIMALS)
Microscopic examination did not reveal treatment related histopathological changes in any of the sampled organs and tissues (epididymides, testes, uterus and ovaria).
OTHER FINDINGS (PARENTAL ANIMALS):
Effects on water consumption were observed (not exactly measured) in the male and female animals of the 350 mg/kg bw/day group from week 3 onwards. In consultation with the study director it was decided to stop registration of water consumption after day 5 of gestation.
Effect levels
- Dose descriptor:
- NOAEL
- Effect level:
- 40 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Based on the effects on mortality in the 350 mg/kg bw/day group and body weight and food consumption in the 116.5 and 350 mg/kg bw/day group.
Target system / organ toxicity
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- A NOAEL of 40 mg/kg bw/day was established in a reproduction/developmental toxicity screening test.
- Executive summary:
In a GLP compliant reproduction/developmental toxicity screening test, performed according to OECD Guideline 421, Wistar rats of both sexes were orally exposed to potassium tetrafluoroborate. 1% carboxymethylcellulose solution in water (CMC) was used as vehicle. Groups of 12 rats per sex were dosed daily with 0, 40, 116.5 and 350 mg KBF4/kg body weight for up to approx. 35 days (males) or during 4 weeks premating, mating, gestation and up to day 4 of lactation (females). Initially a group of male rats was dosed with 1000 mg KBF4/kg body weight. These animals showed a weight loss of approx. 10% after 3 daily dosages. For that reason this group was replaced by the 40 mg KBF4/kg body weight. Two female animals of the 350 mg KBF4/kg body weight died during the lactation period. Daily clinical observations during the study did not reveal any remarkable findings in animals' appearance, general condition or behavior among the dosing and control groups. Effects on water consumption were observed (not exactly measured) in the male and female animals of the 350 mg KBF4/kg body weight group from week 3 onwards. Mean body weight and or body weight change of the male and female animals of the 350 mg KBF4/kg body weight were statistically significantly decreased during several periods of the study. Mean bodyweight or bodyweight change of the 116.5 mg KBF4/kg body weight group was only statistically significantly decreased in the male animals from day 21 onwards. Food consumption of the 350 mg KBF4/kg body weight group was statistically significantly decreased in male and female animals during several periods of the study. Food consumption of the male animals of the 116.5 mg KBF4/kg body weight group was statistically significantly decreased from day 7 to 14. Terminal body weight of the male animals of the 40 and 116.5 mg KBF4/kg body weight groups was statistically significantly decreased. At scheduled necropsy no treatment related gross changes were observed. Microscopic examination did not reveal treatment related histopathological changes in any of the sampled organs and tissues (epididymides, testes, uterus and ovaries). Based on the effects on mortality in the 350 mg KBF4 group/ kg body weight group, (terminal) body weight and food consumption in the 116.5 and 350 mg KBF4/kg body weight groups, the NOAEL for parental toxicity is 40 mg KBF4/kg body weight/day.
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.