重新導向訊息

饮用水中铁的测定

AN-V-222

2020-05

zh

Wide linear range with a low detection limit using the Bi drop electrode and the triethanolamine method

饮用水中铁的存在会导致难闻的味道、污渍,甚至滋生 “铁细菌”,从而堵塞管道并产生异味。时间长了,不溶性铁沉积物的形成会给许多工业和农业应用带来问题。为了避免这些问题,美国环保署(EPA)将水处理和加工厂的二级最大污染物含量(SMCL)定义为饮用水中铁的含量为 0.3 mg/L。在无毒 Bi 滴电极上对三乙醇胺铁络合物进行伏安法测定,既可以检测到极低的含量(检测限为 0.005 mg/L),也可以在高达 0.5 mg/L 的大浓度范围内进行测量。

The presence of iron in drinking water can lead to an unpleasant, harsh metallic taste or reddish-brown stains. In addition, «iron bacteria» which can grow in waters containing Fe as low as 0.1 mg/L, create a reddish-brown slime that can clog plumbing and cause an offensive odor. Over a longer period, the formation of insoluble iron deposits is problematic in many industrial and agricultural applications, such as water supply, system cooling, or field irrigation. To avoid these problems, the U.S. Environmental Protection Agency (EPA) defines the Secondary Maximum Contaminant Level (SMCL) for water treatment and processing plants as 0.3 mg/L Fe in drinking water.

The voltammetric determination of the iron triethanolamine complex on the non-toxic Bi drop electrode does not require enrichment. This system uses catalytic signal enhancement, allowing both the detection at very low levels (limit of detection of 0.005 mg/L) and measurements in a wide range of concentrations up to 0.5 mg/L. This method is best suited for automated systems or process analyzers, allowing fully automatic determination of iron in a large sample series.

Drinking water, mineral water, sea water

The water sample and the supporting electrolyte are pipetted into the measuring vessel. The determination of iron is carried out with a 884 Professional VA using the parameters specified in Table 1. The concentration is determined by two additions of an iron standard addition solution.

The Bi drop electrode is electrochemically activated prior to the first determination.

Figure 1. 884 Professional VA fully automated for VA
Table 1. Parameters
Parameter Setting
Mode DP – Differential Pulse
Start potential -0.75 V
End potential -1.25 V
Peak potential Fe -1 V
  • Working electrode: Bi drop
  • Reference electrode: Ag/AgCl/KCl (3 mol/L)
  • Auxiliary electrode: Glassy carbon rod

The method is suitable for the determination of iron in water samples in concentrations from β(Fe) = 10–500 µg/L. The limit of detection of the method is approximately β(Fe) = 5 µg/L.

Figure 2. Determination of iron in tap water spiked with β(Fe) = 20 µg/L
Table 2. Result
Sample Fe (µg/L)
Tap water spiked with β(Fe) = 20 µg/L 19.1
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