CN104820030B - A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water - Google Patents

A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water Download PDF

Info

Publication number
CN104820030B
CN104820030B CN201510200277.3A CN201510200277A CN104820030B CN 104820030 B CN104820030 B CN 104820030B CN 201510200277 A CN201510200277 A CN 201510200277A CN 104820030 B CN104820030 B CN 104820030B
Authority
CN
China
Prior art keywords
kinds
phthalic acid
acid esters
drinking water
sample
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201510200277.3A
Other languages
Chinese (zh)
Other versions
CN104820030A (en
Inventor
张志朋
彭靖恺
杜娟
宋韶华
黎泳珊
李常丽
邹志勇
黄跃武
易春盛
计晓梅
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Guilin City's Environmental Monitoring Central Station
Original Assignee
Guilin City's Environmental Monitoring Central Station
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Guilin City's Environmental Monitoring Central Station filed Critical Guilin City's Environmental Monitoring Central Station
Priority to CN201510200277.3A priority Critical patent/CN104820030B/en
Publication of CN104820030A publication Critical patent/CN104820030A/en
Application granted granted Critical
Publication of CN104820030B publication Critical patent/CN104820030B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Other Investigation Or Analysis Of Materials By Electrical Means (AREA)

Abstract

The invention discloses a kind of method that LC-MS detects six kinds of phthalic acid esters in drinking water, belongs to drinking water detection technique field.Which comprises the steps:(1) guard column is installed additional;(2) condition determination and mode;(3) Criterion working curve;(4) drinking water detection to be measured.The detection method of the present invention; without the need for carrying out pre-treatment to sample; energy direct injected; so as to rapidly to drinking water in six kinds of phthalic acid esters (DMP, DEP, DBP, BBP, DEHP and DNOP) carry out qualitative and quantitative analysis; have few simple to operation, sampling quantity, low cost, favorable reproducibility, stability strong; it is applicable not only to surroundings monitoring, and the rapid screening suitable for pollutant emergent accident.

Description

A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water
Technical field
The present invention relates to a kind of detection method, more particularly to a kind of simple, quick to six kinds of phthalic acids in drinking water The qualitative and quantitative detection method of ester, belongs to drinking water detection technique field.
Background technology
Phthalate compound (Phthalic acid esters, PAEs) is the important endocrine disruption of a class Thing.Trace PAEs can be enriched with water body, soil, animals and plants, be difficult in the environment degrade, the internal system of human body is caused Interference, directly affects the metabolism of human body, and plasticiser phthalic acid two (2- ethylhexyls) ester (DEHP) toxicity compares trimerization Cyanamide is big 20 times.Research shows that plasticiser can also increase liver kidney burden, cause chronic injury to immune system, digestive system, very To causing liver cancer.In white wine disturbance in 2012, dibutyl phthalate (DBP) the highest detection value being detected in sample reaches 1.04mg/kg.With a large amount of uses of plastic packing product, PAEs is remained and the pollution caused in transition process in the environment Increasingly seriously, part water body and soil also suffer that PAEs pollutes.To the analysis of phthalate compound, detection in environment The new problem faced with the control person that has been environmental monitoring work and new challenge.
EPA is by repefral (DMP), diethyl phthalate (DEP), phthalic acid two Butyl ester (DBP), butyl benzyl phthalate (BBP) phthalic acid two (2- ethylhexyls) ester (DEHP) and adjacent benzene two Formic acid di-n-octyl (DNOP) is classified as priority pollutants.Wherein, DMP, DBP and DNOP are also listed in Environment Priority by China Pollutant blacklist.
At present, the instrument analytical method of PAEs is mainly using gas-chromatography (GC) and liquid chromatogram (LC) method, and sample Pre-treatment is the key for determining PAEs detection sensitivities.The sample-pretreating method of PAEs is different with sample substrate and presence is poor Different.Liquid-liquid extraction method (LLE) is the conventional pre-treating methods of PAEs in the simple matrix liquid sample such as water, white wine, beverage, Chang Cai It is extractant with n-hexane and dichloromethane.Its advantage be simple to operate, but there is also organic solvent consumption big, to environment Cause secondary pollution, time-consuming the longer, rate of recovery is relatively low, emulsion is serious, be difficult to realization the deficiency such as is automatically brought into operation.In recent years, Solid-phase Microextraction (SPME), dispersive liquid-liquid microextraction method (DLLME), dispersive liquid-liquid microextraction-floating solvent cures method (DLLME-SFO), emerging extraction and the purification techniques such as cloud point extraction method (CPE), due to fast etc. with easy to operate, rate of extraction Feature, the extraction and purification of the PAEs being also applied in the samples such as water, soil, but its sample pre-treatments are generally required with reference to super Sound assists extraction (UAE), Microwave assisted extraction method (MAE) or solid phase extraction (SPE).Wherein, solid phase extraction (SPE) tool Have that solvent load is few, enrichment and good purification, simple to operate the features such as, but the bioaccumulation efficiency of different batches adsorbent is different, The repeatability of analysis result is influenced whether, if irreversible absorption occurs can cause the loss of object in sample, sometimes even The phenomenons such as superficial degradation reaction, adsorbent blocking duct can occur.Further, since various PAEs have height phase in structure Like property, and content generally in the sample is relatively low, the qualitative and poor AAS of quantitation capabilities substantially without practical value, It is not suitable for the measure of PAEs in environmental sample.
In consideration of it, being necessary that research is a kind of without the need for carrying out pre-treatment, energy fast qualitative and quantitative determination drinking water to sample In six kinds of phthalic acid esters new detection method.LC-MS (HPLC-MS) technology is with high performance liquid chromatography as separating Means, a kind of separate analytical technique with mass spectrum as Identification Tools efficiently separate ability and mass spectrographic height with liquid chromatogram Sensitivity, extremely strong qualitative exclusive specificity.But at present, there is not yet HPLC-MS is used for six kinds of phthalic acid esters of drinking water The report of qualitative and quantitative analysis.Therefore, set up six kinds of phthalic acid ester Qualitative and quantitative analysis methods of efficient drinking water to use Six kinds of phthalic acid esters in monitoring drinking water are significant.
Content of the invention
Present invention aim to address the deficiencies in the prior art, there is provided six kinds of adjacent benzene in a kind of LC-MS detection drinking water The method of dicarboxylic acid esters.The detection method of the present invention, without the need for carrying out pre-treatment to sample, energy direct injected, so as to rapidly right Six kinds of phthalic acid esters (DMP, DEP, DBP, BBP, DEHP and DNOP) in drinking water carry out qualitative and quantitative analysis.
The technical scheme that the present invention solves above-mentioned technical problem is as follows:Six kinds of adjacent benzene in a kind of LC-MS detection drinking water The method of dicarboxylic acid esters, comprises the steps:
(1) guard column is installed additional:Install chromatographic column additional guard column;
(2) condition determination and mode:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, liquid phase is used Chromatogram-series connection quadrupole rod mass spectrum is measured, and instrument parameter condition is shown in Table 1, Selective reaction monitoring parent ion, daughter ion and collision Energy is shown in Table 2;
The mass spectrographic instrument parameter of 1 liquid chromatography-tandem level Four bar of table
2 Selective reaction monitoring parent ion of table, daughter ion and collision energy and scan mode
(3) Criterion working curve:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, respectively Standard liquid described in accurately drawing 25 μ l, is settled to 10mL respectively with pure water, respectively obtains 6 kinds of phthalic ester concentrations and be The standard solution of 0.5 μ g/mL;0,10,20,40,80,160,200,400,800,1600 μ l above-mentioned standards use is taken respectively Liquid, is settled to 10mL respectively with pure water, obtains the series standard liquid of 0,0.5,1,2,4,8,10,20,40,80 μ g/l, using step Suddenly experimental condition sample introduction listed by Tables 1 and 2 in (2), respectively obtains the peak area of 6 kinds of phthalic acid esters, then with peak area is Ordinate, concentration are abscissa, draw calibration curve respectively, respectively obtain the calibration curve of 6 kinds of phthalic acid esters, Ran Houfen Linear regression analysis is not carried out;
(4) drinking water detection to be measured:Drinking Water Samples to be measured are taken, using experimental condition listed by Tables 1 and 2 in step (2) Sample introduction, obtains the peak area of Drinking Water Samples to be measured, and then the peak area with above-mentioned Drinking Water Samples to be measured is brought into as ordinate The calibration curve of 6 kinds of phthalic acid esters of step (3) gained, obtain final product Drinking Water Samples to be measured 6 kinds of phthalic acid esters dense Angle value.
On the basis of above-mentioned technical proposal, the present invention can also do following improvement.
Further, step (1) method that installs additional that protects is:Connected using connecting tube in the front end of the chromatographic column Install guard column additional, the entrance connection injection port of the guard column, outlet connection chromatographic column, the two ends of the connecting tube have hollow Screw and sealing pressure ring.
Further, 2mL8mm standard mouth screw thread mouth sample bottles are adopted, during analysis sample during determination sample described in step (2) Only use bottle cap, the flow velocity be 0.2mL/min, the column temperature be 30 DEG C, the sample size be 5 μ L, the capillary voltage For 4000V, the atomization gas pressure is 40psi, and the atomization gas flow velocity is 10L/min, and the atomization gas temperature is 350 DEG C.
Further, described in step (3), pure water is plus alkali redistilled water, the preparation method of described plus alkali redistilled water For:Take 400mL brand-new distilled water to be put in cucurbit, add zeolite and 5 grams of NaOH, the uniform placement 1 hour of shaking to heat, Cast out 50mL front-end volatiles, take stage casing 250mL and collect 1 hour, obtain final product.
The invention has the beneficial effects as follows:
1., without the need for carrying out pre-treatment to sample, direct injected, with simple to operation, sampling for the detection method of the present invention Amount less, low cost, favorable reproducibility, strong stability the advantages of.
2. the detection method of the present invention significantly improves detection efficiency, and once experiment can be quickly and accurately to drinking water In six kinds of phthalic acid esters carry out qualitative and quantitative analysis, substantial saving in the working time of testing staff.
3. the detection method of the present invention adopts C18 chromatographic columns, LC-MS (HPLC-MS) technology, with higher sensitive Degree, detection limit are less than 0.6 μ g/L, it is sufficient to ensure the monitoring requirement of daily drunk water, and install additional before sample enters chromatographic column Guard column, plays a part of to purify sample, protection chromatographic column.
4. the blank water of the present invention is adopted plus alkali redistilled water, than ultra-pure water, deionized water, brand-new distilled water, color Spectrum pure water and acid adding redistilled water, the mass spectrum little, blank value of response are minimum, similar with the performance of chromatogram pure water, and cost is lower.
5. the detection method of the present invention has a extensive future, and is applicable not only to surroundings monitoring, and is applied to emergent The rapid screening of pollutant in accident.
Description of the drawings
Fig. 1 is mass spectrum multiple-reaction monitoring figure (MRM) of the repefral (DMP) of the present invention.
Fig. 2 is mass spectrum multiple-reaction monitoring figure (MRM) of the diethyl phthalate (DEP) of the present invention.
Fig. 3 is mass spectrum multiple-reaction monitoring figure (MRM) of the dibutyl phthalate (DBP) of the present invention.
Fig. 4 is mass spectrum multiple-reaction monitoring figure (MRM) of the butyl benzyl phthalate (BBP) of the present invention.
Fig. 5 is mass spectrum multiple-reaction monitoring figure (MRM) of the phthalic acid two (2- ethylhexyls) ester (DEHP) of the present invention.
Fig. 6 is mass spectrum multiple-reaction monitoring figure (MRM) of the dioctyl phthalate (DNOP) of the present invention.
Specific embodiment
The principle and feature of the present invention are described below in conjunction with accompanying drawing, example is served only for explaining the present invention, and Non- for limiting the scope of the present invention.
Embodiment 1
(1) guard column is installed additional:Guard column, protection column inlet connection sample introduction are installed in chromatographic column front end additional using connecting tube series connection Mouthful, outlet connection chromatographic column, there are hollow screw and sealing pressure ring in the two ends of connecting tube;
(2) condition determination and mode:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, liquid phase is used Chromatogram-series connection quadrupole rod mass spectrum is measured, and instrument parameter condition is shown in Table 3, Selective reaction monitoring parent ion, daughter ion and collision Energy is shown in Table 2;Using 2mL8mm standard mouth screw thread mouth sample bottles during the determination sample, only using bottle cap during analysis sample;
The mass spectrographic instrument parameter of 3 liquid chromatography-tandem level Four bar of table
2 Selective reaction monitoring parent ion of table, daughter ion and collision energy and scan mode
(3) Criterion working curve:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, respectively Standard liquid described in accurately drawing 25 μ l, is settled to 10mL respectively with pure water, respectively obtains 6 kinds of phthalic ester concentrations and be The standard solution of 0.5 μ g/mL;The pure water is plus alkali redistilled water that the preparation method of described plus alkali redistilled water is: Take 400mL brand-new distilled water to be put in cucurbit, add zeolite and 5 grams of NaOH, the uniform placement 1 hour of shaking to heat, house 50mL front-end volatiles are removed, stage casing 250mL is taken and is collected 1 hour, obtain final product;10,20,40,80,160,200,400,800,1600 are taken respectively μ l above-mentioned standards use liquid, are settled to 10mL respectively with pure water, obtain the series mark of 0.5,1,2,4,8,10,20,40,80 μ g/l Quasi- liquid, using table 3 in step (2) and experimental condition sample introduction listed by table 2, how anti-the mass spectrum for respectively obtaining 6 kinds of phthalic acid esters is Should monitor figure (MRM) (as shown in Figures 1 to 6) and peak area, then with peak area as ordinate, concentration as abscissa, paint respectively Calibration curve processed, respectively obtains the calibration curve of 6 kinds of phthalic acid esters, then carries out linear regression analysis respectively, linear system Number R>0.9900 can be used as calibration curve, as shown in table 4;
The calibration curve of 46 kinds of phthalic acid esters of table
The intercept and slope value of contrast standard curve, 6 kinds of phthalic acid esters are linearly good in 0~80 μ g/L concentration ranges Good, calibration curve meets quantitative calculating needs.
(4) detection limit is determined:20 blank water samples are taken, is entered using table 3 in step (2) and experimental condition listed by table 2 successively Sample, determines detection limit with the standard deviation of 6 kinds of phthalic acid ester peak areas.According to IUPAC (IUPAC) regulation to detection limit:The standard deviation of D.L=K'Sb/k, K'=3, wherein Sb for peak area, k is calibration curve Slope, the detection limit of 6 kinds of phthalic acid esters is respectively:Repefral (DMP) is 0.62 μ g/L, O-phthalic Diethyl phthalate (DEP) is 0.77 μ g/L, dibutyl phthalate (DBP) is 0.15 μ g/L, butyl benzyl phthalate (BBP) for 0.098 μ g/L, phthalic acid two (2- ethylhexyls) ester (DEHP) be 0.23 μ g/L, dioctyl phthalate (DNOP) it is 0.0086 μ g/L.According to《Water environment quality standard》(GB3838-2002) regulation:Two fourth of phthalic acid Ester (DBP) standard limited value is 3 μ g/L, phthalic acid two (2- ethylhexyls) ester standard limited value is 8 μ g/L, and remaining 4 kinds are not then Do standard and limit regulation.As can be seen here, in the method for the present invention, the detection limit of 6 kinds of phthalic acid esters is well below standard Specified in limit value, it is sufficient to ensure the environmental monitoring requirement of daily drunk water.Therefore, the method for the present invention can apply to concentrate The rapid screening of formula drinking water sources water phthalate pollutant.
(5) method precision and recovery of standard addition:Respectively 6 kinds of phthalic acid esters of preparation steps (2) gained 0.5,2, 8th, the series standard liquid of 4 concentration of 40 μ g/L, each 7 samples of each concentration, is respectively adopted in step (2) listed by Tables 1 and 2 Experimental condition sample introduction, examines or check the precision of method with sample peak area and the relative standard deviation for being calculated concentration.To blank Add the mixed standard solution of 6 kinds of phthalic acid esters in water sample, obtain the standard liquid after mark-on, for simulated environment water Sample, direct injection analysis.To concentration be 0.5,2,8,40 μ g/L mark-on after each 7 samples of standard liquid adopt step (2) Middle table 3 and experimental condition listed by table 2 are measured, and as a result show, 6 kinds of phthalic acid esters are in 0~80 μ g/L concentration ranges Method precision is good, the equal < 5% of quantitative result relative standard deviation.For quick analysis, the precision of the method reaches Arrive test request;In terms of recovery of standard addition, 4 kinds of concentration mark-on results of 6 kinds of phthalic acid esters are controlled 85~120% In the range of, can also meet test request.
(6) drinking water detection to be measured:Water factory of Qu Mou cities Drinking Water Samples 1, using the 2 listed examination of table 3 in step (2) and table Condition sample introduction is tested, the peak area of Drinking Water Samples to be measured is obtained, then with the peak area of above-mentioned Drinking Water Samples to be measured as vertical seat Mark, brings the calibration curve of 6 kinds of phthalic acid esters of step (3) gained into, obtains 6 kinds of phthalic acids of Drinking Water Samples to be measured The concentration of ester is respectively:Repefral (DMP) is 1.25 μ g/L, diethyl phthalate (DEP) is 1.48 μ g/ L, dibutyl phthalate are 0.29 μ g/L, butyl benzyl phthalate (BBP) is 0.37 μ g/L, phthalic acid two (2- ethylhexyls) ester (DEHP) is 0.15 μ g/L, dioctyl phthalate (DNOP) is 0.12 μ g/L.
Embodiment 2
(1) guard column is installed additional:Guard column, protection column inlet connection sample introduction are installed in chromatographic column front end additional using connecting tube series connection Mouthful, outlet connection chromatographic column, there are hollow screw and sealing pressure ring in the two ends of connecting tube;
(2) condition determination and mode:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, liquid phase is used Chromatogram-series connection quadrupole rod mass spectrum is measured, and instrument parameter condition is shown in Table 5, Selective reaction monitoring parent ion, daughter ion and collision Energy is shown in Table 2;Using 2mL8mm standard mouth screw thread mouth sample bottles during the determination sample, only using bottle cap during analysis sample;
The mass spectrographic instrument parameter of 5 liquid chromatography-tandem level Four bar of table
2 Selective reaction monitoring parent ion of table, daughter ion and collision energy and scan mode
(3) Criterion working curve:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, respectively Standard liquid described in accurately drawing 25 μ l, is settled to 10mL respectively with pure water, respectively obtains 6 kinds of phthalic ester concentrations and be The standard solution of 0.5 μ g/mL;The pure water is plus alkali redistilled water that the preparation method of described plus alkali redistilled water is: Take 400mL brand-new distilled water to be put in cucurbit, add zeolite and 5 grams of NaOH, the uniform placement 1 hour of shaking to heat, house 50mL front-end volatiles are removed, stage casing 250mL is taken and is collected 1 hour, obtain final product;10,20,40,80,160,200,400,800,1600 are taken respectively μ l above-mentioned standards use liquid, are settled to 10mL respectively with pure water, obtain the series mark of 0.5,1,2,4,8,10,20,40,80 μ g/l Quasi- liquid, using table 5 in step (2) and experimental condition sample introduction listed by table 2, how anti-the mass spectrum for respectively obtaining 6 kinds of phthalic acid esters is Should monitor figure (MRM) (as shown in Figures 1 to 6) and peak area, then with peak area as ordinate, concentration as abscissa, paint respectively Calibration curve processed, respectively obtains the calibration curve of 6 kinds of phthalic acid esters, then carries out linear regression analysis respectively, linear system Number R>0.9900 can be used as calibration curve, as shown in table 6;
The calibration curve of 66 kinds of phthalic acid esters of table
The intercept and slope value of contrast standard curve, 6 kinds of phthalic acid esters are linearly good in 0~80 μ g/L concentration ranges Good, calibration curve meets quantitative calculating needs.
(3) detection limit is determined:20 blank water samples are taken, is entered using table 5 in step (2) and experimental condition listed by table 2 successively Sample, determines detection limit with the standard deviation of 6 kinds of phthalic acid ester peak areas.According to IUPAC (IUPAC) regulation to detection limit:The standard deviation of D.L=K'Sb/k, K'=3, wherein Sb for peak area, k is calibration curve Slope, the detection limit of 6 kinds of phthalic acid esters is respectively:Repefral (DMP) is 0.54 μ g/L, O-phthalic Diethyl phthalate (DEP) is 0.59 μ g/L, dibutyl phthalate (DBP) is 0.11 μ g/L, butyl benzyl phthalate (BBP) for 0.061 μ g/L, phthalic acid two (2- ethylhexyls) ester (DEHP) be 0.15 μ g/L, dioctyl phthalate (DNOP) it is 0.0043 μ g/L.According to《Water environment quality standard》(GB3838-2002) regulation:Two fourth of phthalic acid Ester (DBP) standard limited value is 3 μ g/L, phthalic acid two (2- ethylhexyls) ester standard limited value is 8 μ g/L, and remaining 4 kinds are not then Do standard and limit regulation.As can be seen here, in the method for the present invention, the detection limit of 6 kinds of phthalic acid esters is well below standard Specified in limit value, it is sufficient to ensure the environmental monitoring requirement of daily drunk water.Therefore, the method for the present invention can apply to concentrate The rapid screening of formula drinking water sources water phthalate pollutant.
(4) method precision and recovery of standard addition:Respectively 6 kinds of phthalic acid esters of preparation steps (2) gained 0.5,2, 8th, the series standard liquid of 4 concentration of 40 μ g/L, each 7 samples of each concentration are respectively adopted in step (2) listed by table 5 and table 2 Experimental condition sample introduction, examines or check the precision of method with sample peak area and the relative standard deviation for being calculated concentration.To blank Add the mixed standard solution of 6 kinds of phthalic acid esters in water sample, obtain the standard liquid after mark-on, for simulated environment water Sample, direct injection analysis.To concentration be 0.5,2,8,40 μ g/L mark-on after each 7 samples of standard liquid adopt step (2) Experimental condition listed by middle Tables 1 and 2 is measured, and as a result shows, 6 kinds of phthalic acid esters are in 0~80 μ g/L concentration ranges Method precision is good, the equal < 5% of quantitative result relative standard deviation.For quick analysis, the precision of the method reaches Arrive test request;In terms of recovery of standard addition, 4 kinds of concentration mark-on results of 6 kinds of phthalic acid esters are controlled 85~120% In the range of, can also meet test request.
(5) drinking water detection to be measured:Water factory of Qu Mou cities Drinking Water Samples 2, using the 2 listed examination of table 5 in step (2) and table Condition sample introduction is tested, the peak area of Drinking Water Samples to be measured is obtained, then with the peak area of above-mentioned Drinking Water Samples to be measured as vertical seat Mark, brings the calibration curve of 6 kinds of phthalic acid esters of step (3) gained into, obtains 6 kinds of phthalic acids of Drinking Water Samples to be measured The concentration of ester is respectively:Repefral (DMP) is 1.22 μ g/L, diethyl phthalate (DEP) is 1.35 μ g/ L, dibutyl phthalate are 0.35 μ g/L, butyl benzyl phthalate (BBP) is 0.24 μ g/L, phthalic acid two (2- ethylhexyls) ester (DEHP) is 0.13 μ g/L, dioctyl phthalate (DNOP) is 0.085 μ g/L.
Embodiment 3
(1) guard column is installed additional:Guard column, protection column inlet connection sample introduction are installed in chromatographic column front end additional using connecting tube series connection Mouthful, outlet connection chromatographic column, there are hollow screw and sealing pressure ring in the two ends of connecting tube;
(2) condition determination and mode:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, liquid phase is used Chromatogram-series connection quadrupole rod mass spectrum is measured, and instrument parameter condition is shown in Table 7, Selective reaction monitoring parent ion, daughter ion and collision Energy is shown in Table 2;Using 2mL8mm standard mouth screw thread mouth sample bottles during the determination sample, only using bottle cap during analysis sample;
The mass spectrographic instrument parameter of 7 liquid chromatography-tandem level Four bar of table
2 Selective reaction monitoring parent ion of table, daughter ion and collision energy and scan mode
(3) Criterion working curve:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, respectively Standard liquid described in accurately drawing 25 μ l, is settled to 10mL respectively with pure water, respectively obtains 6 kinds of phthalic ester concentrations and be The standard solution of 0.5 μ g/mL;The pure water is plus alkali redistilled water that the preparation method of described plus alkali redistilled water is: Take 400mL brand-new distilled water to be put in cucurbit, add zeolite and 5 grams of NaOH, the uniform placement 1 hour of shaking to heat, house 50mL front-end volatiles are removed, stage casing 250mL is taken and is collected 1 hour, obtain final product;10,20,40,80,160,200,400,800,1600 are taken respectively μ l above-mentioned standards use liquid, are settled to 10mL respectively with pure water, obtain the series mark of 0.5,1,2,4,8,10,20,40,80 μ g/l Quasi- liquid, using table 7 in step (2) and experimental condition sample introduction listed by table 2, how anti-the mass spectrum for respectively obtaining 6 kinds of phthalic acid esters is Should monitor figure (MRM) (as shown in Figures 1 to 6) and peak area, then with peak area as ordinate, concentration as abscissa, paint respectively Calibration curve processed, respectively obtains the calibration curve of 6 kinds of phthalic acid esters, then carries out linear regression analysis respectively, linear system Number R>0.9900 can be used as calibration curve, as shown in table 8;
The calibration curve of 86 kinds of phthalic acid esters of table
The intercept and slope value of contrast standard curve, 6 kinds of phthalic acid esters are linearly good in 0~80 μ g/L concentration ranges Good, calibration curve meets quantitative calculating needs.
(4) detection limit is determined:20 blank water samples are taken, is entered using table 7 in step (2) and experimental condition listed by table 2 successively Sample, determines detection limit with the standard deviation of 6 kinds of phthalic acid ester peak areas.According to IUPAC (IUPAC) regulation to detection limit:The standard deviation of D.L=K'Sb/k, K'=3, wherein Sb for peak area, k is calibration curve Slope, the detection limit of 6 kinds of phthalic acid esters is respectively:Repefral (DMP) is 0.57 μ g/L, O-phthalic Diethyl phthalate (DEP) is 0.66 μ g/L, dibutyl phthalate (DBP) is 0.18 μ g/L, butyl benzyl phthalate (BBP) for 0.084 μ g/L, phthalic acid two (2- ethylhexyls) ester (DEHP) be 0.17 μ g/L, dioctyl phthalate (DNOP) it is 0.0064 μ g/L.According to《Water environment quality standard》(GB3838-2002) regulation:Two fourth of phthalic acid Ester (DBP) standard limited value is 3 μ g/L, phthalic acid two (2- ethylhexyls) ester standard limited value is 8 μ g/L, and remaining 4 kinds are not then Do standard and limit regulation.As can be seen here, in the method for the present invention, the detection limit of 6 kinds of phthalic acid esters is well below standard Specified in limit value, it is sufficient to ensure the environmental monitoring requirement of daily drunk water.Therefore, the method for the present invention can apply to concentrate The rapid screening of formula drinking water sources water phthalate pollutant.
(5) method precision and recovery of standard addition:Respectively 6 kinds of phthalic acid esters of preparation steps (2) gained 0.5,2, 8th, the series standard liquid of 4 concentration of 40 μ g/L, each 7 samples of each concentration are respectively adopted in step (2) listed by table 7 and table 2 Experimental condition sample introduction, examines or check the precision of method with sample peak area and the relative standard deviation for being calculated concentration.To blank Add the mixed standard solution of 6 kinds of phthalic acid esters in water sample, obtain the standard liquid after mark-on, for simulated environment water Sample, direct injection analysis.To concentration be 0.5,2,8,40 μ g/L mark-on after each 7 samples of standard liquid adopt step (2) Middle table 7 and experimental condition listed by table 2 are measured, and as a result show, 6 kinds of phthalic acid esters are in 0~80 μ g/L concentration ranges Method precision is good, the equal < 5% of quantitative result relative standard deviation.For quick analysis, the precision of the method reaches Arrive test request;In terms of recovery of standard addition, 4 kinds of concentration mark-on results of 6 kinds of phthalic acid esters are controlled 85~120% In the range of, can also meet test request.
(6) drinking water detection to be measured:Water factory of Qu Mou cities Drinking Water Samples 3, using the listed examination of Tables 1 and 2 in step (2) Condition sample introduction is tested, the peak area of Drinking Water Samples to be measured is obtained, then with the peak area of above-mentioned Drinking Water Samples to be measured as vertical seat Mark, brings the calibration curve of 6 kinds of phthalic acid esters of step (3) gained into, obtains 6 kinds of phthalic acids of Drinking Water Samples to be measured The concentration of ester is respectively:Repefral (DMP) is 1.30 μ g/L, diethyl phthalate (DEP) is 1.32 μ g/ L, dibutyl phthalate are 0.44 μ g/L, butyl benzyl phthalate (BBP) is 0.29 μ g/L, phthalic acid two (2- ethylhexyls) ester (DEHP) is 0.15 μ g/L, dioctyl phthalate (DNOP) is 0.091 μ g/L.
The foregoing is only presently preferred embodiments of the present invention, not in order to limit the present invention, all spirit in the present invention and Within principle, any modification, equivalent substitution and improvements that is made etc. should be included within the scope of the present invention.

Claims (3)

1. a kind of method that LC-MS detects six kinds of phthalic acid esters in drinking water, it is characterised in that comprise the steps:
(1) guard column is installed additional:Install chromatographic column additional guard column, the method that installs additional that protects is:Before the chromatographic column End installs guard column, the entrance connection injection port of the guard column, outlet connection chromatographic column, the connection additional using connecting tube series connection There are hollow screw and sealing pressure ring in the two ends of pipe;
(2) condition determination and mode:Take the standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL, with liquid chromatogram- Series connection quadrupole rod mass spectrum is measured, and instrument parameter condition is specially:Liquid phase chromatogram condition be chromatographic column C18 post, 2.1 × 50mm, 1.8 μm;Guard column C18 posts, 2.1 × 5mm, 1.8 μm;0.05% aqueous formic acid of mobile phase with the volume ratio of acetonitrile is 5:95;0.1~0.3mL/min of flow velocity, 20~40 DEG C of column temperature;2~8 μ L of sample size;Mass Spectrometry Conditions are ion gun ESI cations; Scan mode MRM;Monitoring mode multiple-reaction monitoring;3000~5000V of capillary voltage;Atomization gas 20~60psi of pressure;Atomization 5~15L/min of gas velocity;300~400 DEG C of atomization gas temperature;
Selective reaction monitoring parent ion, daughter ion and collision energy and scan mode are specially:Repefral, m/z1 217.2, fragmentor 76, CE 0, scan pattern MRM;Diethyl phthalate, m/z1 245.2, fragmentor 86, CE 0, scan pattern MRM;Dibutyl phthalate, m/z1 301.2, m/z2 245.2, fragmentor 98, CE 0/8, scan pattern MRM;Butyl benzyl phthalate, m/z1 335.2, m/z2 91.1, m/z3 65.2, fragmentor 92, CE 0/50/93, scan pattern MRM;Phthalic acid two (2- ethylhexyls) ester, m/z1 413.3, m/z2 301.3, m/ Z3 189.1, fragmentor 130, CE 0/13/17, scan pattern MRM;Di-n-octyl phthalate, m/z1 413.4, M/z2 301.4, fragmentor 130, CE 0/15, scan pattern MRM;
(3) Criterion working curve:The standard liquid that 6 kinds of phthalic ester concentrations are 200 μ g/mL is taken, respectively accurately Standard liquid described in 25 μ l is drawn, with adding alkali redistilled water to be settled to 10mL respectively, 6 kinds of phthalic acid esters is respectively obtained dense Degree is the standard solution of 0.5 μ g/mL;0,10,20,40,80,160,200,400,800,1600 μ l above-mentioned standards are taken respectively Using liquid, with adding alkali redistilled water to be settled to 10mL respectively, the series of 0,0.5,1,2,4,8,10,20,40,80 μ g/l is obtained Titer, using experimental condition sample introduction listed by Tables 1 and 2 in step (2), respectively obtains the peak area of 6 kinds of phthalic acid esters, Again with peak area as ordinate, concentration as abscissa, respectively draw calibration curve, respectively obtain the mark of 6 kinds of phthalic acid esters Directrix curve, then carries out linear regression analysis respectively;
(4) drinking water detection to be measured:Drinking Water Samples to be measured are taken, using experimental condition sample introduction listed by Tables 1 and 2 in step (2), The peak area of Drinking Water Samples to be measured is obtained, then the peak area with above-mentioned Drinking Water Samples to be measured brings step into as ordinate (3) calibration curve of 6 kinds of phthalic acid esters of gained, obtains final product the concentration value of 6 kinds of phthalic acid esters of Drinking Water Samples to be measured.
2. the method that a kind of LC-MS according to claim 1 detects six kinds of phthalic acid esters in drinking water, which is special Levy and be, using 2mL8mm standard mouth screw thread mouth sample bottles during determination sample described in step (2), only using bottle during analysis sample Lid, the flow velocity are 0.2mL/min, and the column temperature is 30 DEG C, and the sample size is 5 μ L, and the capillary voltage is 4000V, The atomization gas pressure is 40psi, and the atomization gas flow velocity is 10L/min, and the atomization gas temperature is 350 DEG C.
3. the method that a kind of LC-MS according to claim 1 detects six kinds of phthalic acid esters in drinking water, which is special Levy and be, the preparation method for adding alkali redistilled water described in step (3) is:Take 400mL brand-new distilled water to be put in cucurbit, Addition zeolite and 5 grams of NaOH, the uniform placement 1 hour of shaking are heated, and are cast out 50mL front-end volatiles, are taken stage casing 250mL collections 1 little When, obtain final product.
CN201510200277.3A 2015-04-24 2015-04-24 A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water Expired - Fee Related CN104820030B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510200277.3A CN104820030B (en) 2015-04-24 2015-04-24 A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510200277.3A CN104820030B (en) 2015-04-24 2015-04-24 A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water

Publications (2)

Publication Number Publication Date
CN104820030A CN104820030A (en) 2015-08-05
CN104820030B true CN104820030B (en) 2017-03-15

Family

ID=53730385

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510200277.3A Expired - Fee Related CN104820030B (en) 2015-04-24 2015-04-24 A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water

Country Status (1)

Country Link
CN (1) CN104820030B (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106124657B (en) * 2016-06-17 2018-09-28 苍南县宝丰印业有限公司 A kind of method that graphene/ionic liquid composite material detects phthalic acid ester in aqueous-based food analogies
CN108693279A (en) * 2018-08-08 2018-10-23 吉林省安全生产检测检验股份有限公司 Phthalic acid diformazan in liquid chromatography for measuring water quality(It is two fourths, two pungent)The detection method of ester
CN112903884B (en) * 2019-11-19 2022-07-12 中国科学院深圳先进技术研究院 Method for simultaneously detecting phthalate compounds and metabolites thereof and application thereof
CN110988189A (en) * 2019-12-23 2020-04-10 舟山市食品药品检验检测研究院 Method for rapidly determining phthalate plasticizer in beverage
CN115598263B (en) * 2022-11-25 2023-04-18 国科大杭州高等研究院 Method for simultaneously determining contents of organic phosphate and conversion product thereof

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7981680B2 (en) * 2008-11-11 2011-07-19 GM Global Technology Operations LLC Method for analyzing petroleum-based fuels and engine oils for biodiesel contamination
CN103267816B (en) * 2013-04-15 2015-07-29 江苏省环境监测中心 Measure the method for phthalate compound

Also Published As

Publication number Publication date
CN104820030A (en) 2015-08-05

Similar Documents

Publication Publication Date Title
CN104820030B (en) A kind of method of six kinds of phthalic acid esters in LC-MS detection drinking water
CN106872617B (en) Rapid extraction and LC-MS-MS detection method of benzimidazole and thiazole residual drugs in aquatic products
CN105334277B (en) Quick pretreatment method and detection method for grape wine farming residual analysis
CN102898566A (en) Preparation method of metal organic framework molecularly imprinted polymer used for enriching trace amounts of Metolcarb
CN106596780A (en) Method for detecting contents of various antibiotics in water by combined use of high pressure liquid chromatography and mass spectrum
CN106596751A (en) High performance liquid chromatography and electrospray ionizsation mass spectrometry detection method for chlorinated disinfection by-products including dichloroacetamide and trichloroacetamide
CN109459506B (en) Rapid sample pretreatment method for detecting polychlorinated biphenyl in tea
CN103175931A (en) Method for determining harmful aromatic amine by liquid chromatogram-tandem mass spectrometry
CN102062766B (en) Method for measuring nonyl phenol in cosmetic
CN104374857B (en) Flumetralim, butralin and the measuring method except the logical residual quantity of bud in a kind of tobacco
CN102539592A (en) Method for detecting content of VLCFAs (very long chain fatty acids) in body fluid
CN103353489B (en) Detection method for detecting isophorone diisocyanate by using gas chromatography-mass spectrometer
CN103808822A (en) LC-QTOF (Liquid Chromatography-Quadrupole Time Of Flight) analysis method for distinguishing resveratrol of different resources
CN104458973A (en) Online determination method suitable for zearalenone and metabolites of zearalenone
CN101782560A (en) Method for measuring patulin in apple juice
CN101776656A (en) Method for measuring patulin in fruit jam and vegetable paste
CN105784905B (en) Ochratoxin B Liquid Chromatography-Tandem Mass Spectrometry detection method in pet food
CN107328877A (en) A kind of method of N methyl diethanolamine contents in LC-MS analysis water
CN114200062A (en) Method for detecting tetraethylene glycol dimethyl ether in leather
CN103288839B (en) Chromatographic separation method and quantitative detection method of CL-20 (hexaazaisowurtzitane) and three intermediates CL-20
CN103940936B (en) Detection method of 4alpha-hydroxy-L-proline and trace L-proline in 4alpha-hydroxy-L-proline
CN103344726B (en) Method for extraction of dicyandiamide component in dairy product
CN106153776B (en) A kind of method of LC-MS analysis water sulfolan
CN105758959A (en) Method for detecting salinomycin and monensin in animal product
CN106324169A (en) Solid phase extraction-gas chromatography-tandem mass spectrum detection method for amide fungicides in wine

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
EXSB Decision made by sipo to initiate substantive examination
SE01 Entry into force of request for substantive examination
C53 Correction of patent for invention or patent application
CB03 Change of inventor or designer information

Inventor after: Zhang Zhipeng

Inventor after: Ji Xiaomei

Inventor after: Peng Jingkai

Inventor after: Du Juan

Inventor after: Song Shaohua

Inventor after: Li Yongshan

Inventor after: Li Changli

Inventor after: Zou Zhiyong

Inventor after: Huang Yuewu

Inventor after: Yi Chunsheng

Inventor before: Zhang Zhipeng

Inventor before: Ji Xiaomei

Inventor before: Peng Jingkai

Inventor before: Du Juan

Inventor before: Song Shaohua

Inventor before: Li Yongshan

Inventor before: Li Changli

Inventor before: Zou Zhiyong

Inventor before: Huang Yuewu

Inventor before: Yi Chunsheng

C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20170315

Termination date: 20180424