Xi'an Center for Disease Control and Prevention, Xi'an, 710054, China.
Hangzhou Occupational Disease Prevention and Control Hospital, Hangzhou, 310014, China.
Sci Rep. 2023 Feb 1;13(1):1829. doi: 10.1038/s41598-023-28776-w.
This study developed a method for the simultaneous determination of volatile phenol, cyanide, anionic surfactant, and ammonia nitrogen in drinking water, using a continuous flow analyzer. The samples were first distilled at 145 °C. The phenol in the distillate then subsequently reacted with alkaline ferricyanide and 4-aminoantipyrine to form a red complex that was measured colorimetrically at 505 nm. Cyanide in the distillate subsequently reacted with chloramine T to form cyanogen chloride, which then formed a blue complex with pyridinecarboxylic acid that was measured colorimetrically at 630 nm. The anionic surfactant reacted with basic methylene blue to form a compound that was extracted into chloroform and washed with acidic methylene blue to remove interfering substances. The blue compound in chloroform was determined colorimetrically at 660 nm. Ammonia reacted with salicylate and chlorine from dichloroisocyanuric acid to produce indophenol blue at 37 °C in an alkaline environment that was measured at 660 nm. The relative standard deviations were 0.75-6.10% and 0.36-5.41%, respectively, and the recoveries were 96.2-103.6% and 96.0-102.4% when the mass concentration of volatile phenol and cyanide was in the range of 2-100 μg/L. The linear correlation coefficients were ≥ 0.9999, and the detection limits were1.2 μg/L and 0.9 μg/L, respectively. The relative standard deviations were 0.27-4.86% and 0.33-5.39%, and the recoveries were 93.7-107.0% and 94.4-101.7%. When the mass concentration of anionic surfactant and ammonia nitrogen was 10-1000 μg/L. The linear correlation coefficients were 0.9995 and 0.9999, and the detection limits were 10.7 μg/L and 7.3 μg/L, respectively. When compared to the national standard method, no statistically significant difference was found. This approach saves time and labor, has a lower detection limit, higher precision and accuracy, less contamination, and is more appropriate for the analysis and determination of large-volume samples.
本研究采用连续流动分析仪建立了同时测定饮用水中挥发酚、氰化物、阴离子表面活性剂和氨氮的方法。样品首先在 145°C 下蒸馏。馏出物中的酚随后与碱性铁氰化钾和 4-氨基安替比林反应,形成红色络合物,在 505nm 处比色测定。馏出物中的氰化物随后与氯胺 T 反应生成氰化氯,然后与吡啶甲酸形成蓝色络合物,在 630nm 处比色测定。阴离子表面活性剂与碱性亚甲蓝反应形成化合物,用氯仿萃取,用酸性亚甲蓝洗涤以去除干扰物质。氯仿中的蓝色化合物在 660nm 处比色测定。氨在碱性环境中与水杨酸盐和二氯异氰尿酸中的氯反应,在 37°C 下生成吲哚酚蓝,在 660nm 处测定。当挥发酚和氰化物的质量浓度在 2-100μg/L 范围内时,相对标准偏差分别为 0.75-6.10%和 0.36-5.41%,回收率分别为 96.2-103.6%和 96.0-102.4%。线性相关系数均≥0.9999,检测限分别为 1.2μg/L 和 0.9μg/L。当阴离子表面活性剂和氨氮的质量浓度分别为 10-1000μg/L 时,相对标准偏差分别为 0.27-4.86%和 0.33-5.39%,回收率分别为 93.7-107.0%和 94.4-101.7%。线性相关系数分别为 0.9995 和 0.9999,检测限分别为 10.7μg/L 和 7.3μg/L。与国家标准方法相比,无统计学差异。该方法省时省力,检测限低,精密度和准确度高,污染小,更适合大批量样品的分析和测定。