scholarly journals Rapid assessment of heavy metal pollution using ion-exchange resin sachets and micro-XRF core-scanning

2019 ◽  
Vol 9 (1) ◽  
Author(s):  
Jyh-Jaan Steven Huang ◽  
Sheng-Chi Lin ◽  
Ludvig Löwemark ◽  
Sofia Ya Hsuan Liou ◽  
Queenie Chang ◽  
...  
1992 ◽  
Vol 26 (1-2) ◽  
pp. 189-196 ◽  
Author(s):  
C. N. Mazidji ◽  
B. Koopman ◽  
G. Bitton

A chelating resin (Chelex 50-100) and ion-exchange resin (Dowex 50W-X8) were evaluated for removal of heavy metals in toxicity fractionation. Microtox and β-galactosidase activity were employed as toxicity endpoints. The resins were packed into 4 raL glass Pasteur pipettes for use. Chelating resin provided complete removal of toxicity due to polyvalent heavy metal cations (Cd, Cu, Hg, Pb, Zn). Ion-exchange resin was ineffective in removing mercury toxicity. Neither resin provided complete removal of Ag+ toxicity. Toxicity of organic compounds was, at most, partially removed. Performance of the ion-exchange and chelating resins was insensitive to hardness and pH. Based on these results, chelating resin is recommended for heavy metal removal as part of a toxicity fractionation procedure.


2014 ◽  
Vol 2014 ◽  
pp. 1-9 ◽  
Author(s):  
Supitcha Rungrodnimitchai

This work describes the preparation of the cellulose phosphate with high ion exchange capacity from rice straw and bagasse for removal of heavy metals. In this study, rice straw and bagasse were modified by the reaction with phosphoric acid in the presence of urea. The introduced phosphoric group is an ion exchangeable site for heavy metal ions. The reaction by microwave heating yielded modified rice straw and modified bagasse with greater ion exchange capacities (∼3.62 meq/g) and shorter reaction time (1.5–5.0 min) than the phosphorylation by oil bath heating. Adsorption experiments towards Pb2+, Cd2+, and Cr3+ions of the modified rice straw and the modified bagasse were performed at room temperature (heavy metal concentration 40 ppm, adsorbent 2.0 g/L). The kinetics of adsorption agreed with the pseudo-second-order model. It was shown that the modified rice straw and the modified bagasse could adsorb heavy metal ions faster than the commercial ion exchange resin (Dowax). As a result of Pb2+sorption test, the modified rice straw (RH-NaOH 450W) removed Pb2+much faster in the initial step and reached 92% removal after 20 min, while Dowax (commercial ion exchange resin) took 90 min for the same removal efficiency.


2014 ◽  
Vol 955-959 ◽  
pp. 2230-2233 ◽  
Author(s):  
Yong Gang Zeng ◽  
Long Li

This paper used the ion exchange resin method to treat the heavy metal ion Cu2+ of a chemical wastewater and studied the flow velocity, pH and the temperature’s effect on Cu2+ removal effect by macroporous strongly acidic styrene type cation exchange resin D001. The results shown that: when the flow velocity was 1.5 mL/min, pH was 6.0 and the temperature was 30°C, the removal rate of Cu2+ by D001 reached 99.8%. The chemical wastewater could achieve the wastewater’s discharge standard.


PLoS ONE ◽  
2017 ◽  
Vol 12 (2) ◽  
pp. e0172438 ◽  
Author(s):  
Bifeng Hu ◽  
Songchao Chen ◽  
Jie Hu ◽  
Fang Xia ◽  
Junfeng Xu ◽  
...  

2012 ◽  
Vol 260-261 ◽  
pp. 998-1002
Author(s):  
Xin Ke ◽  
Ying Sun ◽  
Yun Zhang

By the leaching experiment of soil column, e researched speciation analysis and bioavailability of Cr in soil before and after fixing. The contents of Cr in fixed soil including exchangeable chromium, carbonate bound chromium, iron manganese oxide bound chromium, organic matter bound chromium, all lower than the soil before fixing, but residues chromium is higher than the soil before fixing. There is obvious difference bioavailability in soil before and after fixing. Soil heavy metal pollution which brings a threat to agricultural product quality could cause surface water and groundwater contamination, and cause the food chain poisoning[1-2]. Compared with the organic pollutants, heavy metal pollutants does not produce decoration in environmental media, through the soil-plant system enter the food chain therefore affecting the safety of agricultural produces and harm to human health. Therefore, it is essential to begin management of the heavy metal contaminated soil. Currently,heavy metal pollution mainly come from the following fields: chromium compounds used as electroplating, leather tanning, pigments, paints, alloys, dyeing and printing, offset printing. Cr contaminated soil repair method include: biology, agricultural engineering, physico-chemical treatment. By max fixatives into the soil adjusted or changed physical and chemical properties of Cr and produce precipitation adsorption ion-exchange humification and oxidation-reduction series reaction ,situ stabilization is one of treatment methods for physical-chemical, consequently reducing mobility and bioavailability in the soil environment , thereby decreasing the toxicity hazards of Cr elements on plants and animals[5]. Since the 1950s, zeolites have a wide range of applications in various fields. Zeolite is a frame-like structure, moisture content of aluminum silicate minerals, with a porous structure, adsorption and ion exchange[6]. In this paper, not only curing effect of fixatives on the metal has been emphasized, but also fixative for friend of environment has been taken into consideration. Natural Zeolite magnesium oxide and FeSO4 have been chosen as fixative and leaching solvent select demonized water. Provide some theoretical basis and technical support for farmland Cr contaminated soil immobilized system.


2020 ◽  
Author(s):  
Emőke Sikora ◽  
Viktória Hajdu ◽  
Gábor Muránszky ◽  
Kitti Krisztina Katona ◽  
István Kocserha ◽  
...  

Abstract Heavy metal ions are among the most dangerous contaminants, which can cause serious health problems. In this work, ion-exchange resin beads were used as supports for magnetite (Fe3O4) synthesis to produce heavy metal adsorbents which can be easily separated by magnetic field. The first step of the magnetite preparation was the replacement of hydrogen ions with Fe2+ and Fe3+ ions on the sulfonic acid groups of the resin. In the second step, magnetite particle formation was induced by coprecipitating the iron ions with sodium hydroxide. The regeneration of the ion-exchange resin was also carried out by using sodium hydroxide. SEM images verified that relatively large magnetite crystal particles (diameter = 100–150 nm) were created. The ion-exchange effect of the prepared magnetic adsorbent was also confirmed by applying Cu2+, Ni2+, Pb2+ and Cd2+ ions in adsorption experiments.


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