Method for determining sulfide in water by utilizing continuous flow method
A technology for the determination of sulfide and water, applied in the field of chemical detection, can solve the problems of high number of experimenters and ability requirements, complicated operation steps, etc., and achieve the effect of ensuring accuracy and stability, simple steps, and low detection limit
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Embodiment 1
[0025] Embodiment 1 utilizes standard environmental sample to carry out precision analysis to this method
[0026] Take the following steps to test:
[0027] 1. Debugging of the instrument
[0028] Turn on the continuous flow analyzer, first replace the reagent with water, check the sealing of the entire analysis flow path and the smoothness of the liquid flow, and start feeding the reagent after the baseline is stable, and use the standard sulfide use solution for calibration after the baseline is stable again.
[0029] 2. Calibration
[0030] 1) Preparation of calibration solution: For the preparation of calibration solution, pipette an appropriate amount of sulfide standard solution into a 100ml volumetric flask, dilute to volume with 0.01mol / L sodium hydroxide, and prepare a standard series of 9 concentration points, sulfur mass Concentrations are: 0.00mg / L, 0.010mg / L, 0.050mg / L, 0.100mg / L, 0.300mg / L, 0.500mg / L, 1.00mg / L, 1.50mg / L, 2.00mg / L.
[0031] 2) Drawing of the c...
Embodiment 2
[0051] Embodiment 2 The detection limit determination of this method
[0052] According to the steps of Example 1, replace the sample with deionized water, repeat the measurement of n (n=8) blank tests, calculate the standard deviation of 8 parallel determinations, calculate the detection limit of the method according to the following formula, and the specific results are shown in Table 2 .
[0053] MDL=t(n-1,0.99)×S
[0054] In the formula:
[0055] MDL - method detection limit;
[0056] n - the number of parallel determinations of the sample;
[0057] t——the t-distribution (one-sided) when the degree of freedom is n-1 and the confidence level is 99%;
[0058] S——the standard deviation of n parallel determinations.
[0059] When the number of parallel determinations is 8, the t value is 2.998.
[0060] Table 2 Detection limit analysis of sulfide determination method
[0061]
Embodiment 3
[0062] Example 3 The addition and determination of sulfide in a sewage plant water sample
[0063] Using the assay method described in Example 1, a standard addition experiment was carried out on an influent water sample of a certain sewage plant with known sulfur content concentration, and the sulfur content after the addition was measured. The results are as shown in Table 3:
[0064] Table 3 Addition recovery test of sulfide in water samples
[0065]
[0066] It can be seen from the results in the table that the recovery rate of influent water standard addition is 94.6%, which meets the quality control index of the water quality monitoring laboratory, and the data obtained by the method are accurate and reliable.
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