Preconcentration with Bacillus subtilis-Immobilized Amberlite XAD-16: Determination of Cu2+ and Ni2+ in River, Soil, and Vegetable Samples
dc.authorid | Okumus, Veysi/0000-0002-5505-2700 | |
dc.authorid | DUNDAR, ABDURRAHMAN/0000-0002-7930-1054 | |
dc.authorid | Kilinc, Ersin/0000-0001-5223-9919 | |
dc.contributor.author | Okumus, Veysi | |
dc.contributor.author | Ozdemir, Sadin | |
dc.contributor.author | Kilinc, Ersin | |
dc.contributor.author | Dundar, Abdurrahman | |
dc.contributor.author | Yuksel, Uyan | |
dc.contributor.author | Baysal, Zubeyde | |
dc.date.accessioned | 2024-12-24T19:28:16Z | |
dc.date.available | 2024-12-24T19:28:16Z | |
dc.date.issued | 2015 | |
dc.department | Siirt Üniversitesi | |
dc.description.abstract | Solid-phase extraction (SPE) method was developed for the preconcentration of Cu2+ and Ni2+ before their determination by inductively coupled plasma optical emission spectrometry (ICP-OES). Bacillus subtilis-immobilized Amberlite XAD-16 was used as biosorbent. Effects of critical parameters such as pH, flow rate of samples, amount of Amberlite XAD-16 and biosorbent, sample volume, eluent type, and volume and concentration of eluent on column preconcentration of Cu2+ and Ni2+ were optimized. Applicability of the method was validated through the analysis of the certified reference tea sample (NCS ZC73014). Sensitivity of ICP-OES was improved by 36.4-fold for Cu2+ and 38.0-fold for Ni2+ by SPE-ICP-OES method. Limit of quantitation (LOQ) was found to be 0.7 and 1.1ng/ml for Cu2+ and Ni2+, respectively. Concentrations of Cu2+ and Ni2+ were determined by ICP-OES after application of developed method. Relative standard deviations (RSDs) were lower than 4.9% for Cu2+ and 7.9% for Ni2+. The Tigris River that irrigates a large agricultural part of Southeast Turkey is polluted by domestic and industrial wastes. Concentrations of Cu2+ and Ni2+ were determined in water, soil, and some edible vegetables as a biomonitor for heavy metal pollution. | |
dc.identifier.doi | 10.1080/10889868.2014.938724 | |
dc.identifier.endpage | 55 | |
dc.identifier.issn | 1088-9868 | |
dc.identifier.issn | 1547-6529 | |
dc.identifier.issue | 1 | |
dc.identifier.scopus | 2-s2.0-84924056704 | |
dc.identifier.scopusquality | Q2 | |
dc.identifier.startpage | 47 | |
dc.identifier.uri | https://doi.org/10.1080/10889868.2014.938724 | |
dc.identifier.uri | https://hdl.handle.net/20.500.12604/6995 | |
dc.identifier.volume | 19 | |
dc.identifier.wos | WOS:000349826300005 | |
dc.identifier.wosquality | Q4 | |
dc.indekslendigikaynak | Web of Science | |
dc.indekslendigikaynak | Scopus | |
dc.language.iso | en | |
dc.publisher | Taylor & Francis Inc | |
dc.relation.ispartof | Bioremediation Journal | |
dc.relation.publicationcategory | Makale - Uluslararası Hakemli Dergi - Kurum Öğretim Elemanı | |
dc.rights | info:eu-repo/semantics/closedAccess | |
dc.snmz | KA_20241222 | |
dc.subject | sensitivity improvement | |
dc.subject | Cu2+ | |
dc.subject | preconcentration | |
dc.subject | biosorbent | |
dc.subject | solid-phase extraction | |
dc.subject | Ni2+ | |
dc.title | Preconcentration with Bacillus subtilis-Immobilized Amberlite XAD-16: Determination of Cu2+ and Ni2+ in River, Soil, and Vegetable Samples | |
dc.type | Article |