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从地下水中分离和鉴定哈茨木霉:一种用于地下水除氟的有效生物吸附剂。

Isolation and identification of Trichoderma harzianum from groundwater: An effective biosorbent for defluoridation of groundwater.

作者信息

Koshle Shalini, Mahesh S, Swamy S Nanjunda

出版信息

J Environ Biol. 2016 Jan;37(1):135-40.

Abstract

The ability of non-viable form of Trichoderma harzianum, isolated from fluoride rich groundwater, was investigated as biosorbent for defluoridation of groundwater. Biosorption experiments were carried out at laboratory scale for removal of fluoride from groundwater. Significant effect of operational parameters on fluoride biosorption using Trichoderma harzianum as biosorbent was evaluated by varying operational parameters such as: initial fluoride concentration (2-8 mgl(-1)), biosorbent dose (0.4-1.6g/100ml), groundwater pH (6-10), temperature (30-50 degrees C) and biosorption time (30-120 min). The fluoride adsorption isotherms were modeled by Langmuir and Freundlich isotherms. Our result showed that fluoride biosorption, significantly increased with increase in groundwater pH, biosorbent dose, temperature and biosorption time, whereas increase in initial fluoride concentration reduced fluoride removal. The fluoride biosorption was rapid and maximum fluoride uptake was attained with 1.6g 100ml(-1) biosorbent within 60 min. Optimal pH 10 and temperature 50 degrees C gave maximum defluoridation efficiency. Freundlich isotherm fits well for defluoridation of groundwater using Trichoderma harzianum as biosorbent which indicated that biosorbent surface sites were heterogeneous in nature and fitted into heterogeneous site binding model.

摘要

对从富含氟化物的地下水中分离出的哈茨木霉非活性形式作为地下水除氟生物吸附剂的能力进行了研究。在实验室规模下进行了生物吸附实验,以去除地下水中的氟化物。通过改变操作参数,如初始氟化物浓度(2 - 8毫克/升)、生物吸附剂剂量(0.4 - 1.6克/100毫升)、地下水pH值(6 - 10)、温度(30 - 50摄氏度)和生物吸附时间(30 - 120分钟),评估了操作参数对使用哈茨木霉作为生物吸附剂的氟化物生物吸附的显著影响。氟化物吸附等温线采用朗缪尔等温线和弗伦德利希等温线进行建模。我们的结果表明,随着地下水pH值、生物吸附剂剂量、温度和生物吸附时间的增加,氟化物生物吸附显著增加,而初始氟化物浓度的增加则降低了氟化物的去除率。氟化物生物吸附迅速,在60分钟内使用1.6克/100毫升的生物吸附剂可达到最大氟化物吸收量。最佳pH值为10,温度为50摄氏度时,除氟效率最高。弗伦德利希等温线非常适合使用哈茨木霉作为生物吸附剂对地下水进行除氟,这表明生物吸附剂表面位点本质上是不均匀的,符合非均匀位点结合模型。

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