CN107478734B - Ion chromatography detection method for simultaneously measuring sulfate radicals and sulfite radicals in desulfurized seawater - Google Patents
Ion chromatography detection method for simultaneously measuring sulfate radicals and sulfite radicals in desulfurized seawater Download PDFInfo
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- 238000001514 detection method Methods 0.000 title claims abstract description 46
- 239000013535 sea water Substances 0.000 title claims abstract description 28
- 238000004255 ion exchange chromatography Methods 0.000 title claims abstract description 12
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- 150000002500 ions Chemical class 0.000 claims abstract description 27
- LSNNMFCWUKXFEE-UHFFFAOYSA-L sulfite Chemical compound [O-]S([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-L 0.000 claims abstract description 26
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 21
- 238000012360 testing method Methods 0.000 claims abstract description 12
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- ZGTMUACCHSMWAC-UHFFFAOYSA-L EDTA disodium salt (anhydrous) Chemical compound [Na+].[Na+].OC(=O)CN(CC([O-])=O)CCN(CC(O)=O)CC([O-])=O ZGTMUACCHSMWAC-UHFFFAOYSA-L 0.000 claims abstract 2
- 239000000243 solution Substances 0.000 claims description 24
- GEHJYWRUCIMESM-UHFFFAOYSA-L sodium sulfite Chemical compound [Na+].[Na+].[O-]S([O-])=O GEHJYWRUCIMESM-UHFFFAOYSA-L 0.000 claims description 10
- 239000012528 membrane Substances 0.000 claims description 9
- 239000012086 standard solution Substances 0.000 claims description 9
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 8
- 239000011259 mixed solution Substances 0.000 claims description 7
- LSNNMFCWUKXFEE-UHFFFAOYSA-M Bisulfite Chemical compound OS([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-M 0.000 claims description 6
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 claims description 6
- 239000003480 eluent Substances 0.000 claims description 6
- 238000007865 diluting Methods 0.000 claims description 5
- 238000001914 filtration Methods 0.000 claims description 5
- 150000001450 anions Chemical group 0.000 claims description 4
- 229910000029 sodium carbonate Inorganic materials 0.000 claims description 4
- 229910052938 sodium sulfate Inorganic materials 0.000 claims description 4
- 235000011152 sodium sulphate Nutrition 0.000 claims description 4
- 235000010265 sodium sulphite Nutrition 0.000 claims description 4
- 239000007787 solid Substances 0.000 claims description 4
- 239000007788 liquid Substances 0.000 claims description 3
- 238000005303 weighing Methods 0.000 claims description 3
- BQCIDUSAKPWEOX-UHFFFAOYSA-N 1,1-Difluoroethene Chemical compound FC(F)=C BQCIDUSAKPWEOX-UHFFFAOYSA-N 0.000 claims description 2
- 239000011347 resin Substances 0.000 claims description 2
- 229920005989 resin Polymers 0.000 claims description 2
- -1 magnesium cations Chemical class 0.000 abstract description 30
- 238000000034 method Methods 0.000 abstract description 24
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 abstract description 23
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 abstract description 9
- 239000011575 calcium Substances 0.000 abstract description 9
- 238000006477 desulfuration reaction Methods 0.000 abstract description 8
- 230000023556 desulfurization Effects 0.000 abstract description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 abstract description 7
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 abstract description 6
- 229910001424 calcium ion Inorganic materials 0.000 abstract description 6
- 229910001425 magnesium ion Inorganic materials 0.000 abstract description 6
- 229910052791 calcium Inorganic materials 0.000 abstract description 4
- 239000011777 magnesium Substances 0.000 abstract description 4
- 229910052749 magnesium Inorganic materials 0.000 abstract description 4
- 238000011002 quantification Methods 0.000 abstract description 3
- 238000002203 pretreatment Methods 0.000 abstract description 2
- 230000035945 sensitivity Effects 0.000 abstract description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 abstract 1
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 10
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 7
- 230000003647 oxidation Effects 0.000 description 6
- 238000007254 oxidation reaction Methods 0.000 description 6
- 238000011084 recovery Methods 0.000 description 6
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 239000003546 flue gas Substances 0.000 description 3
- 238000004458 analytical method Methods 0.000 description 2
- 229940101006 anhydrous sodium sulfite Drugs 0.000 description 2
- 239000012490 blank solution Substances 0.000 description 2
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 238000004587 chromatography analysis Methods 0.000 description 2
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- 229960001484 edetic acid Drugs 0.000 description 2
- 238000010828 elution Methods 0.000 description 2
- 230000002401 inhibitory effect Effects 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 229940001482 sodium sulfite Drugs 0.000 description 2
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 description 2
- 229910052815 sulfur oxide Inorganic materials 0.000 description 2
- 229910021642 ultra pure water Inorganic materials 0.000 description 2
- 239000012498 ultrapure water Substances 0.000 description 2
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000005571 anion exchange chromatography Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- GBAOBIBJACZTNA-UHFFFAOYSA-L calcium sulfite Chemical compound [Ca+2].[O-]S([O-])=O GBAOBIBJACZTNA-UHFFFAOYSA-L 0.000 description 1
- 235000010261 calcium sulphite Nutrition 0.000 description 1
- 125000002091 cationic group Chemical group 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 238000012937 correction Methods 0.000 description 1
- 238000010612 desalination reaction Methods 0.000 description 1
- YNLAOSYQHBDIKW-UHFFFAOYSA-M diethylaluminium chloride Chemical compound CC[Al](Cl)CC YNLAOSYQHBDIKW-UHFFFAOYSA-M 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 239000000834 fixative Substances 0.000 description 1
- 239000008098 formaldehyde solution Substances 0.000 description 1
- 239000003112 inhibitor Substances 0.000 description 1
- 238000012417 linear regression Methods 0.000 description 1
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 description 1
- 239000000347 magnesium hydroxide Substances 0.000 description 1
- 229910001862 magnesium hydroxide Inorganic materials 0.000 description 1
- JESHZQPNPCJVNG-UHFFFAOYSA-L magnesium;sulfite Chemical compound [Mg+2].[O-]S([O-])=O JESHZQPNPCJVNG-UHFFFAOYSA-L 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000003918 potentiometric titration Methods 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 239000011550 stock solution Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- NIAGBSSWEZDNMT-UHFFFAOYSA-M tetraoxidosulfate(.1-) Chemical compound [O]S([O-])(=O)=O NIAGBSSWEZDNMT-UHFFFAOYSA-M 0.000 description 1
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- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/02—Column chromatography
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/02—Column chromatography
- G01N30/04—Preparation or injection of sample to be analysed
- G01N30/06—Preparation
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- Health & Medical Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Biochemistry (AREA)
- General Health & Medical Sciences (AREA)
- General Physics & Mathematics (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
Abstract
本发明为一种脱硫海水中同时测定硫酸根和亚硫酸根的离子色谱检测方法。本发明优化了色谱条件，通过特定浓度的甲醛、氢氧化钠、乙二胺四乙酸二钠的溶液组合，实现了对样品的预处理，调节特定离子色谱检测参数实现对亚硫酸根和硫酸根的基线分离，即提出了新的样品前处理方法，在实现硫酸根离子和亚硫酸根离子同时准确定量的基础上，去除钙、镁离子对测试的影响。结果表明，硫酸根检出限为0.04mg/L，亚硫酸根检出限为0.03mg/L。本方法检测快速、灵敏度高、准确性好，适合于海水脱硫体系中的硫酸根和亚硫酸根离子的同时定量检测，也适用于存在钙、镁阳离子的水质中硫酸根和亚硫酸根单一离子的检测。
The invention relates to an ion chromatography detection method for simultaneously measuring sulfate and sulfite in desulfurized seawater. The method optimizes the chromatographic conditions, realizes the pretreatment of the sample through the solution combination of formaldehyde, sodium hydroxide and disodium EDTA in specific concentrations, and adjusts the detection parameters of specific ion chromatography to realize the detection of sulfite and sulfate. The baseline separation of , that is, a new sample pretreatment method is proposed to remove the influence of calcium and magnesium ions on the test on the basis of realizing the simultaneous and accurate quantification of sulfate ions and sulfite ions. The results showed that the detection limit of sulfate was 0.04 mg/L, and the detection limit of sulfite was 0.03 mg/L. The method has rapid detection, high sensitivity and good accuracy, and is suitable for simultaneous quantitative detection of sulfate and sulfite ions in seawater desulfurization systems, and is also suitable for sulfate and sulfite single ions in water with calcium and magnesium cations. detection.
Description
Technical Field
The invention belongs to the technical field of chemical analysis, and particularly relates to a detection method for simultaneously determining sulfate radicals and sulfite radicals in a water body containing calcium ions and magnesium ions, in particular to an ion chromatography detection method for simultaneously determining sulfate radicals and sulfite radicals in desulfurized seawater.
Background
The seawater flue gas desulfurization method is the preferred desulfurization method for coal-fired power plants in coastal areas, sulfur in the fire coal is converted into sulfur oxides after combustion, and sulfate and sulfite are generated after the sulfur oxides are dissolved in seawater. The solubility (wt%, 25 ℃) of calcium sulfite in water was 0.005g, the solubility (wt%, 25 ℃) of calcium sulfate was 0.2g, and the solubility (wt%, 25 ℃) of magnesium sulfite was 0.6 g. Therefore, trace sulfate radicals and sulfite radicals in the desulfurized seawater are simultaneously and accurately quantified, so that the thorough degree of seawater desulfurization can be monitored, and the significance of the combination of flue gas desulfurization and seawater desalination and decalcification technology can be understood.
The detection of sulfite comprises a pararosaniline hydrochloride method, a distillation method, an iodometry method and the like, the detection limit of the methods is 1mg/L, and sulfite ions with lower concentration in seawater are difficult to detect; the arbitration detection of sulfate ions adopts a gravimetric method, the method has long operation time, the detection limit of water quality detection is 2.5mg/L, the detection limits of an EDTA volumetric method and a potentiometric titration method are both more than 1mg/L, and the method is difficult to realize the analysis of sulfate ions with lower concentration.
In a desulfurization seawater system, sulfate ions and sulfite ions exist simultaneously, and sulfite is easily oxidized into sulfate in an acid solution; the existence of calcium and magnesium ions enables the mobile phase of a carbonate system to react with each other to form precipitates to block a chromatographic column, and an appropriate method needs to be selected to remove the influence of the calcium and magnesium ions; in addition, sulfate and sulfite have the same nuclear charge number and similar hydrated ion radius, so that baseline separation is difficult to realize in ion chromatography detection, and difficulty is brought to ion chromatography for simultaneously measuring sulfate and sulfite in the desulfurized seawater.
Disclosure of Invention
The invention aims to overcome the defects in the prior art: the method can only analyze and quantify single ions, has high detection limit, is difficult to analyze ions with the concentration lower than 1mg/L, and is difficult to respectively and simultaneously quantify two ions by the existing detection method under the condition that the two ions exist simultaneously. The invention provides an ion chromatography detection method for simultaneously measuring sulfate radicals and sulfite radicals in desulfurized seawater. The method realizes the pretreatment of the sample by the combination of solutions of formaldehyde, sodium hydroxide and disodium ethylene diamine tetraacetate with specific concentrations; and regulating specific ion chromatographic detection parameters to realize baseline separation of sulfite and sulfate radicals. On the basis of realizing the simultaneous accurate quantification of sulfate ions and sulfite ions, the invention also provides a novel sample pretreatment method to remove the influence of calcium and magnesium ions on the test, simultaneously inhibits the oxidation of sulfite, and solves the defects of the existing detection method.
The technical scheme of the invention is as follows:
an ion chromatography detection method for simultaneously measuring sulfate radicals and sulfite radicals in desulfurized seawater comprises the following steps:
a. drawing a sulfate ion and sulfite ion mixed standard curve:
weighing sodium sulfite and sodium sulfate solids, dissolving and diluting the sodium sulfite and sodium sulfate solids by using a pretreatment solution to prepare 5-12 groups of mixed standard solutions with the same sulfate radical and sulfite radical concentration and gradually increased concentration, wherein the ion concentration is 5.00-100.00 mg/L; filtering the mixed standard solution by an organic microporous filter membrane respectively, and testing by an instrument to obtain respective peak areas A (mu S & min) of sulfate ions and sulfite ions in the mixed solution; and (3) plotting by taking the ion concentration as an abscissa and taking the peak area as an ordinate, and obtaining two univariate linear equations of the ion concentration and the related peak area according to the plot: where a is the integral of conductance over time in μ S · min, C is the concentration in mg/L, and k and b are dimensionless constants, i.e. the univariate linear equation for the sulfate ion concentration and its peak area is: c1 ═ k1 · a1+ b 1; the unary linear equation of the concentration of sulfite ions and the peak area thereof is as follows: c2 ═ k2 · a2+ b 2;
the test instrument is specifically an anion chromatography detection system.
The test instrument is preferably a quantitative loop volume of 25 mu L, a conductivity detector, an ASRS4mm anion suppressor and an IonPacAS9-HC separation column, and the test instrument is preferably under the working conditions of an eluent solution of 9mmol/L sodium carbonate and an eluent flow rate of 1.2 mL/min.
The pretreatment solution is a solution containing 0.5 mass percent of formaldehyde, 1 mole percent of sodium hydroxide and 0.5 mole percent of disodium ethylene diamine tetraacetate;
the number of the series of mixed standard solutions is preferably six, wherein the concentrations of sulfate radicals and sulfite radicals are 5.00mg/L, 10.00mg/L, 20.00mg/L, 50.00mg/L, 80.00mg/L and 100.00mg/L respectively;
taking the pretreatment solution with the same composition as a blank solution to be detected; k1 and b1, k2 and b2 are obtained by regression of actual instrument test.
Wherein, the concentration detection range C1 is 0.04-100.00 mg/L, and C2 is 0.03-100.00 mg/L;
the organic microporous filter membrane is a vinylidene fluoride resin membrane, and the pore diameter is preferably 0.22 μm.
b. Determining the concentration of sulfate ions and sulfite ions in the desulfurized seawater to be detected:
filtering the liquid to be measured through an organic microporous filter membrane, measuring the peak areas of sulfate ions and sulfite ions by adopting the same instrument in the step of drawing a mixed standard curve of the sulfate ions and the sulfite ions, and then substituting the peak areas into the linear equation obtained in the step a, wherein the unitary linear equation of the concentration of the sulfate ions and the peak areas thereof is as follows: c1 ═ k1 · a1+ b 1; the unary linear equation of the concentration of sulfite ions and the peak area thereof is as follows: c2 ═ k2 · a2+ b 2; and calculating the concentration of the ion according to the measured peak area A and the dimensionless constants k and b.
The invention has the substantive characteristics that:
in the invention, when the sulfite is pretreated, the influence of pH on the existence mode of the sulfite in the solution and the influence of pH on the oxidation rate of the sulfite are preferably considered, the pH is adjusted to 10 to eliminate the bisulfite easy to be oxidized, and the reducing agent formaldehyde with specific concentration is added on the basis, thereby achieving the purpose of better inhibiting the oxidation of the sulfite. And finally, selecting a method for adjusting the pH to 10 and treating an ethylene diamine tetraacetic acid solution to fix calcium and magnesium ions by screening the cationic fixative. Through selecting proper instrument parameters, the treated sample is analyzed, and the detection of sulfate ions and sulfite ions is not adversely affected by the EDTA ions.
The invention has the beneficial effects
The invention utilizes the oxidation rate property of sulfite in the solution to control the pH of the solution and simultaneously uses 0.5 percent formaldehyde solution as an oxidation inhibitor to effectively prevent sulfite ions from being oxidized. The interference of calcium and magnesium cations on ion chromatography detection is effectively fixed by innovatively adopting an ethylene diamine tetraacetic acid solution and a method for adjusting pH. The method is suitable for simultaneously and quantitatively detecting sulfate ions and sulfite ions in a seawater desulfurization system, and is also suitable for detecting single ions of the sulfate ions and the sulfite ions in water with calcium and magnesium cations.
The invention realizes the simultaneous and accurate quantification of sulfate ions and sulfite ions by using the ion chromatography, and solves the problem that the existing detection method has no suitable detection method under the condition that two ions exist at the same time and the concentration of the ions is low (lower than 1 mg/L). In the invention, the detection limit of sulfate radicals is 0.04mg/L, which is lower than 2.5mg/L of the prior optimal water quality detection method; the detection limit of the sulfite is 0.03mg/L, which is lower than 1mg/L of the prior method.
Drawings
FIG. 1 is a standard curve for sulfate ion and sulfite ion tests.
FIG. 2 shows the detection results of the desulfurized seawater sample.
Detailed Description
The present solution is further illustrated by the following specific examples.
Example 1
a. Drawing a sulfate ion and sulfite ion mixed standard curve, accurately weighing 1.5741g of anhydrous sodium sulfite and 1.4785g of anhydrous sodium sulfate superior pure reagent in the same beaker, diluting the anhydrous sodium sulfite and anhydrous sodium sulfate superior pure reagent to a 1000ml volumetric flask by using a mixed solution, and preparing a mixed standard stock solution; continuously using the mixed solution to dilute step by step to prepare a series of mixed standard solutions with the concentrations of sulfate radical and sulfite radical of 5.00mg/L, 10.00mg/L, 20.00mg/L, 50.00mg/L, 80.00mg/L and 100.00mg/L, drawing a sulfate radical ion and sulfite radical ion test standard curve by using the relation of anion concentration C (mg/L) in the prepared standard solution to ion chromatographic characteristic peak area A (mu S.min) under the working conditions of the elution solution with the parameters of 9mmol/L sodium carbonate solution, the elution solution flow rate of 1.2mL/min and the IonPACA 9-HC separation column, and referring to the attached figure 1, wherein the figure 1 shows that the concentrations in the detected concentration range are 5.00mg/L, 10.00mg/L, 20.00mg/L, 50.And the ion concentration and the integral area of the corresponding ion characteristic peak are in a linear relation, and the obtained linear regression equation is as follows: c (SO)4 2-) 28.4171a +0.0042 and C (SO)3 2-) 13.7005a + 0.0031; according to the signal-to-noise ratio of 3 times, the detection limit of sulfate ions is 0.04mg/L, and the detection limit of sulfite ions is 0.03 mg/L; by detecting the sample, the integral area A of the characteristic peak conductance of sulfite and sulfate ions to time can be directly obtained, and the concentration of the corresponding ions can be calculated by directly reading the integral area and substituting the integral area into the linear equation of the corresponding ions; wherein the solvent of the mixed solution is ultrapure water, the solutes are formaldehyde and sodium hydroxide, the mass percentage concentration of the formaldehyde in the mixed solution is 0.5%, the molar percentage concentration of the sodium hydroxide is 0.5%, and the molar percentage concentration of the disodium ethylene diamine tetraacetate is 0.5%;
TABLE 1 customized ion Standard series to be tested
b. Pretreating the desulfurized Schleicher artificial seawater, inhibiting sulfite oxidation, fixing calcium and magnesium cations, transferring 1mL of desulfurized seawater to be detected, diluting the desulfurized seawater to be detected to be 100mL by using a mixed solution of 0.5% by mass of formaldehyde, 1% by mole of sodium hydroxide solution and 0.5% by mole of disodium ethylenediamine tetraacetate, filtering the diluted solution by using a 0.20-micrometer water-based microporous filter membrane, and removing calcium hydroxide and magnesium hydroxide precipitates to prepare a liquid to be detected; synchronously preparing blank solution to be detected by using ultrapure water;
c. performing ion chromatographic analysis on the solution to be detected, performing ion chromatographic analysis on the desulfurized seawater pretreated in the step b, referring to the attached drawing 2, wherein the eluent is 9mmol/L sodium carbonate solution, the flow rate of the eluent is 1.2mL/min, the volume of a quantitative ring is 25 mu L, and the integral area of the characteristic peak of the desulfurized seawater after blank correction of sulfate ions and sulfite ions is measured; the characteristic peak position of sulfite is 15.067min, the concentration is 20.88mg/L, the characteristic peak position of sulfate is 17.217min, and the concentration is 4.74 mg/L;
the applicable detection concentration of the ions related to the scheme is respectively as follows: the concentration of sulfite is more than 0.03mg/L of detection limit concentration, the concentration of sulfate is more than 0.04mg/L of detection limit concentration, and the error can be kept within 1% by gradually diluting to the concentration range of a standard curve in the solubility range of sulfite and sulfate.
Example 2
The precision, accuracy and recovery rate of the detection method are tested.
The accuracy and precision of the method are confirmed by the standard addition recovery experiment and the precision experiment of the sample.
In the recovery experiment, after a certain amount of sulfate radical and sulfite radical ion standard solution is added into the desulfurized Schleicher artificial seawater, the sample standard addition recovery rate after treatment is detected according to the method, and the test result is shown in Table 2.
Table 2 sulfate and sulfite ion precision and standard recovery test results (n ═ 3)
The method is used for simultaneously and quantitatively detecting sulfate radicals and sulfite ions in the desulfurized seawater, the linearity is good in the concentration range of 5.00-100.00 mg/L, the correlation coefficient is above 0.999, the standard recovery rate range of the sulfate radicals and the sulfite ions is 96.5-104.3%, and the RSD is 0.3-1.9%. The detection limit of sulfite is 0.03mg/L, and the detection limit of sulfate is 0.04 mg/L. The method has the advantages of rapid detection, high sensitivity and good accuracy, and provides technical support for the research of the seawater flue gas desulfurization technology.
The invention is not the best known technology.
Claims (1)
1. An ion chromatography detection method for simultaneously measuring sulfate radicals and sulfite radicals in desulfurized seawater is characterized by comprising the following steps:
a. drawing a sulfate ion and sulfite ion mixed standard curve:
weighing sodium sulfite and sodium sulfate solids, dissolving and diluting the sodium sulfite and sodium sulfate solids by using a pretreatment solution to prepare 5-12 groups of mixed standard solutions with the same sulfate radical and sulfite radical concentration and gradually increased concentration, wherein the ion concentration is 5.00-100.00 mg/L; filtering the mixed standard solution by an organic microporous filter membrane respectively, and testing by an instrument to obtain respective peak areas A of sulfate ions and sulfite ions in the mixed solution; and (3) plotting by taking the ion concentration as an abscissa and taking the peak area as an ordinate, and obtaining two univariate linear equations of the ion concentration and the related peak area according to the plot: c = k · a + b, where a is the integral of conductance over time in μ S · min, C is the concentration in mg/L, k and b are dimensionless constants, i.e. the unitary linear equation for sulfate ion concentration and its peak area is: c1= k1 · a1+ b 1; the unary linear equation of the concentration of sulfite ions and the peak area thereof is as follows: c2= k2 · a2+ b 2;
b. determining the concentration of sulfate ions and sulfite ions in the desulfurized seawater to be detected:
filtering the liquid to be measured through an organic microporous filter membrane, measuring the peak areas of sulfate ions and sulfite ions by adopting the same instrument in the step of drawing a mixed standard curve of the sulfate ions and the sulfite ions, and then substituting the peak areas into the linear equation obtained in the step a, wherein the unitary linear equation of the concentration of the sulfate ions and the peak areas thereof is as follows: c1= k1 · a1+ b 1; the unary linear equation of the concentration of sulfite ions and the peak area thereof is as follows: c2= k2 · a2+ b 2; according to the measured peak area A and the dimensionless constants k and b, calculating to obtain the concentration of the ion;
the instrument is an anion chromatographic detection system and comprises a quantitative ring with the volume of 25 mu L, a conductivity detector, an ASRS4mm anion suppressor and an IonPac AS9-HC separation column, wherein the eluent is 9mmol/L sodium carbonate solution, and the flow rate of the eluent is 1.2 mL/min;
the pretreatment solution is a solution containing 0.5% by mass of formaldehyde, 1% by mole of sodium hydroxide and 0.5% by mole of disodium ethylenediaminetetraacetate;
the number of the series of mixed standard solutions is six, wherein the concentrations of sulfate radicals and sulfite radicals are 5.00mg/L, 10.00mg/L, 20.00mg/L, 50.00mg/L, 80.00mg/L and 100.00mg/L respectively;
the concentration range is C1= 0.04-100.00 mg/L, C2= 0.03-100.00 mg/L;
the organic microporous filter membrane is a vinylidene fluoride resin membrane with the aperture of 0.22 mu m.
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