CN106053631A - Automatic dispersed liquid-liquid micro-extraction system and applications thereof - Google Patents

Automatic dispersed liquid-liquid micro-extraction system and applications thereof Download PDF

Info

Publication number
CN106053631A
CN106053631A CN201610341550.9A CN201610341550A CN106053631A CN 106053631 A CN106053631 A CN 106053631A CN 201610341550 A CN201610341550 A CN 201610341550A CN 106053631 A CN106053631 A CN 106053631A
Authority
CN
China
Prior art keywords
mouth
sample
extractant
dispersant
liquid
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.)
Pending
Application number
CN201610341550.9A
Other languages
Chinese (zh)
Inventor
冷庚
铁博
杜亚鹏
胡涵林
何钰
乔晓慧
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.)
University of Electronic Science and Technology of China
Original Assignee
University of Electronic Science and Technology of China
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 University of Electronic Science and Technology of China filed Critical University of Electronic Science and Technology of China
Priority to CN201610341550.9A priority Critical patent/CN106053631A/en
Publication of CN106053631A publication Critical patent/CN106053631A/en
Pending legal-status Critical Current

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
    • G01N2030/025Gas 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
    • G01N2030/062Preparation extracting sample from raw material

Abstract

The invention discloses an automatic dispersed liquid-liquid micro-extraction system, which comprises an injection pump, an 8-position electromagnetic rotary valve, a three-way valve, a mixer, and a control device. On the basis of the system, an automatic in-situ DLLME method is established, the DLLME method is used to extract PAEs in natural water and has the advantages of simpleness, miniaturization, and efficiency, and after extraction, the sample is analyzed by gas chromatography-mass spectrum (GC-MS). The test results show that the provided system can be used to in-situ extract PAEs from a ground water sample, the detection limit is low, moreover, the extraction time is short, the sample throughput is large, and the system can be used to process trace PAEs in natural water onsite automatically.

Description

A kind of full-automatic dispersion liquid-liquid current micro-extraction system and application thereof
Technical field
The present invention relates to a kind of full-automatic dispersion liquid-liquid current micro-extraction system, further relate to its O-phthalic in Environmental Water Application in esters of gallic acid extracting substances.
Background technology
Phthalic acid ester (being commonly called as plasticiser, PAEs) can increase the plasticity of plastic, is widely used in industry Produce and in goods.Owing to PAEs is more weak with the intermolecular forces of polymer, the PAEs in plastic is very easy to be released to In food, beverage and natural water.There are some researches show, PAEs is a kind of environmental endocrine disruptors, can be to human body Kidney, hormonal system, reproductive system and respiratory system cause serious harm.Therefore, PAEs is all classified as preferential dirt by various countries Dye thing is strictly monitored and controlled.But PAEs concentration in environment water is the lowest, and aqueous samples is complicated, is often analyzing Need sample is effectively separated enrichment before.
Dispersion liquid-liquid micro-extraction (DLLME) is a kind of simplification, milligram ammonia and high efficiency separation and concentration technology, and It is successfully applied to the extraction of PAEs.In DLLME, the extractant of trace and appropriate dispersant, then it is rapidly injected In sample, under the effect of dispersant, the extractant of trace disperses in the sample with the form of superfine microdroplet, forms dispersion System.Under such dispersion, on the one hand add the contact area of extractant and sample, on the other hand decrease object To the mass transfer distance of extractant, therefore extraction efficiency is greatly improved.After extraction, by centrifugal, extractant is deposited on test tube Bottom or float over sample surfaces, Instrumental Analysis can be entered with microsyringe after pipetting.
At present, common dispersion liquid-liquid micro-extracting method includes multiple, such as ionic liquid-dispersive liquid-liquid microextraction, super Sound wave aid dispersion liquid-liquid micro-extraction-organic drop solid-state that suspends, air aid dispersion liquid-liquid micro-extraction etc..But, at these In method, it is all manual operation, complex operation, the longest, and detection limit is higher, and the original position being also unsuitable for sample is (the most existing Field on field) process.
Therefore, it is necessary to set up a kind of simple, miniaturization, efficient full-automatic DLLME system in situ for Environmental Water The extraction of PAEs in body.
Summary of the invention
For solving the problems referred to above, the invention provides a kind of full-automatic dispersion liquid-liquid current micro-extraction system, it includes injection Pump, 8 electromagnetic rotating valves, three-way valve, blender and control device;
Described syringe pump, three-way valve are connected with control device with electromagnetic valve;
Described syringe pump is provided with syringe;
Described electromagnetic valve is provided with discharging opening, logical blender mouth, enters air scoop, water inlet, injection port, waste discharge mouth, enters point Powder mouth and enter extractant mouth;
Described three-way valve includes liquid outlet (A), inlet (B) and commutation mouth (C);
Wherein, the inlet (B) of described three-way valve is communicated by connecting tube with the discharging opening of electromagnetic valve, commutation mouth (C) with The geat of syringe communicates;Logical blender mouth on described electromagnetic valve is communicated by connecting tube with blender.
Further, it is additionally provided with between described blender with logical blender mouth and mixes circle.
Further, described connecting tube is the polyfluortetraethylene pipe of 0.79mm internal diameter.
Present invention also offers a kind of phthalate extracting substances method in Environmental Water, described phthalic acid Ester includes any one in dibutyl phthalate, dimethyl phthalate and dioctyl phthalate or many Kind, it uses weighs aforesaid full-automatic dispersion liquid-liquid current micro-extraction system, comprises the following steps:
(1) syringe and pipeline are cleaned:
Making inlet (B) and commutation mouth (C) communicate, syringe sucks ultra-pure water from water inlet, then by waste discharge mouth 5 row Go out;
(2) extractant and the mixing of dispersant:
Syringe is first from entering dispersant mouth suction dispersant and sucking extractant from entering extractant mouth, then inhales from entering air scoop Enter air, then discharge it into formation mixed liquor in blender, then by this mixed liquor inhalation syringe;
Wherein, the order sucking dispersant and suction extractant can be optional.
(3) sample injects:
Syringe sucks testing sample from injection port, mixes with the mixed liquor of step (3), forms dispersion;
(4) extraction and the collection of object:
After stratification goes out organic facies, make liquid outlet (A) and commutation mouth (C) communicate, discharge organic facies from liquid outlet (A), Collect stand-by;
(5) waste liquid is discharged:
Make liquid outlet (B) and commutation mouth (C) communicate, remaining sample is discharged by waste discharge mouth.
Further, in step (2), described extractant is selected from toluene or dimethylbenzene, and dispersant is selected from acetone, acetonitrile or first Alcohol;Preferably extractant is toluene, and dispersant is acetonitrile.
Further, in step (2), the dispersant of described suction and extractant volume ratio are 20:1.
Further, in step (3), the suction speed of described suction sample is 125mL/min.
Further, in step (4), the time of described stratification is 60 seconds.
Further, described Environmental Water is surface water.
Further, described phthalate material includes dibutyl phthalate, dimethyl phthalate With any one or more in dioctyl phthalate.
Therefore, the invention provides a kind of full-automatic dispersion liquid-liquid current micro-extraction system, on the basis of this system, set up A kind of simple, miniaturization, the efficient full-automatic extraction of PAEs in natural water of DLLME method in situ, extracted After finishing, sample is analyzed through gas chromatography mass spectrometer (GC-MS).
The present invention optimizes the key parameter of method the most further, such as extractant and the kind of dispersant and consumption, sample Product injection rate, extraction time, sample pH value, salt effect and matrix effect etc..Finally, the inventive method is used for reagent ground The situ extracting of PAEs in table water sample, has relatively low detection limit, and extraction time is short, and sample throughput is big, it is adaptable to The on-the-spot full automatic treatment of trace PAEs in natural water.
Obviously, according to the foregoing of the present invention, according to ordinary technical knowledge and the customary means of this area, without departing from Under the present invention above-mentioned basic fundamental thought premise, it is also possible to make the amendment of other various ways, replace or change.
The detailed description of the invention of form by the following examples, remakes the most specifically the foregoing of the present invention Bright.But this should not being interpreted as, the scope of the above-mentioned theme of the present invention is only limitted to Examples below.All based on foregoing of the present invention The technology realized belongs to the scope of the present invention.
Accompanying drawing explanation
Fig. 1 is present system structural representation.
Fig. 2 is the optimum decision system structural representation employed in the embodiment of the present invention 1, and electromagnetic valve is provided with discharging port A, leads to Blender mouth 1, enter air scoop 2, water inlet 3, injection port 4, waste discharge mouth 5, enter dispersant mouth 7 and enter extractant mouth 8;SP be complete from Dynamic syringe pump;MPV is one 8 electromagnetic rotating valves (MPV);V is dedicated three-way selector valve.
Fig. 3 is full-automatic DLLME effect of extracting schematic diagram: (a) rinse;(b) extractant and the mixing of dispersant;(c) sample Product inject, and dispersion is formed;(d) stratification;The collection of (e) organic facies.
Fig. 4 is different extractant and full-automatic DLLME effect of extracting is affected by dispersant.Wherein 1 toluene-acetone 2 toluene- Acetonitrile 3 methylbenzene methanol l;4 dimethylbenzene acetone;5 dimethylbenzene-acetonitrile 6 dimethylbenzene-methanol;7 normal hexane-acetone;8 hexamethylene-the third Ketone;9 isobutyltrimethylmethane .s-acetone. experiment condition: sample volume 5mL;Sample injection rate 150ml/min;Extraction time 2min;Do not increase Add ionic strength;Sample mark-on 5.0ng;N=3.
Fig. 5 is that extractant and dispersant volume are to DLLME influential effect.
Fig. 6 is full-automatic DLLME-GC-MS chromatogram. (a) sample mark-on 5.0ng;B () is mark-on sample.
Detailed description of the invention
Reagent and material:
The PAEs standard reserving solution of 1g/L, including dibutyl phthalate (DBP), dimethyl phthalate (DMP), Dioctyl phthalate (DNOP) is purchased from Germany Merck;PAEs standard working solution is diluted by standard reserving solution ultra-pure water Obtain.
Chromatographically pure normal hexane, toluene, dimethylbenzene, isobutyltrimethylmethane., hexamethylene, and analytically pure sodium chloride, hydrochloric acid, hydrogen-oxygen Change sodium purchased from Chengdu Ke Long Reagent Company.
Chromatographically pure methanol, acetonitrile, acetone are purchased from U.S. Tedia.
For avoiding PAEs to pollute, first all glass drying ovens need to soak 6h in acetone, then dry 4h at 140 DEG C.
The system and method for embodiment 1 present invention
(1) system of the present invention
Full-automatic DLLME system schematic used by the present embodiment is as shown in Figure 2.This full-automatic DLLME system is by one The full-automatic injecting pump (SP) of 9600 steps and one 8 electromagnetic rotating valves (MPV) are constituted.All connecting tubes are by 0.79mm internal diameter Politef (PTFE) pipe is constituted.The syringe of dedicated three-way selector valve (V) and 1 10mL is provided on SP.MPV is used for sample The transfer of product, extractant, dispersant, high purity water, air, waste liquid and other reagent and switching.Mixing pit (MC) is by 5mL's Barrel syringe is constituted, for dispersant and the mixing of extractant.Whole system (except notebook computer) is by an AC adapter It is powered with one group of lithium battery, and runs under 24V DC.Whole system is light and handy, portable, and weight is only 2.6kg and (includes electricity Source).
Sample after extraction is combined 5975 type mass spectrographs by 7890 type gas chromatograies of Agilent company of the U.S. to be carried out Quantitative analysis.Chromatographic column: HP-5MS (5%phenyl, 95%methylpolysiloxane, 30m × 0.25mm id × 0.25 μ M) capillary column;Helium (> 99.999%) make carrier gas, flow 1.0mL/min.Injector temperature: 250 DEG C;Sample introduction pattern: regardless of Stream.Column temperature program is as follows: 60 DEG C, keeps 1min, with 20 DEG C of min-1It is warming up to 220 DEG C, keeps 1min, with 5 DEG C of min-1Heat up To 280 DEG C, keep 4min.Mass detector uses Salbutamol Selected Ion Monitoring pattern (SIM).Solvent delay 6min.Sweep time and Monitoring ion is as follows: DMP, 6.0min, m/z 163,77,135;DBP,10.0min,m/z149,223,205;DNOP, 18.0min,149,279,167。
(2) sample and DLLME system operation programs
Natural water sample picks up from clear water river (Chengdu, China).After sample collecting, it is introduced directly into complete after crossing 0.22 μm filter membrane Automatically DLLME system processes.
Electromagnetic valve is provided with discharging port A, logical blender mouth 1, enters air scoop 2, water inlet 3, injection port 4, waste discharge mouth 5, enters Dispersant mouth 7 and enter extractant mouth 8.
DLLME working procedure:
(1) clean syringe pump and pipeline: SP sucks 10mL ultra-pure water (, No. 3 positions, V is in b position for MPV), then by waste liquid Send (, No. 5 positions, V is in b position for MPV), the most reciprocal 3 times.
(2) extractant and the mixing of dispersant: SP suck 1mL dispersant (, No. 7 positions, V is in b position for MPV), 50 μ L successively Extractant (, No. 8 positions, V is in b position for MPV) and 2mL air (, No. 2 positions, V is in b position for MPV), discharge it into the most again In MC (, No. 1 position, V is in b position for MPV), for more effectively making dispersant and extractant mixing, the most reciprocal 2 times of this step, and During the mixed liquor of dispersant and extractant sucks SP the most at last.
(3) sample injects: 5mL sample is quickly sucked in SP with the speed of 125mL/min, and (, No. 4 positions, V is at b for MPV Number position), it is consequently formed dispersion.
(4) extraction and the collection of object: after forming dispersion, stands, and target substance is quickly at sample and extractant Between reach balance, after 60s, organic facies floats on sample top layer, and switching V (a position) slowly promotes SP, 60 μ L min-1, by organic It is collected in mutually in sample bottle, preserves to be measured.
(5) discharge waste liquid: switching MPV and V (, No. 5 positions, V is in b position for MPV), remaining sample is sent by waste liquid.
The effect of whole extraction process is as shown in Figure 3.
The craft screening of embodiment 2 the inventive method
1 extractant and the impact of dispersant
Compare variety classes extractant (normal hexane, toluene, dimethylbenzene, isobutyltrimethylmethane., hexamethylene) and dispersant (acetonitrile, Acetone, methanol) impact on effect of extracting.
Sample volume 5mL;Sample injection rate 150ml/min;Extraction time 2min;Do not increase ionic strength;Sample adds Mark 5.0ng;N=3;The ratio of all extractants and dispersant is 1:19, and cumulative volume is 1mL.Result is as shown in Figure 4.Result Show, when toluene is as extractant, when acetonitrile is as dispersant, best results.
2 extractants and the impact of dispersant volume
The study tour extractant of different volumes (50to 150 μ L) and dispersant (0.25to 1.25mL) are to extraction effect The impact of fruit, result is as shown in Figure 5.
Result shows, in 3, plasticiser variation tendency is similar, when 50 μ L extractants and 1mL dispersant are used for DLLME system Time, extracting and enriching multiple is the highest, and effect of extracting is best.Wherein, enrichment times increases along with the minimizing of the amount of extractant, but When extractant volume is less than 50 μ L, organic facies becomes unstable and is difficult to collect.It addition, enrichment times is along with the amount of dispersant Increase and increase, but when the amount of dispersant is more than 1mL, declining occurs in enrichment times,
Therefore, 50 μ L extractants and 1mL dispersant selected be optimal.
The impact on effect of extracting of the 3 sample suction velocities
In the methods of the invention, sample is quickly sucked into SP, and with extractant/dispersant, formed dispersion. Inventor have studied different sample and sucks speed (30to 150mL min-1) to this DLLME influential effect.
Result shows, increases to 125mL min along with sample sucks speed from 30-1, recovery of extraction and enrichment times increase Add, when sample sucks speed more than 125mL min-1Time, effect of extracting is unaffected.The pump speed of two-forty can affect it and use the longevity Life, therefore the inventive method selects 125mL min-1Sample suck speed be optimal.
The impact of 4 extraction times
In the methods of the invention, extraction time be defined as sample be inhaled into formation dispersion and proceed by sample receive This time interval between collection.Have studied different extraction time (30,45,60,90,120,180,240and 300s) to extraction Take the impact of effect.
Research shows, when extraction time is less than 30s, it is impossible to realize two-phase laminated flow, and recovery of extraction and enrichment times with The increase of extraction time and increase.But, after extraction time is more than 60s, effect of extracting is without significant change.Therefore, the extraction of 60s The time of taking is considered optimal.
5 salt effects and the impact of sample pH value
Have studied the impact on effect of extracting of the different sample pH value (2 to 11).Utilize 0.1M HCl and NaOH to regulate sample pH.Result shows, along with the change of sample pH value, effect of extracting is without significant change.Therefore, extraction process is without regulating sample pH value.
In liquid-phase extraction, it will usually add salt and improve sample ions intensity, thus improve effect of extracting.Therefore, grind Study carefully the impact having investigated different ionic strength to effect of extracting, add the NaCl (0to 5%, m/v) of variable concentrations in the sample, Result shows, the sample extraction response rate and enrichment times reduce along with the increase of salinity.
Therefore, in the methods of the invention without adding salt.
6 method performance parameters
Fig. 6 is under optimal conditions, utilizes the chromatogram of the PAEs that the inventive method obtains.The main performance of the inventive method Parameter, including detection limit, the range of linearity, correlation coefficient, enrichment times, the response rate and repeatability etc., is shown in Table 1.Full-automatic DLLME The extraction of method single sample is spaced apart 170s, and sample throughput is 21h-1
The full-automatic DLLME-GC/MS methods analyst performance parameter of PAEs in table 1 natural water
A:n=3;B: sample mark-on 1.0ng PAEs;C: sample mark-on 5.0ng PAEs;D: sample mark-on 10ng PAEs.
The inventive method is compared with other non-automated DLLME methods, the results are shown in Table 2.
The contrast of the non-full-automatic DLLME method of table 2 the inventive method and other PAEs
aIonic liquid-dispersive liquid-liquid microextractionb1-octyl group-3-Methylimidazole. hexafluorophosphatecUltrasonic assistant dispersion liquid Liquid micro-extraction-suspend organic drop solid statedThe dispersion of extractant is realized by 8 air injections
[1]Pérez-Outeiral J.,Millán E.,Garcia-Arrona R.,Determination of phthalates in food simulants and liquid samples using ultrasound-assisted dispersive liquid-liquid microextraction followed by solidification of floating organic drop.Food Control,2016,62,171-177.
[2]Mousa A.,Basheer C.,Al-Arfaj A.R.,Determination of phthalate esters in bottled water using dispersive liquid-liquid microextraction coupled with GC-MS.J.Sep.Sci.2013,36,2003-2009.
[3]Chen S.,Zhong Y.,Cheng S.,Qian T.,Sun H.,Development of an ionic liquid-based dispersive liquid-liquid micro-extraction method for the determination of phthalate esters in water samples.J.Sep.Sci.2011,34,1503- 1507.
[4]Farajzadeh M.A.,Mogaddam M.R.A.,Air-assisted liquid-liquid microextraction method as a novel microextraction technique;Application in extraction and preconcentration of phthalate esters in aqueous sample followed by gas chromatography-flame ionization detection.Anal.Chim.Acta 2012,728,31-38.
[5]Farahani H.,Norouzi P.,Dinarvand R.,Ganjali M.R.,Development of dispersive liquid-liquid microextraction combined with gas chromatography- mass spectrometry as a simple,rapid and highly sensitive method for the determination of phthalate esters in water samples.J.Chromatogr.A 2007,1172, 105-112
Comparing compared with these methods existing, the inventive method has relatively low detection limit, and, the inventive method extracts Taking the time short, sample throughput is big, it is adaptable to the on-the-spot full automatic treatment of trace PAEs in natural water.
7 actual sample analyses
Utilize the inventive method that the PAEs in 6 samples of clear water river section (Chengdu, China) is processed and divided Analysis, the results are shown in Table 3.
PAEs result in the full-automatic DLLME extractive analysis actual sample in situ of table 3
aN=3bSample mark-on 5.0ng PAEscDo not detect
Result shows, has all detected the DBP of variable concentrations in all samples.Additionally, the recovery testu of variable concentrations Effect is satisfactory, shows that the inventive method is accurate, capacity of resisting disturbance strong, without matrix effect.
In sum, the invention provides a kind of full-automatic dispersion liquid-liquid current micro-extraction system, on the basis of this system, Establish a kind of simple, miniaturization, efficient full-automatic DLLME method extraction of PAEs in natural water in situ, extraction After taking, sample is analyzed through gas chromatography mass spectrometer (GC-MS).
The present invention optimizes the key parameter of method the most further, such as extractant and the kind of dispersant and consumption, sample Product injection rate, extraction time, sample pH value, salt effect and matrix effect etc..Finally, the inventive method is used for reagent ground The situ extracting of PAEs in table water sample, has relatively low detection limit, and extraction time is short, and sample throughput is big, it is adaptable to The on-the-spot full automatic treatment of trace PAEs in natural water.

Claims (10)

1. a full-automatic dispersion liquid-liquid current micro-extraction system, it is characterised in that: it include syringe pump, 8 electromagnetic rotating valves, three Logical valve, blender and control device;
Described syringe pump, three-way valve are connected with control device with electromagnetic valve;
Described syringe pump is provided with syringe;
Described electromagnetic valve is provided with discharging opening, logical blender mouth, enters air scoop, water inlet, injection port, waste discharge mouth, enters dispersant Mouthful and enter extractant mouth;
Described three-way valve includes liquid outlet (A), inlet (B) and commutation mouth (C);
Wherein, the inlet (B) of described three-way valve is communicated by connecting tube with the discharging opening of electromagnetic valve, commutation mouth (C) and injection The geat of device communicates;Logical blender mouth on described electromagnetic valve is communicated by connecting tube with blender.
System the most according to claim 1, it is characterised in that: it is additionally provided with between described blender with logical blender mouth and mixes Circle.
System the most according to claim 1 and 2, it is characterised in that: described connecting tube is the polytetrafluoroethyl-ne of 0.79mm internal diameter Alkene pipe.
4. the phthalate extracting substances method in an Environmental Water, it is characterised in that: described phthalate Material includes any one or more in dibutyl phthalate, dimethyl phthalate and dioctyl phthalate, It uses the full-automatic dispersion liquid-liquid current micro-extraction system described in any one of claim 1-3, comprises the following steps:
(1) syringe and pipeline are cleaned:
Making inlet (B) and commutation mouth (C) communicate, syringe sucks ultra-pure water from water inlet, is then discharged by waste discharge mouth;
(2) extractant and the mixing of dispersant:
Syringe is first from entering dispersant mouth suction dispersant and sucking extractant from entering extractant mouth, then sucks sky from entering air scoop Gas, then discharge it into formation mixed liquor in blender, then by this mixed liquor inhalation syringe;
(3) sample injects:
Syringe sucks testing sample from injection port, mixes with the mixed liquor of step (3), forms dispersion;
(4) extraction and the collection of object:
After stratification goes out organic facies, make liquid outlet (A) and commutation mouth (C) communicate, discharge organic facies from liquid outlet (A), collect Stand-by;
(5) waste liquid is discharged:
Make liquid outlet (B) and commutation mouth (C) communicate, remaining sample is discharged by waste discharge mouth.
Method the most according to claim 4, it is characterised in that: in step (2), described extractant is selected from toluene or diformazan Benzene, dispersant is selected from acetone, acetonitrile or methanol;Preferably extractant is toluene, and dispersant is acetonitrile.
Method the most according to claim 5, it is characterised in that: in step (2), the dispersant of described suction and extractant body Long-pending ratio is 20:1.
Method the most according to claim 4, it is characterised in that: in step (3), the suction speed of described suction sample is 125mL/min。
Method the most according to claim 4, it is characterised in that: in step (4), the time of described stratification is 60 seconds.
Extracting method the most according to claim 9, it is characterised in that: described Environmental Water is surface water.
Extracting method the most according to claim 8 or claim 9, it is characterised in that: described phthalate material includes neighbour Any one or more in phthalic acid dibutyl ester, dimethyl phthalate and dioctyl phthalate.
CN201610341550.9A 2016-05-19 2016-05-19 Automatic dispersed liquid-liquid micro-extraction system and applications thereof Pending CN106053631A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610341550.9A CN106053631A (en) 2016-05-19 2016-05-19 Automatic dispersed liquid-liquid micro-extraction system and applications thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610341550.9A CN106053631A (en) 2016-05-19 2016-05-19 Automatic dispersed liquid-liquid micro-extraction system and applications thereof

Publications (1)

Publication Number Publication Date
CN106053631A true CN106053631A (en) 2016-10-26

Family

ID=57177408

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610341550.9A Pending CN106053631A (en) 2016-05-19 2016-05-19 Automatic dispersed liquid-liquid micro-extraction system and applications thereof

Country Status (1)

Country Link
CN (1) CN106053631A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106501424A (en) * 2016-11-10 2017-03-15 嘉兴职业技术学院 The residual detection method of agriculture based on automatization's preprocessing system
CN106802328A (en) * 2017-01-18 2017-06-06 电子科技大学 A kind of full-automatic dispersive liquid-liquid microextraction method of mercury shape material in ambient water
CN107782724A (en) * 2017-12-04 2018-03-09 深圳市朗诚科技股份有限公司 A kind of nutritive salt in-situ analyzer and nutrient concentrations analysis method
CN108872106A (en) * 2018-06-26 2018-11-23 电子科技大学 A kind of method of trace sulphite in measurement water body
CN114113282A (en) * 2021-11-18 2022-03-01 中国检验检疫科学研究院 Small portable mass spectrum on-site rapid detection method for harmful dyes in textiles

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20150121993A1 (en) * 2013-11-05 2015-05-07 King Abdulaziz City For Science And Technology Dispersive liquid-liquid microextraction method of detecting n-nitrosoamines

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20150121993A1 (en) * 2013-11-05 2015-05-07 King Abdulaziz City For Science And Technology Dispersive liquid-liquid microextraction method of detecting n-nitrosoamines

Non-Patent Citations (11)

* Cited by examiner, † Cited by third party
Title
BURKHARD HORSTKOTTE ET AL.: "Automatic determination of copper by in-syringe dispersive liquid–liquid microextraction of its bath ocuproine-complex using long path-length spectrophotometric detection", 《TALANTA》 *
FERNANDO MAYA ET AL.: "Completely automated in-syringe dispersive liquid–liquid microextraction using solvents lighter than water", 《ANAL BIOANAL CHEM》 *
RUTH SUAREZ ET AL.: "Fully-Automated Fluorimetric Determination of Aluminum in Seawater by In-Syringe Dispersive Liquid−Liquid Microextraction Using Lumogallion", 《ANALYTICAL CHEMISTRY》 *
RUTH SUÁREZ ET AL.: "In-syringemagneticstirring-assisteddispersiveliquid–liquid microextraction for automation and downscaling of methyleneblue active substances assay", 《TALANTA》 *
SABRINA CLAVIJO ET AL.: "In-syringe-assisted dispersive liquid–liquid microextraction coupled to gas chromatography with mass spectrometry for the determination of six phthalates in water samples", 《J.SEP.SCI.》 *
刘艽岩 等: "分散液液微萃取在酸性模拟体系中塑料包装材料PAEs的溶出应用", 《河北大学学报(自然科学版)》 *
刘芄岩 等: "分散液液微萃取-气相色谱法测定白洋淀水中PAEs", 《环境监测管理与技术》 *
唐婧 等: "超声波辅助分散液液微萃取-气相色谱法测定水中的邻苯二甲酸二乙酯和菲", 《化学研究与应用》 *
庞世敏 等: "气相色谱法测定邻苯二甲酸酯类增塑剂的研究", 《华南师范大学学报(自然科学版)》 *
曹江平 等: "分散液液微萃取.高效液相色谱法测定白酒中的酞酸酯", 《食品科学》 *
谢利 等: "GC-FID法测定食品级瓶盖垫圈中五种邻苯二甲酸酯类增塑剂的含量", 《西安理工大学学报》 *

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106501424A (en) * 2016-11-10 2017-03-15 嘉兴职业技术学院 The residual detection method of agriculture based on automatization's preprocessing system
CN106802328A (en) * 2017-01-18 2017-06-06 电子科技大学 A kind of full-automatic dispersive liquid-liquid microextraction method of mercury shape material in ambient water
CN106802328B (en) * 2017-01-18 2019-12-13 电子科技大学 Full-automatic dispersion liquid-liquid micro-extraction method for mercury form substances in environmental water
CN107782724A (en) * 2017-12-04 2018-03-09 深圳市朗诚科技股份有限公司 A kind of nutritive salt in-situ analyzer and nutrient concentrations analysis method
WO2019109658A1 (en) * 2017-12-04 2019-06-13 深圳市朗诚科技股份有限公司 In-situ analyzer for nutritive salt and nutritive salt content analysis method
CN108872106A (en) * 2018-06-26 2018-11-23 电子科技大学 A kind of method of trace sulphite in measurement water body
CN114113282A (en) * 2021-11-18 2022-03-01 中国检验检疫科学研究院 Small portable mass spectrum on-site rapid detection method for harmful dyes in textiles
CN114113282B (en) * 2021-11-18 2023-12-22 中国检验检疫科学研究院 Small portable mass spectrum on-site rapid detection method for harmful dye in textile

Similar Documents

Publication Publication Date Title
CN106053631A (en) Automatic dispersed liquid-liquid micro-extraction system and applications thereof
CN108663471B (en) Method for determining contents of multiple endocrine disruptors in estuary sediments
CN104090039B (en) Measure inorganic anion and the method for organic acid anions in salt lake bittern simultaneously
CN104076109B (en) The Simultaneously test method of seven kinds of indicative polychlorinated biphenyl in high fat content food
CN103335878B (en) The preprocess method of phthalic ester plasticizer in a kind of edible oil
CN107543876A (en) A kind of method that SPE liquid chromatography tandem mass spectrometry detects 9 kinds of estrogenic chemicalses in water body simultaneously
CN107389825A (en) The method that algae toxin in water is determined based on full-automatic on-line solid phase extraction ultra performance liquid chromatography linear ion hydrazine tandem mass spectrum
CN102841161A (en) Gas chromatography-mass spectrometric detection method for octyl phenol and nonyl phenol in aquatic products
CN103901129A (en) Method for detecting ten types of organophosphorus pesticides by using magnetic separation-gas chromatography
CN111487327A (en) Method for detecting multiple persistent organic chemical pollutants in sample
CN103399099A (en) Method for detecting nine organophosphorus pesticides simultaneously
CN104807688B (en) A kind of method of micro polycyclic aromatic hydrocarbon in extracting and enriching large volume environmental water sample
CN105203666B (en) A kind of method of methyl mercury, ethyl mercury and inorganic mercury in detection aquatic feeds
CN205263037U (en) Element form on -line measuring device
CN103901139B (en) A kind of pre-treating method analyzed for tetrabromobisphenol A in biological urine
CN103776879B (en) A kind of method of molecular engram solid phase extraction technology-potentiometry combination detection organic pollution
CN103076420B (en) Method for detecting multicomponent microcystins through ultra-high performance liquid chromatography/triple quadrupole tandem mass spectrometry
CN106033080A (en) Rapid detection method for detecting multiple residual pesticides in edible plant oil and pretreatment method thereof
CN107102087B (en) Method for detecting contents of various organic acids in coptis chinensis by ion chromatography
CN111085006A (en) Process for extracting organic pollutants in environment
CN102590416A (en) Method for extracting negative ions from extract medicine by means of matrix solid phase dispersion and ion chromatographic detection method
CN103901143A (en) Pretreatment method for analyzing tetrabromobisphenol A in small amount of biologic serum
CN108387660A (en) The detection method of BaP in a kind of sootiness sturgeon
Dong et al. Determination of pyrethroid pesticide residues in vegetables by solvent sublation followed by high-performance liquid chromatography
CN108802242B (en) Method for simultaneously determining 6 chiral pesticide enantiomer residues in water environment

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20161026