Hansen H R, Raab A, Francesconi K A, Feldmann I
Environmental Analytical Chemistry, Department of Chemistry, University of Aberdeen, Meston Walk, Old Aberdeen AB24 3UE, U.K.
Environ Sci Technol. 2003 Mar 1;37(5):845-51. doi: 10.1021/es026074n.
Information on the effects of long-term organoarsenical consumption by mammals is limited despite the fact that foodstuffs, especially seafood, often contain organoarsenicals at very high concentrations. Here we evaluate the intake, uptake, and excretion (urine and feces) of arsenic by sheep that live on North Ronaldsay in the Orkney Islands and naturally consume large amounts of arsenosugars through their major food source-seaweed. The sheep eat a broad variety of seaweed species, and arsenic concentrations were determined in all the species observed eaten by the sheep (5.7-74.0 mg kg(-1) dry mass). Because of preference and availability, they feed mostly on the seaweed species found to contain the highest arsenic concentrations: Laminaria digitata and Laminaria hyperborea (74 +/- 4 mg kg(-1) dry mass). To quantify the arsenic intake by the sheep, a feeding experiment reflecting natural conditions as close as possible was set up. In the feeding trial, the average daily intake of arsenic by 12 ewes was 35 +/- 6 mg (97% of water-extractable arsenic was present as arsenosugars) gained from feeding on the two brown algae. To test the possible influence of microflora on the metabolism of arsenosugars, six of the sheep were adapted to feeding on grass for 5 months before the start of the trial (control sheep), and the remaining six sheep were kept on their normal seaweed diet (wild sheep). No significant difference in seaweed/arsenic intake and arsenic excretion was found between the two groups of sheep. The arsenic excreted in the feces represents 13 +/- 10% (n = 12) of the total consumed, and on the assumption of that, the average urinary excretion is estimated to 86%.The main arsenic metabolite excreted in urine was dimethylarsinic acid (DMA(V)) (60 +/- 22%) and minor amounts of dimethylarsinoylethanol (DMAE), methylarsonic acid (MA(V)),tetramethylarsonium ion (TMA+), and arsenate (As(V)) together with seven unknown arsenic compounds were also excreted. The urinary arsenic excretion pattern showed a lag period (>4 h) before significant quantities appeared in the urine, an excretion rate that peaked between 4 and 28 h after seaweed intake and a relatively slow half-life (17 h) after end of intake.
尽管事实上食物,尤其是海产品,常常含有高浓度的有机砷,但关于哺乳动物长期食用有机砷的影响的信息却很有限。在此,我们评估了生活在奥克尼群岛北罗纳德里赛岛、通过其主要食物来源——海藻自然摄入大量砷糖的绵羊对砷的摄取、吸收及排泄(尿液和粪便)情况。这些绵羊食用多种海藻,我们测定了绵羊所食用的所有观察到的海藻种类中的砷浓度(干重5.7 - 74.0毫克/千克)。由于偏好和可得性,它们主要以发现含砷浓度最高的海藻种类为食:掌状海带和巨藻(干重74 ± 4毫克/千克)。为了量化绵羊的砷摄入量,我们设置了一个尽可能反映自然条件的饲养实验。在饲养试验中,12只母羊通过食用这两种褐藻,每日平均砷摄入量为35 ± 6毫克(97%的水可提取砷以砷糖形式存在)。为了测试微生物群对砷糖代谢的可能影响,在试验开始前,其中6只绵羊先适应以草为食5个月(对照绵羊),其余6只绵羊则保持正常的海藻饮食(野生绵羊)。两组绵羊在海藻/砷摄入量和砷排泄方面未发现显著差异。粪便中排泄的砷占总摄入量的13 ± 10%(n = 12),据此估计平均尿排泄量为86%。尿液中排泄的主要砷代谢物是二甲基胂酸(DMA(V))(60 ± 22%),同时还排泄了少量的二甲基胂酰乙醇(DMAE)、甲基胂酸(MA(V))、四甲基胂离子(TMA+)和砷酸盐(As(V)),以及七种未知的砷化合物。尿液砷排泄模式显示,在大量砷出现在尿液之前有一个滞后期(>4小时),摄入海藻后4至28小时排泄率达到峰值,摄入结束后半衰期相对较慢(17小时)。