Determination of some trace metals in environmental samples by flame AAS following solid phase extraction with amberlite XAD-2000 resin after complexing with 8-hydroxyquinoline

被引:41
作者
Duran, Celal [1 ]
Senturk, H. Basri
Gundogdu, Ali
Bulut, V. Numan
Elci, Latif
Soylak, Mustafa
Tufekci, Mehmet
Uygur, Yaprak
机构
[1] Karadeniz Tech Univ, Dept Chem, Fac Arts & Sci, TR-61080 Trabzon, Turkey
[2] Karadeniz Tech Univ, Giresun Fac Arts & Sci, Dept Chem, TR-28049 Giresun, Turkey
[3] Pamukkale Univ, Fac Arts & Sci, Dept Chem, TR-20020 Denizli, Turkey
[4] Erciyes Univ, Fac Arts & Sci, Dept Chem, TR-38039 Kayseri, Turkey
关键词
water and vegetable sample; trace metal; preconcentration; amberlite XAD-2000; FAAS; 8-hydroxyquinoline;
D O I
10.1002/cjoc.200790040
中图分类号
O6 [化学];
学科分类号
0703 ;
摘要
A procedure for preconcentration of Mn(H), Fe(II), Co(II), Cu(II), Cd(II), Zn(II), Pb(II) and Ni(II) based on retention of their complexes with 8-hydroxyquinoline (HQ) on Amberlite XAD-2000 resin in a column was proposed for the analysis of environmental samples by flame AAS. Various parameters such as pH, eluent type, volume, concentration, flow rate and volume of sample solution, and matrix interference effect on the retention of the metal ions were investigated. The optimum pHs for the retention of metal complexes in question were about 6 except for Mn2+ for whose value is 8. The loading capacity of the adsorbent for these metals and their recoveries from the resin under the optimum conditions were in the range 6.82-9.26 mg.g(-1) and 95%-101%, respectively. The enrichment factor was calculated as 100 and the limit of detection was in the range 0.3-2.2 mu g.L-1 (n=20, blank + 3s). The proposed enrichment method was applied to tap water, stream water and vegetable samples. The validation of the procedure was carried out by analysis of certified reference material and standard addition. The analytes were determined with a relative standard deviation lower than 6% in all samples.
引用
收藏
页码:196 / 202
页数:7
相关论文
共 48 条
[1]   Separation and preconcentration of silver ion using 2-mercaptobenzothiazole immobilized on surfactant-coated alumina [J].
Absalan, G ;
Mehrdjardi, MA .
SEPARATION AND PURIFICATION TECHNOLOGY, 2003, 33 (01) :95-101
[2]   Organically modified silica gel and flame atomic absorption spectrometry: employment for separation and preconcentration of nine trace heavy metals for their determination in natural aqueous systems [J].
Akl, MAA ;
Kenawy, IMM ;
Lasheen, RR .
MICROCHEMICAL JOURNAL, 2004, 78 (02) :143-156
[3]   On-line preconcentration and determination of copper, lead and chromium(VI) using unloaded polyurethane foam packed column by flame atomic absorption spectrometry in natural waters and biological samples [J].
Anthemidis, AN ;
Zachariadis, GA ;
Stratis, JA .
TALANTA, 2002, 58 (05) :831-840
[4]  
Baytak S, 2004, TURK J CHEM, V28, P243
[5]   Use of Amberlite XAD-2 loaded with 1-(2-pyridylazo)-2-naphthol as a preconcentration system for river water prior to determination of Cu2+, Cd2+ and Pb2+ by flame atomic absorption spectroscopy [J].
Bermejo-Barrera, P ;
Nancy, MA ;
Cristina, DL ;
Adela, BB .
MICROCHIMICA ACTA, 2003, 142 (1-2) :101-108
[6]   Preconcentration of manganese(II) from natural and sea water on a palmitoyl quinolin-8-ol functionalized XAD copolymer resin and spectrophotometric determination with the formaldoxime reagent [J].
Dogutan, M ;
Filik, H ;
Apak, R .
ANALYTICA CHIMICA ACTA, 2003, 485 (02) :205-212
[7]  
DURAN C, 2000, 14 NAT CHEM C SER DI, P339
[8]  
DURAN C, 1999, 13 NAT CHEM C SER SA, P60
[9]   Determination of trace amounts of some metals in samples with high salt content by atomic absorption spectrometry after cobalt-diethyldithiocarbamate coprecipitation [J].
Elci, L ;
Sahin, U ;
Oztas, S .
TALANTA, 1997, 44 (06) :1017-1023
[10]   Determination of trace impurities in some nickel compounds by flame atomic absorption spectrometry after solid phase extraction using Amberlite XAD-16 resin [J].
Elçi, L ;
Soylak, M ;
Uzun, A ;
Büyükpatir, E ;
Dogan, M .
FRESENIUS JOURNAL OF ANALYTICAL CHEMISTRY, 2000, 368 (04) :358-361