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EC number: - | 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
Specific investigations: other studies
Administrative data
Link to relevant study record(s)
Description of key information
The data indicates that any endocrine effects are secondary to germ cell changes and that boric acid does not bind directly to the estrogen receptor. The structure of boric acid is fundamentally different from the multi-ringed chemical structures that are more often found to be estrogenic.
Additional information
Boric acid does not exhibit the properties or characteristics of hormones, including estrogens and androgens. Several studies have evaluated possible endocrine effects of boron compounds (Wang et al., 2008; Sauls et al., 1992; Anderson et al., 1992; Fail et al., 1992, Fail et al., 1991; Treinen & Chapin, 1991; Linder et al., 1990; Grizzle et al., 1989; Lee et al., 1978). The data indicates that any endocrine effects are secondary to germ cell changes since histologic changes occurred by Day 7 while peripheral hormone changes were not detected before Day 14 of treatment (Fail et al. 1998). Boric acid-induced testicular toxicity in rodents appears to be due to a direct effect on Sertoli cells (not an effect on the endocrine system). Boric acid was not carcinogenic in either mice (NTP, 1987) or rats (Weir and Fisher, 1972); endocrine-disrupting substances typically produce hormonally-related tumors in chronic toxicity studies in animals. Boric acid was negative in a yeast two-hybrid estrogenicity assay, indicating that boric acid does not bind directly to the estrogen receptor and mimic endogenous estrogen (Nishihara et al 2000). The structure of boric acid is fundamentally different from the multi-ringed chemical structures that are more often found to be estrogenic. Boric acid may be too small molecularly to interact with the estrogen receptor or other steroid hormone receptors. Conflicting evidence of estrogenic activity was observed in a battery of short-term in vitro and in vivo studies (Wang et al., 2008). For example, an increase in “organ coefficient of uterus” (wet uterine weight/body weight) was observed at the high dose in ovariectomized rats administered boric acid (Wang et al., 2008); however, uterine and body weights were not reported, and a dose-response relationship was not demonstrated. In comparison, boric acid did not stimulate the proliferation of MCF-7 human breast cancer cells (Wang et al., 2008).
No evidence of hormonally-related clinical symptoms have been reported in workers exposed to boric acid (Whorton et al., 1994; Sayli et al., 1998; Scialli et al., 2010; Robbins et al., 2010). An increase in the serum concentrations of both 17b-estradiol and testosterone were reported in postmenopausal women given a daily boron supplement (3 mg B/day) following 119 days on a boron-deficient diet; the elevation appeared more marked when dietary magnesium was low (Nielsen et al., 1987; Nielsen, 1994). In contrast,decreasesin serum 17b-estradiol and progesterone were reported in another study of postmenopausal women given 3.25 mg/B in the diet when dietary magnesium was low compared to postmenopausal women receiving a boron-deficient diet (Nielsen, 2004). In a NASA study of young male bodybuilders, boron supplementation had no effect on blood testosterone levels or lean body mass (Green and Ferrando, 1994).
Epidemiological, animal, and cell culture studies have identified boric acid as a chemopreventative agent in prostate cancer (Cui et al., 2004; Barranco and Eckhert, 2004; Barranco and Eckhert, 2006; Barranco et al., 2007; Barranco et al., 2009; Henderson et al., 2009). Although estrogens are frequently used to treat prostate cancer, the chemopreventative effects of boric acid on prostate cancer appear to have a non-endocrine mode of action. It was recently demonstrated in human prostate cancer cells that boron causes a dose dependent decrease of Ca(2+) release from ryanodine receptor sensitive stores, suggesting that higher boric acid blood levels lower the risk of prostate cancer by reducing intracellular Ca(2+) signals and storage (Henderson et al., 2009). Similarly, Barranco et al. (2009) hypothesized that the toxicity of boric acid in human prostate cancer cells stems from the ability of high concentrations to impair Ca2+ signaling.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.
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