CN102620952B - Method for undisturbedly collecting and determining sample of underground water polluted by volatile organic matters - Google Patents

Method for undisturbedly collecting and determining sample of underground water polluted by volatile organic matters Download PDF

Info

Publication number
CN102620952B
CN102620952B CN201210090038.3A CN201210090038A CN102620952B CN 102620952 B CN102620952 B CN 102620952B CN 201210090038 A CN201210090038 A CN 201210090038A CN 102620952 B CN102620952 B CN 102620952B
Authority
CN
China
Prior art keywords
sampling
sample
well
water
bottle
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201210090038.3A
Other languages
Chinese (zh)
Other versions
CN102620952A (en
Inventor
李辉
林匡飞
刘勇弟
陆强
吕树光
杨洁
李忠元
王晓丽
黄爽
周栋
范利花
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.)
East China University of Science and Technology
Shanghai Academy of Environmental Sciences
Original Assignee
East China University of Science and Technology
Shanghai Academy of Environmental Sciences
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 East China University of Science and Technology, Shanghai Academy of Environmental Sciences filed Critical East China University of Science and Technology
Priority to CN201210090038.3A priority Critical patent/CN102620952B/en
Publication of CN102620952A publication Critical patent/CN102620952A/en
Application granted granted Critical
Publication of CN102620952B publication Critical patent/CN102620952B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Sampling And Sample Adjustment (AREA)

Abstract

The invention discloses a sampling device for collecting a sample of underground water polluted by volatile organic matters and a method by utilizing the sampling device to undisturbedly collect and determine the sample. The method for collecting and determining the sample of the underground water polluted by the volatile organic matters comprises steps of well flushing, sampling preparation, sampling, storage and transportation, preprocessing and determination. Well flushing is carried out before the sampling, so that distortion of investigation data caused by the reason that rainy water enters the underground water can be avoided, a water sample is manually collected by utilizing a self-made sampling device, the water sample is stored in a 40ml volatile organic compound (VOC) sample bottle being equipped with a polytetrafluoroethylene (PTFE) spacing bottle cover and then is instantaneously stored in a refrigerator, and the water sample is analyzed through a gas chromatograph in a laboratory, so that the pollution situation of the volatile organic matters in the underground water can be accurately known. The method is low in cost and simple in equipment. Data with high authenticity can be acquired by strictly executing the operation according to the disclosed method, an important practical value is realized, and firsthand data can be provided to the site investigation of chlorohydrocarbon polluted field.

Description

A kind of undisturbed collection and assay method of underground water polluted by volatile organic compound sample
Technical field
The present invention relates to investigation and the analytical technology of organic contaminant in the underground environment of place, specifically, relate to a kind of undisturbed collection and assay method of underground water polluted by volatile organic compound sample.
Background technology
Chlorinated solvents, for example trichloroethanes (TCA) and triclene (TCE), be pollutant common in underground water.These solvents start to be widely used in metal degreasing or dry-cleaning very early.To phase late 1970s, because rise and the chemical analysis technology of site investigation develops into the pollutant that ug/L level concentration in water can be detected, in underground water, the pollution level of organic solvent is just found.People impel the standard of potable water to be reduced to the order of magnitude of ug/L to healthy worry, and then have promoted investigation and the reparation of organic contaminant in the underground environment of place.Just repair and must first carry out site investigation place underground water, wherein the monitoring of underground water is exactly a kind of method of site investigation, and in groundwater monitoring, Sampling techniques and sample analysis occupy very important status.
Developed country pays much attention to groundwater sampling technology, and groundwater sampling technology is conducted in-depth research.In recent years, the groundwater contamination of China has also caused the great attention of government, and the method for Groundwater Contamination Investigation is also being studied.China Geological Survey Hydrogeology Environment Geological Survey Center was studied groundwater sampling technology since 2005, and developed a series of ground water fixed depth sampling thiefs, such as air compressor draw water sampling and inertial pump's sampling of drawing water.
Air compressor draws water to sample and refers to when air compressor draws water, in wellhole, be equipped with one and be enclosed within bottom with air-supply pipeline and a set of lifting pipe of air and liquid mixer, using air compressor that air is pressed into ajutage line sprays through air and liquid mixer, in lifting pipe, form countless minute bubbles and generation " gaslift " effect of expanding gradually, the water extraction in well is raised to earth's surface.But air compressor pumping method cannot be used at the more shallow monitor well of the degree of depth.
Inertial pump draws water to sample and refers to that inertial pump consists of the small pipe line that bottom valve is housed, and during decline, bottom valve is opened, and valve closing during rising, by swinging up and down the liter waterborne making in pipeline, is discharged into earth's surface.Inertial pump be in all underground water sampling pumps, the most easily use and cost minimum.The degree of depth in 30 m, inertial pump can manually use.Inertial pump is relatively applicable to the monitor well of minor diameter.But, when inertial pump draws water, due to shake up and down, sample is produced to disturbance, so be not suitable for gathering the underground water sample that contains volatile organic matter.
And in water sample aspect the analysis of volatile organic matter, at present the most frequently used is to analyze with gas chromatograph.But carry out the analysis of sample at chromatography of gases before, need to carry out pre-treatment to sample.Pre-treating method has: liquid-liquid extraction method, Static Headspace method, solid absorption analytical method and Puffing and trapping.Wherein Puffing and trapping, bioaccumulation efficiency advantages of higher few with its sampling amount, is all subject to the attention of environment circle for a long time.
Summary of the invention
The object of the invention is to for existing volatile organic matter technology, a kind of underground water polluted by volatile organic compound sample sampling thief is provided.
Second object of the present invention, provides water sampling and the analytical approach of underground water polluted by volatile organic compound, utilizes the sampling thief of speciality, can realize the sample that undisturbed gathers underground water polluted by volatile organic compound, and sample is analyzed accurately.
For realizing first object of the present invention, the invention discloses a kind of underground water polluted by volatile organic compound sample collector, comprise body, pipe end mouth and bale handle, pipe end mouth is positioned at body lower end, diameter is less than body, in pipe end mouth, a movable ball valve is set, pipe end mouth top arranges a tripod baffle plate, and bale handle is positioned at body upper end, it is characterized in that, body upper end arranges a serum cap, in the middle of described serum cap, an aperture is set, the inside radius of serum cap and body external radius equal and opposite in direction, serum cap inside surface is coated with poly tetrafluoroethylene.
As a preferred version, described body length is 0.37 m, and diameter is 0.04 m, and tripod baffle plate is 0.06 m apart from the distance of pipe Di Kou bottom, and end nozzle diameter is 0.018 m, and ball valve diameter is 0.015 m.
When entering water, ball valve is opened, and water enters in pipe, and tripod baffle plate is in order to control the position of ball valve; When upper carrying, ball valve is closed, and water sample rests in pipe, and in well, water sample is removed.The serum cap on body top is in order to prevent the volatilization of volatile organic matter in water sample.Meanwhile, the appropriate length of sampling thief can prevent the disturbance of body to underground water, can not collect the sedimentary particle of bottom.
For realizing second object of the present invention, the technical scheme that the present invention takes is: a kind of undisturbed collection and assay method of underground water polluted by volatile organic compound sample, it is characterized in that, and comprise the following steps:
(1) well-flushing, pays close attention to weather condition before well-flushing, within 3 days, there is no the weather of precipitation after first 3 days of well-flushing of selection and well-flushing; Each sampled well is prepared disposable Beile's pipe, and sample collector prepares protective clothing, respirator and emgloves; Use Beile to manage the water in reciprocal stirring well, to cleaning the earth of shaft bottom alluvial, when the water extracting is 3-5 times of WIH volume, pH value, DO and the conductivity value of WIH are stable, at this moment think well-flushing success;
(2) before sampling, prepare, 24 h samplings after well-flushing, during this period of time in WIH position and current reach balance, can truly reflect this sampled point underground water present situation; Before sampling, prepare sampling bottle, each well location is furnished with the VOC bottle of 2 40 mL as sampling bottle, and the some position information that will sample writes on the label of sampling bottle, these sampling bottles are placed in the insulation can that ice bag is housed, sample collector prepares protective clothing, respirator and emgloves;
(3) sampling, utilize above-mentioned collector collected specimens, with cord, tie up on the bale handle of sampling thief, from the aperture of serum cap, pass, sampling thief is hung in well, until water does not have the upper end of over-sampling device, this process is slow especially, prevent excessive velocities stirring well water, cause the mud in shaft bottom to be rushed in sampling thief, the water of getting is up put at leisure in the VOC bottle of 40 mL, bottle reduces current while expiring soon, to reduce the bubble producing in water flow process, the bottle of having sampled is put in insulation can and is preserved, transport laboratory back;
(4) pre-treatment and mensuration, the pollution determination in sampling of ground water adopts purge and trap coupling gas chromatography to measure.
VOC bottle described in step (2) is furnished with teflon pad bottle cap; In described VOC bottle, drip the 0.1 mL1:1 concentrated sulphuric acid.
Sample in sampling bottle described in step (3) is to preserve without bubble.
The pre-treating method of underground water sample in step (4), purge and trap parameter is set to: trap tube model: OI-10#; U-shaped pipe: 5 mL; Gas flow: 40 mL/min; Initial trapping temperature: according to environment temperature; Desorption temperature: 180 ℃; Baking temperature: 210 ℃; Purge time: 11 min; Desorption time: 4 min; Valve temperature: 110 ℃; Transmission line temperature: 110 ℃; Baking time: 2 min; The washing times of sample room: 2 times.
In step (4), gas chromatography instrument parameter arranges: Agilent 7890A gas chromatography; Agilent chem workstation; Capillary chromatographic column: DB-VRX 60 mm * 1.4, m * 0.25 μ m; Sample introduction temperature: 240 ℃; Helium column flow velocity: 2 mL/min; Initial temperature: 45 ℃, keep 0 min; Heating schedule: 12 ℃/min rises to 190 ℃, keeps 2 min; Working time: 12.3 min; Split ratio: 20:1; Stop running temperature: 235 ℃, keep 0 min; Transmission line temperature: 230 ℃.
Volatile organic matter described in the present invention mainly refers to chlorinated hydrocarbon organic contaminant.
Beneficial effect of the present invention is: (1) is used self-control sampling thief to carry out the artificial sampling of extracting, and the advantage of this sampling thief is for not being subject to the restriction of the monitor well degree of depth and diameter, easy to use.The size of this sampling thief is little, prevents from causing sedimental disturbance in well because of oversize, affects follow-up determination experiment, is specially adapted to the underground water well sampling that the degree of depth is less, water level is lower.The serum cap that the inside surface adding on top is coated with Teflon can effectively prevent the loss of volatile organic matter in water sample, and middle aperture can make again intraductal atmospheric pressure and atmospheric pressure communicate, and water sample can be entered in VOC sample bottle smoothly.This sampling thief is made simple, and low price, is convenient to practical operation.
(2) use purge and trap to coordinate gas chromatograph to carry out the analysis of volatile organic matter, can realize the detection of the pollutant of low concentration, and accuracy is high.
(3) the undisturbed collection of VOC monitoring organic compounds investigation in a kind of underground water and the method for pollutant Accurate Determining are disclosed, the whole series method has that cost is low, the simple advantage of equipment, in strict accordance with a whole set of method operation disclosed by the invention, can obtain the data that authenticity is higher, there is important practical value, can provide the firsthand information for the site investigation of chlorohydrocarbon contaminated site.
Accompanying drawing explanation
Fig. 1 is the schematic diagram of sampling thief, wherein, and 1-Guan Dikou; 2-ball valve; 3-tripod baffle plate; 4-body; 5-bale handle; 6-serum cap; 7-aperture.
Fig. 2 is the process flow diagram of sampling and mensuration.
Embodiment
Below in conjunction with specific embodiment, further set forth the present invention.The experimental technique using in following embodiment if no special instructions, is conventional method.In following embodiment, material used, reagent etc., if no special instructions, all can obtain from commercial channels.Should be understood that these embodiment are only not used in and limit the scope of the invention for the present invention is described.
Embodiment 1, underground water polluted by volatile organic compound sample sampling thief
Teflon FEP(fluorinated vinyl propylene of sampling thief body material) make.As shown in Figure 1, comprise body 4, pipe end mouth 1 and bale handle 5, pipe end mouth 1 is positioned at body 4 lower ends, pipe end mouth 1 diameter is less than body 4 diameters, the pipe end mouth 1 interior movable ball valve 2 that arranges, pipe mouth 1 top, the end arranges a tripod baffle plate 3, bale handle 5 is positioned at body 4 upper ends, it is characterized in that, body 4 upper ends arrange a serum cap 6, and the aperture 7 of Radius approximately 0.0025 m is set in the middle of described serum cap 6, the inside radius of serum cap 6 and body 4 external radius equal and opposite in directions, serum cap 6 inside surfaces are coated with Teflon(teflon) film.
Described body 4 length are 0.37 m, and diameter is 0.04 m, and tripod baffle plate 3 is 0.06 m apart from the distance of pipe end mouth 1, and bottom tube mouth 1 diameter is 0.018 m, and ball valve 2 diameters are 0.015 m.Long 0.37 m of sampling thief, diameter 0.04 m, above bale handle, add that a centre is with the serum cap 6 of radius approximately 0.0025 m aperture 7, the external radius of the inside radius of serum cap 6 and body 4 equates, height is 0.05 m, tripod baffle plate 3 is 0.06m apart from the distance of pipe end mouth 1, and bottom tube mouth 1 diameter is 0.018m, and ball valve 2 diameters are 0.015 m.When entering water, ball valve 2 is opened, and water enters in pipe, and tripod baffle plate 3 is in order to control the position of ball valve 2; When upper carrying, ball valve 2 is closed, and water sample rests in pipe, and in well, water sample is removed.The serum cap 6 on body 4 tops is in order to prevent the volatilization of volatile organic matter in water sample.Meanwhile, the appropriate length of sampling thief can prevent the disturbance of 4 pairs of underground water of body, can not collect the sedimentary particle of bottom.
Collection and the analysis of embodiment 2, Dp-01 monitor well sample
Monitor well: the Dp-01 monitor well in the factory area of PVG.
Sample mode: suction in sampling thief well.
Sample bottle: 40 mL Brown Glass Brown glass bottles and jars onlys, are used teflon gasket in cap.
Store means of transportation: be put in Refrigerated Transport in the insulation can of several ice bags.
Analytical approach: purge and trap---gas chromatograph.
Sampling and the concrete steps of measuring are as follows:
(1) well-flushing, pays close attention to weather condition before well-flushing, within 3 days, there is no the weather of precipitation after first 3 days of well-flushing of selection and well-flushing; Each sampled well is prepared a disposable Teflon FEP Beile pipe, and sample collector prepares protective clothing, respirator and emgloves; Use Beile to manage the water in reciprocal stirring well, to cleaning the earth of shaft bottom alluvial, when the water extracting is 3~5 times of WIH volume, the pH value of WIH, DO(dissolved oxygen DO) and conductivity value stable, at this moment think that well-flushing is successful;
(2) before sampling, prepare, sampling in 24 hours after well-flushing, during this period of time in WIH position and current reach balance, can truly reflect this sampled point underground water present situation; Before sampling, prepare sampling bottle, each well location is furnished with the VOC(volatile organic matter of 2 40 mL) bottle is as sampling bottle, and the some position information that will sample writes on the label of sampling bottle, these sampling bottles are placed in the insulation can that ice bag is housed, sample collector prepares protective clothing, respirator and emgloves;
(3) sampling, ties up to cord on the bale handle of sampling thief, from the aperture of serum cap, passes, sampling thief is hung in well, until water does not have the upper end of over-sampling device, this process is slow especially, prevent excessive velocities stirring well water, cause the mud in shaft bottom to be rushed in sampling thief; The water of getting is up put at leisure in the VOC bottle of 40 mL, bottle reduces current while expiring soon, to reduce the bubble producing in water flow process.The bottle of having sampled is put in insulation can and is preserved, transport laboratory back;
(4) pre-treatment and mensuration, the pollution determination in sampling of ground water adopts purge and trap coupling gas chromatography to measure.
The pre-treating method of underground water sample in step (4), purge and trap parameter is set to: trap tube model: OI-10#; U-shaped pipe: 5 mL; Gas flow: 40 mL/min; Initial trapping temperature: according to environment temperature; Desorption temperature: 180 ℃; Baking temperature: 210 ℃; Purge time: 11 min; Desorption time: 4 min; Valve temperature: 110 ℃; Transmission line temperature: 110 ℃; Baking time: 2 min; The washing times of sample room: 2 times.
In step (4), gas chromatography instrument parameter arranges: Agilent 7890A gas chromatography; Agilent chem workstation; Capillary chromatographic column: DB-VRX 60 mm * 1.4, m * 0.25 μ m; Sample introduction temperature: 240 ℃; Helium column flow velocity: 2 mL/min; Initial temperature: 45 ℃, keep 0 min; Heating schedule: 12 ℃/min rises to 190 ℃, keeps 2 min; Working time: 12.3 min; Split ratio: 20:1; Stop running temperature: 235 ℃, keep 0 min; Transmission line temperature: 230 ℃.
Analysis result: VC:968 ug/L, CA:104000 ug/L, DCE:5590 ug/L, DCA:272000 ug/L, TCA:548000 ug/L.
Collection and the analysis of embodiment 3, Dp-03 monitor well sample
Monitor well: the DP-03 monitor well in the factory area of PVG.
Sample mode: suction in sampling thief well.
Sample bottle: 40 mL Brown Glass Brown glass bottles and jars onlys, are used teflon gasket in cap.
Store means of transportation: be put in Refrigerated Transport in the insulation can of several ice bags.
Analytical approach: purge and trap---gas chromatograph.
The concrete steps of sampling and mensuration are with embodiment 2.
Analysis result: VC:670 ug/L, CA:50300 ug/L, DCE:3090 ug/L, DCA:293000 ug/L, TCA:354000 ug/L.
Collection and the analysis of embodiment 4, DP-16 monitor well sample
Monitor well: the DP-16 monitor well in the factory area of PVG.
Sample mode: suction in sampling thief well.
Sample bottle: 40 mL Brown Glass Brown glass bottles and jars onlys, are used teflon gasket in cap.
Store means of transportation: be put in Refrigerated Transport in the insulation can of several ice bags.
Analytical approach: purge and trap-gas chromatograph.
The concrete steps of sampling and mensuration are with embodiment 2.
Analysis result: VC:321 ug/L, CA:130000 ug/L, DCE:1690 ug/L, DCA:107000 ug/L, TCA:440000 ug/L.
Collection and the analysis of embodiment 5, MW-201 monitor well sample
Monitor well: the MW-201 monitor well in the factory area of PVG.
Sample mode: suction in sampling thief well.
Sample bottle: 40 mL Brown Glass Brown glass bottles and jars onlys, are used teflon gasket in cap.
Store means of transportation: be put in Refrigerated Transport in the insulation can of several ice bags.
Analytical approach: purge and trap---gas chromatograph.
The concrete steps of sampling and mensuration are with embodiment 2.
Analysis result: VC:50 ug/L, CA:43500 ug/L, DCE:105 ug/L, DCA:4460 ug/L, TCA:2320 ug/L.
Collection and the analysis of embodiment 6, MW-210 monitor well sample
Monitor well: the MW-210 monitor well in the factory area of PVG.
Sample mode: suction in sampling thief well.
Sample bottle: 40 mL Brown Glass Brown glass bottles and jars onlys, are used teflon gasket in cap.
Store means of transportation: be put in Refrigerated Transport in the insulation can of several ice bags.
Analytical approach: purge and trap---gas chromatograph.
The concrete steps of sampling and mensuration are with embodiment 2.
Analysis result: VC:579 ug/L, CA:82700 ug/L, DCE:4680 ug/L, DCA:206000 ug/L, TCA:971000 ug/L.
Collection and the analysis of embodiment 7, MW-26-4 monitor well sample
Monitor well: the MW-26-4 monitor well in the factory area of PVG.
Sample mode: suction in sampling thief well.
Sample bottle: 40 mL Brown Glass Brown glass bottles and jars onlys, are used teflon gasket in cap.
Store means of transportation: be put in Refrigerated Transport in the insulation can of several ice bags.
Analytical approach: purge and trap---gas chromatograph.
The concrete steps of sampling and mensuration are with embodiment 2.
Analysis result: VC:154 ug/L, CA:7780 ug/L, DCE:741 ug/L, DCA:35600 ug/L, TCA:96200 ug/L.
Collection and the analysis of embodiment 8, MW-27 monitor well sample
Monitor well: the MW-27 monitor well in the factory area of PVG.
Sample mode: suction in sampling thief well.
Sample bottle: 40 mL Brown Glass Brown glass bottles and jars onlys, are used teflon gasket in cap.
Store means of transportation: be put in Refrigerated Transport in the insulation can of several ice bags.
Analytical approach: purge and trap---gas chromatograph.
The concrete steps of sampling and mensuration are with embodiment 2.
Analysis result: VC:50 ug/L, CA:5560 ug/L, DCE:50 ug/L, DCA:12500 ug/L, TCA:1880 ug/L.
The above is only the preferred embodiment of the present invention; it should be pointed out that for those skilled in the art, under the premise without departing from the principles of the invention; can also make some improvements and modifications, these improvements and modifications also should be considered as protection scope of the present invention.

Claims (6)

1. undisturbed collection and the assay method of underground water polluted by volatile organic compound sample, is characterized in that, comprises the following steps:
(1) well-flushing, pays close attention to weather condition before well-flushing, within 3 days, there is no the weather of precipitation after first 3 days of well-flushing of selection and well-flushing; Each sampled well is prepared disposable Beile's pipe, and sample collector prepares protective clothing, respirator and emgloves; Use Beile to manage the water in reciprocal stirring well, to cleaning the earth of shaft bottom alluvial, when the water extracting is 3-5 times of WIH volume, pH value, DO and the conductivity value of WIH are stable, at this moment think well-flushing success;
(2) before sampling, prepare, 24 h samplings after well-flushing, during this period of time in WIH position and current reach balance, can truly reflect sampled point underground water present situation; Before sampling, prepare sampling bottle, each well location is furnished with the VOC bottle of 2 40 mL as sampling bottle, and the some position information that will sample writes on the label of sampling bottle, these sampling bottles are placed in the insulation can that ice bag is housed, sample collector prepares protective clothing, respirator and emgloves;
(3) sampling, utilize collector collected specimens, described collector comprises body, pipe end mouth and bale handle, pipe end mouth is positioned at body lower end, diameter is less than body, in pipe end mouth, a movable ball valve is set, pipe end mouth top arranges a tripod baffle plate, bale handle is positioned at body upper end, body upper end arranges a serum cap, one aperture is set in the middle of described serum cap, the inside radius of serum cap and body external radius equal and opposite in direction, serum cap inside surface is coated with poly tetrafluoroethylene, with cord, tie up on the bale handle of sampling thief, from the aperture of serum cap, pass, sampling thief is hung in well, until water does not have the upper end of over-sampling device, this process is slow especially, prevent excessive velocities stirring well water, cause the mud in shaft bottom to be rushed in sampling thief, the water of getting is up put at leisure in the VOC bottle of 40 mL, bottle reduces current while expiring soon, to reduce the bubble producing in water flow process, the bottle of having sampled is put in insulation can and is preserved, transport laboratory back,
(4) pre-treatment and mensuration, the pollution determination in sampling of ground water adopts purge and trap coupling gas chromatograph to measure.
2. undisturbed collection and the assay method of a kind of underground water polluted by volatile organic compound sample according to claim 1, is characterized in that, the VOC bottle described in step (2) is furnished with teflon pad bottle cap.
3. undisturbed collection and the assay method of a kind of underground water polluted by volatile organic compound sample according to claim 1, is characterized in that, drips the 0.1 mL1:1 concentrated sulphuric acid described in step (2) in VOC bottle.
4. undisturbed collection and the assay method of a kind of underground water polluted by volatile organic compound sample according to claim 1, is characterized in that, the sample in the sampling bottle described in step (3) is to preserve without bubble.
5. undisturbed collection and the assay method of a kind of underground water polluted by volatile organic compound sample according to claim 1, is characterized in that, the pre-treating method of underground water sample in step (4), and purge and trap parameter is set to: trap tube model: OI-10#; U-shaped pipe: 5 mL; Gas flow: 40 mL/min; Initial trapping temperature: according to environment temperature; Desorption temperature: 180 ℃; Baking temperature: 210 ℃; Purge time: 11 min; Desorption time: 4 min; Valve temperature: 110 ℃; Transmission line temperature: 110 ℃; Baking time: 2 min; The washing times of sample room: 2 times.
6. undisturbed collection and the assay method of a kind of underground water polluted by volatile organic compound sample according to claim 1, is characterized in that, in step (4), gas chromatography instrument parameter arranges: Agilent 7890A gas chromatography; Agilent chem workstation; Capillary chromatographic column: DB-VRX 60 mm * 1.4, m * 0.25 μ m; Sample introduction temperature: 240 ℃; Helium column flow velocity: 2 mL/min; Initial temperature: 45 ℃, keep 0 min; Heating schedule: 12 ℃/min rises to 190 ℃, keeps 2 min; Working time: 12.3 min; Split ratio: 20:1; Stop running temperature: 235 ℃, keep 0 min; Transmission line temperature: 230 ℃.
CN201210090038.3A 2012-03-30 2012-03-30 Method for undisturbedly collecting and determining sample of underground water polluted by volatile organic matters Expired - Fee Related CN102620952B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210090038.3A CN102620952B (en) 2012-03-30 2012-03-30 Method for undisturbedly collecting and determining sample of underground water polluted by volatile organic matters

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210090038.3A CN102620952B (en) 2012-03-30 2012-03-30 Method for undisturbedly collecting and determining sample of underground water polluted by volatile organic matters

Publications (2)

Publication Number Publication Date
CN102620952A CN102620952A (en) 2012-08-01
CN102620952B true CN102620952B (en) 2014-02-26

Family

ID=46561001

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210090038.3A Expired - Fee Related CN102620952B (en) 2012-03-30 2012-03-30 Method for undisturbedly collecting and determining sample of underground water polluted by volatile organic matters

Country Status (1)

Country Link
CN (1) CN102620952B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109828041A (en) * 2019-01-25 2019-05-31 北京建工环境修复股份有限公司 The measuring method of volatile organic matter total amount in a kind of underground water

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU2013286767B2 (en) * 2012-07-03 2017-07-13 Chevron U.S.A. Inc Detection of hydrocarbons in aqueous environments
CN107064444A (en) * 2017-02-28 2017-08-18 江苏和顺环保有限公司 Underground water automatic sampling system and its method for sampling
CN110221013A (en) * 2019-07-04 2019-09-10 河北省地质环境监测院 Simple, Practical Determination Method of VOCs in underground water

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN86206798U (en) * 1986-09-03 1987-08-05 周望祖 Universal automatic water sampler
CN2173955Y (en) * 1992-09-10 1994-08-10 邹涛录 Liquid sampler
CN2856965Y (en) * 2005-12-12 2007-01-10 中华人民共和国蛇口出入境检验检疫局 Fixed-point liquid sampler
CN101696915B (en) * 2009-10-15 2011-04-20 中国地质科学院水文地质环境地质研究所 Device for manually and quickly collecting groundwater samples in well-less soft soil layer areas
KR101168046B1 (en) * 2010-08-09 2012-07-24 한국지질자원연구원 Apparatus and method for groundwater sampling using hydraulic coupler

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109828041A (en) * 2019-01-25 2019-05-31 北京建工环境修复股份有限公司 The measuring method of volatile organic matter total amount in a kind of underground water

Also Published As

Publication number Publication date
CN102620952A (en) 2012-08-01

Similar Documents

Publication Publication Date Title
US20100212406A1 (en) Collection of dissolved gases from groundwater
CN104062368B (en) The steam head space enrichment detecting method of Determination of Trace Volatile organic contaminant in a kind of seawater
CN103234778B (en) Device for enriching semi-volatile organic compounds in underground water
McCarthy Jr Mercury vapor and other volatile components in the air as guides to ore deposits
CN102620952B (en) Method for undisturbedly collecting and determining sample of underground water polluted by volatile organic matters
CN103323290A (en) Sampler for sediment pore water sampling in rivers or lakes
CN204269595U (en) For the monitoring device of volatile organic matter concentration in continuous on-line detection water
CA2478992A1 (en) Aboveground leak detection system for detecting sub-surface fluid leaks from fluid containing vessels
US6706094B2 (en) Collection of dissolved gases from groundwater
CN103792310B (en) For the sampling device that water body release gas gas phase measures
CN104316622A (en) Adsorption enrichment device and method for organic matters in gas
Gui-Peng et al. Purge-and-trap gas chromatography method for analysis of methyl chloride and methyl bromide in seawater
CN106644618B (en) Gas sampling system and application thereof
CN103954477B (en) The disposable depthkeeping in-situ sampling of the organic water sample of volatility bottle
CN212610476U (en) Extraction device of dissolved gas in high-vacuum double-valve glass bottle water sample
Rasmussen et al. Atmospheric carbonyl sulfide (OCS): techniques for measurement in air and water
CN209570404U (en) A kind of collection device of portable coastal building surface chloride ion
CN209603986U (en) For CO2On-spot collection system of flooding extraction well gas
CN209085982U (en) A kind of sampler for contaminated site investigation
CN203720155U (en) Sample feeding device for measuring gas phase of water body release gas
CN206710151U (en) Microcell sampling instrument annex
Ullom Soil gas sampling
Smith et al. Sampling unsaturated‐zone water for trichloroethene at Picatinny Arsenal, New Jersey
CN203178108U (en) Enriching device for semi-volatile organic compounds in underground water
CN203837953U (en) Volatile organic water sample one-time depthkeeping normal-position sampling bottle

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
ASS Succession or assignment of patent right

Owner name: SHANGHAI ACADEMY OF ENVIRONMENTAL SCIENCES

Effective date: 20140102

C41 Transfer of patent application or patent right or utility model
C53 Correction of patent for invention or patent application
CB03 Change of inventor or designer information

Inventor after: Li Hui

Inventor after: Zhou Dong

Inventor after: Fan Lihua

Inventor after: Lin Kuangfei

Inventor after: Liu Yongdi

Inventor after: Lu Qiang

Inventor after: Lv Shuguang

Inventor after: Yang Jie

Inventor after: Li Zhongyuan

Inventor after: Wang Xiaoli

Inventor after: Huang Shuang

Inventor before: Li Hui

Inventor before: Lin Kuangfei

Inventor before: Liu Yongdi

Inventor before: Shen Tingting

Inventor before: Lv Shuguang

Inventor before: Lu Qiang

COR Change of bibliographic data

Free format text: CORRECT: INVENTOR; FROM: LI HUI LIN KUANGFEI LIU YONGDI SHEN TINGTING LV SHUGUANG LU QIANG TO: LI HUI LIN KUANGFEI LIU YONGDI LU QIANG LV SHUGUANG YANG JIE LI ZHONGYUAN WANG XIAOLI HUANG SHUANG ZHOU DONG FAN LIHUA

TA01 Transfer of patent application right

Effective date of registration: 20140102

Address after: 200237 Meilong Road, Shanghai, No. 130, No.

Applicant after: East China University of Science and Technology

Applicant after: Shanghai Academy of Environmental Sciences

Address before: 200237 Meilong Road, Shanghai, No. 130, No.

Applicant before: East China University of Science and Technology

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

Granted publication date: 20140226

Termination date: 20160330

CF01 Termination of patent right due to non-payment of annual fee