尼日利亚拉各斯奥罗格泻湖周边地区工业废水亚致死暴露后非洲鲇鱼的血液学和肝脏反应

A. Adeboyejo, E. Clarke, A. M. Hammed, Roseline O. Adaramoye
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引用次数: 3

摘要

本研究研究了非洲鲶鱼幼鱼对尼日利亚拉各斯奥洛格泻湖环境中工业废水亚致死毒性的血液学和肝脏反应。鱼在五种浓度的工业废水中养殖:0%(对照)、5%、15%、25%和35%。试验分三次进行,为期十二(12)周。培养系统是静态可再生生物测定系统,在拉各斯州立大学Ojo-Lagos渔业实验室进行。每周理化参数:测定每个处理池的温度(°C)、pH、电导率(ppm)和溶解氧(DO, mg/L)。12周后测定血液学指标:堆积细胞体积(PCV)、红细胞(RBC)、白细胞(WBC)、中性粒细胞、淋巴细胞等,并测定肝功能变化。理化参数分析表明,pH值范围为7.82±0.25~8.07±0.02。DO范围为1.92±0.66~4.43±1.24 mg/L。电导率随电解液浓度的增加而升高,而温度差异不显著,平均值在26.08±2.14~26.38±2.28之间。DO差异有统计学意义(p < 0.05)。虽然亚致死期存活率为100%,但血液学结果显示,加里平叶螨PCV范围为13.0±1.7~27.7±0.6,红细胞范围为4.7±0.6~9.1±0.1,中性粒细胞范围为26.7±4.6~61.0±1.0等。这些参数在对照组中最高,在35%时最低。虽然WBC和淋巴细胞被观察到相反的作用,但在对照组中肝脏显示正常的肝细胞(0%),但在更高的毒性水平下,有:空泡,肝实质破坏,组织变得嗜酸性(即倾向于致癌性)和肝脐带结构的严重破坏。因此,这项研究表明,如果长期暴露在水环境中,将污水排入水生环境会损害鱼类的正常肝功能,阻碍重要的生理过程,从而影响鱼类的健康(亚致死效应)。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Haematological and Hepatic Responses of the African Catfish Clarias gariepinus to Sublethal Exposure of Industrial Effluents from Ologe Lagoon Environs, Lagos, Nigeria
The present study is on the haematological and hepatic responses of the African catfish fingerlings Clarias gariepinus to sublethal toxicity of industrial effluents (IE) from the environment of Ologe Lagoon, Lagos, Nigeria. The fish were cultured in five concentrations of industrial effluents: 0% (control), 5%, 15%, 25%, and 35%. Trials were carried out in triplicates for twelve (12) weeks. The culture system was a static renewable bioassay and was carried out in the fisheries laboratory of the Lagos State University, Ojo-Lagos. Weekly physico-chemical parameters: Temperature (°C), pH, conductivity (ppm) and dissolved oxygen (DO in mg/L) were measured in each treatment tank. Haematological parameters: packed cell volume (PCV), red blood cells (RBC), white blood cell (WBC), neutrophil and lymphocytes etc., and hepatological alterations were measured after 12 weeks. The physico-chemical parameters showed that the pH ranged from 7.82±0.25~8.07±0.02. DO ranged from 1.92±0.66~4.43±1.24 mg/L. The conductivity values increased with increase in concentration of I.E. While the temperature difference remained insignificant with mean value range between 26.08±2.14~26.38±2.28. The DO showed significant differences at p < 0.05. Though survival was 100% during the sublethal study, haematological results showed that C. gariepinus had PCV ranging from 13.0±1.7~27.7±0.6, RBC ranged from 4.7±0.6~9.1±0.1, and neutrophil ranged from 26.7±4.6~61.0±1.0 amongst others. The highest values of these parameters were obtained in the control and lowest at 35%. While the reverse effects were observed for WBC and lymphocytes, the liver shows normal liver cells in the control (0%), but at higher toxic levels, there were: vacoulation, destruction of the hepatic parenchyma, tissue becoming eosinophilic (i.e. tending towards Carcinogenicity) and severe disruption of the hepatic cord architecture. This study therefore shows that disposal of effluents into the aquatic environment affects the health of fishes by impairing normal hepatic functions and hindering vital physiological processes if exposure continues for a long period of time (sublethal effect).
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