CN106596780A - Method for detecting contents of various antibiotics in water by combined use of high pressure liquid chromatography and mass spectrum - Google Patents

Method for detecting contents of various antibiotics in water by combined use of high pressure liquid chromatography and mass spectrum Download PDF

Info

Publication number
CN106596780A
CN106596780A CN201611192699.1A CN201611192699A CN106596780A CN 106596780 A CN106596780 A CN 106596780A CN 201611192699 A CN201611192699 A CN 201611192699A CN 106596780 A CN106596780 A CN 106596780A
Authority
CN
China
Prior art keywords
water
solid
phase extraction
extraction column
high pressure
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
CN201611192699.1A
Other languages
Chinese (zh)
Other versions
CN106596780B (en
Inventor
许柯
任洪强
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.)
Jiangsu Zhongyi Co Ltd Analysis Of Gold
Nanjing University
Original Assignee
Jiangsu Zhongyi Co Ltd Analysis Of Gold
Nanjing University
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 Jiangsu Zhongyi Co Ltd Analysis Of Gold, Nanjing University filed Critical Jiangsu Zhongyi Co Ltd Analysis Of Gold
Priority to CN201611192699.1A priority Critical patent/CN106596780B/en
Publication of CN106596780A publication Critical patent/CN106596780A/en
Application granted granted Critical
Publication of CN106596780B publication Critical patent/CN106596780B/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
    • 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
    • G01N2030/022Column chromatography characterised by the kind of separation mechanism
    • G01N2030/027Liquid chromatography

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 discloses a method for detecting the contents of various antibiotics in water by combined use of high pressure liquid chromatography and mass spectrum. The method comprises the following steps of (1) regulating pH of a water sample; (2) performing solid-phase extraction, enriching and concentration on the water sample subjected to pH regulation; (3) performing detection by a high pressure liquid chromatography and mass spectrum instrument; (4) performing result analysis. The method for detecting the contents of various antibiotics in water by combined use of high pressure liquid chromatography and mass spectrum has the characteristics of short detection time and high sensitivity, and belongs to a novel method for detecting the contents of various kinds of antibiotics in the water environment sample. The method has the advantages that the interference on the detection of a target material is greatly reduced; the high-sensitivity detection can be performed on trace antibiotics and various kinds of antibiotics. When the detection method provided by the invention is used, the mass accuracy on 9 kinds of antibiotics is less than 1 ppm; the detection limit is 0.1 to 5 ug/L; the addition recovery rate is 70 to 100 percent; the relevant deviation difference is smaller than 10 percent.

Description

The method of Multiple Classes of Antibiotics content in high pressure liquid chromatography-mass spectrometry detection water
Technical field
The present invention relates to technical field of environmental detection, is specifically related to many in high pressure liquid chromatography-mass spectrometry detection water The method for planting antibiotic content.
Background technology
Increasingly improve and the newtype drug of the general level of the health constantly puts into clinical practice makes the dependence of the raw element of people's antagonism more next Stronger, all in the trend for increasing year by year, a large amount of use of antibiotic is inevitably led for the species or quantity of antibiotic Cause it to pass through number of ways and enter environment.It is certain that increasing research finds that the antibiotic in environment has to environmental organism Toxicity, the antibiotic in environment has been increasingly becoming generally acknowledged emerging pollutant, and the detection to antibiotic in environment has been current Home and abroad environment detection, the important content administered and evaluate.
At present, the detection of antibiotic mainly has gas chromatography, liquid chromatography, GC-MS, liquid phase Chromatograph-mass spectrometer coupling method.Gas-chromatography and liquid chromatogram rely primarily on chromatogram post separation and detector to antibiotic responsiveness, right Antibiotic detection in one pack system or simple system has a preferably qualitatively and quantitatively effect, and due to water environment matrix it is more multiple Miscellaneous, comprising gas chromatography matter or interfering ion, there is certain difficulty in chromatogram on antibiotic is qualitative and quantitative.Gas-chromatography- Mass spectrometry and liquid chromatograph mass spectrography mainly utilize chromatogram post separation, mass analyzer according to determine molecular weight and The intensity of the Middle Molecular Substance carries out qualitative and quantitative, and than gas-chromatography and liquid chromatogram, chromatogram and mass spectrometric hyphenated technique can The qualitative and quantitative of complex sample is preferably completed, yet with there is substantial amounts of organic matter in environment, ambient interferences are more serious, The substance classes of identical molecular weight are still a lot, so easily causing the false positive of measurement result.
Triple level Four pole technologies are broken into pieces compound molecule by applying energy, and every kind of compound is in certain condition Under have the fragments characteristic of oneself, compound is carried out by determining compound molecular weight itself and fragments characteristic molecular weight simultaneously Qualitative and quantitative not only can reduction reduces false positive and judges to the erroneous judgement of compound, and greatly improves detection sensitivity.At present It is domestic less to antibiotic research in high pressure liquid chromatography-mass spectrograph combination method measure water, reducing to qualitative and quantitative interference Difficult problem aspect is also no to cause concern in environment measuring industry.
The content of the invention
Present invention solves the technical problem that being to provide a kind of quick, easy, sensitivity height, and effectively reduce or eliminate Multiple Classes of Antibiotics contains in the high pressure liquid chromatography of the complex matrices interference antibiotic content from water environment-mass spectrometry detection water The method of amount.
The technical scheme is that:The method of Multiple Classes of Antibiotics content in high pressure liquid chromatography-mass spectrometry detection water, Comprise the following steps:
1) pH of water sample is adjusted:A 250mL water samples are measured, appropriate formic acid is added, pH to 2.0 is adjusted, portion is separately measured 250mL water samples, add appropriate ammoniacal liquor, adjust pH to 12.0;
2) the solid phase extraction concentration concentration of water sample after pH is adjusted:Respectively with 5mL methyl alcohol and 10mL deionized water activated solids Extraction column 1, flow velocity is that the 250mL water samples that pH is adjusted to 2.0 are crossed into solid-phase extraction column after 5-10mL/min activation, and flow velocity is 3-5mL/ Min, after the excessively complete solid-phase extraction column of water sample, with 5mL deionized waters solid-phase extraction column is got express developed, and flow velocity is 5-10mL/min, so After be dried solid-phase extraction column 30min, finally with 5mL methyl alcohol with 3mL/min flow velocitys elute solid-phase extraction column, collect eluent, mark It is designated as eluent 1;Respectively with 5mL methyl alcohol and 10mL deionized water activated solids extraction column 2, flow velocity is after 5-10mL/min activation The 250mL water samples that pH is adjusted to 12.0 are crossed into solid-phase extraction column, flow velocity is 3-5mL/min, after the excessively complete solid-phase extraction column of water sample, used 5mL deionized waters get solid-phase extraction column express developed, and flow velocity is 5-10mL/min, is then dried solid-phase extraction column 30min, is finally used 5mL methyl alcohol elutes solid-phase extraction column with 3mL/min flow velocitys, collects eluent, is labeled as eluent 2;Merge eluent 1 and 2, In 40 DEG C of water-baths, dried up with gentle nitrogen, be finally settled to 1mL with water, after 0.45um teflon membrane filters, that is, obtained Sample solution;
3) using high pressure liquid chromatography-mass spectrograph detection:
A. the preparation of standard liquid:Standard items antibiotic is accurately weighed respectively, using deionized water dissolving, is made into respectively The Standard Stock solutions of 0.2mg/mL, according to the response of each antibiotic when using, deionized water is diluted to standard working solution;
B. using high pressure liquid chromatography-mass spectrograph examination criteria working solution and sample solution:Inhaled respectively by automatic sampler Standard working solution and sample solution are taken, in injection high pressure liquid chromatography-mass spectrograph, the antibiotic group lease making liquid chromatogram in sample Post separation, the detection of mass spectrograph multiple-reaction monitoring pattern;
4) data analysis:With the parent ion and daughter ion of compound as quota ion and qualitative ion;With standard working solution Mass concentration X be abscissa, the peak area Y of quantitative and qualitative ion is ordinate, draws standard working curve, is worked with standard Curve carries out single ion quantified by external standard method to sample;With in sample solution occur chromatographic peak retention time and parent ion/son from Son is qualitative to carrying out.
Further, in such scheme, formic acid used and ammoniacal liquor are top pure grade in the step 1.
Further, in such scheme, solid-phase extraction column used is solid for Waters Oasis HLB in the step 2 Phase extraction column, specification is 6cc/500mg, 60um.
Further, in such scheme, the antibiotic standard items in the step 3 be respectively hygromycin, Lovastatin, Acarbose, tylosin, erythromycin, sulphadiazine, gentamicin, penicillin, sulfamethoxazole.
Further, in such scheme, liquid phase chromatogram condition in the step 3:Chromatographic column:SB-C18,3.5um, 2.1 ×150mm;Mobile phase:A is 0.1% formic acid, and B is acetonitrile;Gradient elution:0-2min, 10%B;2-7min, 10-40%B, 7- 9min, 40-90%B, 9-10min, 90-100%B;Column temperature:Room temperature.
Further, in such scheme, Mass Spectrometry Conditions in the step 3:Mass analyzer:Triple level Four bars, scanning Pattern:Cation-reaction monitoring pattern, ion gun:Electric spray ion source, spray voltage:4.5kV, removes solvent temperature:500 DEG C, Remove solvent gas flow velocity:600L/h.
The invention has the beneficial effects as follows:Multiple Classes of Antibiotics contains in the high pressure liquid chromatography of the present invention-mass spectrometry detection water The method of amount has the characteristics of detection time is short, sensitivity is high, is a kind of new for Multiple Classes of Antibiotics in environmental water sample The assay method of content, the method greatly reduces the interference of the detection to object, can be same to trace and Multiple Classes of Antibiotics The highly sensitive detections of Shi Jinhang.Using the detection method of the present invention for the mass accuracy of 9 kinds of antibiotic is less than 1ppm, inspection Survey is limited to 0.1-5ug/L, and TIANZHU XINGNAO Capsul is 70-100%, and relative standard deviation is less than 10%.
Description of the drawings
Fig. 1 is corresponding multiple-reaction monitoring (MRM) chromatogram of 9 kinds of antibiotic (100 μ g/L).
Specific embodiment
Below in conjunction with the accompanying drawings to the side of Multiple Classes of Antibiotics content in the high pressure liquid chromatography-mass spectrometry detection water of the present invention Method is described further:
As shown in figure 1, selecting hygromycin, Lovastatin, acarbose, tylosin, erythromycin, sulphadiazine, celebrating big Mycin, penicillin, sulfamethoxazole are carried out various in high pressure liquid chromatography-mass spectrometry detection water as antibiotic standard items Antibiotic content, concrete grammar is comprised the following steps:
1) pH of water sample is adjusted:A 250mL water samples are measured, appropriate formic acid is added, pH to 2.0 is adjusted, portion is separately measured 250mL water samples, add appropriate ammoniacal liquor, adjust pH to 12.0;Formic acid and ammoniacal liquor are top pure grade;
2) the solid phase extraction concentration concentration of water sample after pH is adjusted:Respectively with 5mL methyl alcohol and 10mL deionized water activated solids Extraction column 1, flow velocity is that the 250mL water samples that pH is adjusted to 2.0 are crossed into solid-phase extraction column after 7mL/min activation, and flow velocity is 4mL/min, After the excessively complete solid-phase extraction column of water sample, with 5mL deionized waters solid-phase extraction column is got express developed, flow velocity is 7mL/min, be then dried solid Phase extraction column 30min, finally elutes solid-phase extraction column with 5mL methyl alcohol with 3mL/min flow velocitys, collects eluent, is labeled as wash-out Liquid 1;Respectively with 5mL methyl alcohol and 10mL deionized water activated solids extraction column 2, flow velocity is to be adjusted to pH after 7mL/min activation 12.0 250mL water samples cross solid-phase extraction column, and flow velocity is 4mL/min, after the excessively complete solid-phase extraction column of water sample, uses 5mL deionized waters Solid-phase extraction column is got express developed, flow velocity is 7mL/min, is then dried solid-phase extraction column 30min, finally with 5mL methyl alcohol with 3mL/ Min flow velocitys elute solid-phase extraction column, collect eluent, are labeled as eluent 2;Above-mentioned solid-phase extraction column used is Waters Oasis HLB solid-phase extraction columns, specification is 6cc/500mg, 60um;Merge eluent 1 and 2, in 40 DEG C of water-baths, with gentle Nitrogen is dried up, and is finally settled to 1mL with water, after 0.45um teflon membrane filters, that is, obtains sample solution;
3) using high pressure liquid chromatography-mass spectrograph detection:
A. the preparation of standard liquid:Standard items antibiotic, hygromycin, Lovastatin, acarbose, Thailand are accurately weighed respectively Happy rhzomorph, erythromycin, sulphadiazine, gentamicin, penicillin, sulfamethoxazole, using deionized water dissolving, are made into respectively The Standard Stock solutions of 0.2mg/mL, according to the response of each antibiotic when using, deionized water is diluted to standard working solution;
B. using high pressure liquid chromatography-mass spectrograph examination criteria working solution and sample solution:Inhaled respectively by automatic sampler Standard working solution and sample solution are taken, in injection high pressure liquid chromatography-mass spectrograph, the antibiotic group lease making liquid chromatogram in sample Post separation, liquid phase chromatogram condition:Chromatographic column:SB-C18,3.5um, 2.1 × 150mm;Mobile phase:A is 0.1% formic acid, and B is second Nitrile;Gradient elution:0-2min, 10%B;2-7min, 10-40%B, 7-9min, 40-90%B, 9-10min, 90-100%B;Post Temperature:Room temperature;The detection of mass spectrograph multiple-reaction monitoring pattern, Mass Spectrometry Conditions:Mass analyzer:Triple level Four bars, scan pattern:Just from Son-reaction monitoring pattern, ion gun:Electric spray ion source, spray voltage:4.5kV, removes solvent temperature:500 DEG C, remove solvent gas Rate of flow of fluid:600L/h;
4) data analysis:As shown in table 1, with the parent ion and daughter ion of compound as quota ion and qualitative ion;With Mass concentration X of standard working solution is abscissa, and the peak area Y of quantitative and qualitative ion is ordinate, draws standard working curve, Single ion quantified by external standard method is carried out to sample with standard working curve;With the chromatographic peak retention time and mother that occur in sample solution Ion/daughter ion is qualitative to carrying out, and the chromatogram for obtaining is shown in Fig. 1.
Table 1:The mass spectrometry parameters of 9 kinds of antibiotic
Title Parent ion/(m/z) Daughter ion/(m/z) Taper hole voltage/V Collision energy/V
Gentamicin 478.28 157.16 26 20
Lovastatin 405.16 131.35 52 38
Penicillin 335.07 217.10 56 16
Sulfamethoxazole 254.02 156.00 28 16
Sulphadiazine 251.02 155.99 24 16
Tylosin 916.55 174.12 90 36
Erythromycin 734.49 158.12 44 38
Acarbose 646.28 304.19 40 26
Hygromycin 528.26 177.11 52 32
Finally it should be noted that:Above example only to illustrate technical scheme, rather than a limitation;Although The present invention has been described in detail with reference to the foregoing embodiments, it will be understood by those within the art that:It still may be used To modify to the technical scheme described in previous embodiment, or equivalent is carried out to which part technical characteristic;And These modifications are replaced, and do not make the spirit and model of the essence disengaging embodiment of the present invention technical scheme of appropriate technical solution Enclose.

Claims (4)

1. the method that high pressure liquid chromatography-mass spectrometry detects Multiple Classes of Antibiotics content in water, it is characterised in that including following step Suddenly:
1) pH of water sample is adjusted:A 250mL water samples are measured, appropriate formic acid is added, pH to 2.0 is adjusted, a 250mL is separately measured Water sample, adds appropriate ammoniacal liquor, adjusts pH to 12.0;
2) the solid phase extraction concentration concentration of water sample after pH is adjusted:Extracted with 5mL methyl alcohol and 10mL deionized waters activated solid respectively Post 1, flow velocity is that the 250mL water samples that pH is adjusted to 2.0 are crossed into solid-phase extraction column after 5-10mL/min activation, and flow velocity is 3-5mL/min, After the excessively complete solid-phase extraction column of water sample, with 5mL deionized waters solid-phase extraction column is got express developed, flow velocity is 5-10mL/min, Ran Hougan Dry solid-phase extraction column 30min, finally elutes solid-phase extraction column with 5mL methyl alcohol with 3mL/min flow velocitys, collects eluent, is labeled as Eluent 1;Respectively with 5mL methyl alcohol and 10mL deionized water activated solids extraction column 2, flow velocity is by pH after 5-10mL/min activation The 250mL water samples for being adjusted to 12.0 cross solid-phase extraction column, and flow velocity is 3-5mL/min, after the excessively complete solid-phase extraction column of water sample, is gone with 5mL Ionized water gets solid-phase extraction column express developed, and flow velocity is 5-10mL/min, is then dried solid-phase extraction column 30min, finally uses 5mL first Alcohol elutes solid-phase extraction column with 3mL/min flow velocitys, collects eluent, is labeled as eluent 2;Merge eluent 1 and 2, at 40 DEG C In water-bath, dried up with gentle nitrogen, be finally settled to 1mL with water, that is, obtain sample solution.
3) using high pressure liquid chromatography-mass spectrograph detection:
A. the preparation of standard liquid:Standard items antibiotic is accurately weighed respectively, using deionized water dissolving, 0.2mg/ is made into respectively The Standard Stock solutions of mL, according to the response of each antibiotic when using, deionized water is diluted to standard working solution;
B. using high pressure liquid chromatography-mass spectrograph examination criteria working solution and sample solution:Mark is drawn respectively by automatic sampler Quasi- working solution and sample solution, in injection high pressure liquid chromatography-mass spectrograph, the antibiotic group lease making liquid-phase chromatographic column in sample point From the detection of mass spectrograph multiple-reaction monitoring pattern.
4) data analysis:With the parent ion and daughter ion of compound as quota ion and qualitative ion;With the matter of standard working solution Amount concentration X is abscissa, and the peak area Y of quantitative and qualitative ion is ordinate, draws standard working curve, uses standard working curve Single ion quantified by external standard method is carried out to sample;With the chromatographic peak retention time and parent ion/daughter ion pair that occur in sample solution Carry out qualitative.
2. the method that high pressure liquid chromatography as claimed in claim 1-mass spectrometry detects Multiple Classes of Antibiotics content in water, it is special Levy and be, formic acid used and ammoniacal liquor are top pure grade in the step 1.
3. the method that high pressure liquid chromatography as claimed in claim 2-mass spectrometry detects Multiple Classes of Antibiotics content in water, it is special Levy and be, solid-phase extraction column used is Waters Oasis HLB solid-phase extraction columns in the step 2, and specification is 6cc/ 500mg, 60um.
4. the method that high pressure liquid chromatography as claimed in claim 1-mass spectrometry detects Multiple Classes of Antibiotics content in water, it is special Levy and be, the antibiotic standard items in the step 3 are respectively hygromycin, Lovastatin, acarbose, tylosin, red mould Element, sulphadiazine, gentamicin, penicillin, sulfamethoxazole.
CN201611192699.1A 2016-12-21 2016-12-21 The method of Multiple Classes of Antibiotics content in high pressure liquid chromatography-mass spectrometry detection water Active CN106596780B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611192699.1A CN106596780B (en) 2016-12-21 2016-12-21 The method of Multiple Classes of Antibiotics content in high pressure liquid chromatography-mass spectrometry detection water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611192699.1A CN106596780B (en) 2016-12-21 2016-12-21 The method of Multiple Classes of Antibiotics content in high pressure liquid chromatography-mass spectrometry detection water

Publications (2)

Publication Number Publication Date
CN106596780A true CN106596780A (en) 2017-04-26
CN106596780B CN106596780B (en) 2019-06-25

Family

ID=58602318

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611192699.1A Active CN106596780B (en) 2016-12-21 2016-12-21 The method of Multiple Classes of Antibiotics content in high pressure liquid chromatography-mass spectrometry detection water

Country Status (1)

Country Link
CN (1) CN106596780B (en)

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107941928A (en) * 2017-10-24 2018-04-20 东莞市环境监测中心站 A kind of method of antibiotic in liquid chromatography mass Simultaneous Determination environment water
CN108896677A (en) * 2018-07-17 2018-11-27 大连职业技术学院 The method for quickly detecting metrafenone in water using LC-MS technology
CN109738565A (en) * 2019-01-31 2019-05-10 徐敦明 The method of compound is illegally added in a kind of measurement health food
CN110133131A (en) * 2019-05-15 2019-08-16 上海大学 The quick determination method of statins in water body
CN111707741A (en) * 2020-06-02 2020-09-25 南京大学 Non-target identification method for trace organic pollutant conversion product in environment medium
CN112595801A (en) * 2020-12-31 2021-04-02 公安部物证鉴定中心 Method for detecting blood fat reducing medicine in sample to be detected containing organism fingerprint
CN115166101A (en) * 2022-08-04 2022-10-11 南京理工大学 Comprehensive screening method for comprehensively identifying new pollutants in water sample

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103293248A (en) * 2013-06-20 2013-09-11 中国环境科学研究院 Method for separating and enriching sulfanilamide antibiotics in water
CN104483427A (en) * 2014-12-08 2015-04-01 华东理工大学 Method for separating, enriching and detecting 12 antibiotics in drinking water source
CN104990996A (en) * 2015-05-19 2015-10-21 江苏出入境检验检疫局动植物与食品检测中心 Method for detecting antibiotic residues in milk, and application thereof
CN105388245A (en) * 2015-12-25 2016-03-09 浙江省水产技术推广总站 Screening method suitable for 46 kinds of medicine in aquatic products
CN105548392A (en) * 2015-12-11 2016-05-04 中国农业科学院农业资源与农业区划研究所 Method for simultaneously detecting various antibiotics in livestock and poultry manure by high performance liquid chromatography
CN105699537A (en) * 2016-04-07 2016-06-22 大连理工大学 Synchronous detection method for plurality of types of drug residues in water body
CN106093220A (en) * 2016-05-30 2016-11-09 天津大学 Detection method while 12 kinds of typical antibiotic in sewage and mud

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103293248A (en) * 2013-06-20 2013-09-11 中国环境科学研究院 Method for separating and enriching sulfanilamide antibiotics in water
CN104483427A (en) * 2014-12-08 2015-04-01 华东理工大学 Method for separating, enriching and detecting 12 antibiotics in drinking water source
CN104990996A (en) * 2015-05-19 2015-10-21 江苏出入境检验检疫局动植物与食品检测中心 Method for detecting antibiotic residues in milk, and application thereof
CN105548392A (en) * 2015-12-11 2016-05-04 中国农业科学院农业资源与农业区划研究所 Method for simultaneously detecting various antibiotics in livestock and poultry manure by high performance liquid chromatography
CN105388245A (en) * 2015-12-25 2016-03-09 浙江省水产技术推广总站 Screening method suitable for 46 kinds of medicine in aquatic products
CN105699537A (en) * 2016-04-07 2016-06-22 大连理工大学 Synchronous detection method for plurality of types of drug residues in water body
CN106093220A (en) * 2016-05-30 2016-11-09 天津大学 Detection method while 12 kinds of typical antibiotic in sewage and mud

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
张俊 等: "水体中磺胺、四环素、喹诺酮类抗生素检测方法", 《中国环境监测》 *
杜鹃 等: "固相萃取-高效液相色谱-串联质谱法同时测定养殖海水中23种抗生素", 《色谱》 *
闾幸 等: "固相萃取-液相色谱-串联质谱法测定猪栏废水中10种抗生素", 《理化检验(化学分册)》 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107941928A (en) * 2017-10-24 2018-04-20 东莞市环境监测中心站 A kind of method of antibiotic in liquid chromatography mass Simultaneous Determination environment water
CN108896677A (en) * 2018-07-17 2018-11-27 大连职业技术学院 The method for quickly detecting metrafenone in water using LC-MS technology
CN109738565A (en) * 2019-01-31 2019-05-10 徐敦明 The method of compound is illegally added in a kind of measurement health food
CN109738565B (en) * 2019-01-31 2021-09-24 徐敦明 Method for determining illegally added compounds in health food
CN110133131A (en) * 2019-05-15 2019-08-16 上海大学 The quick determination method of statins in water body
CN111707741A (en) * 2020-06-02 2020-09-25 南京大学 Non-target identification method for trace organic pollutant conversion product in environment medium
CN112595801A (en) * 2020-12-31 2021-04-02 公安部物证鉴定中心 Method for detecting blood fat reducing medicine in sample to be detected containing organism fingerprint
CN112595801B (en) * 2020-12-31 2024-05-10 公安部物证鉴定中心 Method for detecting hypolipidemic drugs in sample to be detected containing organism fingerprint
CN115166101A (en) * 2022-08-04 2022-10-11 南京理工大学 Comprehensive screening method for comprehensively identifying new pollutants in water sample

Also Published As

Publication number Publication date
CN106596780B (en) 2019-06-25

Similar Documents

Publication Publication Date Title
CN106596780A (en) Method for detecting contents of various antibiotics in water by combined use of high pressure liquid chromatography and mass spectrum
Chen et al. Analysis of alkaloids in Coptis chinensis Franch by accelerated solvent extraction combined with ultra performance liquid chromatographic analysis with photodiode array and tandem mass spectrometry detections
CN104535664B (en) A kind of method simultaneously detecting multiple mycotoxin in sesame paste
CN102353742B (en) Method for selectively measuring 7 benzene series in white latex for cigarette through static headspace-gas chromatograph mass spectrum
CN103048401B (en) Determining method for 15 kinds of forbidden nitro imidazoles antibiotics in cosmetics
Hu Simultaneous determination of phenylurea herbicides in yam by capillary electrophoresis with electrochemiluminescence detection
CN108318613A (en) The detection method of antibiotic in a kind of environmental sample
CN102798689B (en) Method for separation enrichment and detection of trace fluoroquinolone antibiotic in water environment
CN105784894B (en) Pesticide residue detection method for traditional Chinese medicine
CN106855545A (en) Liposoluble vitamin simultaneously in detection feed and the method for water soluble vitamin
CN105548431B (en) Detect the method for oxamyl and oxamyl oxime residual quantity in vegetables/fruit simultaneously
CN109682897A (en) A kind of method of a variety of incretion interferents in while determination of the environment water sample
CN102944636B (en) High-efficiency liquid chromatography to mass spectrum detection method for ethyl carbamate in distilled liquor
CN111830141A (en) Method for screening pesticide residues in medicine-food homology food by using pesticide residue mass spectrum database
CN110455961B (en) High-flux detection method for multiple components in health-care wine
CN103364514A (en) High performance liquid chromatography-time-of-flight mass spectrometry hyphenated method capable of simultaneously and rapidly screening and identifying alkaloid in water sample
CN108008056B (en) Application of gelsemium elegans alkaloid as biological marker of toxic honey
Yang et al. Determination of swainsonine in the endophytic Undifilum fungi by high-performance liquid chromatography with evaporative light-scattering detector
CN110887911B (en) Gas chromatography-tandem mass spectrometry detection method for clotrimazole residues in animal-derived food
CN102944635B (en) Method for determining tris (2,3-dibromopropyl) phosphate content of water
Li et al. Simultaneous quantification of 17 bioactive constituents in Sarcandra glabra by liquid chromatography-electrospray ionisation-mass spectrometry
CN105158372A (en) Method for determining urocanic acid and ethyl ester thereof in cosmetics
CN112986476B (en) Method for measuring residual quantity of cuaminosulfate in vegetables and fruits
CN114878708A (en) Method for detecting 5 amanitin toxins, dephosphorized naked cap mushroom essence and toad tryptamine
CN102901778A (en) Pretreatment method for detecting chloramphenicol in milk or mild products and method for detecting chloramphenicol in milk or mild products

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