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EC number: 204-468-9 | CAS number: 121-43-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Toxicity to reproduction: other studies
Administrative data
- Endpoint:
- toxicity to reproduction: other studies
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Meets generally accepted scientific standards with acceptable restrictions.
Cross-reference
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Blood boron concentrations in pregnant rats fed boric acid throughout gestation
- Author:
- Price CJ, Strong PL, Murray FJ and Goldber MM
- Bibliographic source:
- Reproductive Toxicology, Vol 11, No 6 pp 833-842
Materials and methods
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Timed-mated Sprague-Dawley rats were exposed to boric acid in the diet from Gestational day 0 to 20. Dietary concentrations of Boric acid yielded average daily intakes equivalent to 0, 3, 6, 10, 13 and 25 mg/kg/d. At termination on Gestational day 20, maternal whole blood was collected in heparinized vacutainer tubes, stored frozen (-20°C) and subsequently prepared by a high-temperature alkaline ashing procedure for analysis of boron by inductively coupled plasma optical emission spectrometry.
- GLP compliance:
- yes
- Type of method:
- in vivo
Test material
- Reference substance name:
- Boric acid
- EC Number:
- 233-139-2
- EC Name:
- Boric acid
- Cas Number:
- 10043-35-3
- IUPAC Name:
- 10043-35-3
- Reference substance name:
- Boric acid
- IUPAC Name:
- Boric acid
- Details on test material:
- - Name of test material (as cited in study report): BA (CAS No 10043-35-30
- Analytical purity:
99% by ICP
98% by titration with 0.1 N sodium hydroxide
- Lot/batch No.:872703
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source:Charles River Laboratories Inc. (Raleigh, NC)
- Diet: ad libitum
- Water: ad libitum
Further details are reported in: Price et al, Developmental toxicity NOAEL and postnatal recovery in rats fed boric acid during gestation, Funamental applied toxicology. 1996 32: 179-93
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- not specified
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- ICP
LOQ 0.00281% - Duration of treatment / exposure:
- Gestation day 0 to 20
- Frequency of treatment:
- In feed, ad libitum
- Duration of test:
- 20 days
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0.025%, 0.050%, 0.075%, 0.100%, 0.200%
Basis:
analytical conc.
- Remarks:
- Doses / Concentrations:
0, 19, 36, 55, 76, 143 mg Boric acid/kg BW/day
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
Equivalent to 0, 3, 6, 10, 13, 25 mg Boron/kg BW/day
Basis:
actual ingested
- No. of animals per sex per dose:
- 28 to 32
- Control animals:
- yes, plain diet
- Statistics:
- In order to determin the degree to which calculated maternal boron intake predicted maternal blood boron concentration on gestation day 20, a linear regreassion by least square estimation was performed using the regression tool in Excel.
Results and discussion
Any other information on results incl. tables
Blood boron concentrations on gestation day 20:
Almost all of the boron concentration in the control group and 2 of 29 in the low dose group fell between the LOD and the LOQ (LOD = 0.105µg B/g blood, LOQ = 0.350µg B/g blood).All remaining samples where above the LOQ. Blood samples had boron concentrations that were clearly related to the concentration of boric acid in the diet.
Table 1: Boron concentration (µg boron/g) in whole blood on gestation day 20
Boric acid in feed (% in feed gestation day 0 to 20) |
Control |
0.025% |
0.050% |
0.075% |
0.100% |
0.200% |
Boron intake (mg B/kg BW/day) |
- |
3.3±0.1 |
6.3±0.1 |
9.6±0.1 |
13.3±0.2 |
25.4±0.4 |
Blood boron (µg B/g blood) |
0.229±0.143 (n=24) |
0.564±0.211* (n=29) |
0.975±0.261* (n=27) |
1.27±0.298* (n=25) |
1.53±0.546* (n=26) |
2.82±0.987* (n=24) |
Relative SD (%) |
62.6 |
37.5 |
26.8 |
23.4 |
35.7 |
35.1 |
Minimum (µg B /g blood) |
0.122 |
0.189 |
0.407 |
0.705 |
0.222 |
1.09 |
Maximum (µg B /g blood) |
0.695 |
1.34 |
1.57 |
1.75 |
2.47 |
5.13 |
*Statistically significant (one tailed Studentt-test (P<0.05)
Correlation of blood boron concentrations on gestation day 20 with dietary intake and time of blood collection:
Maternal blood boron concentrations at termination showed a robust positive correlation with measured boron intake expressed as either the average daily intake for the entire exposure period (gestation day 0-20) or for the final 24 h (gestation day 19-20).
Correlation of selected developmental toxicity endpoints with blood boron concentration on gestation day 20:
Examples of affected and unaffected developmental toxicity endpoints were selected as response variables for regression analysis.
Three related exposure indices were used as the regressors, specifically nominal concentration of boric acid in feed (%), individual maternal daily intake (mg boron/kg body weight/d), and individual maternal blood boron concentrations (µg boron/g) on gestation day 20. The regression analyses for number of live foetuses per litter yielded R2 values close to zero for all three indices of boron exposure. This is consistent with the finding that the number of live foetuses per litter was not affected by ingestion of diets containing 0 to 0.2% boric acid.
Three embryo/foetal endpoints were affected on gestation day 20 following exposure to ≥0.1% boric acid in the diet, specifically decreased foetal body weight and increased incidences of short rib and wavy rib. Data for the rib endpoints were not suitable for regression analysis, due to the large proportion of litters that exhibited no foetuses with either of these findings in most of the dose groups. Therefore, foetal body weight was the only affected embryo/foetal endpoint used for regression analysis. Regression analyses for foetal body weight indicated a significant, though not robust, correlation between average male or female body weight per litter and each of the three exposure indices. Because R2 values were similar for male or female foetuses, the scatter plot for the female foetal body weight per litter versus maternal blood boron are provided to demonstrate the outcome of the regression analyses for foetal body weight. These results are consistent with the finding that average foetal body weight per litter on gestation day 20 (both sexes) was significantly reduced following exposure to 0.1% or 0.2% BA (94% or 88% of control foetal weight, respectively).
Table 2: Correlation of individual maternal blood boron (µg boron/g) with developmental toxicity endpoints
Response variable |
Toxic effect |
Regressor |
R2 |
No live foetuses/litter |
No effect |
Intake Blood Dose |
-0.00554 -0.00525 -0.00612 |
Female foetal body wt (g)/litter |
↓* |
Intake Blood Dose |
0.253 0.340 0.290 |
Male foetal body wt (g)/litter |
↓* |
Intake Blood Dose |
0.239 0.343 0.273 |
*Mean foetal body weights (g/litter) were significantly reduced treatment groups fed 0.100% or 0.200% boric acid in the diet
Applicant's summary and conclusion
- Executive summary:
Average concentration of boron in the blood increased with increased dietary exposure.
Concentrations in whole blood from the 0.075% and 0.1% exposure groups (1.27 and 1.53 µg B/g blood) coresponded to the NOAEL and LOAEL (10 and 13 mg B/kg bw/d respectively) reported previously
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