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机构地区:[1]绍兴市环境监测中心站,绍兴312000 [2]杭州萧山供水有限公司,杭州310002 [3]浙江龙盛集团股份有限公司,绍兴312000
出 处:《现代科学仪器》2015年第5期109-111,共3页Modern Scientific Instruments
基 金:本文系国家重大科学仪器设备开发专项(No.2012YQ09022903);浙江省自然科学基金(Nos.Y4110532,LQl38050001,Z148070002);浙江省公益性科技计划(分析测试)项目(No.2012C37038),国家海洋局海洋-大气化学与全球变化重点实验室基金(Nos.GCMAC1208,GCMAC1109),浙江省公益性技术应用研究计划项目(No.2013C37073)
摘 要:建立了离子色谱一直接电导法测定环境水样中叠氮根的方法。环境水样经滤膜过滤后直接进样。将样品先通过一根高聚物反相柱进行在线预处理,除去水溶性有机杂质,采用阴离子富集柱TAC-ULPl收集叠氮根离子并进入分析系统分析。以IonPac AG18(4mm×50mm)+IonPac ASl8(4m×250mm)色谱柱进行分离,采用氢氧化钾梯度淋洗,流速为1.0mL/min,柱温50℃,进样体积200μL,电导检测器检测。实验结果表明,叠氮根在0.01~2.0mg/L范围内线性关系良好(r=0.9994),检测限(LOD)为2.51μg/L(S/N=3)。该方法操作简单、灵敏度高、重现性好,可用于测定环境水体中的叠氮根。A method has been proposed for determination of azide in environment water by ion chromatography with large volume injection and column-switching techique. Samples were filtered through H column and 0.22μm filter membrane. A reversed-phase column was used as a pretreatment column to eliminate organics on-line. Azide was collected by TAC-ULP1 column and delivered to the analytical system to analyze. KOH gradient elution was selected as the eluent at a flow rate of 1.0mL/min. IonPac AG18(4 mm× 50 mm) and IonPac AS 18(4 mm×250 mm) were chosen for separation with suppressed conductivity detection. The results showed that azide has good linear in the range of 0.01-2.0mg/L(r=0.9994). The detection limit(LOD) of the method is 2.51μg/L(S/N=3), under the conditions of 200μL sample volume. The method has the advantage of simple operation, and can meet the quantitative analysis requirements of environment water.
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