Determination of landfill leachate COD by UV-1200 ultraviolet spectrophotometry

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Determination of COD in landfill leachate by ultraviolet spectrophotometry

UV spectrophotometric determination of landfill leachate COD Keywords: UV spectrophotometry; landfill leachate; U.S. instrument UV-1200
The main characteristics of landfill leachate are high COD concentration, CODcr up to 80,000 mg / L, complex composition, in addition to a certain color and suspended matter, if directly discharged, will cause serious pollution, so the treatment of landfill leachate More and more people are paying attention. An important indicator for evaluating the treatment effect is the COD value of landfill leachate.
The standard method for COD determination, potassium dichromate method, is reliable and reproducible. However, the method is cumbersome to operate, time-consuming, power-consuming, large amount of reagents, and the use of highly toxic mercury sulfate, the secondary pollution is more serious. Therefore, it has become a goal of people to explore a method that is fast, energy-saving, reagent-saving, less polluting, reliable, and suitable for batch determination of COD in water samples.
Ultraviolet spectrophotometry uses a wavelength range of 200 to 400 nm and can be used for unsaturated hydrocarbons and compounds with asymmetric electrons (including some inorganic compounds), especially for the analysis and study of compounds containing conjugated systems. Most of the components of landfill leachate have unsaturated hydrocarbon bonds or asymmetric electrons. The composition of the material contained in landfill leachate generally does not change much, so UV absorbance can be used as a comprehensive indicator for evaluating organic pollution of water quality. If the UV absorbance of the landfill leachate can be measured to replace the cumbersome COD measurement or as an approximate estimate of the COD value, the measurement time can be shortened, chemical reagents are eliminated, and the COD measurement procedure is simplified, thereby saving costs.
We obtained the landfill leachate water sample from the regulation tank of a garbage sanitary landfill without filtering. At the same time, the absorbance of the UV spectrophotometer was directly measured and the COD value was determined by the national standard method. The mathematical statistics method was used to obtain the two. A linear regression equation between.
1 test
1.1 Main instruments and reagents UV-visible spectrophotometer UV-1200, produced by Meifang (China) Instrument Co., Ltd. 1cm quartz cuvette. Distilled water.
1.2 Test method The obtained leachate water sample was diluted with distilled water by a certain multiple. At a wavelength of 254 nm, the absorbance of the diluted water sample was measured with a 1 cm cuvette and distilled water as a reference, and the absorbance of the diluted water sample was measured with a 752 type UV-visible spectrophotometer. The COD value of raw water is determined by the national standard method.
2 results and discussion
2.1 Determination of absorption wavelength When the absorbance of the solution to be tested is determined by ultraviolet spectrophotometry, the absorption wavelength should first be selected. When the absorption wavelength is selected, the solution to be tested should generally be scanned at full wavelength, and the wavelength at the absorption peak on the scan curve is preferably selected according to the scanning result. To this end, the landfill leachate with a COD concentration of 1814.4 mg/L was selected, diluted 10 times, and 3 mL was placed in a cuvette with a path length of 1 cm. The distilled water was used as a blank water sample, and the full wavelength was performed in 200-400 nm. Scan, the scan results are shown in Figure 1.

Src="http://i.bosscdn.com/blog/nophoto.gif" /></p> As can be seen from Figure 1, the absorbance decreases with increasing wavelength, and there is no obvious absorption peak. . Considering the UV absorbance at a wavelength of 254 nm, UV254 is an important control parameter for measuring organic matter in water. It has been widely accepted and used by water treatment research and management personnel after nearly 20 years of research abroad. To this end, we selected a wavelength of 254 nm as the wavelength at which the absorbance of the landfill leachate was measured. Here, UV254 is not measured for an organic substance, that is, UV254 reflects not the existence and content of an organic substance, but as an alternative parameter that indirectly reflects a class of organic substances, so the index can also be called non-specificity. UV254. 2.2 Correlation between absorbance and COD 2.2.1 Absorbance UV254 and COD correlation  The absorbance of nine water samples was measured at a wavelength of 254 nm. The corresponding measurement results are shown in Table 1. Taking the absorbance UV254 as the abscissa, the COD value measured by the national standard method is the ordinate, and the correlation between the absorbance UV254 and COD is shown in Fig. 2.  Table 1 absorbance UV254 and COD measurement results <p align="center"><img border="0" alt=

Figure 2 Correlation between absorbance UV254 and COD

Src="http://i.bosscdn.com/blog/nophoto.gif" /></p> The data in Table 1 is calculated by linear regression using least squares method: correlation coefficient r=0.9984, The regression equation is: COD = b × UV254 - a = 317.87 × UV254 - 67.99. The sample size of this experiment is n=9, and the correlation coefficient ra value of the correlation coefficient is obtained: r0.001(7)=0.8982. This experiment >> r 0.001, indicating that the linear regression effect of UV254 and COD is very significant. When the confidence of the coefficient b is 95%, the interval of b is estimated to be between 317.87 and 16.67, and the corresponding regression equation is: COD=(317.87 soil 16.67)×UV254-67.99.  2.2.2, absorbance ΔUV and COD correlation  In order to investigate the effect of suspended matter on the measurement results, based on the previous work, the correlation between absorbance ΔUV and COD was studied. ΔUV = UV254-UV365, where UV365 refers to the UV absorbance at a wavelength of 365 nm. The corresponding measurement results are shown in Table 2. The correlation between absorbance ΔUV and COD is shown in Fig. 3.  Table 2 △ UV and COD measurement results <p align="center"><img border="0" alt=

Figure 3: Correlation between absorbance ΔUV and COD

Src="http://i.bosscdn.com/blog/nophoto.gif" /></p> The data in Table 2 is calculated by linear regression using least squares method: correlation coefficient r=0.9962, The regression equation is: COD=3158.25×ΔUV-280.21. The linear regression effect of absorbance ΔUV and COD was very significant using the same method as the linear regression effect of UV 254 and COD. When the confidence of the coefficient b is 95%, the interval of b is estimated to be between 3158.25±246.19, and the corresponding regression equation is: COD=(3158.25±246.19)×△UV-280.21. 3 Conclusions3.1 Linear range0~250mg/L, the linear regression effect of UV254 and COD, absorbance ΔUV and COD of landfill leachate is very significant, and the correlation coefficient r is greater than 0.995.  3.2 Water sample without pretreatment  No matter whether UV 254 or ΔUV is measured, no need to pretreat the landfill leachate, which can simplify the measurement process. 3.3UV254 can be used as a parameter to evaluate the COD of landfill leachateIn the linear regression equation of UV254 and COD, absorbance ΔUV and COD in the landfill leachate, the correlation coefficient of the former is slightly larger than the latter. At the same time, when the confidence of the slope b is 95%, the interval of b is estimated to be better than the latter; finally, the measurement of UV254 is easier than the determination of ΔUV, so UV254 is more suitable for evaluating landfill leachate COD than ΔUV. Parameters. Key words: ultraviolet spectrophotometry; landfill leachate; instrumentation UV-1200</p> </div> </div> <div class="tech-detail-share"> <!-- Baidu Button BEGIN - -> <div class="bdsharebuttonbox"> <a href="#" class="bds_qzone" data-cmd="qzone" title="Share to QQ space"></a> <a href="#" class ="bds_tsina" data-cmd="tsina" title="Share to Sina Weibo"></a> <a href="#" class="bds_weixin" data-cmd="weixin" title="Share to WeChat "></a> <span>Share to:</span> </div> <script>window._bd_share_config = { "common": { "bdSnsKey": {}, "bdText": "", "bdMini" : "1", "bdMiniList": false, "bdPic": "", "bdStyle": "2", "bdSize": "16" }, "share": {} }; with (document) 0[( getElementsByTagName(

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