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使用IEHR评估人类发育和生殖毒性的评估程序对硼酸和硼砂进行评估。专家科学委员会。

An assessment of boric acid and borax using the IEHR Evaluative Process for Assessing Human Developmental and Reproductive Toxicity of Agents. Expert Scientific Committee.

作者信息

Moore J A

出版信息

Reprod Toxicol. 1997 Jan-Feb;11(1):123-60. doi: 10.1016/s0890-6238(96)00204-3.

DOI:10.1016/s0890-6238(96)00204-3
PMID:9138630
Abstract

BACKGROUND

Boron is a ubiquitous element widely distributed in nature in the form of borates at low concentrations in soils and rocks. Boron is released from these minerals by the natural weathering processes in the form of boric acid, which is water soluble and biologically available. High levels of boric acid are naturally found in sea water. Boric acid and borax are used in the greatest quantities and represent the major boron chemical exposures to humans and the environment. The principal use of boric acid and borax is in the manufacture of various types of glass products that do not result in exposure to the consumer. Boric acid and borax are also found in an array of consumer goods including fireproofing for fabrics and wood, insecticides, and in many cosmetics and personal care products as well. Boron may be an essential element for higher animals including humans.

HUMAN EXPOSURE

Boric acid and borax are considered to be completely absorbed by the oral route of exposure. Absorption through intact skin is considered negligible, although absorption can occur through denuded or irritated skin. Boron levels in the body do not persist upon cessation of exposure. People may be exposed to boron through three primary sources: 1) consumption of private, municipal, or commercial (bottled) sources of drinking water; 2) dietary consumption of crops and other foodstuffs (including dietary supplements for body building); and 3) inhalation of boron compounds during their mining, manufacturing, and other industrial processing. While boron has been detected in 81.8% of the municipal water systems, it is a minor source of boron in most parts of the U.S. The mean boron concentration is reported as 0.2 mg B/L. However, residents of California and other western states with boron-rich geologic deposits may be regularly exposed to higher levels in drinking water. Individuals who drink bottled mineral water may also increase their exposure to boron. An EPA health advisory, recommends boron concentrations in drinking water not exceed 0.6 mg B/L [0.06 mM B] over a lifetime of exposure. Dietary exposure to boron for an adult typically ranges from ranges from 0.25 to 3.1 mg B/d with an average of 1.5 mg B/d. The high end of the exposure range, 3.1 mg B/d, was selected by the Expert Committee as best estimate of exposure. It should be noted that a diet high in fruits, vegetables, grains, legumes, and other food stuffs with high boron contents may lead to daily exposures as high as 10 mg B/d from diet alone. Some body building supplements contain boron at levels ranging from 1.5 to 10 mg B, with a median of 4 mg B. Use of the supplements containing the median concentration of boron could equal the daily intake an individual receives from diet and drinking water combined. Adults in the U.S. at the high end of the food exposure range may typically ingest up to 3.5 mg B/d, or a daily dose of 0.005 mmol B/kg b.wt., through exposure from diet (3.1 mg B/d) and drinking water (0.4 mg B/d). Individuals who also use body-building supplements may have a total daily boron intake of 7.5 mg B resulting in a daily dose of 0.01 mmol B/kg b.wt./d. Occupational exposure to boron is mainly through inhalation of borate containing dust during mining and manufacturing processes. Current occupational exposures to boron are reported to result in a daily dose of < 0.0001 to 0.2 mmol B/kg b.wt./d. Current U.S. OSHA permissible exposure limit (PEL) for sodium tetraborates is 10 mg/m3, and the California Occupational Safety and Health Administration PEL is 5 mg/m3. An exposure of 5 mg B/m3 translates to approximately 0.01 mmol B/kg b.wt./d that, coincidentally, is the same as exposure levels associated with combined municipal drinking water, diet, and body building supplement consumption. Infants may receive exposures to boric acid when it is used as a household insecticide for cockroach control. Exposure from boric acid-containing cosmetic and personal care products applie

摘要

背景

硼是一种广泛存在的元素,在自然界中以硼酸盐的形式广泛分布于土壤和岩石中,浓度较低。硼通过自然风化过程以硼酸的形式从这些矿物质中释放出来,硼酸可溶于水且具有生物可利用性。海水中天然存在高浓度的硼酸。硼酸和硼砂的使用量最大,是人类和环境接触硼化学物质的主要形式。硼酸和硼砂的主要用途是制造各类玻璃产品,不会导致消费者接触到硼。硼酸和硼砂也存在于一系列消费品中,包括织物和木材的防火剂、杀虫剂以及许多化妆品和个人护理产品中。硼可能是包括人类在内的高等动物的必需元素。

人类接触

硼酸和硼砂被认为可通过口服途径完全吸收。通过完整皮肤的吸收可忽略不计,不过通过破损或受刺激的皮肤可能会发生吸收。停止接触后,体内的硼水平不会持续存在。人们可能通过三种主要途径接触硼:1)饮用私人、市政或商业(瓶装)饮用水;2)食用农作物和其他食品(包括健身膳食补充剂);3)在硼化合物的开采、制造和其他工业加工过程中吸入硼化合物。虽然在美国81.8%的市政供水系统中检测到了硼,但在大多数地区,它是硼的次要来源。据报道,硼的平均浓度为0.2毫克硼/升。然而,加利福尼亚州和其他西部有富含硼地质矿床的州的居民可能经常接触到饮用水中更高水平的硼。饮用瓶装矿泉水的人也可能增加硼的接触量。美国环境保护局的一项健康咨询建议,在一生的接触过程中,饮用水中硼的浓度不应超过0.6毫克硼/升[0.06毫摩尔硼]。成年人通过饮食接触硼的量通常在0.25至3.1毫克硼/天之间,平均为1.5毫克硼/天。专家委员会选择接触范围的上限3.1毫克硼/天作为最佳接触估计值。应当指出,富含水果、蔬菜、谷物、豆类和其他高硼含量食品的饮食可能导致仅饮食方面的每日接触量高达10毫克硼/天。一些健身膳食补充剂含硼量在1.5至10毫克硼之间,中位数为4毫克硼。使用含硼中位数浓度的补充剂可能相当于个人从饮食和饮用水中获得的每日摄入量总和。美国处于食物接触范围上限的成年人通常可能通过饮食(3.1毫克硼/天)和饮用水(0.4毫克硼/天)摄入高达3.5毫克硼/天,即每日剂量为0.005毫摩尔硼/千克体重。同时使用健身膳食补充剂的人每日硼的总摄入量可能为7.5毫克硼,导致每日剂量为0.01毫摩尔硼/千克体重/天。职业性接触硼主要是在采矿和制造过程中吸入含硼酸盐的粉尘。据报道,目前职业性接触硼导致的每日剂量为<0.0001至0.2毫摩尔硼/千克体重/天。美国职业安全与健康管理局目前对四硼酸钠的允许接触限值为10毫克/立方米,加利福尼亚职业安全与健康管理局的允许接触限值为5毫克/立方米。5毫克硼/立方米的接触量约相当于0.01毫摩尔硼/千克体重/天,巧合的是,这与市政饮用水、饮食和健身膳食补充剂综合接触水平相同。婴儿在硼酸用作家庭蟑螂杀虫剂时可能接触到硼酸。含硼酸的化妆品和个人护理产品的接触情况适用…… (原文最后一句不完整)

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