Health implications of exposure to environmental nitrogenous compounds.

Tjeert T Mensinga, Gerrit J Speijers, Jan Meulenbelt
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引用次数: 321

Abstract

All living systems need nitrogen for the production of complex organic molecules, such as proteins, nucleic acids, vitamins, hormones and enzymes. Due to the intense use of synthetic nitrogen fertilisers and livestock manure in modern day agriculture, food (particularly vegetables) and drinking water may contain higher concentrations of nitrate than in the past. The mean intake of nitrate per person in Europe is about 50-140 mg/day and in the US about 40-100 mg/day. In the proximal small intestine, nitrate is rapidly and almost completely absorbed (bioavailability at least 92%). In humans, approximately, 25% of the nitrate ingested is secreted in saliva, where some 20% (about 5-8% of the nitrate intake) is converted to nitrite by commensal bacteria. The nitrite so formed is then absorbed primarily in the small intestine. Nitrate may also be synthesised endogenously from nitric oxide (especially in case of inflammation), which reacts to form nitrite. Normal healthy adults excrete in the urine approximately 62 mg nitrate ion/day from endogenous synthesis. Thus, when nitrate intake is low and there are no additional exogenous sources (e.g. gastrointestinal infections), the endogenous production of nitrate is more important than exogenous sources. Nitrate itself is generally regarded nontoxic. Toxicity is usually the result of the conversion of nitrate into the more toxic nitrite. There are two major toxicological concerns regarding nitrite. First, nitrite may induce methaemoglobinaemia, which can result in tissue hypoxia, and possibly death. Secondly, nitrite may interact with secondary or N-alkyl-amides to form N-nitroso carcinogens. However, epidemiological investigations and human toxicological studies have not shown an unequivocal relationship between nitrate intake and the risk of cancer. The Joint Expert Committee of the Food and Agriculture Organization of the United Nations/World Health Organization (JECFA) and the European Commission's Scientific Committee on Food have set an acceptable daily intake (ADI) for nitrate of 0-3.7 mg nitrate ion/kg bodyweight; this appears to be safe for healthy neonates, children and adults. The same is also true of the US Environmental Protection Agency (EPA) Reference Dose (RfD) for nitrate of 1.6 mg nitrate nitrogen/kg bodyweight per day (equivalent to about 7.0 mg nitrate ion/kg bodyweight per day). This opinion is supported by a recent human volunteer study in which a single dose of nitrite, equivalent to 15-20 times the ADI for nitrate, led to only mild methaemoglobinaemia (up to 12.2%), without other serious adverse effects. The JECFA has proposed an ADI for nitrite of 0-0.07 mg nitrite ion/kg bodyweight and the EPA has set an RfD of 0.1 mg nitrite nitrogen/kg bodyweight per day (equivalent to 0.33 mg nitrite ion/kg bodyweight per day). These values are again supported by human volunteer studies.

接触环境含氮化合物对健康的影响。
所有生命系统都需要氮来生产复杂的有机分子,如蛋白质、核酸、维生素、激素和酶。由于在现代农业中大量使用合成氮肥和牲畜粪便,食物(特别是蔬菜)和饮用水中硝酸盐的浓度可能比过去更高。欧洲人均硝酸盐摄入量约为50-140毫克/天,美国约为40-100毫克/天。在近端小肠中,硝酸盐被迅速且几乎完全吸收(生物利用度至少92%)。在人体中,摄入的硝酸盐中约有25%被分泌到唾液中,其中约20%(约5-8%)被共生细菌转化为亚硝酸盐。这样形成的亚硝酸盐主要在小肠中被吸收。硝酸盐也可以由内源性一氧化氮合成(特别是在炎症的情况下),一氧化氮反应形成亚硝酸盐。正常健康成人每天从尿液中排出内源性合成的硝酸盐离子约62毫克。因此,当硝酸盐摄入量较低且没有额外的外源(如胃肠道感染)时,硝酸盐的内源性生产比外源更重要。硝酸盐本身通常被认为是无毒的。毒性通常是硝酸盐转化为毒性更大的亚硝酸盐的结果。关于亚硝酸盐有两个主要的毒理学问题。首先,亚硝酸盐可诱发甲基血红蛋白血症,导致组织缺氧,甚至死亡。其次,亚硝酸盐可能与仲胺或n -烷基酰胺相互作用,形成n -亚硝基致癌物。然而,流行病学调查和人类毒理学研究并没有明确显示硝酸盐摄入量与癌症风险之间的关系。联合国粮食及农业组织/世界卫生组织联合专家委员会(JECFA)和欧洲委员会食品科学委员会制定了硝酸盐的可接受每日摄入量(ADI)为0-3.7毫克硝酸盐离子/公斤体重;这似乎对健康的新生儿、儿童和成人都是安全的。美国环境保护署(EPA)的硝酸盐参考剂量(RfD)也是如此,即每天每公斤体重1.6毫克硝酸盐氮(相当于每天每公斤体重约7.0毫克硝酸盐离子)。这一观点得到了最近一项人类志愿者研究的支持,在该研究中,单剂量亚硝酸盐(相当于硝酸盐推荐摄入量的15-20倍)仅导致轻度的甲基血红蛋白血症(高达12.2%),没有其他严重的不良反应。JECFA建议亚硝酸盐的每日推荐摄入量为0-0.07 mg亚硝酸盐离子/kg体重,EPA设定的RfD为每天0.1 mg亚硝酸盐氮/kg体重(相当于每天0.33 mg亚硝酸盐离子/kg体重)。这些数值再次得到了人类志愿者研究的支持。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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