Jadhav S H, Sarkar S N, Ram G C, Tripathi H C
Division of Pharmacology and Toxicology, Indian Veterinary Research Institute, Izatnagar, 243122, Uttar Pradesh, India.
Arch Environ Contam Toxicol. 2007 Oct;53(3):450-8. doi: 10.1007/s00244-006-0177-1. Epub 2007 Jul 26.
Immunotoxicity is an important health hazard of heavy metal exposure. Because the risk of combined exposure in the population cannot be neglected, we examined whether subchronic exposure to a mixture of metals (arsenic, cadmium, lead, mercury, chromium, nickel, manganese, and iron) via drinking water at contemporary Indian groundwater contamination levels and at concentrations equivalent to the WHO maximum permissible limit (MPL) in drinking water can induce immunotoxicity in male rats. Data on groundwater contamination with metals in India were collected from literature and metals were selected on the basis of their frequency of occurrence and contamination level above the MPL. Male albino Wistar rats were exposed to the mixture at 0, 1, 10, and 100 times the mode concentrations (the most frequently occurring concentration) of the individual metals in drinking water for 90 days. In addition, one group was exposed to the mixture at a concentration equal to the MPL of the individual metal and another group was used as positive control for immune response studies. The end points assessed were weights of organs, hematological indices, humoral and cell-mediated immune responses, and histopathology of skin and spleen. The MPL and 1x doses did not significantly affect any of the parameters and none of the doses induced any significant changes after 30 days of exposure. The mixture at 10x and 100x doses increased the relative weight of the spleen, but that of thymus, adrenals, and popliteal lymphnodes were increased with the 100x dose. After 90 days, 10x and 100x doses decreased serum protein and globulin contents and increased the albumin:globulin ratio; the albumin level was decreased only with the 100x dose. After 60 days, the total erythrocyte count (TEC), hemoglobin (Hb) level, and packed cell volume (PCV) were decreased with the 100x dose, whereas after 90 days, 10x and 100x doses reduced the TEC, total leukocyte count, Hb level, PCV, mean corpuscular volume, and mean corpuscular hemoglobin. With the 100x dose, the lymphocyte count was decreased after 60 and 90 days, but the neutrophil number was increased after 90 days. Antibody titer was decreased after 75 days with the 100x dose, but after 90 days, it was decreased with both the 10x and 100x doses. In delayed-type hypersensitivity response, these two doses decreased ear thickness after 24 and 48 h and skin biopsies showed a dose-dependent decrease in inflammatory changes. Histologically, the spleen revealed depletion of lymphoid cells and atrophic follicles with reduced follicular activity with higher doses. The findings suggest that hematopoietic and immune systems are toxicologically sensitive to the mixture, which could lead to anemia and suppression of humoral and cell-mediated immune responses in male rats at 10 and 100 times the mode concentrations of the individual components in contaminated groundwater.
免疫毒性是重金属暴露的一项重要健康危害。由于人群中混合暴露的风险不容忽视,我们研究了以当代印度地下水污染水平以及相当于世界卫生组织(WHO)饮用水最大允许限量(MPL)的浓度,通过饮用水对雄性大鼠进行亚慢性金属混合物(砷、镉、铅、汞、铬、镍、锰和铁)暴露,是否会诱发免疫毒性。从文献中收集了印度金属污染地下水的数据,并根据其出现频率和高于MPL的污染水平选择了金属。将雄性白化Wistar大鼠暴露于饮用水中各金属模式浓度(最常出现的浓度)的0、1、10和100倍的混合物中90天。此外,一组暴露于各金属MPL浓度的混合物中,另一组用作免疫反应研究的阳性对照。评估的终点指标包括器官重量、血液学指标、体液和细胞介导的免疫反应以及皮肤和脾脏的组织病理学。MPL和1倍剂量对任何参数均无显著影响,且在暴露30天后,各剂量均未引起任何显著变化。10倍和100倍剂量的混合物增加了脾脏的相对重量,但100倍剂量使胸腺、肾上腺和腘窝淋巴结的相对重量增加。90天后,10倍和100倍剂量降低了血清蛋白和球蛋白含量,增加了白蛋白与球蛋白的比值;仅100倍剂量使白蛋白水平降低。60天后,100倍剂量使总红细胞计数(TEC)、血红蛋白(Hb)水平和红细胞压积(PCV)降低,而90天后,10倍和100倍剂量降低了TEC、白细胞总数、Hb水平、PCV、平均红细胞体积和平均红细胞血红蛋白含量。100倍剂量在60天和90天后使淋巴细胞计数降低,但90天后中性粒细胞数量增加。100倍剂量在75天后使抗体滴度降低,但90天后,10倍和100倍剂量均使其降低。在迟发型超敏反应中,这两个剂量在24小时和48小时后使耳厚度降低,皮肤活检显示炎症变化呈剂量依赖性降低。组织学上,脾脏显示高剂量时淋巴细胞耗竭、滤泡萎缩且滤泡活性降低。研究结果表明,造血和免疫系统对该混合物在毒理学上敏感,在受污染地下水中各成分模式浓度的10倍和100倍时,可能导致雄性大鼠贫血以及体液和细胞介导的免疫反应受到抑制。