CN107300597A - The detection method of the sulfonic acid of 2 phenylbenzimidazol 5 in a kind of soil - Google Patents

The detection method of the sulfonic acid of 2 phenylbenzimidazol 5 in a kind of soil Download PDF

Info

Publication number
CN107300597A
CN107300597A CN201710671617.XA CN201710671617A CN107300597A CN 107300597 A CN107300597 A CN 107300597A CN 201710671617 A CN201710671617 A CN 201710671617A CN 107300597 A CN107300597 A CN 107300597A
Authority
CN
China
Prior art keywords
soil
sample
sulfonic acid
solution
silica gel
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.)
Granted
Application number
CN201710671617.XA
Other languages
Chinese (zh)
Other versions
CN107300597B (en
Inventor
奈世杰
李焕明
姜红
牟文超
卢燕华
刘安栋
奈欣慧
杨素云
胡睿
刘子叶
王鹏程
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.)
Shandong Sigma Inspection Technology Service Co Ltd
Original Assignee
Shandong Sigma Inspection Technology Service Co Ltd
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 Shandong Sigma Inspection Technology Service Co Ltd filed Critical Shandong Sigma Inspection Technology Service Co Ltd
Priority to CN201710671617.XA priority Critical patent/CN107300597B/en
Publication of CN107300597A publication Critical patent/CN107300597A/en
Application granted granted Critical
Publication of CN107300597B publication Critical patent/CN107300597B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N30/00Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
    • G01N30/02Column chromatography
    • G01N30/04Preparation or injection of sample to be analysed
    • G01N30/06Preparation
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N30/00Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
    • G01N30/02Column chromatography
    • G01N30/88Integrated analysis systems specially adapted therefor, not covered by a single one of the groups G01N30/04 - G01N30/86

Landscapes

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

Abstract

The invention belongs to environmental analysis field, the detection method of the sulfonic acid of 2 phenylbenzimidazol 5 in specifically related to a kind of soil, research currently for PBSA is concentrated mainly on contents level in cosmetics and product, and mechanism of degradation is studied in water environment, but PBSA detection method research and contents level research almost blank in soil, therefore, in order to understand the concentration level and environmental behaviour of PBSA in soil environment, need to set up a kind of efficient quick, the high analysis method of sensitivity, qualitative and quantitative detection for the sulfonic acid of 2 phenylbenzimidazol of trace in soil 5, the purpose of invention is to provide a kind of analyzing detecting method of the sulfonic acid of 2 phenylbenzimidazol 5 (PBSA) in soil, in particular it is to use ultrasonic extraction, silica gel column chromatography column purification and the analysis method of high performance liquid chromatography GC-MS detection.

Description

The detection method of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in a kind of soil
First, technical field
The invention belongs to environmental analysis field, and in particular to 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in a kind of soil Detection method.
2nd, background technology
In recent years, because whitening and ultraviolet protection are increasingly valued by people, the use increasingly frequency of sun-screening agent It is numerous.Sun-screening agent after use, as people's activity can be directly entered in environment, or is introduced into town sewage on people's skin In processing system, then being discharged into environment with sludge and sewage.Many researchs show that sun-screening agent can be in many water rings Detected in border, as a kind of emerging pollutant, have been received by the attention of environmental administration and Environmental Scientific Research worker.Some research tables Bright, Orangic sunscreen has endocrine disrupting and bioaccumulation in the environment, has to environment potentially hazardous.
2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID (2-Phenylbenzimidazole-5-sulfonic acid, abbreviation PBSA) It is a kind of conventional sun-screening agent, due to its excellent sun-proof performance, is widely used in sun care preparations.
The essential information of the 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID of table 1
Research currently for PBSA is concentrated mainly on contents level in cosmetics and product, and is dropped in water environment Study mechanism is solved, but PBSA detection method research and contents level in soil study almost blank.Therefore, to know clearly PBSA concentration level and environmental behaviour is, it is necessary to set up the high analysis side of a kind of efficient quick, sensitivity in solution soil environment Method, the qualitative and quantitative detection for trace 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in soil.
3rd, the content of the invention
The purpose of invention is to be directed to problem above and deficiency, is to provide 2-Phenylbenzimidazole -5- sulphurs in a kind of soil The analyzing detecting method of sour (PBSA), is in particular to use ultrasonic extraction, silica gel column chromatography column purification and high performance liquid chromatography The analysis method of GC-MS detection.
Technical scheme comprises the following steps:
(1) ultrasonic extraction
After collecting soil sample, dry and remove the larger impurity such as stone cleaning and plant tissue, grinding sieving.Weigh soil Inner mark solution is added dropwise in centrifuge tube with cover in earth sample, treats that solvent volatilizees;Extractant is added, lid is tightened, is well mixed Afterwards, ultrasonic extraction, is centrifuged, and draws supernatant liquor in pear-shaped flask;Extraction step is repeated, extract is incorporated in pears In shape flask, and rotary evaporated to dryness.
(2) silica gel column chromatography column purification
Load a small amount of mineral wool in glass chromatography column bottom, sequentially add after silica gel and anhydrous sodium sulfate, flat surface, Add solvent cleaning and activated silica gel.Solvent is added into pear-shaped flask to dissolve again, and solution is transferred to silica gel column chromatography In;The part efflux needed for chromatographic column is received with glass tube, is dried up in nitrogen evaporator.1mL methanol is added into glass tube Again dissolve, after filtering, to preserve to be measured in 2mL brown sample introduction bottles.
(3) standard working solution is prepared
The standard substance of PBSA and internal standard compound is weighed with assay balance, storing solution is made into respectively, and it is molten to be diluted to work Liquid, is finally configured to the standard working solution of gradient concentration.
(4) high performance liquid chromatography GC-MS is detected
The standard working solution of gradient concentration is determined in high performance liquid chromatography GC-MS, built using internal standard method Vertical standard working curve.The sample solution in step (2) is injected in high performance liquid chromatography GC-MS under the same conditions It is measured, the chromatographic peak area of target compound in sample is substituted into standard working curve, obtains the qualitative of PBSA in sample Quantitative result.If the PBSA concentration working curve range of linearity that is above standard is reached the standard grade in sample, sample size weight should be accordingly reduced New extraction and cleaning and detection.
In step (1), it is preferred to use freeze-drying, sample grinding consequence 0.90mm sieves, sealing preserve is in 4 DEG C Environment in.
In step (1), pedotheque amount is preferably 5~10g.
In step (1), internal standard compound is preferably 2- methyl -4- chlorine amoxy propionic acid (mecoprop).
In step (1), extractant is the mixed solvent of ethyl acetate and formic acid, and both volume ratios are 50:1~100: 1。
In step (1), specific extraction process tightens lid to add 7~10mL of extractant, and vortex mixed 30s surpasses Sound extracts 15~20min, 2500rpm centrifugation 15min, draws supernatant liquor in pear-shaped flask, repeats extraction 2~3 times, Combining extraction liquid is in pear-shaped flask, rotary evaporated to dryness.
In step (2), silica gel and anhydrous sodium sulfate are respectively 1.0g and 0.5g.
In step (2), silica gel activating concrete operations are:Sequentially add 10mL methanol, 10 mL ethyl acetate and 10mL just oneself Alkane, liquid level cannot be below interface on anhydrous sodium sulfate during noting.
In step (2), sample solution is added and the detailed process of elution is:Into pear-shaped flask add 2~3mL just oneself Alkane is dissolved again, and solution is transferred in silica gel column chromatography, discards efflux, repeats step 2 time;Into pear-shaped flask Add 2~3mL ethyl acetate to dissolve again, and solution is transferred in silica gel column chromatography, efflux is received with glass tube, then Repeat step 2 times, merges efflux, is dried up in nitrogen evaporator.
In step (3), internal standard compound preferably is 2- methyl -4- chlorine amoxy propionic acid (mecoprop), standard working curve Gradient concentration at least five more than.
In step (4), chromatographic condition preferably is as follows:Chromatographic column is Agilent SB-C18 (3.0 × 100mm, 1.8 μ M), column temperature is 40 DEG C, and mobile phase is water (A) and acetonitrile (B);Gradient elution program is the Mobile phase Bs of 0~2min 50~90%, 2 The Mobile phase Bs of~5min 90%, flow velocity 0.30mL/min.
In step (4), Mass Spectrometry Conditions preferably are as follows:Electro-spray ionization ion gun (ESI) negative mode;Dry temperature 300 DEG C of degree, flow velocity 3mL/min;The psi of nebulizer pressure 30;250 DEG C of sheath temperature degree, flow velocity 11mL/min;Capillary voltage 3000V, spray nozzle voltage 1000V.On this condition, PBSA and interior target mass spectrometry parameters are as shown in table 2.
Table 2PBSA and the interior mass spectrometry parameters for being marked on high performance liquid chromatography mass spectrometry
A runics are quota ion
The present invention is built using ultrasonic extraction, silica gel column chromatography column purification and high performance liquid chromatography GC-MS detection technique Found the analyzing detecting method of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID, effectively to the trace 2-Phenylbenzimidazole in soil- 5- sulfonic acid carries out qualitative and quantitative detection, and the present invention has following innovative point.
(1) polarity of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is stronger, and the present invention uses the ethyl acetate conduct that formic acid is acidified Extraction solvent, can suppress ionization of the 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in extraction process, increase the rate of recovery, while in The ethyl acetate solvent of isopolarity can reduce the undue extraction of chaff interference in soil, reduce the matrix interference of method, improve Sensitivity.
(2) soil matrix is complicated, for the matrix interference of method, and the present invention uses homemade silica gel column chromatography column purification, first Non polar impurities are eluted using n-hexane, then target compound 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is eluted with ethyl acetate, are reached To purification purpose, method sensitivity is further increased.
(3) present invention uses inner mark method ration, after instrument condition optimizes, the internal standard compound 2- methyl -4- chlorine penta of selection Epoxide propionic acid and the target compound peak type in instrument are good, and retention time is close, and is added to before extraction in sample, Counteract in the error caused by target compound loses in extraction process, many experiments and all achieve the good rate of recovery.
(4) China is less to the 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID concern in soil environment at present, due to soil environment Matrix is complicated, and conventional method of analysis serious interference causes analysis difficulty, and its analysis and detection technology is still in technological gap.This hair The detection technique of the bright 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID from a set of soil is provided in terms of extraction, purification and Instrumental Analysis, Average recovery rate is 91.8%~92.1%, and detection is limited to 0.19~0.22ng/g, is quantitatively limited to 0.64~0.74ng/g, is fitted Analysis detection for 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in soil.
The beneficial effect of the present invention is to set up the high analysis method of a kind of efficient quick, sensitivity, for trace 2- in soil The qualitative and quantitative detection of phenylbenzimidazol -5- sulfonic acid
Brief description of the drawings
Fig. 1 is 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID (PBSA) and 2- methyl -4- chlorine amoxy propionic acid (mecoprop) Characteristic ion flow graph.
5th, embodiment
Embodiment 1
(1) ultrasonic extraction
Collecting soil sample 100g, is freeze-dried and removes stone cleaning and the larger impurity such as plant tissue, ground 0.90mm is sieved.5g pedotheques are weighed in centrifuge tube with cover, the 100 μ L 1mg/L oxygen of internal standard compound 2- methyl -4- chlorine penta is added dropwise Base propionic acid working solution, treats that solvent volatilizees;Add 10mL ethyl acetate and formic acid mixed solvent (volume ratio 50:1) lid, is tightened Son, vortex mixed 30s, ultrasonic extraction 15min, 2500rpm centrifugation 15min, draws supernatant liquor in pear-shaped flask, then weigh Extract 2 times again, combining extraction liquid is in pear-shaped flask, 45 DEG C of rotary evaporated to dryness.
(2) silica gel column chromatography column purification
Load a small amount of mineral wool in glass chromatography column bottom, sequentially add 1g silica gel and 0.5g anhydrous sodium sulfates, rap glass Glass post flat surface, sequentially adds 10mL methanol, 10mL ethyl acetate and 10mL n-hexane activated silica gel posts, during noting Liquid level cannot be below interface on anhydrous sodium sulfate.2mL n-hexanes are added into pear-shaped flask to dissolve again, and solution is shifted Into silica gel column chromatography, efflux is discarded, step 2 time is repeated;2mL ethyl acetate is added into pear-shaped flask to dissolve again, And solution is transferred in silica gel column chromatography, efflux is received with glass tube, step 2 time is repeated, merges efflux, in nitrogen Blow in instrument and dry up.1mL methanol is added into glass tube to dissolve again, after filtering, is treated with being preserved in 2mL brown sample introduction bottles Survey.
(3) standard working solution is prepared
The reference material of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID and 2- methyl -4- chlorine amoxy propionic acid is weighed with assay balance Matter, 100mg/L stock solutions are configured to methanol and 1 mg/L working solutions are diluted to respectively, be finally configured to concentration for 1,5, 10th, 20,50,100 and 200 μ g/L standard working solution, wherein internal standard compound concentration are 100 μ g/L.
(4) high performance liquid chromatography GC-MS is detected
The standard working solution of gradient concentration is determined in high performance liquid chromatography GC-MS, built using internal standard method Vertical standard working curve.The sample solution in step (2) is injected in high performance liquid chromatography GC-MS under the same conditions It is measured, the chromatographic peak area of target compound in sample is substituted into standard working curve, obtains the qualitative of PBSA in sample Quantitative result.
Qualitative Identification:Under the conditions of same instruments, if the chromatographic peak of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID retains in sample Time is consistent with the retention time in standard working solution, and qualitative and quota ion pair abundance ratio and standard liquid Equally, then it can determine whether there is 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in sample.
Quantitative analysis:Standard working curve, the μ g/L of the range of linearity 0~200, standard curve phase relation are set up with internal standard method Number>0.999, the concentration of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in sample solution is calculated by software, is finally calculated by sample size The concentration of 2-Phenylbenzimidazole -5- sulfonic acid in sample.
Recovery of standard addition, repeatability and matrix effect:
The rate of recovery uses 3 parallel mark-ons, and mark-on method is:100 μ L 1mg/L 2- are added in 5.0g pedotheques Phenylbenzimidazol -5- sulfonic acid standard liquids so that the concentration of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is 20ng/g in sample, etc. 30min is treated, after solvent volatilization completely, is extracted and is detected.The mark-on sample concentration of practical measurement is subtracted into blank sample dense Degree, and be compared with theory addition concentration, the rate of recovery of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is obtained, with 3 parallel mark-ons As a result standard deviation method for expressing repeatability.Matrix effect is tested by the following method:Blank sample is extracted and is concentrated into After 1mL, 100 μ L sample solution is taken in sample introduction bottle, is dried up on nitrogen evaporator, and it is respectively 100 μ to add 100 μ L concentration G/L 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID and the mixed standard solution of 2- methyl -4- chlorine amoxy propionic acid, vortex mixing are equal It is even, upper machine testing.The mark-on sample concentration of practical measurement is subtracted into blank sample concentration, and compared with theory addition concentration Compared with obtaining the matrix effect result of method.Recovery of standard addition, repeatability and the matrix effect of method the results are shown in Table shown in 3, can To find out, in the case that spiked levels are 20ng/g in soil, the average recovery rate of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is 91.8%, standard deviation is 1.4%, and matrix effect is 92.2%, and the illustration method rate of recovery and reproducible, matrix interference are low, Detection available for pedotheque.
Detection limit and quantitative limit:
Corresponding concentration is detection limit when signal to noise ratio is 3, and corresponding concentration is quantitative limit when signal to noise ratio is 10, specific behaviour As:The signal to noise ratio under spiked levels is calculated by data processing software, with the spiked levels divided by signal to noise ratio, the result 3 times be method test limit, 10 times be quantitative limit.The detection limit and quantitative limit result of method are as shown in table 3, it can be seen that soil In the case that spiked levels are 20ng/g in earth, the detection of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is limited to 0.19ng/g, quantitative limit For 0.64ng/g, illustrate that the sensitivity of this detection method is high, available for trace 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in pedotheque Detection.
The method rate of recovery of table 3, matrix effect, detection limit and quantitative limit
aAverage value ± standard deviation (%) (n=3);bAverage value ± standard deviation (%) (n=3);c(ng/g);d(ng/ g)
Embodiment 2
(1) ultrasonic extraction
Collecting soil sample 100g, is freeze-dried and removes stone cleaning and the larger impurity such as plant tissue, ground 0.90mm is sieved.10g pedotheques are weighed in centrifuge tube with cover, 100 μ L 1mg/L internal standard compound 2- methyl -4- chlorine penta is added dropwise Epoxide propionic acid working solution, treats that solvent volatilizees;Add 10mL ethyl acetate and formic acid mixed solvent (volume ratio 100:1), tighten Lid, vortex mixed 30s, ultrasonic extraction 15min, 2500rpm centrifugation 15min, draws supernatant liquor in pear-shaped flask, then Repeat to extract 2 times, combining extraction liquid is in pear-shaped flask, 45 DEG C of rotary evaporated to dryness.
(2) silica gel column chromatography column purification
Load a small amount of mineral wool in glass chromatography column bottom, sequentially add 1g silica gel and 0.5g anhydrous sodium sulfates, rap glass Glass post flat surface, sequentially adds 10mL methanol, 10mL ethyl acetate and 10mL n-hexane activated silica gel posts, during noting Liquid level cannot be below interface on anhydrous sodium sulfate.2mL n-hexanes are added into pear-shaped flask to dissolve again, and solution is shifted Into silica gel column chromatography, efflux is discarded, step 2 time is repeated;2mL ethyl acetate is added into pear-shaped flask to dissolve again, And solution is transferred in silica gel column chromatography, efflux is received with glass tube, step 2 time is repeated, merges efflux, in nitrogen Blow in instrument and dry up.1mL methanol is added into glass tube to dissolve again, after filtering, is treated with being preserved in 2mL brown sample introduction bottles Survey.
(3) standard working solution is prepared
The reference material of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID and 2- methyl -4- chlorine amoxy propionic acid is weighed with assay balance Matter, 100mg/L stock solutions are configured to methanol and 1 mg/L working solutions are diluted to respectively, be finally configured to concentration for 1,5, 10th, 20,50,100 and 200 μ g/L standard working solution, wherein internal standard compound concentration are 100 μ g/L.
(4) high performance liquid chromatography GC-MS is detected
The standard working solution of gradient concentration is determined in high performance liquid chromatography GC-MS, built using internal standard method Vertical standard working curve.The sample solution in step (2) is injected in high performance liquid chromatography GC-MS under the same conditions It is measured, the chromatographic peak area of target compound in sample is substituted into standard working curve, obtains the qualitative of PBSA in sample Quantitative result.
Qualitative Identification:Under the conditions of same instruments, if the chromatographic peak of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID retains in sample Time is consistent with the retention time in standard working solution, and qualitative and quota ion pair abundance ratio and standard liquid Equally, then it can determine whether there is 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in sample.
Quantitative analysis:Standard working curve, the μ g/L of the range of linearity 0~200, standard curve phase relation are set up with internal standard method Number>0.999, the concentration of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in sample solution is calculated by software, is finally calculated by sample size The concentration of 2-Phenylbenzimidazole -5- sulfonic acid in sample.
Recovery of standard addition, repeatability and matrix effect:
The rate of recovery uses 3 parallel mark-ons, and mark-on method is:100 μ L 1mg/L 2- are added in 10.0g pedotheques Phenylbenzimidazol -5- sulfonic acid standard liquids so that the concentration of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is 10ng/g in sample, etc. 30min is treated, after solvent volatilization completely, is extracted and is detected.The mark-on sample concentration of practical measurement is subtracted into blank sample dense Degree, and be compared with theory addition concentration, the rate of recovery of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is obtained, with 3 parallel mark-ons As a result standard deviation method for expressing repeatability.Matrix effect is tested by the following method:Blank sample is extracted and is concentrated into After 1mL, 100 μ L sample solution is taken in sample introduction bottle, is dried up on nitrogen evaporator, and it is respectively 100 μ to add 100 μ L concentration G/L 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID and the mixed standard solution of 2- methyl -4- chlorine amoxy propionic acid, vortex mixing are equal It is even, upper machine testing.The mark-on sample concentration of practical measurement is subtracted into blank sample concentration, and compared with theory addition concentration Compared with obtaining the matrix effect result of method.Recovery of standard addition, repeatability and the matrix effect of method the results are shown in Table shown in 4, can To find out, in the case that spiked levels are 10ng/g in soil, the average recovery rate of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is 90.5%, standard deviation is 1.2%, and matrix effect is 91.1%, and the illustration method rate of recovery and reproducible, matrix interference are low, Detection available for pedotheque.
Detection limit and quantitative limit:
Corresponding concentration is detection limit when signal to noise ratio is 3, and corresponding concentration is quantitative limit when signal to noise ratio is 10, specific behaviour As:The signal to noise ratio under spiked levels is calculated by data processing software, with the spiked levels divided by signal to noise ratio, the result 3 times be method test limit, 10 times be quantitative limit.The detection limit and quantitative limit result of method are as shown in table 4, it can be seen that soil In the case that spiked levels are 10ng/g in earth, the detection of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID is limited to 0.22ng/g, quantitative limit For 0.74ng/g, illustrate that the sensitivity of this detection method is high, available for trace 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in pedotheque Detection.
The method rate of recovery of table 4, matrix effect, detection limit and quantitative limit
aAverage value ± standard deviation (%) (n=3);bAverage value ± standard deviation (%) (n=3);c(ng/g);d(ng/ g)
Above-described embodiment is preferably embodiment, but embodiments of the present invention are not by above-described embodiment of the invention Limitation, other any Spirit Essences without departing from the present invention and the change made under principle, modification, replacement, combine, it is simple Change, should be equivalent substitute mode, be included within protection scope of the present invention.

Claims (4)

1. the detection method of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in a kind of soil, it is characterised in that comprise the following steps:
(1) ultrasonic extraction
After collecting soil sample, dry and remove the larger impurity such as stone cleaning and plant tissue, grinding sieving weighs pedotheque In centrifuge tube with cover, inner mark solution is added dropwise, treats that solvent volatilizees;Extractant is added, lid is tightened, after being well mixed, ultrasound Extraction, is centrifuged, and draws supernatant liquor in pear-shaped flask;Extract is incorporated in pear-shaped flask, and rotary evaporation is extremely It is dry;
(2) silica gel column chromatography column purification
Load a small amount of mineral wool in glass chromatography column bottom, sequentially add after silica gel and anhydrous sodium sulfate, flat surface, add molten Agent cleaning and activated silica gel, into pear-shaped flask, addition solvent is dissolved again, and solution is transferred in silica gel column chromatography;Use glass Glass pipe receives the part efflux needed for chromatographic column, is dried up in nitrogen evaporator, 1mL methanol is added into glass tube again molten Solution, after filtering, into glass tube, addition 1mL methanol dissolves again, molten as sample using in 2mL brown sample introduction bottles after filtering Liquid preserves to be measured;
(3) standard working solution is prepared
The standard substance of PBSA and internal standard compound is weighed with assay balance, storing solution is made into respectively, and is diluted to working solution, is prepared Into the standard working solution of gradient concentration;
(4) liquid chromatography mass combined instrument is detected
The standard working solution of gradient concentration is determined in liquid chromatography mass combined instrument, setting up standard using internal standard method works Curve, the sample solution in step (2) is injected and is measured in liquid chromatography mass combined instrument, by target compound in sample Chromatographic peak area substitute into standard working curve, obtain the qualitative, quantitative result of PBSA in sample.
2. according to claim 1 in a kind of soil 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID detection method, it is characterized in that:Institute State in step (1), drying means uses freeze-drying, crosses 0.90mm sieves after sample grinding, sealing preserve is in 4 DEG C of environment In, in the step (1), pedotheque amount is 5~10g, in the step (1), and inner mark solution is preferably 2- methyl -4- chlorine penta In epoxide propionic acid, the step (1), extractant is the mixed solvent of ethyl acetate and formic acid, and both volume ratios are 50:1~ 100:1, in the step (1), 7~10mL of extractant is added, lid is tightened, vortex mixed 30s, ultrasonic extraction 15~ 20min, 2500rpm centrifuge 15min, draw supernatant liquor in pear-shaped flask, repeat extraction 2~3 times, combining extraction liquid in In pear-shaped flask, rotary evaporated to dryness.
3. according to claim 1 in a kind of soil 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID detection method, it is characterized in that:Institute State in step (2), silica gel and anhydrous sodium sulfate are respectively the specific behaviour of activated silica gel making in 1.0g and 0.5g, the step (2) As:Sequentially add 10mL methanol, 10mL ethyl acetate and 10mL n-hexanes, during liquid level cannot be below on anhydrous sodium sulfate Sample solution is added in interface, the step (2) and the detailed process of elution is:2~3mL n-hexanes are added into pear-shaped flask Again dissolve, and solution is transferred in silica gel column chromatography, discard efflux, repeat step 2 time;Added into pear-shaped flask 2~3mL ethyl acetate is dissolved again, and solution is transferred in silica gel column chromatography, is received efflux with glass tube, is repeated step Rapid 2 times, merge efflux, dried up in nitrogen evaporator.
4. according to claim 1 in a kind of soil 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID detection method, it is characterized in that, institute State in step (3), internal standard compound is 2- methyl -4- chlorine amoxy propionic acid, more than gradient concentration at least five of standard working curve, In the step (4), chromatographic condition is as follows:Chromatographic column is that Agilent SB-C18 column temperatures are 40 DEG C, and mobile phase is water (A) and second Nitrile (B);Gradient elution program is the Mobile phase Bs of 0~2min 50~90%, the Mobile phase Bs of 2~5min 90%, flow velocity 0.30mL/ Mass Spectrometry Conditions are as follows in min, the step (4):Electro-spray ionization ion gun (ESI) negative mode;300 DEG C of temperature degree is dried, Flow velocity 3mL/min;Nebulizer pressure 30psi;250 DEG C of sheath temperature degree, flow velocity 11mL/min;Capillary voltage 3000V, nozzle electricity Press 1000V.
CN201710671617.XA 2017-08-08 2017-08-08 The detection method of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in a kind of soil Active CN107300597B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710671617.XA CN107300597B (en) 2017-08-08 2017-08-08 The detection method of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in a kind of soil

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710671617.XA CN107300597B (en) 2017-08-08 2017-08-08 The detection method of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in a kind of soil

Publications (2)

Publication Number Publication Date
CN107300597A true CN107300597A (en) 2017-10-27
CN107300597B CN107300597B (en) 2019-08-13

Family

ID=60133725

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710671617.XA Active CN107300597B (en) 2017-08-08 2017-08-08 The detection method of 2-PHENYLBENZIMIDAZOLE-5-SULFONIC ACID in a kind of soil

Country Status (1)

Country Link
CN (1) CN107300597B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114894938A (en) * 2022-05-30 2022-08-12 山东诺正检测有限公司 Method for detecting brassinolide in soil

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001073112A1 (en) * 2000-03-29 2001-10-04 Council Of Scientific And Industrial Research Method for identifying uv-filter compounds
CN103063763A (en) * 2012-12-21 2013-04-24 林维宣 High performance liquid chromatography detection method for residual quantity of multiple ultraviolet absorbents in cosmetics
CN105891344A (en) * 2014-12-15 2016-08-24 上海出入境检验检疫局动植物与食品检验检疫技术中心 Technology for rapidly detecting and confirming multiple ultraviolet light absorbers in cosmetics
CN106908539A (en) * 2017-03-03 2017-06-30 广州中科检测技术服务有限公司 The detection method of 1 hydroxybenzotriazole in a kind of soil and plant

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001073112A1 (en) * 2000-03-29 2001-10-04 Council Of Scientific And Industrial Research Method for identifying uv-filter compounds
CN103063763A (en) * 2012-12-21 2013-04-24 林维宣 High performance liquid chromatography detection method for residual quantity of multiple ultraviolet absorbents in cosmetics
CN105891344A (en) * 2014-12-15 2016-08-24 上海出入境检验检疫局动植物与食品检验检疫技术中心 Technology for rapidly detecting and confirming multiple ultraviolet light absorbers in cosmetics
CN106908539A (en) * 2017-03-03 2017-06-30 广州中科检测技术服务有限公司 The detection method of 1 hydroxybenzotriazole in a kind of soil and plant

Non-Patent Citations (6)

* Cited by examiner, † Cited by third party
Title
ANTONIO NIETO 等: "Determination of personal care products in sewage sludge by pressurized liquid extraction and ultra high performance liquid chromatography–tandem mass spectrometry", 《JOURNAL OF CHROMATOGRAPHY A》 *
M.S. DI´AZ-CRUZ 等: "Analysis of selected emerging contaminants in sewage sludge", 《TRENDS IN ANALYTICAL CHEMISTRY》 *
XIAOLING ZHANG 等: "Catalytic degradation of 2-phenylbenzimidazole-5-sulfonic acid by peroxymonosulfate activated with nitrogen and sulfur co-doped CNTs-COOH loaded CuFe", 《CHEMICAL ENGINEERING JOURNAL》 *
何乔桑 等: "高效液相色谱法测定化妆品中的12种紫外吸收剂", 《色谱》 *
孟宪双 等: "高效液相色谱法同时测定防晒类化妆品中15种紫外线吸收剂", 《色谱》 *
林维宣 等: "液相色谱-串联质谱法同时检测防晒化妆品中的11种紫外吸收剂", 《色谱》 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114894938A (en) * 2022-05-30 2022-08-12 山东诺正检测有限公司 Method for detecting brassinolide in soil

Also Published As

Publication number Publication date
CN107300597B (en) 2019-08-13

Similar Documents

Publication Publication Date Title
Turkelson et al. Separation of the citric acid cycle acids by liquid chromatography
CN101498692B (en) Method for measuring pesticide residue quantity in leather
CN102735784B (en) Method for simultaneously determining one hundred pesticide residuals in traditional Chinese medicine through ultrahigh performance liquid chromatography-tandem quadrupole mass spectrum
CN102183611B (en) Method for detecting pesticide residue in white paeony root crude drug
CN106568873B (en) The quantitative detecting method of Rynaxypyr residual quantity in a kind of soil
Vandemark et al. Liquid-chromatographic procedure for tricyclic drugs and their metabolites in plasma.
CN106526009B (en) A kind of quantitative detecting method of universal Rynaxypyr residual quantity
CN105758946A (en) Method for determining residual quantity of 15 kinds of triazole type pesticides in fruit
CN108318613A (en) The detection method of antibiotic in a kind of environmental sample
CN106442781B (en) The ultra performance liquid chromatography Mass Spectrometry detection method of Hostathion in a kind of Sediments
CN101865898B (en) Method for determining phthalate ester in soil
CN108562673A (en) A kind of ultra performance liquid chromatography tandem mass spectrum detection method measuring Ningnanmycin content in tomato
Chen et al. Determination of four major saponins in the seeds of Aesculus chinensis Bunge using accelerated solvent extraction followed by high-performance liquid chromatography and electrospray-time of flight mass spectrometry
CN105548431B (en) Detect the method for oxamyl and oxamyl oxime residual quantity in vegetables/fruit simultaneously
CN109270180A (en) The detection method of antibiotic in soil
CN104535665A (en) Detection method of radix codonopsis medicinal material
CN103123345B (en) Method for rapidly detecting phenoxyacetic acid herbicide in soil
CN107300597A (en) The detection method of the sulfonic acid of 2 phenylbenzimidazol 5 in a kind of soil
CN104280495B (en) Detect the method for the jinggangmycin A in water and rice plant
CN106546675B (en) The quantitative detecting method of Rynaxypyr residual quantity in a kind of tealeaves
CN106908539B (en) Method for detecting 1-hydroxybenzotriazole in soil and plants
CN111085006A (en) Process for extracting organic pollutants in environment
CN108663464B (en) Method for detecting fenhexamid in fruits, vegetables or soil
Zhang et al. Analysis of flavonoids in leaves of Adinandra nitida by capillary electrochromatography on monolithic columns with stepwise gradient elution
CN110333307A (en) The method of arsenic morphology in HPLC-ICP-MS combination measurement soil

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant