GFAAS Determination of Trace Amount of Copper in Environmental Water Samples with Cloud Point Extraction
摘 要
以5-(5-碘-2-吡啶偶氮)-2,4-二氨基甲苯(5-I-PADAT)为络合剂,以聚乙二醇辛基苯基醚(Triton X-114)为萃取剂,采用石墨炉原子吸收光谱法测定环境水样中痕量铜。优化的试验条件如下:①乙酸-乙酸钠缓冲溶液的pH为5.3;②1.0×10-3mol·L-1 5-I-PADAT溶液的用量为0.25 mL;③ 10 g·L-1 Triton X-114溶液的用量为1.0 mL;④水浴加热时间为15 min;⑤水浴加热温度为60℃;⑥0.1 mol·L-1硝酸-甲醇溶液的用量为70 μL。铜的质量浓度在1.0~14 μg·L-1内与其对应的吸光度呈线性关系,检出限(3s/k)为0.216 μg·L-1。方法用于2种环境水样的分析,加标回收率为102%,100%,测定值的相对标准偏差(n=6)为4.5%,4.3%。
Abstract
GFAAS was applied to the determination of trace amount of copper in environmental water samples with 5-(5-iodine-2-pyridylazo)-2,4-diaminotoluene (5-I-PADAT) as complexing agent and p-octyl polyethylene glycol phenyl ether (Triton X-114) as extracting agent. The optimized conditions found were as follows:①pH of buffer solution of acetic acid and sodium acetate:5.3; ② amount of 1.0×10-3mol·L-1 5-I-PADAT solution:0.25 mL; ③ amount of 10 g·L-1 Triton X-114 solution:1.0 mL; ④water bath heating time:15 min;⑤ water bath heating temperature:60℃; ⑥ amount of 0.1 mol·L-1 HNO3-methanol solution:70 μL. Linear relationship between values of absorbance and mass concentration of copper was obtained in the range of 1.0-14 μg·L-1, with detection limit (3s/k) of 0.216 μg·L-1. The proposed method was applied to the analysis of 2 environmental water samples, giving values of recovery of 102%, 100%, and values of RSD's (n=6) of 4.5%, 4.3%.
中图分类号 O657.31 DOI 10.11973/lhjy-hx201708005
所属栏目 工作简报
基金项目 国家自然科学基金项目(21545014);西安市科技计划项目(CXY1531WL34;CXY1531WL22);陕西省教育厅项目(16JK2194)
收稿日期 2017/1/4
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备注霍燕燕(1983-),女,陕西榆林人,实验师,硕士,研究方向为现代光谱分析,huoyeye@163.com
引用该论文: HUO Yanyan,CHEN Jiale,DU Yufeng,HAN Quan,YANG Xiaohui. GFAAS Determination of Trace Amount of Copper in Environmental Water Samples with Cloud Point Extraction[J]. Physical Testing and Chemical Analysis part B:Chemical Analysis, 2017, 53(8): 890~893
霍燕燕,陈家乐,杜宇凤,韩权,杨晓慧. 浊点萃取-石墨炉原子吸收光谱法测定环境水样中痕量铜[J]. 理化检验-化学分册, 2017, 53(8): 890~893
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【2】ROLDANPS S. Simultaneous flow injection preconcentration of lead and cadmium using cloud point extraction and determination by atomic absorption spectrometry[J]. J Hazard Mater, 2009,161(1):142-147.
【3】MANZOORI J L, ABDOLMOHAMMAD-ZADEH H. Extraction and preconcentration of lead using cloud point methodology:Application to its determination in real samples by flame atomic absorption spectrometry[J]. Acta Chim Slov, 2007,54(2):378-384.
【4】SATIROGLU N, ARPA C. Cloud point extraction for the determination of trace copper in water samples by flame atomic absorption spectrometry[J]. Microchim Acta, 2008,162:107-112.
【5】SU Y D, ZHANG L J, ZHU Y Y, et al. Determination of trace copper in water sample by flame atomic absorption spectrometry with cloud point extraction preconcentration[J]. Metall Anal, 2008,28:36-38.
【6】CHEN J R, TEO K C. Determination of cadmium, copper, lead and zinc in water samples by flame atomic absorption spectrometry after cloud point extraction[J].Anal Chim Acta, 2001,450:215-222.
【7】CHEN J G, CHEN H W, CHEN S H, et al. Determination of ultratrace amounts of copper(Ⅱ) in water samples by electrothermal atomic absorption spectrometry after cloud point extraction[J]. Chem Res Chin Univ, 2007,23:143-147.
【8】XIAO X M, HUANG H, GUO Y P. Determination of trace Cu(Ⅱ) in river water by spectrophotometry after cloud point with 5-Br-PADAP[J]. J Baoji Univ Arts Sci, 2008,28:37-40.
【9】HASSANIEN M M, ABDEL-RHMAN M H, EL-ASMY A A. Cloud point extraction and spectrophotometric determination of Cu(Ⅱ) in saturated saline solutions using 4-ethyl-1-(pyridin-2-yl)thiosemicarbazide[J]. Transition Met Chem, 2007,32:1025-1029.
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