Bencko Vladimir, Yan Li Foong Florence
Institute of Hygiene and Epidemiology, First Faculty of Medicine, Charles University, Prague, Czech Republic.
Ann Agric Environ Med. 2017 Jun 12;24(2):312-316. doi: 10.26444/aaem/74715.
Arsenicals in agriculture. Beginning in the 1970s, the use of arsenic compounds for such purposes as wood preservatives, began to grow. By 1980, in the USA, 70% of arsenic had been consumed for the production of wood preservatives. This practice was later stopped, due to the US Environmental Protection Agency (EPA) ban of the arsenic-and chromium-based wood preservative chromated copper arsenate. In the past, arsenical herbicides containing cacodylic acid as an active ingredient have been used extensively in the USA, from golf courses to cotton fields, and drying-out the plants before harvesting. The original commercial form of Agent Blue was among 10 toxic insecticides, fungicides and herbicides partially deregulated by the US EPA in February 2004, and specific limits on toxic residues in meat, milk, poultry and eggs, were removed. Today, however, they are no longer used as weed-killers, with one exception - monosodium methanearsonate (MSMA), a broadleaf weed herbicide for use on cotton. Severe poisonings from cacodylic acid caused headache, dizziness, vomiting, profuse and watery diarrhea, followed by dehydration, gradual fall in blood pressure, stupor, convulsions, general paralysis and possible risk of death within 3-14 days.The relatively frequent use of arsenic and its compounds in both industry and agriculture points to a wide spectrum of opportunities for human exposure. This exposure can be via inhalation of airborne arsenic, contaminated drinking water, beverages, or from food and drugs. Today, acute organic arsenical poisonings are mostly accidental. Considerable concern has developed surrounding its delayed effects, for its genotoxic and carcinogenic potential, which has been demonstrated in epidemiological studies and subsequent animal experiments. There is substantial epidemiological evidence for an excessive risk, mostly for skin and lung cancer, among humans exposed to organic arsenicals in occupational and environmental settings. Furthermore, the genotoxic and carcinogenic effects have only been observed at relatively high exposure rates. Current epidemiological and experimental studies are attempting to elucidate the mechanism of this action, pointing to the question whether arsenic is actually a true genotoxic, or rather an epigenetic carcinogen. Due to the complexity of its effects, both options remain plausible. Its interactions with other toxic substances still represent another important field of interest.
农业中的砷化物。从20世纪70年代开始,砷化合物用于木材防腐等用途的用量开始增加。到1980年,在美国,70%的砷用于生产木材防腐剂。由于美国环境保护局(EPA)禁止使用含砷和铬的木材防腐剂铬酸铜砷酸盐,这种做法后来被停止。过去,以二甲胂酸为活性成分的砷类除草剂在美国被广泛使用,从高尔夫球场到棉田,用于在收获前使植物干枯。“蓝剂”最初的商业形式是2004年2月美国环境保护局部分解除管制的10种有毒杀虫剂、杀菌剂和除草剂之一,肉类、牛奶、家禽和蛋类中有毒残留物的具体限量被取消。然而如今,除了一种用于棉花的阔叶杂草除草剂甲胂酸单钠(MSMA)外,它们不再用作除草剂。二甲胂酸导致的严重中毒会引起头痛、头晕、呕吐、大量水样腹泻,随后出现脱水、血压逐渐下降、昏迷、抽搐、全身麻痹,在3至14天内可能有死亡风险。砷及其化合物在工业和农业中相对频繁的使用表明人类有广泛的接触机会。这种接触可以通过吸入空气中的砷、受污染的饮用水、饮料,或通过食物和药物。如今,急性有机砷中毒大多是意外情况。由于其遗传毒性和致癌潜力,人们对其延迟效应产生了相当大的关注,这已在流行病学研究和随后的动物实验中得到证实。有大量流行病学证据表明,在职业和环境环境中接触有机砷的人群中存在过高风险,主要是皮肤癌和肺癌。此外,遗传毒性和致癌作用仅在相对高的接触率下才被观察到。目前的流行病学和实验研究正试图阐明这种作用的机制,这就引出了一个问题,即砷实际上是一种真正的遗传毒性物质,还是一种表观遗传致癌物。由于其作用的复杂性,两种选择似乎都有道理。它与其他有毒物质的相互作用仍然是另一个重要的研究领域。