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Effect of Leachate-contaminated Groundwater on the Growth and Blood of Albino of Rats

机译:渗滤液污染的地下水对大鼠白化病生长和血液的影响

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The results of effect of daily consumption of leachate-contaminated groundwater for 65days on rats' Packed Cell Volume (PCV), Haemoglobin (Hb), White Blood Cell (WBC), Red Blood Cell (RBC), neutrophil and platelet are presented. The PCV (%) of rats treated with leachate was found to be 26±4 while that of animals treated with control tap water was 40±2. Hb (g/dl) of control rats was observed to be 14.3±0.3 while that of leachate treated rats was 10.9±0.3. The experimental results indicated that consumption of leachate-contaminated groundwater may lead to ill health particularly anaemia. Introduction Pollutants can escape from improperly designed landfill in a variety of ways (Carla, 2000). If soil above or below a landfill is permeable, leachate can escape to contaminate groundwater (Carla, 2000). Recent studies indicate that small landfills (waste volume up to 50,000yd 3 ) may impact groundwater (Friedman, 1988 and Bagchi, 2004).Once the groundwater is polluted, the pollution may be difficult to correct or even to detect. Carla (1997) predicted that in the next few decades, more contaminated aquifers will be discovered, new contaminants will be identified, and more polluted groundwater will discharged into wetlands, streams, and lakes as this groundwater passes through the hydrologic cycle. By the time groundwater pollution is detected, it may be very widespread, and the exact extent of the problem may not be readily determined without the drilling of many monitoring wells across the affected area (Bagchi, 2004). Even the source can be hard to identify unless the chemistry of the contamination is distinctive (Carla, 1997).Contaminants carried in leachate are dependent on solid waste composition and on the simultaneously occurring physical, chemical and biological activities within the landfill (Monroe, 2001). Heavy metals such as lead, mercury, chromium, copper and cadmium, together with household chemicals and poisons can be concentrated in groundwater supplies beneath landfills (Wagner and Rhyner, 1984). These contaminants have been reported to possibly cause growth retardation and haematological abnormalities (Hogson, 2004).In Lagos, Nigeria exists a typical landfill located in Ojota area (Detail of location described elsewhere (Adeyemi et al., 2007)). The landfill is not lined and receives both hazardous and non-hazardous wastes without prior consideration for their highly polluting effect on the surrounding groundwater. Residential houses with groundwater (Wells and Boreholes) as only source of water were constructed at about 1.5km radius to the landfill. These groundwater sources are continually being consumed by home owners without the knowledge of the possible hazardous effect which the landfill leachate can have on the water quality and public health. Reports presented at seminars and conferences also attested to the prevalence of water related diseases in the inhabitants (LAWMA, 2000). The present study, therefore, examines the effect of such leachate-contaminated groundwater on the growth and blood of rats. Materials and methods Chemicals and solvents are of analytical grade and are products of Sigma-Aldrich, inc., St. Louis, U.S.A. The experimental water for the study was collected from the residential areas located within the vicinity of Odo Iya Alaro landfill in Ojota, Lagos, Nigeria. The water samples were obtained from two different wells located at about 1 and 1.5km respectively from the landfill; and two boreholes located at about 1 and 1.5km respectively from the landfill. The water samples were collected using stainless steel buckets. Solid wastes were collected at the Odo Iya Alaro landfill located in Ojota, Lagos, Nigeria in December, 2004. Leachate simulation was carried out following the ASTM method (Perket et al, 1982). In this method a sample (0.3kg) of the landfill waste was shredded and packed in a 2l glass flask. A volume of distilled water, four times the sample weight, was added. The resulting sa
机译:呈现了每天饮用渗滤液污染的地下水65天对大鼠的堆积细胞体积(PCV),血红蛋白(Hb),白细胞(WBC),红细胞(RBC),中性粒细胞和血小板的影响的结果。发现用渗滤液处理的大鼠的PCV(%)为26±4,而用对照自来水处理的动物的PCV为40±2。观察到对照大鼠的Hb(g / dl)为14.3±0.3,而渗滤液处理的大鼠的Hb为10.9±0.3。实验结果表明,消耗被沥滤液污染的地下水可能会导致身体不适,尤其是贫血。引言污染物可以通过各种方式从设计不当的垃圾填埋场逸出(Carla,2000)。如果垃圾填埋场上方或下方的土壤是可渗透的,渗滤液可以逸出以污染地下水(Carla,2000)。最近的研究表明,小的垃圾填埋场(废物量高达50,000 yd 3)可能会影响地下水(Friedman,1988年和Bagchi,2004年)。一旦地下水被污染,污染就可能难以纠正甚至被发现。 Carla(1997)预测,在接下来的几十年中,随着地下水通过水文循环,将发现更多受污染的含水层,将发现新的污染物,并且更多被污染的地下水将排入湿地,溪流和湖泊。到发现地下水污染时,它可能已经非常广泛了,如果不在受影响地区钻许多监测井,就很难确定问题的确切程度(Bagchi,2004)。除非污染的化学性质不同(Carla,1997),否则甚至很难确定污染源(渗滤液中携带的污染物)取决于固体废物的成分以及垃圾填埋场中同时发生的物理,化学和生物活动(Monroe,2001)。 )。铅,汞,铬,铜和镉等重金属,以及日用化学品和毒药,可以集中在垃圾掩埋场的地下水供应中(Wagner和Rhyner,1984年)。据报道,这些污染物可能导致生长迟缓和血液学异常(Hogson,2004年)。在拉各斯,尼日利亚存在一个典型的垃圾填埋场,位于Ojota地区(其他地方描述了该地点的详细信息(Adeyemi等,2007))。垃圾填埋场没有衬砌,可以同时接收危险废物和非危险废物,而无需事先考虑它们对周围地下水的高度污染作用。在距垃圾填埋场约1.5公里的半径范围内建造了以地下水(井和井眼)为唯一水源的住宅。业主不断消耗这些地下水源,却不知道垃圾渗滤液可能对水质和公共卫生产生有害影响。在研讨会和会议上发表的报告也证明了居民中与水有关的疾病的流行(LAWMA,2000)。因此,本研究检查了这种渗滤液污染的地下水对大鼠生长和血液的影响。材料和方法化学和溶剂均为分析纯,是美国圣路易斯的Sigma-Aldrich,Inc.的产品。本研究的实验用水来自位于Ojota的Odo Iya Alaro垃圾填埋场附近的居民区。尼日利亚拉各斯。水样是从分别位于垃圾填埋场约1公里和1.5公里处的两个不同的井中获得的;两个钻孔分别位于距离垃圾填埋场约1公里和1.5公里处。使用不锈钢桶收集水样品。 2004年12月,在位于尼日利亚拉各斯Ojota的Odo Iya Alaro垃圾填埋场收集了固体废物。按照ASTM方法(Perket等,1982)对渗滤液进行了模拟。用这种方法将垃圾填埋场废物样品(0.3千克)切碎并装在2升玻璃烧瓶中。加入体积为样品重量四倍的蒸馏水。结果sa

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