CN106885780A - A kind of method for determining soil nitrate-N - Google Patents
A kind of method for determining soil nitrate-N Download PDFInfo
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- 238000000034 method Methods 0.000 title claims abstract description 60
- 239000002689 soil Substances 0.000 title claims abstract description 49
- 238000002835 absorbance Methods 0.000 claims abstract description 34
- 238000004821 distillation Methods 0.000 claims abstract description 28
- 238000000870 ultraviolet spectroscopy Methods 0.000 claims abstract description 9
- 229910002651 NO3 Inorganic materials 0.000 claims abstract description 6
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 claims abstract description 6
- 238000000605 extraction Methods 0.000 claims abstract description 5
- 238000002386 leaching Methods 0.000 claims abstract 5
- 238000000205 computational method Methods 0.000 claims abstract 4
- 238000001914 filtration Methods 0.000 claims abstract 2
- MMDJDBSEMBIJBB-UHFFFAOYSA-N [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] Chemical compound [O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O.[NH6+3] MMDJDBSEMBIJBB-UHFFFAOYSA-N 0.000 claims description 72
- 238000002798 spectrophotometry method Methods 0.000 claims description 14
- 238000005259 measurement Methods 0.000 claims description 7
- FGIUAXJPYTZDNR-UHFFFAOYSA-N potassium nitrate Chemical compound [K+].[O-][N+]([O-])=O FGIUAXJPYTZDNR-UHFFFAOYSA-N 0.000 claims description 6
- 239000002904 solvent Substances 0.000 claims description 6
- 238000002360 preparation method Methods 0.000 claims description 5
- 239000004323 potassium nitrate Substances 0.000 claims description 3
- 235000010333 potassium nitrate Nutrition 0.000 claims description 3
- 238000012937 correction Methods 0.000 claims description 2
- 150000001875 compounds Chemical class 0.000 claims 3
- 239000007788 liquid Substances 0.000 claims 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 14
- JVMRPSJZNHXORP-UHFFFAOYSA-N ON=O.ON=O.ON=O.N Chemical compound ON=O.ON=O.ON=O.N JVMRPSJZNHXORP-UHFFFAOYSA-N 0.000 abstract description 11
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 7
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 abstract description 5
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 description 30
- 239000000243 solution Substances 0.000 description 27
- 239000000284 extract Substances 0.000 description 22
- 239000001103 potassium chloride Substances 0.000 description 15
- 235000011164 potassium chloride Nutrition 0.000 description 15
- 238000004364 calculation method Methods 0.000 description 9
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 4
- 239000000956 alloy Substances 0.000 description 3
- 229910045601 alloy Inorganic materials 0.000 description 3
- 229910052793 cadmium Inorganic materials 0.000 description 3
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical compound [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 3
- 230000007935 neutral effect Effects 0.000 description 3
- 239000012266 salt solution Substances 0.000 description 3
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 239000003905 agrochemical Substances 0.000 description 2
- 238000009614 chemical analysis method Methods 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 238000004737 colorimetric analysis Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000000618 nitrogen fertilizer Substances 0.000 description 2
- 239000011550 stock solution Substances 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- VRZJGENLTNRAIG-UHFFFAOYSA-N 4-[4-(dimethylamino)phenyl]iminonaphthalen-1-one Chemical compound C1=CC(N(C)C)=CC=C1N=C1C2=CC=CC=C2C(=O)C=C1 VRZJGENLTNRAIG-UHFFFAOYSA-N 0.000 description 1
- JXBUOZMYKQDZFY-UHFFFAOYSA-N 4-hydroxybenzene-1,3-disulfonic acid Chemical compound OC1=CC=C(S(O)(=O)=O)C=C1S(O)(=O)=O JXBUOZMYKQDZFY-UHFFFAOYSA-N 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-O Ammonium Chemical compound [NH4+] QGZKDVFQNNGYKY-UHFFFAOYSA-O 0.000 description 1
- FRPHFZCDPYBUAU-UHFFFAOYSA-N Bromocresolgreen Chemical compound CC1=C(Br)C(O)=C(Br)C=C1C1(C=2C(=C(Br)C(O)=C(Br)C=2)C)C2=CC=CC=C2S(=O)(=O)O1 FRPHFZCDPYBUAU-UHFFFAOYSA-N 0.000 description 1
- KGBXLFKZBHKPEV-UHFFFAOYSA-N boric acid Chemical compound OB(O)O KGBXLFKZBHKPEV-UHFFFAOYSA-N 0.000 description 1
- 239000004327 boric acid Substances 0.000 description 1
- -1 distillation Chemical compound 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000000706 filtrate Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- CEQFOVLGLXCDCX-WUKNDPDISA-N methyl red Chemical compound C1=CC(N(C)C)=CC=C1\N=N\C1=CC=CC=C1C(O)=O CEQFOVLGLXCDCX-WUKNDPDISA-N 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 239000002881 soil fertilizer Substances 0.000 description 1
- 239000012086 standard solution Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000004448 titration Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000012795 verification Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
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Abstract
Description
技术领域technical field
本发明涉及土壤中硝态氮的测定,具体的说是一种改进土壤硝态氮的测定方法。The invention relates to the determination of nitrate nitrogen in soil, in particular to an improved determination method of soil nitrate nitrogen.
背景技术Background technique
土壤中无机氮可分为水溶态、交换态及固定态等。测定土壤中的铵态、硝态及亚硝态氮素,通常是测定水溶态及交换态两者总量。交换态为可被中性盐溶液交换提取的部分(中性盐溶液为氯化钾或氯化钠)。中性盐溶液与土壤混合、震荡,将土壤吸附的铵态氮交换浸出,其中也包含水溶态。此提取物经过滤,滤液再进行各种形态氮的测定。常用的测定铵态氮方法有蒸馏法和靛酚蓝比色法,然而测定硝态氮的方法却有很多,包括蒸馏法,酚二磺酸法,镉还原法和双波长紫外分光光度法(文献1:鲁如坤,土壤农业化学分析方法,北京:中国农业科技出版社,2000:156-165)。Inorganic nitrogen in soil can be divided into water-soluble state, exchange state and fixed state. The determination of ammonium, nitrate and nitrite nitrogen in soil is usually the total amount of water-soluble and exchangeable nitrogen. The exchanged state is the part that can be exchanged and extracted by neutral salt solution (neutral salt solution is potassium chloride or sodium chloride). The neutral salt solution is mixed and shaken with the soil to exchange and leach the ammonium nitrogen adsorbed by the soil, which also includes the water-soluble state. The extract was filtered, and the filtrate was subjected to the determination of various forms of nitrogen. Commonly used methods for the determination of ammonium nitrogen include distillation and indophenol blue colorimetry, but there are many methods for the determination of nitrate nitrogen, including distillation, phenol disulfonic acid method, cadmium reduction method and dual-wavelength ultraviolet spectrophotometry ( Document 1: Lu Rukun, Soil Agricultural Chemical Analysis Methods, Beijing: China Agricultural Science and Technology Press, 2000: 156-165).
需要说明的是亚硝态氮也属于交换态氮,在作物生长过程中,作为有效氮肥为作物提供养分,即使其含量及低,不足硝态氮的5%。上述测定土壤硝态氮的方法中测定的值均可含有亚硝态氮。在这里我们所涉及的是测定土壤硝态氮和亚硝态氮总和的方法。What needs to be explained is that nitrite nitrogen is also an exchange nitrogen. During the growth of crops, it is used as an effective nitrogen fertilizer to provide nutrients for crops, even if its content is extremely low, less than 5% of nitrate nitrogen. The values measured in the above methods for measuring soil nitrate nitrogen can all contain nitrite nitrogen. Here we are concerned with methods for determining the sum of nitrate-nitrogen and nitrite-nitrogen in soils.
常用的测定硝态氮方法有以下缺点:蒸馏法需要特定装置,能源消耗大,且定氮合金很难磨细过100目筛;酚二磺酸法操作步骤过于繁琐、土壤浸提液水分蒸发时间长、费能源且多种物质存在干扰;镉柱还原法虽然干扰少、精度高,但操作繁琐且镉是高毒性的重金属,易污染环境;双波长紫外分光光度法中测定波长没有统一标准(文献2:涂常青,温欣荣,双波长紫外分光光度法测定土壤硝态氮,土壤肥料,2006(1):50-51)。Commonly used methods for determining nitrate nitrogen have the following disadvantages: the distillation method requires a specific device, consumes a lot of energy, and it is difficult to grind nitrogen-fixing alloys through a 100-mesh sieve; It takes a long time, consumes energy, and interferes with various substances; although the cadmium column reduction method has less interference and high precision, it is cumbersome to operate and cadmium is a highly toxic heavy metal, which is easy to pollute the environment; there is no unified standard for the determination of wavelength in dual-wavelength ultraviolet spectrophotometry (Document 2: Tu Changqing, Wen Xinrong, Determination of soil nitrate nitrogen by dual-wavelength ultraviolet spectrophotometry, Soil Fertilizer, 2006 (1): 50-51).
发明内容Contents of the invention
本发明的目的是提供一种操作简单,不添加任何试剂,重复性好,重现性高的测定土壤硝态氮的方法。The purpose of the invention is to provide a method for measuring soil nitrate nitrogen with simple operation, no addition of any reagent, good repeatability and high reproducibility.
为实现上述目的,本发明采用的技术方案如下:To achieve the above object, the technical scheme adopted in the present invention is as follows:
一种测定土壤硝态氮的方法,A method for measuring soil nitrate nitrogen,
1)以2mol/L KCl为溶剂配制浓度为0.1–20mg N/L范围内的6个以上不同浓度的硝态氮溶液,分别用紫外-可见分光光度计在220nm和275nm波长处测定各个所配制溶液吸光度A220和A275;用A220–2×A275的计算方法求得吸光度,以硝态氮浓度为横坐标,计算的吸光度值为纵坐标制作标准曲线;1) Use 2mol/L KCl as a solvent to prepare more than 6 different concentrations of nitrate nitrogen solutions in the range of 0.1-20mg N/L, and use a UV-visible spectrophotometer to measure the concentration of each prepared solution at 220nm and 275nm wavelengths respectively. Solution absorbance A 220 and A 275 ; use the calculation method of A 220-2 ×A 275 to obtain the absorbance, take the nitrate nitrogen concentration as the abscissa, and calculate the absorbance value as the ordinate to make a standard curve;
2)土壤浸提液制备:将土壤样品用4倍重量体积(g/ml)的2mol/L KCl溶液振荡浸提1h以上,过滤,得浸提液;2) Preparation of soil extract: shake and extract the soil sample with 2 mol/L KCl solution of 4 times the weight volume (g/ml) for more than 1 hour, filter to obtain the extract;
3)将浸提液直接置于紫外-可见分光光度计中测定220nm和270nm吸光度值,用A220–2×A275的计算方法求得吸光度,通过求得的吸光度于步骤1)制作的标准曲线中查询获得浸提液中硝态氮浓度;3) Place the extract solution directly in a UV-visible spectrophotometer to measure the absorbance values at 220nm and 270nm, use the calculation method of A 220 -2×A 275 to obtain the absorbance, and use the obtained absorbance to make the standard in step 1) Query the curve to obtain the concentration of nitrate nitrogen in the extract;
4)将紫外分光光度法法测定值校正成为蒸馏法测定值,公式为y=1.021x-0.223,其中x为紫外分光光度法的土壤硝态氮浓度测定值,y为蒸馏法的土壤硝态氮浓度测定值。4) The UV spectrophotometry measured value is corrected into the distillation method measured value, the formula is y=1.021x-0.223, wherein x is the soil nitrate nitrogen concentration measured value of the UV spectrophotometric method, and y is the soil nitrate state of the distillation method Measured value of nitrogen concentration.
所述步骤1)配制硝态氮溶液的具体过程为:以2mol/L KCl为溶剂配制浓度为0.1–20mg N/L范围内的6个以上不同浓度的硝态氮溶液,其中包括0.1mgN/L和20mg N/L二个端值浓度的硝态氮溶液,以及大于0.1mg N/L至小于20mg N/L的4个以上不同浓度的硝态氮溶液。The specific process of the step 1) preparing the nitrate nitrogen solution is: using 2mol/L KCl as a solvent to prepare nitrate nitrogen solutions with a concentration of more than 6 different concentrations in the range of 0.1-20mg N/L, including 0.1mgN/ Nitrate nitrogen solutions with two extreme concentrations of L and 20mg N/L, and more than 4 different concentrations of nitrate nitrogen solutions from more than 0.1mg N/L to less than 20mg N/L.
所述步骤1)配制硝态氮溶液的具体过程为:以2mol/L KCl为溶剂配制浓度为0.1–15mg N/L范围内的6个以上不同浓度的硝态氮溶液,其中包括0.1mgN/L和15mg N/L二个端值浓度的硝态氮溶液,以及大于0.1mg N/L至小于15mg N/L的4个以上不同浓度的硝态氮溶液。The specific process of the step 1) preparing the nitrate nitrogen solution is: using 2mol/L KCl as a solvent to prepare nitrate nitrogen solutions with a concentration of more than 6 different concentrations within the range of 0.1-15mg N/L, including 0.1mgN/ Nitrate nitrogen solutions with two extreme concentrations of L and 15mg N/L, and more than 4 different concentrations of nitrate nitrogen solutions from more than 0.1mg N/L to less than 15mg N/L.
所述步骤1)的具体过程为:分别吸取浓度为100mg N/L的硝态氮溶液0.05、0.25、0.5、2.5、5.0、7.5mL于50mL容量瓶中,加入2mol/L KCl至50mL刻度线,摇匀,用紫外-可见分光光度计在220nm和275nm波长处测定吸光度;用A220–2×A275的计算方法求得吸光度,以硝态氮浓度为横坐标,计算的吸光度值为纵坐标制作标准曲线,标准曲线线性范围为0.1–15mg N/L,标准曲线一般为多项式方程。The specific process of the step 1) is as follows: draw 0.05, 0.25, 0.5, 2.5, 5.0, and 7.5 mL of nitrate nitrogen solutions with a concentration of 100 mg N/L in a 50 mL volumetric flask, and add 2 mol/L KCl to the 50 mL mark , shake well, and measure the absorbance at 220nm and 275nm wavelengths with a UV-visible spectrophotometer; use the calculation method of A 220 – 2×A 275 to obtain the absorbance, take the nitrate nitrogen concentration as the abscissa, and calculate the absorbance value as the ordinate Coordinates to make a standard curve, the linear range of the standard curve is 0.1-15mg N/L, and the standard curve is generally a polynomial equation.
所述配制硝态氮溶液采用的溶质为硝酸钾。The solute used for preparing the nitrate nitrogen solution is potassium nitrate.
具体过程可为:一种测定土壤硝态氮的方法,The specific process can be: a method for measuring soil nitrate nitrogen,
1)制作标准曲线:吸取100mg N/L硝态氮溶液(2mol/L KCl配制)0.05,0.25,0.5,2.5,5.0,7.5mL于50mL容量瓶中,加入2mol/L KCl定容,摇匀,用紫外-可见分光光度计在220nm和275nm波长测定吸光度,用A220–2×A275的计算方法求得吸光度,以硝态氮浓度为横坐标,计算的吸光度值为纵坐标制作标准曲线;1) Make a standard curve: draw 0.05, 0.25, 0.5, 2.5, 5.0, 7.5mL of 100mg N/L nitrate nitrogen solution (prepared with 2mol/L KCl) into a 50mL volumetric flask, add 2mol/L KCl to constant volume, and shake well , use a UV-visible spectrophotometer to measure the absorbance at 220nm and 275nm wavelengths, use the calculation method of A 220 – 2×A 275 to obtain the absorbance, take the concentration of nitrate nitrogen as the abscissa, and calculate the absorbance value as the ordinate to make a standard curve ;
2)土壤浸提液制备:将土壤样品用4倍重量体积(g/ml)的2mol/L KCl溶液振荡浸提1h,过滤,得浸提液;2) Preparation of soil extract: shake and extract the soil sample with 4 times the weight volume (g/ml) of 2mol/L KCl solution for 1 hour, filter to obtain the extract;
3)将浸提液直接置于紫外-可见分光光度计中测定220nm和270nm吸光度值,用A220–2×A275的计算方法求得吸光度,查询标准曲线计算浸提液中硝态氮浓度;3) Place the extract directly in a UV-Vis spectrophotometer to measure the absorbance at 220nm and 270nm, use the calculation method of A 220 -2×A 275 to obtain the absorbance, and query the standard curve to calculate the concentration of nitrate nitrogen in the extract ;
4)将紫外分光光度法法测定值校正成为蒸馏法测定值,公式为y=1.021x-0.223(R2=0.9722,n=20),其中x为紫外分光光度法法测定值,y为蒸馏法测定值。4) Correct the value measured by UV spectrophotometry into the value measured by distillation, the formula is y=1.021x-0.223 (R 2 =0.9722, n=20), where x is the value measured by UV spectrophotometry, and y is the value of distillation measured value.
使用该方法测定土壤中硝态氮含量,有如下优点:Using this method to determine the content of nitrate nitrogen in soil has the following advantages:
1.该方法操作简便,步骤少,不用添加任何试剂,直接进行浸提液的紫外吸收测定,人为误差小。1. The method is easy to operate, with few steps, without adding any reagents, and the ultraviolet absorption measurement of the extract is directly carried out, and the human error is small.
2.该方法省事。原有的蒸馏法或者比色法一天测定硝态氮不超过100个,相同时间内可用该方法测定1000个,效率提高9倍。2. This method saves trouble. The original distillation method or colorimetric method can measure no more than 100 nitrate nitrogen in one day, but this method can be used to measure 1000 nitrate nitrogen in the same time, and the efficiency is increased by 9 times.
3.使用该方法测定的土壤硝态氮浓度与蒸馏法测定值相关性极好(R2=0.9722,n=20),因此可以将测定值校正后与蒸馏法测定铵态氮相结合,建立一套完整、高效、准确的土壤有效态无机氮测定方法体系。3. The soil nitrate nitrogen concentration measured by this method has an excellent correlation with the value determined by the distillation method (R 2 =0.9722, n=20), so the measured value can be corrected and combined with the determination of ammonium nitrogen by the distillation method to establish A complete, efficient and accurate method system for the determination of soil available inorganic nitrogen.
本发明方法重复性好,重现性高,简单易行。The method of the invention has good repeatability, high reproducibility, and is simple and easy to implement.
附图说明Description of drawings
图1硝态氮测定标准曲线-1;Fig. 1 nitrate nitrogen determination standard curve-1;
图2硝态氮测定标准曲线-2;Fig. 2 nitrate nitrogen determination standard curve-2;
图3蒸馏法和紫外分光光度法测定土壤硝态氮结果比对;Figure 3 Comparison of the results of the determination of soil nitrate nitrogen by distillation and ultraviolet spectrophotometry;
图4验证蒸馏法和紫外分光光度法测定硝态氮的相关性。Figure 4 validates the correlation between distillation and UV spectrophotometry for the determination of nitrate nitrogen.
具体实施方式detailed description
实施例1Example 1
建立紫外分光光度法测定硝态氮标准曲线Establishment of Standard Curve for Determination of Nitrate Nitrogen by Ultraviolet Spectrophotometry
由于土壤浸提液中硝态氮浓度是不经任何操作直接测定,因此硝态氮浓度应全部落在标准曲线线性范围中,否则测定结果不准确。经计算,当土壤溶液中硝态氮浓度为15mg N/L时,土壤硝态氮含量约为66kg/mg,相当于氮肥施用量158kg N/ha(0-20cm土壤容重为1.2g/cm3),因此标准曲线中硝态氮最大浓度设置为15m N g/L(如果需要,也可以设置为20mg N/L),完全可以满足实验需要。Since the concentration of nitrate nitrogen in the soil extract is directly measured without any operation, the concentration of nitrate nitrogen should all fall within the linear range of the standard curve, otherwise the determination result will be inaccurate. After calculation, when the nitrate nitrogen concentration in the soil solution is 15mg N/L, the soil nitrate nitrogen content is about 66kg/mg, which is equivalent to the nitrogen fertilizer application rate of 158kg N/ha (0-20cm soil bulk density is 1.2g/ cm3 ), so the maximum concentration of nitrate nitrogen in the standard curve is set to 15m N g/L (if necessary, it can also be set to 20mg N/L), which can fully meet the needs of the experiment.
经测定,紫外分光光度法测定硝态氮和亚硝态氮都在220nm处出现较强的吸收峰,因此该方法的测定结果包含了亚硝态氮含量,这与蒸馏法测定的硝态氮和亚硝态氮总和相匹配,成为将该法与蒸馏法相互验证的实验基础。另外,土壤亚硝态氮是土壤硝化作用的中间过程,含量极低,在测定过程中通常忽略不计,因此标准曲线溶液不加入标准亚硝态氮,其吸光度对照硝态氮计算。After determination, both nitrate nitrogen and nitrite nitrogen measured by ultraviolet spectrophotometry have strong absorption peaks at 220nm, so the measurement results of this method include the content of nitrite nitrogen, which is different from the nitrite nitrogen measured by distillation. Matching with the sum of nitrite nitrogen becomes the experimental basis for the mutual verification of this method and the distillation method. In addition, soil nitrite nitrogen is an intermediate process of soil nitrification, and its content is extremely low, which is usually negligible during the determination process. Therefore, the standard curve solution does not add standard nitrite nitrogen, and its absorbance is calculated against nitrate nitrogen.
具体过程如下:The specific process is as follows:
1)配制硝态氮储备液:准确称取7.216g烘干硝酸钾,加入2mol/L KCl溶解,定容至1L容量瓶中,此溶液含有硝态氮1000mg/L。将此储备液按10倍数稀释,2mol/L KCl定容,得到浓度为100mg N/L的溶液;1) Preparation of nitrate nitrogen stock solution: Accurately weigh 7.216g of dried potassium nitrate, add 2mol/L KCl to dissolve, and dilute to a 1L volumetric flask. This solution contains 1000mg/L of nitrate nitrogen. Dilute this stock solution by a factor of 10, and constant volume with 2mol/L KCl to obtain a solution with a concentration of 100mg N/L;
2)制作标准曲线:吸取上述硝态氮溶液0.05,0.25,0.5,2.5,5.0,7.5mL于50mL容量瓶中,加入2mol/L KCl至刻度线,摇匀,用紫外-可见分光光度计在220nm和275nm波长处测定吸光度。用A220–2×A275的计算方法求得吸光度,以硝态氮浓度为横坐标,计算的吸光度值为纵坐标制作标准曲线。结果如图1所示,标准曲线符合多项式方程,R2=0.998(n=7)。2) Make a standard curve: draw 0.05, 0.25, 0.5, 2.5, 5.0, 7.5mL of the above-mentioned nitrate nitrogen solution into a 50mL volumetric flask, add 2mol/L KCl to the mark, shake well, and use a UV-visible spectrophotometer to Absorbance was measured at wavelengths of 220 nm and 275 nm. Use the calculation method of A 220 -2×A 275 to obtain the absorbance, take the concentration of nitrate nitrogen as the abscissa, and calculate the absorbance value as the ordinate to make a standard curve. The results are shown in Figure 1, the standard curve conforms to the polynomial equation, R 2 =0.998 (n=7).
实施例2Example 2
紫外分光光度法与蒸馏法测定硝态氮浓度比对Comparison of Ultraviolet Spectrophotometry and Distillation Method for Determination of Nitrate Nitrogen Concentration
具体实施过程:The specific implementation process:
1)土壤浸提液制备:将土壤样品(共n=44个土壤样品)分别用4倍重量体积(g/ml)的2mol/L KCl溶液振荡浸提1h,过滤,得浸提液。此浸提样品分成两部分,一部分(共n=20个土壤样品)用来确定两种方法测定硝态氮浓度的相关性,剩余样品(共n=24个土壤样品)用于验证该相关性的准确性;1) Preparation of soil extract: soil samples (n=44 soil samples in total) were oscillated and extracted with 4 times the weight volume (g/ml) of 2mol/L KCl solution for 1 hour, filtered to obtain the extract. This extraction sample is divided into two parts, and a part (total n=20 soil samples) is used for determining the correlation of two kinds of methods to measure nitrate nitrogen concentration, and remaining sample (total n=24 soil samples) is used for verifying this correlation accuracy;
2)制作标准曲线:吸取浓度为100mg N/L的硝态氮溶液0.05,0.25,0.5,2.5,5.0,7.5mL于50mL容量瓶中,加入2mol/L KCl至刻度线,摇匀,用紫外-可见分光光度计在220nm和275nm波长处测定吸光度。用A220–2×A275的计算方法求得吸光度,以硝态氮浓度为横坐标,计算的吸光度值为纵坐标制作标准曲线(图2);标准曲线一般为多项式方程;2) Make a standard curve: draw 0.05, 0.25, 0.5, 2.5, 5.0, and 7.5 mL of nitrate nitrogen solution with a concentration of 100 mg N/L into a 50 mL volumetric flask, add 2 mol/L KCl to the mark, shake well, and use a UV - Visible spectrophotometer to measure absorbance at wavelengths of 220nm and 275nm. Use the calculation method of A 220-2 ×A 275 to obtain the absorbance, take the nitrate nitrogen concentration as the abscissa, and calculate the absorbance value as the ordinate to make a standard curve (Figure 2); the standard curve is generally a polynomial equation;
3)紫外分光光度法测定浸提液中硝态氮浓度:将步骤1)中浸提液(共n=20个土壤样品)分别直接置于紫外-可见分光光度计中测定220nm和270nm吸光度值A220和A275,用A220–2×A275的计算方法求得吸光度,查询上述标准曲线计算浸提液中硝态氮浓度;3) Determination of nitrate nitrogen concentration in the extract by ultraviolet spectrophotometry: the extract in step 1) (total n=20 soil samples) is directly placed in the ultraviolet-visible spectrophotometer to measure the absorbance values at 220nm and 270nm respectively A 220 and A 275 , use the calculation method of A 220 -2×A 275 to obtain the absorbance, query the above standard curve to calculate the concentration of nitrate nitrogen in the extract;
4)蒸馏法测定浸提液中硝态氮浓度:分别取上述测定步骤3)同样的浸提液(共n=20个土壤样品)50mL于蒸馏瓶中,同时于一蒸馏瓶中做空白组(内装有50mL 2mol/L KCl溶液)进行对照,分别加入1g氧化镁,置于蒸馏装置中,立即分别向浸提液和空白组中通入水蒸汽进行加热蒸馏,至冷凝管下端接收馏出液的三角瓶中馏出液体积达100mL时,终止蒸馏,移去接收馏出液的三角瓶,此步骤目的为去除铵态氮。将接收馏出液的三角瓶换成一个盛有15mL重量浓度为2%的硼酸加一滴(0.05mL)混合指示剂(0.066g甲基红和0.099g溴甲酚绿用体积浓度95%乙醇定容至100ml)的接收瓶于冷凝管下端,继续分别向蒸馏瓶中加入0.2g定氮合金(合金组成:Cu 50%,Al 45%,Zn 5%),继续分别向蒸馏瓶中通入水蒸汽进行蒸馏,至接收瓶中的馏出液体积达100mL时,终止蒸馏,移去接收瓶。用0.003mol·L-1硫酸标准溶液进行滴定,当溶液由灰色中显现红色时即为滴定终点。根据样品消耗的硫酸量计算硝态氮含量(文献1:鲁如坤,土壤农业化学分析方法,北京:中国农业科技出版社,2000:156-165);4) Determination of nitrate nitrogen concentration in the extract by distillation: take 50mL of the same extract from the above-mentioned determination step 3) (a total of n=20 soil samples) in a retort, and make a blank group in a retort at the same time (with 50mL 2mol/L KCl solution inside) for comparison, add 1g of magnesium oxide respectively, place in the distillation device, immediately pass water vapor into the extraction solution and the blank group for heating and distillation, and receive the distillate at the lower end of the condenser tube When the volume of the distillate in the Erlenmeyer flask reaches 100mL, stop the distillation and remove the Erlenmeyer flask receiving the distillate. The purpose of this step is to remove ammonium nitrogen. Replace the triangular flask receiving the distillate with one containing 15mL of boric acid with a weight concentration of 2% plus one drop (0.05mL) of a mixed indicator (0.066g of methyl red and 0.099g of bromocresol green with a volume concentration of 95% ethanol). 100ml) of the receiving bottle at the lower end of the condenser, continue to add 0.2g nitrogen-fixing alloy (alloy composition: Cu 50%, Al 45%, Zn 5%) to the retort respectively, and continue to feed water vapor into the retort respectively Carry out distillation until the volume of the distillate in the receiving bottle reaches 100mL, stop the distillation and remove the receiving bottle. Titrate with 0.003mol·L -1 sulfuric acid standard solution, when the solution turns red from gray, it is the titration end point. Calculate the nitrate nitrogen content according to the amount of sulfuric acid consumed by the sample (document 1: Lu Rukun, Soil Agricultural Chemical Analysis Methods, Beijing: China Agricultural Science and Technology Press, 2000: 156-165);
测定结果见图3,随机选取的土壤浸提液硝态氮浓度变异较大,范围从0.1-3.7mg/L,代表性强。两种方法的相关系数R=0.986,说明两种方法的相关性较好,可以用紫外分光光度法取代繁琐的蒸馏法,用于测定土壤硝态氮含量。The measurement results are shown in Figure 3. The concentration of nitrate nitrogen in the randomly selected soil extracts varies greatly, ranging from 0.1-3.7 mg/L, which is highly representative. The correlation coefficient of the two methods is R=0.986, which shows that the correlation between the two methods is good, and the tedious distillation method can be replaced by ultraviolet spectrophotometry for the determination of soil nitrate nitrogen content.
5)取剩下的24个土壤浸提液,按照上述3)-4)步骤所述,使用两种方法对其硝态氮浓度进行测定,并将紫外分光光度法测定结果按照公式y=1.021x-0.223校正,所得结果与蒸馏法测定结果进行比对,结果如图4所示。结果表明两种方法相关性极好,特别是浓度很低的样品,测定结果依然很吻合,说明操作简单的紫外分光光度法完全可以取代操作繁琐的蒸馏法,成为测定土壤硝态氮的重要方法。5) Take the remaining 24 soil extracts, according to the above-mentioned 3)-4) steps, use two methods to measure its nitrate nitrogen concentration, and measure the results by ultraviolet spectrophotometry according to the formula y=1.021 x-0.223 correction, the obtained result is compared with the distillation method measurement result, and the result is shown in Figure 4. The results show that the correlation between the two methods is very good, especially for samples with very low concentrations, the measurement results are still very consistent, indicating that the simple operation of ultraviolet spectrophotometry can completely replace the cumbersome distillation method and become an important method for the determination of soil nitrate nitrogen .
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