CN103592242B - A kind of method measuring seawater cod - Google Patents
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- 238000000034 method Methods 0.000 title claims abstract description 40
- 239000013535 sea water Substances 0.000 title claims abstract description 39
- 238000002835 absorbance Methods 0.000 claims abstract description 42
- 239000012086 standard solution Substances 0.000 claims abstract description 33
- 238000005070 sampling Methods 0.000 claims abstract description 27
- 239000012286 potassium permanganate Substances 0.000 claims abstract description 21
- 238000012417 linear regression Methods 0.000 claims abstract description 13
- OUYCCCASQSFEME-QMMMGPOBSA-N L-tyrosine Chemical compound OC(=O)[C@@H](N)CC1=CC=C(O)C=C1 OUYCCCASQSFEME-QMMMGPOBSA-N 0.000 claims abstract description 5
- OUYCCCASQSFEME-UHFFFAOYSA-N tyrosine Natural products OC(=O)C(N)CC1=CC=C(O)C=C1 OUYCCCASQSFEME-UHFFFAOYSA-N 0.000 claims abstract description 5
- 238000002798 spectrophotometry method Methods 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- 239000000243 solution Substances 0.000 claims description 4
- 239000012153 distilled water Substances 0.000 claims description 3
- 238000007865 diluting Methods 0.000 claims 1
- 239000012895 dilution Substances 0.000 claims 1
- 238000010790 dilution Methods 0.000 claims 1
- 238000006467 substitution reaction Methods 0.000 claims 1
- 239000000126 substance Substances 0.000 abstract description 19
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 14
- 239000001301 oxygen Substances 0.000 abstract description 14
- 229910052760 oxygen Inorganic materials 0.000 abstract description 14
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 abstract 1
- 229910052700 potassium Inorganic materials 0.000 abstract 1
- 239000011591 potassium Substances 0.000 abstract 1
- 238000005259 measurement Methods 0.000 description 5
- 238000012544 monitoring process Methods 0.000 description 5
- 238000010521 absorption reaction Methods 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- KMUONIBRACKNSN-UHFFFAOYSA-N potassium dichromate Chemical compound [K+].[K+].[O-][Cr](=O)(=O)O[Cr]([O-])(=O)=O KMUONIBRACKNSN-UHFFFAOYSA-N 0.000 description 2
- 238000010561 standard procedure Methods 0.000 description 2
- 238000000870 ultraviolet spectroscopy Methods 0.000 description 2
- WQZGKKKJIJFFOK-GASJEMHNSA-N Glucose Natural products OC[C@H]1OC(O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-GASJEMHNSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 125000003118 aryl group Chemical group 0.000 description 1
- WQZGKKKJIJFFOK-VFUOTHLCSA-N beta-D-glucose Chemical compound OC[C@H]1O[C@@H](O)[C@H](O)[C@@H](O)[C@@H]1O WQZGKKKJIJFFOK-VFUOTHLCSA-N 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000005670 electromagnetic radiation Effects 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 239000008103 glucose Substances 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 235000019341 magnesium sulphate Nutrition 0.000 description 1
- 238000000691 measurement method Methods 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- IWZKICVEHNUQTL-UHFFFAOYSA-M potassium hydrogen phthalate Chemical compound [K+].OC(=O)C1=CC=CC=C1C([O-])=O IWZKICVEHNUQTL-UHFFFAOYSA-M 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
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Abstract
本发明公开了一种测定海水化学需氧量的方法,包括如下步骤:(1)用酪氨酸配标准溶液,用碱性高锰酸钾法测定标准溶液的COD;(2)用紫外分光光度法测定每个标准溶液在波峰、波谷和400nm处吸光度;(3)吸光度与COD线性拟合,得线性回归方程;(4)随机在待测海域取样;(5)利用碱性高锰酸钾法测步骤(4)取样点的COD;测定3个平行样的波峰处、波谷处和400nm处吸光度;(6)对线性回归方程进行检验与修正;(7)对待测海水取三个平行样,测定与步骤(5)相同的波峰、波谷及400nm处的吸光度,取3个平行样在各处吸光度的平均值;代入步骤(6)获得待测海水化学需氧量。本发明方法简单、操作方便。The invention discloses a method for measuring seawater chemical oxygen demand, which comprises the following steps: (1) preparing a standard solution with tyrosine, and measuring the COD of the standard solution with an alkaline potassium permanganate method; (2) using ultraviolet spectroscopic Photometrically measure the absorbance of each standard solution at the peak, trough and 400nm; (3) linearly fit the absorbance and COD to obtain a linear regression equation; (4) randomly sample in the sea area to be tested; (5) use alkaline permanganate Potassium method for measuring step (4) COD at the sampling point; measure the absorbance at the peak, trough and 400nm of 3 parallel samples; (6) check and correct the linear regression equation; (7) take three parallel samples of seawater to be tested For the sample, measure the same peak, trough and absorbance at 400nm as in step (5), and take the average of the absorbance of 3 parallel samples at each place; substitute it into step (6) to obtain the chemical oxygen demand of the seawater to be measured. The method of the invention is simple and convenient to operate.
Description
技术领域technical field
本发明属于环境监测技术领域,涉及一种测定海水化学需氧量的方法。The invention belongs to the technical field of environmental monitoring and relates to a method for measuring seawater chemical oxygen demand.
背景技术Background technique
化学需氧量(ChemicalOxygenDemand简称COD),是指在一定条件下,水体中易被强氧化剂氧化的还原性物质所消耗的氧化剂的量,以氧的(mg/L)来表示。它是表征水体还原性物质的综合性指标。对于河流和工业废水的研究及污水处理厂的效果评价来说,它是一个重要而相对易得的参数,是环境监测中的必测项目。Chemical Oxygen Demand (Chemical Oxygen Demand referred to as COD) refers to the amount of oxidant consumed by reducing substances in water that are easily oxidized by strong oxidants under certain conditions, expressed in mg/L of oxygen. It is a comprehensive index to characterize the reducing substances in water body. For the study of river and industrial wastewater and the effect evaluation of sewage treatment plants, it is an important and relatively easy-to-obtain parameter, and it is a must-test item in environmental monitoring.
传统测量COD的方法主要有重铬酸钾法和高锰酸盐指数法,高锰酸盐指数法包括碱性高锰酸钾法和酸性高锰酸钾法,目前海水COD测量的国标方法为碱性高锰酸钾法,碱性高锰酸钾法需要人工采样在实验室进行测量,操作复杂、资金投入较大,由于使用较多化学试剂对环境造成污染。The traditional COD measurement methods mainly include potassium dichromate method and permanganate index method. The permanganate index method includes alkaline potassium permanganate method and acid potassium permanganate method. The current national standard method for seawater COD measurement is Alkaline potassium permanganate method, the alkaline potassium permanganate method requires manual sampling for measurement in the laboratory, the operation is complicated, the capital investment is large, and the environment is polluted due to the use of more chemical reagents.
分光光度法是建立在朗伯比尔定律之上的一种利用被测物质的分子或离子对特征电磁辐射的吸收程度进行定量分析的方法,是一种纯物理的光学检测方法,无需化学试剂、无二次污染,同时操作简便,耗时短。实验证明,紫外吸光度能反映水中有机污染的程度,特别是对水中的一大类芳香族有机物和带双键有机物尤为灵敏。近年来很多人开始研究利用污染小、速度快的紫外分光光度法测定淡水化学需氧量,但由于海水中影响因素复杂,在海水方面研究还较少。并没有成熟的方法报道。Spectrophotometry is a method based on Lambert-Beer's law, which uses the molecules or ions of the measured substance to quantitatively analyze the absorption degree of characteristic electromagnetic radiation. It is a purely physical optical detection method without chemical reagents. There is no secondary pollution, and the operation is simple and time-consuming. Experiments have proved that ultraviolet absorbance can reflect the degree of organic pollution in water, especially sensitive to a large class of aromatic organic substances and organic substances with double bonds in water. In recent years, many people have begun to study the use of ultraviolet spectrophotometry with low pollution and high speed to measure the chemical oxygen demand of freshwater. However, due to the complex influencing factors in seawater, there are few studies on seawater. There is no mature method reported.
发明内容Contents of the invention
本发明的目的是克服现有技术存在的操作复杂、耗费时间长,易产生二次污染的不足,提供一种无污染、速度快、能实时监测的快速测定海水化学需氧量的方法。The purpose of the present invention is to overcome the disadvantages of complex operation, long time-consuming, and easy to produce secondary pollution in the prior art, and provide a method for quickly measuring seawater chemical oxygen demand without pollution, fast, and capable of real-time monitoring.
本发明的技术方案概述如下:Technical scheme of the present invention is summarized as follows:
一种测定海水化学需氧量的方法,其特征是包括如下步骤:A method for measuring seawater chemical oxygen demand is characterized in that it comprises the steps:
(1)称取0.2462g酪氨酸加人工海水至1000mL,配成COD浓度为100mg/L的溶液并用人工海水稀释配制成理论COD浓度为1-10mg/L范围内的6个标准溶液,用碱性高锰酸钾法测定所述6个标准溶液的COD;所述人工海水的配方为:称取NaCl26.8g,MgSO4·7H2O8.6g,用蒸馏水稀释至1L;(1) Weigh 0.2462g of tyrosine and add artificial seawater to 1000mL, make a solution with a COD concentration of 100mg/L and dilute it with artificial seawater to prepare 6 standard solutions with a theoretical COD concentration within the range of 1-10mg/L. Alkaline potassium permanganate method was used to measure the COD of the 6 standard solutions; the formula of the artificial seawater was: weigh 26.8g of NaCl, 8.6g of MgSO 4 7H 2 O, and dilute to 1L with distilled water;
(2)用紫外分光光度法测定步骤(1)所述每个标准溶液在波峰处、波谷处和400nm处吸光度;(2) Measure the absorbance at the peak, trough and 400nm of each standard solution described in step (1) by ultraviolet spectrophotometry;
(3)将步骤(2)获得的标准溶液的吸光度与步骤(1)碱性高锰酸钾法测定的标准溶液的COD进行线性拟合,得到线性回归方程;COD(Mn)=21.4664X1-0.0003X2-16.6895X3,其中,X1为每个标准溶液在波峰处的吸光度,X2为每个标准溶液在波谷处的吸光度,X3为每个标准溶液在400nm处的吸光度,COD(Mn)为每个标准溶液通过碱性高锰酸钾法测定的COD;(3) Linearly fit the absorbance of the standard solution obtained in step (2) with the COD of the standard solution measured by the alkaline potassium permanganate method in step (1) to obtain a linear regression equation; COD(Mn)=21.4664X1- 0.0003X2-16.6895X3, wherein, X1 is the absorbance of each standard solution at the peak, X2 is the absorbance of each standard solution at the trough, X3 is the absorbance of each standard solution at 400nm, and COD (Mn) is each The COD of a standard solution measured by the alkaline potassium permanganate method;
(4)随机在待测海域的6-8个海水采样点取样,每个取样点取3个平行样;(4) Randomly sample 6-8 seawater sampling points in the sea area to be tested, and take 3 parallel samples at each sampling point;
(5)利用碱性高锰酸钾法测定步骤(4)的每个取样点的3个平行样COD,并取3个平行样COD的平均值;并用紫外分光光度法分别测定3个平行样的波峰处、波谷处和400nm处的吸光度,并取3个平行样在各处吸光度的平均值;(5) Use the alkaline potassium permanganate method to measure the COD of the 3 parallel samples at each sampling point in step (4), and take the average value of the COD of the 3 parallel samples; and measure the 3 parallel samples by UV spectrophotometry Absorbance at the peak, trough and 400nm, and take the average of the absorbance of 3 parallel samples;
(6)用步骤(5)获得每个取样点的COD的平均值和吸光度的平均值对步骤(3)所得到的线性回归方程进行检验与修正,得到修正的线性回归方程,回归方程形式为COD(Mn)=aY1+bY2-cY3,其中Y1、Y2、Y3分别为步骤(5)获得的波峰处、波谷处和400nm处的吸光度的平均值,COD(Mn)为步骤(5)获得的COD的平均值;利用MATLAB作图软件,输入已有Y1、Y2、Y3及COD(Mn)数据,得到图象与系数a、b、c;(6) Use step (5) to obtain the average value of COD and the average value of absorbance of each sampling point to test and correct the linear regression equation obtained in step (3), and obtain a revised linear regression equation. The form of the regression equation is COD(Mn)=aY1+bY2-cY3, where Y1, Y2, and Y3 are the average absorbance at the peak, trough and 400nm obtained in step (5) respectively, and COD(Mn) is obtained in step (5) The average value of COD; using MATLAB drawing software, input the existing Y1, Y2, Y3 and COD (Mn) data, and get the image and coefficients a, b, c;
(7)对待测海水取三个平行样,测定与步骤(5)相同的波峰处、波谷处及400nm处的吸光度,并取3个平行样在各处吸光度的平均值;分别为Y1、Y2、Y3,代入步骤(6)获得的回归方程形式为COD(Mn)=aY1+bY2-cY3中,由于a、b、c已知,获得COD(Mn)即为待测海水化学需氧量。(7) Take three parallel samples of the seawater to be tested, measure the absorbance at the same peak, trough and 400nm as in step (5), and take the average of the absorbance of the three parallel samples; Y1, Y2 respectively , Y3, into the regression equation obtained in step (6) in the form of COD(Mn)=aY1+bY2-cY3, since a, b, and c are known, the obtained COD(Mn) is the chemical oxygen demand of the seawater to be measured.
本发明用氧化率较高且有紫外吸收的酪氨酸代替邻苯二甲酸氢钾或葡萄糖配制标准溶液;将紫外分光光度测量的结果与国标法(碱性高锰酸钾法)测量结果对应起来,快速测定海水化学需氧量;方法简单、操作方便、耗时较短,且重现性好,解决了传统方法操作复杂、造成二次污染的问题;快速方便对海水COD进行评价;测量效率高,有利于进一步开发为海水COD的实时监控方法。In the present invention, tyrosine with high oxidation rate and ultraviolet absorption is used instead of potassium hydrogen phthalate or glucose to prepare a standard solution; the results of ultraviolet spectrophotometry are corresponding to the measurement results of the national standard method (alkaline potassium permanganate method) It can quickly measure the chemical oxygen demand of seawater; the method is simple, convenient to operate, short in time, and has good reproducibility, which solves the problem of complicated operation and secondary pollution caused by traditional methods; it is fast and convenient to evaluate seawater COD; measure The efficiency is high, which is conducive to further development as a real-time monitoring method for seawater COD.
附图说明Description of drawings
图1为人工配制的0-10mg/LCOD浓度的标准溶液的紫外分光光度法测量结果。Fig. 1 is the ultraviolet spectrophotometric measurement result of the artificially prepared standard solution of 0-10mg/LCOD concentration.
图2为人工配制的0-10mg/LCOD浓度的标准溶液碱性高锰酸钾法和紫外分光光度法测定结果的线性拟合。Fig. 2 is the linear fitting of the standard solution alkaline potassium permanganate method and the ultraviolet spectrophotometry measurement result of the artificially prepared 0-10mg/LCOD concentration.
图3为所取待测海水的紫外分光光度法测量结果。Fig. 3 is the ultraviolet spectrophotometric measurement result of the seawater to be tested.
图4为待测海水的碱性高锰酸钾法和紫外分光光度法测定结果的线性拟合。Fig. 4 is the linear fitting of the measurement results of the alkaline potassium permanganate method and the ultraviolet spectrophotometry of the seawater to be tested.
具体实施方式detailed description
本发明只是在初期进行拟合时使用碱性高锰酸钾法,但当拟合结果确定,可以在一个相当的时间内利用机器操作,成本低,污染较少。The present invention only uses the alkaline potassium permanganate method when fitting at the initial stage, but when the fitting result is confirmed, it can be operated by machine within a considerable period of time, with low cost and less pollution.
下面结合具体实施例对本发明作进一步的说明。但以下的实施例仅限于解释本发明,并不对本发明作任何限制。The present invention will be further described below in conjunction with specific examples. But the following examples are only for explaining the present invention, and do not limit the present invention in any way.
实施例1Example 1
一种快速测定海水化学需氧量的方法,包括如下步骤:A method for rapidly measuring seawater chemical oxygen demand, comprising the steps of:
(1)称取在105℃下干燥2h的0.2462g酪氨酸加人工海水至1000mL,配成COD浓度为100mg/L的溶液并用人工海水稀释配制成理论COD浓度为1.0、2.0、3.0、4.0、5.0、6.0、8.0、10.0mg/L8个标准溶液,用碱性高锰酸钾法测定6个标准溶液的COD分别为0.6565、1.2274、1.7226、2.2966、3.2870、3.4452、4.5938、5.1844mg/L;所述人工海水的配方为:称取NaCl26.8g,MgSO4·7H2O8.6g,用蒸馏水稀释至1L;(1) Weigh 0.2462g of tyrosine dried at 105°C for 2 hours and add artificial seawater to 1000mL to make a solution with a COD concentration of 100mg/L and dilute it with artificial seawater to prepare a theoretical COD concentration of 1.0, 2.0, 3.0, 4.0 , 5.0, 6.0, 8.0, 10.0mg/L8 standard solutions, the COD of the 6 standard solutions measured by the alkaline potassium permanganate method were 0.6565, 1.2274, 1.7226, 2.2966, 3.2870, 3.4452, 4.5938, 5.1844mg/L ; The formula of the artificial seawater is: weigh NaCl26.8g, MgSO4 · 7H2O8.6g, dilute to 1L with distilled water;
(2)使用Kmac便携型分光光度计,采用人工海水作为参比水样,用紫外分光光度法测定步骤(1)所述每个标准溶液在波峰处、波谷处和400nm处吸光度,得到COD标准溶液的紫外光谱图,见图1;吸光度见表1;(2) Using a Kmac portable spectrophotometer, artificial seawater is used as a reference water sample, and the absorbance of each standard solution described in step (1) at the peak, trough and 400nm is measured by ultraviolet spectrophotometry to obtain the COD standard The ultraviolet spectrogram of the solution is shown in Figure 1; the absorbance is shown in Table 1;
(3)将步骤(2)获得的标准溶液的吸光度与步骤(1)碱性高锰酸钾法测定的标准溶液的COD进行线性拟合,得到线性回归方程;COD(Mn)=21.4664X1-0.0003X2-16.6895X3见图2,其相关系数可达0.9914,其中,X1为每个标准溶液在波峰处(220nm)的吸光度,X2为每个标准溶液在波谷处(236nm)的吸光度,X3为每个标准溶液在400nm处的吸光度,COD(Mn)为每个标准溶液通过碱性高锰酸钾法测定的COD;(3) Linearly fit the absorbance of the standard solution obtained in step (2) with the COD of the standard solution measured by the alkaline potassium permanganate method in step (1) to obtain a linear regression equation; COD(Mn)=21.4664X1- 0.0003X2-16.6895X3 is shown in Figure 2, and its correlation coefficient can reach 0.9914, where X1 is the absorbance of each standard solution at the peak (220nm), X2 is the absorbance of each standard solution at the trough (236nm), and X3 is The absorbance of each standard solution at 400nm, COD (Mn) is the COD measured by the alkaline potassium permanganate method for each standard solution;
(4)随机在待测海域的6个海水采样点取样,每个取样点取3个平行样;(4) Randomly sample 6 seawater sampling points in the sea area to be tested, and take 3 parallel samples at each sampling point;
(5)利用碱性高锰酸钾法测定步骤(4)的每个取样点的3个平行样COD,并取3个平行样COD的平均值(见表2);并用紫外分光光度法分别测定3个平行样的波峰处、波谷处和400nm处的吸光度,并取3个平行样在各处吸光度的平均值(见图3,表3);(5) Use the alkaline potassium permanganate method to measure the COD of 3 parallel samples at each sampling point in step (4), and take the average value of the COD of the 3 parallel samples (see Table 2); Measure the absorbance at the peak, trough and 400nm of the 3 parallel samples, and take the average of the absorbance of the 3 parallel samples (see Figure 3, Table 3);
(6)用步骤(5)获得每个取样点的COD的平均值和吸光度的平均值对步骤(3)所得到的线性回归方程进行检验与修正,得到修正的线性回归方程,回归方程形式为COD(Mn)=aY1+bY2-cY3,其中Y1、Y2、Y3分别为步骤(5)获得的波峰处、波谷处和400nm处的吸光度的平均值,COD(Mn)为步骤(5)获得的COD的平均值;利用MATLAB作图软件,输入已有Y1、Y2、Y3及COD(Mn)数据,得到图象(见图4)与系数a=-42.4436,b=204.3414,c=248.9574;(6) Use step (5) to obtain the average value of COD and the average value of absorbance of each sampling point to test and correct the linear regression equation obtained in step (3), and obtain a revised linear regression equation. The form of the regression equation is COD(Mn)=aY1+bY2-cY3, where Y1, Y2, and Y3 are the average absorbance at the peak, trough and 400nm obtained in step (5) respectively, and COD(Mn) is obtained in step (5) The average value of COD; using MATLAB drawing software, input the existing Y1, Y2, Y3 and COD (Mn) data, and get the image (see Figure 4) and coefficient a=-42.4436, b=204.3414, c=248.9574;
(7)对待测海水取三个平行样,测定与步骤(5)相同的波峰处(223nm)、波谷处(236nm)及400nm处的吸光度,并取3个平行样在各处吸光度的平均值,分别为0.1158、0.0123、-0.0126;分别为Y1、Y2、Y3,代入步骤(6)获得的回归方程COD(Mn)=-42.4436Y1+204.3414Y2-248.9574Y3,中,由于a、b、c已知,获得COD(Mn)即为待测海水化学需氧量为0.7353mg/L。(7) Take three parallel samples of the seawater to be tested, measure the absorbance at the same peak (223nm), trough (236nm) and 400nm as in step (5), and take the average of the absorbance of the three parallel samples at each place , respectively 0.1158, 0.0123, -0.0126; respectively Y1, Y2, Y3, substituting into the regression equation obtained in step (6) COD(Mn)=-42.4436Y1+204.3414Y2-248.9574Y3, in, due to a, b, c It is known that obtaining COD(Mn) means that the chemical oxygen demand of seawater to be tested is 0.7353 mg/L.
海水环境变动不大的情况下,技术人员仅需每季度进行一次步骤(1)-(6),获得该海域海水紫外分光光度与COD(Mn)的线性回归方程,海水环境突然变化时,也需进行步骤(1)-(6)对线性回归方程进行修正,其余监测时间仅需进行步骤(7),获得海水的化学需氧量,方便快捷,无二次污染。When the seawater environment does not change much, technicians only need to perform steps (1)-(6) once a quarter to obtain the linear regression equation of seawater UV spectrophotometry and COD(Mn). Steps (1)-(6) need to be carried out to correct the linear regression equation, and the rest of the monitoring time only needs to be carried out in step (7) to obtain the chemical oxygen demand of seawater, which is convenient and quick without secondary pollution.
考虑到不同的海区,其主要的有机物有可能并不一样造成其紫外吸收有所不同,因此针对不同的海区,需要通过用本发明的方法修正拟合方程。Considering that in different sea areas, the main organic substances may be different, resulting in different ultraviolet absorption, so for different sea areas, the fitting equation needs to be corrected by using the method of the present invention.
表1Table 1
表2Table 2
表3table 3
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