评价利用花卉废物生物吸附剂处理受污染的水

Subhashish Dey, Ganugula Taraka Naga Veerendra, Siva Shanmukha Anjaneya Babu Padavala, Akula Venkata Phani Manoj
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引用次数: 0

摘要

人类和工业活动已经污染了地下水和地表水。这是今天的一个重要问题。因此,水质分析至关重要。本研究的目的是评价不同地点地下水的水质指数(WQI),进行理化分析。采用统计分析方法计算当前水质状况,在水质指标中考虑了以下参数:pH、总溶解固形物、总碱度、氯化物、硬度、溶解氧、生化需氧量、化学需氧量。将获得的结果与印度饮用水标准IS: 10500-2012进行比较。对该地下水样品的理化和生物学特性的研究表明,对水质参数和资源进行评价是必要的。在6个不同地方的水质指数中,古德拉瓦勒鲁、Ainampudi、Penjendra、古德拉瓦勒鲁、Angaluru和Kondiparru。在这六个地方,pH值从(6.72-8.3),温度从(34°C-36.5°C),酸度从(15-40),碱度从(10-25),浊度从(0.8-60.4),DO从(3.7-6.2),COD从(209-477),铁从(3-5),氟化物为零,磷从(0-0.5),铵从(0-1),硝酸盐从(0-5),氯化物从(375-575),硬度从(200-505),亚硝酸盐从(0-1),总固体从(729-1573),悬浮物从(468-971)和溶解固体从(301-602)变化。利用干花生物吸附剂对污水中的重金属进行生物吸附或处理受污染的地下水。将花废生物吸附剂的细粉、干粉加入到污染水中,会发生控制污染水浓度的生物反应。在这项研究中,我们使用了四种不同的花卉废物生物吸附剂,包括靶标或万寿菊花废物,Ixora-coccinea花废物,芙蓉花废物和Allamanda花废物。在四种花卉废物生物吸附剂中,金盏花废物生物吸附剂的去除水中有毒金属的性能最高。进一步优化生物吸附剂用量、接触时间、pH值、温度、搅拌速度等参数,以提高对污染物的生物吸附剂。需要进一步研究生物吸附剂的机理、金属吸收的动力学和可重复利用性、生物吸附剂的回收和再生、工艺设计以及目标或金盏花垃圾生物吸附剂的商业应用。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Evaluate the use of flower waste biosorbents for treatment of contaminated water

Human and industrial activities have contaminated the groundwater and surface water. This is a significant issue today. Therefore, the analysis of water quality is crucial. The purpose of this study is to evaluate the water quality index (WQI) of groundwater at various locations for physiochemical analysis. For calculating the current water quality status using statistical analysis and in the water quality index, the following parameters were considered: pH, total dissolved solids, total alkalinity, chlorides, hardness, dissolved oxygen, Biochemical oxygen demand, and chemical oxygen demand. The acquired results are compared to the Indian drinking water standard IS: 10500–2012. The investigation of the physicochemical and biological characteristics of this ground water sample indicates that the evaluation of water quality parameters and resources is necessary. In the water quality index of six different places Gudlavalleru, Ainampudi, Penjendra, Gudlavalleru Gudem, Angaluru and Kondiparru. In the six locations the pH value vary from (6.72–8.3), temperature vary from (34 °C-36.5 °C), acidity vary from (15–40), alkanity vary from (10–25), turbidity vary from (0.8–60.4), DO vary from (3.7–6.2), COD vary from (209–477), Iron vary from (3–5), fluorides is zero, phosphorous vary from (0–0.5), ammonium vary from (0–1), nitrates vary from (0–5), chlorides vary from (375–575), hardness vary from (200–505), nitrites vary from (0–1), total solids vary from (729–1573), suspended solids vary from (468–971) and dissolved solids vary from (301–602). Using dry flowers biosorbents for biosorptions of heavy metals from polluted water or treat contaminated groundwater. Biological reactions occur to control the concentration of contaminated water when fine, dried powder of flower waste biosorbents is added to contaminated water. In this study, we employ four different flower waste biosorbents, including Targets or marigold flower waste, Ixora-coccinea flower waste, Hibiscus flower waste, and Allamanda flower waste. The Targets or marigold flower waste biosorbents have the highest performance for removing toxic metals from contaminated water among the four flower waste biosorbents. Further optimization of the various parameters, i.e. biosorbents dosage, contact time, pH, temperature, and agitation speed, was performed on Targets or marigold flowers waste biosorbents in order to increase pollutant biosorption. Further research is required into the mechanisms of biosorbents, the kinetics and reusability of metal uptake, the recovery and regeneration of biosorbents, process design, and the commercial application of Targets or marigold flower refuse biosorbents.

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