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In situ and ex situ bioremediation of seleniferous soils from northwestern India

机译:原位和前南北部硒土壤的原地生物修复

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PurposeSelenium (Se) toxicity or deficiency disorders are chiefly associated with Se concentration and speciation in soils. Elevated soil Se content may lead to contamination of water bodies and groundwaters due to the leaching caused by rainfall and irrigation. This study is focused on Se removal by in situ (biostimulation and bioaugmentation) and ex situ (soil washing) bioremediation as well as on its recovery.Materials and methodsIn this research, in situ bioremediation of Se-rich soil collected from rice fields in Ludhiana, Northwest India was studied in microcosms. The effect of biostimulation was determined by amending soil with different organic sources (fermentable, non-fermentable, and non-hydrolysable electron donors). The effect of bioaugmentation was determined by adding anaerobic granular sludge to the microcosms. With regard to ex situ bioremediation, the Se-rich soil was leached with water and the resulting leachate was biologically treated in an upflow anaerobic sludge blanket (UASB) reactor using lactate as electron donor. The UASB reactor was operated for 78days in different conditions of lactate (electron donor) dosing to achieve maximum Se removal and recovery as elemental Se(0) on the granular sludge. The effluent of the UASB reactor was regularly analyzed to determine Se removal efficiencies.Results and discussionThe effect of biostimulation and bioaugmentation showed no significant difference in terms of Se reduction profiles in the microcosms. This suggested that the indigenous Se-reducing microorganisms and oxidizable organic carbon present in the soil are sufficient for in situ soil bioremediation. During treatment of soil leachate in the UASB reactor, 90% Se removal was achieved irrespective of the lactate dosing and mineral salt medium composition of the reactor influent. Analysis of the granular sludge using scanning electron microscopy coupled with energy dispersive X-ray spectroscopy (SEM-EDS) and powder X-ray diffraction (P-XRD) confirmed the presence of elemental Se on the granular sludge. The total Se concentration in the anaerobic granular sludge amounted to 43.5 (0.7) g Se per gram of granular sludge.Conclusions p id=Par4 In situ bioremediation achieved Se reduction in the Se-rich soil investigated. However, risk of Se re-oxidation and leaching into groundwater after in situ remediation cannot be disregarded. In contrast, during ex situ treatment, effluent from the UASB reactor contained less than the USEPA guideline value 5gL(-1) Se. This study showed biological treatment of Se-rich soils is suitable for cleaning the soil, Se recovery, and environmentally acceptable effluent discharge of the soil washing leachate treatment.
机译:催碱(SE)毒性或缺乏障碍主要与土壤中的SE浓度和形态相关。由于降雨量和灌溉引起的浸出,升高的土壤SE含量可能导致水体和地下水的污染。本研究重点是通过原位(生物刺激和生物沉积)和原地(土壤洗涤)生物化以及康复土壤的恢复方法的恢复方法,以恢复,从卢迪亚纳的稻田收集的富含土壤的材料和方法进行恢复。 ,印度西北部是在微科学的研究。通过用不同的有机源(可发酵,不发酵和非水解电子供体)修补土壤来确定生物抑制的效果。通过将厌氧颗粒污泥添加到微观粒度来确定生物沉积的影响。关于ex原位生物修复,富含Se的土壤用水浸出,得到的浸出液在上流厌氧污泥毯(UASB)反应器中使用乳酸作为电子供体在溢出中处理。 UASB反应器在不同条件下运行78天的乳酸(电子供体)给药,以在粒状污泥上实现最高的Se除去和恢复作为元素SE(0)。定期分析UASB反应器的流出物以确定SE去除效率。结果和讨论生物刺激和生物沉积化的效果在微观微观中的SE减少曲线方面没有显着差异。这表明土着减少土壤中存在于土壤中的微生物和可氧化的有机碳足以原位土壤生物化。在治疗UASB反应器中的土壤渗滤液期间,无论反应器流入的乳酸剂量给料和矿物盐培养基组成如何,实现了90%的SE去除。使用扫描电子显微镜与能量分散X射线光谱(SEM-EDS)和粉末X射线衍射(P-XRD)进行粒状污泥的分析证实了元素SE对粒状污泥的存在。厌氧颗粒污泥中的总浓度为每克颗粒污泥的43.5(0.7)G SE。Conclusions p id = Par4原位生物化达到了Se的富含土壤的减少。然而,在原位修复之后,SE重新氧化和浸出到地下水中的风险不能忽视。相反,在EX原位处理期间,来自UASB反应器的流出物含有小于USEPA准则值5GL(-1)SE。该研究表明,富含SE的土壤的生物处理适用于清洁土壤,SE回收和环境可接受的土壤洗涤渗滤液处理。

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