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Arsenic(III) Immobilization on Rice Husk

TLDR
In this article, the effect of quaternized rice husk on the adsorption of As(III) was examined and the results showed that the extent of adaption was dependent on pH, As (III) concentration, contact time, and rice hull dose.
Abstract
A number of large aquifers in various parts of the world have been identified with contamination by arsenic. Long-term exposure to arsenic in drinking water causes cancer of the skin, lungs, urinary bladder and kidney, as well as skin pigmentation and hyperkeratosis. Arsenic occurs in groundwater in two valence states, as trivalent arsenite [As(III)] and pentavalent arsenate [As(V)]. As(III) is more toxic and more difficult to remove from water by adsorption on activated alumina. In this study, immobilization (adsorption) of As(III) by quaternized rice husk was examined. Batch adsorption test showed that extent of adsorption was dependent on pH, As (III) concentration, contact time and rice husk dose. Maximum adsorption occurred at pH 7-8, and equilibrium adsorption was attained in 2 h. Equilibrium adsorption data were described by the Langmuir and Freundlich isotherm models. According to the Langmuir isotherm, adsorption capacity of quaternized rice husk is 0.775 mg As(III)/g, which is 4.3x higher than that (0.180 mg As(III)/g) of activated alumina. Quaternized rice husk is a potentially useful adsorbent for removing arsenic from groundwater.

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Evaluation of industrial based adsorbents for simultaneous removal of arsenic and fluoride from drinking water

TL;DR: In this article, a study aimed to assess selected industrial waste materials for simultaneous removal of arsenic and fluoride from drinking water in order to find cost effective adsorbent, using X-Ray Diffractrometry techniques.
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Adsorptive removal of arsenic by novel iron/olivine composite: Insights into preparation and adsorption process by response surface methodology and artificial neural network.

TL;DR: An artificial neural network was applied for the multivariate optimization of the adsorption process from the experimental data of the univariate optimization study and the optimized model showed low values of error functions and high R2 values of more than 0.99 for As(III)T and As(V)T.
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Enhancing arsenic sequestration on ameliorated waste molasses nanoadsorbents using response surface methodology and machine-learning frameworks

TL;DR: The development of a novel nanobiosorbent derived from waste molasses for the adsorptive removal of arsenic (As) and the low-cost facile synthesis of the IOCN nanosorbent from agro-industrial waste indicate their potential for commercial applications.
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Development of a New Dolomite-Based Adsorbent with Phosphorus and the Adsorption Characteristics of Arsenic (III) in an Aqueous Solution

TL;DR: In this article , a low-cost hydroxyapatite adsorbent (Ca5(PO4)3OH) was developed by reacting the Ca component of calcined dolomite with phosphorus.
References
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Arsenic contamination of groundwater in Bangladesh

TL;DR: A survey of well waters from throughout Bangladesh, excluding the Chitt;agong Hill Tracts, has shown that water from 27% of the'shallow' tubewells, that is, wells less than 150 m deep, exceeded the Bangladesh standard for arsenic in drinking water (50 flg L -I) as mentioned in this paper.
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Adsorption of arsenite and arsenate within activated alumina grains: Equilibrium and kinetics

TL;DR: The agreement among the models and experimental data indicated that the adsorption and diffusion of arsenate and arsenite can be simulated by the proposed model.
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Equilibrium, kinetics and thermodynamic studies for adsorption of As(III) on activated alumina

TL;DR: In this paper, the effect of adsorbent dose, solution pH, and contact time has been investigated to remove arsenite ions [As(III)] by activated alumina.
Journal ArticleDOI

Magnitude of arsenic pollution in the Mekong and Red River Deltas--Cambodia and Vietnam.

TL;DR: The sediments of 12-40 m deep cores from the Red River delta contain arsenic levels of 2-33 microg/g and show a remarkable correlation with sediment-bound iron and in all three areas, the groundwater arsenic pollution seem to be of natural origin and caused by reductive dissolution of arsenic-bearing iron phases buried in aquifers.
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