CN110346472A - A kind of method of organic matter in Gas Chromatography-Mass Spectrometry deposit - Google Patents

A kind of method of organic matter in Gas Chromatography-Mass Spectrometry deposit Download PDF

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Publication number
CN110346472A
CN110346472A CN201910614696.XA CN201910614696A CN110346472A CN 110346472 A CN110346472 A CN 110346472A CN 201910614696 A CN201910614696 A CN 201910614696A CN 110346472 A CN110346472 A CN 110346472A
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organic matter
gas chromatography
mass spectrometry
deposit
sample
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白亚之
胡利民
刘季花
汪虹敏
王小静
崔菁菁
高晶晶
朱爱美
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First Institute of Oceanography MNR
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First Institute of Oceanography MNR
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    • 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
    • G01N30/04Preparation or injection of sample to be analysed
    • G01N2030/042Standards
    • G01N2030/045Standards internal
    • 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 present invention provides a kind of method of organic matter in Gas Chromatography-Mass Spectrometry deposit, the method specifically includes deposit is dehydrated after it is dry, be ground up, sieved, sample be made;It extracts: sample being subjected to ASE extraction, obtains extract liquor;Purification: extract liquor is concentrated, concentrate is separated using chromatographic column;Measurement: purified sample is subjected to qualitative and quantitative analysis with gas chromatography-mass spectrography.The present invention extracts object using accelerated solvent extraction method, and upper glass chromatography column carries out stage purification after extracting solution concentration, and the laggard GC-MS qualitative and quantitative analysis of constant volume is concentrated.Characteristic ion according to chromatographic peak retention time and object is qualitative, inner mark method ration.This method sample treatment of five kinds of organic matters, analysis test suitable for coastal waters, river mouth, bay, culture zone deposit.

Description

A kind of method of organic matter in Gas Chromatography-Mass Spectrometry deposit
Technical field
The invention belongs to field of chemical detection, and in particular to organic matter in a kind of Gas Chromatography-Mass Spectrometry deposit Method.
Background technique
It is deposited on water-bed various deposits, such as bed mud.Source has: (1) river, river, lake, the mud carried secretly in seawater body The suspended matters such as sand;(2) remains and its decomposition product of aquatile;(3) water pollutant, especially mercury, cadmium, lead, zinc, nickel The organic matter of equal heavy metals and strong adsorption.By the specificity analysis of physics, chemistry, biology to benthal deposit etc., and The research of depositional environment, can find out over the type of pollutant in some time, determine pollution level, determine pollution sources position It sets.
Summary of the invention
The object of the present invention is to provide a kind of methods of organic matter in Gas Chromatography-Mass Spectrometry deposit, by right The comparisons of different extraction conditions selects suitable extraction conditions, select suitable method for concentration and purification pillar to sample into Row thickening-purification technology classification processing, tests object different in sample using different analysis methods.
For achieving the above object, the present invention is achieved by the following scheme:
A kind of method of organic matter in Gas Chromatography-Mass Spectrometry deposit, the described method comprises the following steps:
(1) it prepares: deposit being dehydrated, ground 100~150 mesh, sample is made;
(2) it extracts: sample being subjected to ASE extraction, obtains extract liquor;
(3) it purifies: extract liquor being concentrated, concentrate is separated using chromatographic column, collects eluent respectively;
(4) it measures: the organic matter in eluent is subjected to qualitative and quantitative analysis with gas chromatography-mass spectrography, wherein Characteristic ion according to chromatographic peak retention time and object is qualitative, inner mark method ration.
Further: the organic matter is polycyclic aromatic hydrocarbon, Polychlorinated biphenyls, six six six, DDT and n-alkane.
Further: the method dehydrated in the step (1) is to use freeze drier vacuum freeze drying.
Further: the solvent that ASE extraction uses in the step (2) is methylene chloride;Extraction conditions is system pressure 10~11MPa, 90~110 DEG C of extraction temperature, 3~7min of heating time, 5~10min of quiet hour, flush volume is extraction The 60~70% of pond body product, recycle 2~3 times.
Further: after the step (2) further includes extraction, the copper powder that addition has activated is non-discolouring to copper powder, obtains To extract liquor.
Further: the diameter of chromatographic column is 8mm, the fill method of the chromatographic column are as follows: under in the step (3) To the upper deactivation neutral alumina for successively filling out 3~4cm, the deactivation neutral silica gel of 3~4cm, the anhydrous sodium sulfate of 1~2cm.
It is further: the specific steps separated in the step (3) are as follows:
Concentrate is added drop-wise in chromatographic column, successively with n-hexane, n-hexane and methylene chloride, methylene chloride and methanol Chromatographic column is eluted, non-polar component, middle polarity component and polar compound are respectively obtained;
After rotary evaporation and nitrogen are blown, non-polar component adds inner mark solution PCNB and HMB, and middle polarity component adds internal standard HMB, with n-hexane constant volume.
It is further: the condition of gas-chromatography in the step (4) are as follows:
Chromatographic column: column length 30m, diameter 0.25mm, 0.25 μm of film thickness;250~300 DEG C of temperature of vaporization chamber;Carrier gas is high-purity He;0.9~1.2mL/min of flow velocity;1 μ L of sample volume;Input mode is Splitless injecting samples.
It is further: the temperature program of the condition of gas-chromatography in the step (4) are as follows:
Polycyclic aromatic hydrocarbon:, keeping 1~2min by 50~70 DEG C, rises to 250~300 DEG C with 5 DEG C/min, keeps 15~20min;
Polychlorinated biphenyls, six six six, DDT:, rising to 180~200 DEG C with 30 DEG C/min by 80~100 DEG C, then with 3 DEG C/ Min rises to 200~210 DEG C, keeps 2~5min, then rise to 250~300 DEG C with 5 DEG C/min, keeps 3~6min;
N-alkane:, keeping 1~2min by 50~80 DEG C, rises to 150~200 DEG C with 12 DEG C/min, keeps 1~2min, 270~310 DEG C are risen to 8 DEG C/min again, keeps 0.5~1min;300~350 DEG C are risen to again with 12 DEG C/min, keep 10~ 15min。
It is further: Mass Spectrometry Conditions in the step (4) are as follows: electron impact ion source;Electron energy 70eV;Transmission line 280~300 DEG C of temperature;230~250 DEG C of ion source temperature;130~170 DEG C of quadrupole rod temperature;The solvent delay time 3~ 6min。
Compared with prior art, advantages of the present invention and have the technical effect that five kinds of organic pollutants include petroleum hydrocarbon point It analyses, five kinds of organic pollutants (PAHs, PCBs, HCHs, DDTs, n-alkanes) in deposit use accelerated solvent extraction side Method is extracted, and upper glass chromatography column carries out stage purification after extracting solution concentration, and the laggard GC-MS qualitative and quantitative analysis of constant volume is concentrated. Characteristic ion according to chromatographic peak retention time and object is qualitative, inner mark method ration.This method is suitable for coastal waters, river mouth, port The sample treatment of five kinds of organic matters, analysis test in gulf, culture zone deposit.
Detailed description of the invention
Fig. 1 is the total ion chromatogram of polycyclic aromatic hydrocarbon;
Fig. 2 is Polychlorinated biphenyls, six six six, the total ion chromatogram of DDT;
Fig. 3 is the total ion chromatogram of n-alkane.
Specific embodiment
With reference to embodiments by the technical scheme of the present invention will be explained in further detail.
Embodiment 1
One, the scope of application
The organic matter of test is analyzed in the present embodiment are as follows: polycyclic aromatic hydrocarbon, Polychlorinated biphenyls, six six six, DDT and N-alkanes Hydrocarbon.5 kinds of organic matters difference is as follows:
The polycyclic aromatic hydrocarbon (PAHs) include 16 kinds: naphthalene, acenaphthylene, acenaphthene, fluorenes, phenanthrene, anthracene, fluoranthene, pyrene, benzanthracene,Benzene And (b) fluoranthene, benzo (k) pyrene, benzo (a) pyrene, indenes benzene (1,2,3, cd) pyrene, dibenzanthracene, benzo (ghi) pyrene.
The Polychlorinated biphenyls (PCBs) includes 28 kinds: CB-8, CB-18, CB-28, CB-52, CB-44, CB-66, CB- 101、CB-77、CB-81、CB-114、CB-118、CB-123、CB-153、CB-105、 CB-138、CB-126、CB-187、CB- 128、CB-167、CB-156、CB-157、CB-180、CB-169、 CB-170、CB-189、CB-195、CB-206、CB-209。
The six six six (HCHs) includes 4 kinds: α -666, γ -666, β -666, δ -666.
The DDT (DDTs) includes 4 kinds: PP '-DDE, OP '-DDT, PP '-DDD, PP '-DDT
The n-alkane (n-alkane) includes: nC10H22、nC11H24、nC12H26、nC13H28、nC14H30、 nC15H32、 nC16H34、nC17H36、Pristane、nC18H38、Phytane、nC19H40、nC20H42、nC21H44、 nC22H46、nC23H48、 nC24H50、nC25H52、nC26H54、nC27H56、nC28H58、nC29H60、nC30H62、 nC31H64、nC32H66、nC33H68、nC34H70、 nC35H72
Two, reagent and its preparation
Unless otherwise indicated, chromatography pure reagent that meet national standards is used when analysis.Experimental water is super for Mili-Q Pure water.
Acetone (C3H6O): chromatographically pure;N-hexane (C6H14): chromatographically pure;Methylene chloride (CH2Cl2): chromatographically pure;Methanol (CH3OH): chromatographically pure;Hydrochloric acid (HCl): 1+1 is mixed with top grade pure hydrochloric acid according to 1: 1 volume ratio;N-hexane-methylene chloride is mixed Bonding solvent: 1+1 n-hexane and methylene chloride are mixed by 1: 1 volume ratio;Methylene chloride-methanol mixed solution: 1+1 dichloro Methane and methanol are mixed by 1: 1 volume ratio;
Anhydrous sodium sulfate: take appropriate anhydrous sodium sulfate in Muffle furnace in 450 DEG C of high temperature sintering 4h, after being cooled to room temperature It is spare.
Silica gel/aluminium oxide: take proper silica gel/aluminium oxide (100-200 mesh) with methylene chloride in Accelerate solvent extraction instrument Decontamination is rinsed, excessive organic solvent is extracted and is cooled to room temperature using preceding 130 DEG C of activation 4h in an oven, every 100g silica gel/ Aluminium oxide adds the ultrapure water of 3-5mL to deactivate.Be placed in tool plug bottle in it is spare, in 7 days effectively.
Copper powder (200 mesh, purity 99.8%): embathing half a minute with hydrochloric acid solution, and incline acid, is washed with water to neutrality, then use Acetone cleans for several times, logical to be dried with nitrogen, and is stored in spare in the tool plug vial filled with nitrogen.
Silica wool: taking appropriate silica wool, in 450 DEG C of high temperature sintering 4h, to be cooled to room temperature in Muffle furnace, is stored in tool plug It is spare in vial.
Polycyclic aromatic hydrocarbon Standard Stock solutions: 2000 μ g/mL are dissolved in benzene: dichlorotoleune (1: 1)
Polycyclic aromatic hydrocarbon standard intermediate solution: the hybrid standard stock solution of appropriate volume is accurately pipetted, is diluted with n-hexane To required concentration, 2-8 DEG C is kept in dark place.
Polycyclic aromatic hydrocarbon internal standard stock solution: it is molten to accurately weigh 0.01g hexamethylbenzene (Hexamethylbenzene, HMB) In 10mL n-hexane solvent, it is prepared as the stock solution that concentration is 1000 μ g/mL.
Polycyclic aromatic hydrocarbon internal standard uses solution: accurately pipetting the hybrid standard stock solution of appropriate volume, is diluted with n-hexane To required concentration, 2-8 DEG C is kept in dark place.
The polycyclic aromatic hydrocarbon rate of recovery indicates standard solution: 2000mg/L is dissolved in methylene chloride, contains five kinds of deuterated polycyclic aromatic hydrocarbons Compound: acenaphthene-d10, phenanthrene-d10,- d12 ,-d12, naphthalene-d8.
The polycyclic aromatic hydrocarbon rate of recovery indicates intermediate solution: accurately pipetting the polycyclic aromatic hydrocarbon rate of recovery instruction standard of appropriate volume Solution is diluted to required concentration with n-hexane, is kept in dark place.
Polycyclic aromatic hydrocarbon hybrid standard working solution: appropriate mixing intermediate solution, rate of recovery instruction solution are accurately pipetted and is fitted Amount internal standard be dissolved in suitable n-hexane solvent using solution be prepared into polycyclic aromatic hydrocarbon concentration be 0.05 μ g/mL, 0.1 μ g/mL, 0.5 μ g/mL, 1 μ g/mL, 2 μ g/mL, 5 μ g/mL and containing the internal standard object concentration be 1 μ g/mL hybrid standard working solution, 2-8 DEG C It is kept in dark place.
Polychlorinated biphenyls Standard Stock solutions: 100 μ g/mL are dissolved in isooctane.
Polychlorinated biphenyls standard intermediate solution: the hybrid standard stock solution of appropriate volume is accurately pipetted, is diluted with isooctane To required concentration, 2-8 DEG C is kept in dark place.
Polychlorinated biphenyls internal standard stock solution: accurately weigh 0.01g pentachloronitrobenzene (Pentachloronitrobenzene, PCNB it) is dissolved in 10mL n-hexane solvent, is prepared as the stock solution that concentration is 1000 μ g/mL.
Polychlorinated biphenyls internal standard uses solution: accurately pipetting the hybrid standard stock solution of appropriate volume, is diluted with n-hexane To required concentration, 2-8 DEG C is kept in dark place.
Six six six, DDT Standard Stock solutions: 100 μ g/mL are dissolved in toluene.
Six six six, DDT standard intermediate solution: accurately pipetting the hybrid standard stock solution of appropriate volume, use just oneself Alkane is diluted to required concentration, and 2-8 DEG C is kept in dark place.
The chlorine-containing compound rate of recovery indicates that standard solution: 2,4,5,6- tetra- chloro-m-xylenes (TCmX), 1000 μ g/mL are molten In n-hexane, ten chlordiphenyls (PCB-209), 100ng/ μ L is dissolved in hexamethylene.
The chlorine-containing compound rate of recovery indicates working solution: accurately pipetting the chlorine-containing compound rate of recovery instruction of appropriate volume Standard solution is diluted to required concentration with n-hexane, is kept in dark place.
Polychlorinated biphenyls hybrid standard working solution: appropriate mixing intermediate solution, rate of recovery instruction solution are accurately pipetted and is fitted Amount internal standard is dissolved in suitable n-hexane solvent using solution is prepared into Polychlorinated biphenyls concentration as 0.005 μ g/mL, 0.01 μ g/ The hybrid standard that mL, 0.05 μ g/mL, 0.1 μ g/mL, 0.2 μ g/mL, 0.5 μ g/mL and containing the internal standard object concentration are 1 μ g/mL works Solution, 2-8 DEG C is kept in dark place.
N-alkane Standard Stock solutions: 500 μ g/mL are dissolved in toluene.
N-alkane standard intermediate solution: the hybrid standard stock solution of appropriate volume is accurately pipetted, is diluted with n-hexane To required concentration, 2-8 DEG C is kept in dark place.
The n-alkane rate of recovery indicates stock solution: accurately weighing the deuterated n-tetracosane (nC of 0.01g24D50) be dissolved in In 10mL n-hexane solvent, it is prepared as the stock solution that concentration is 1000 μ g/mL.
The n-alkane rate of recovery uses solution: the hybrid standard stock solution of appropriate volume is accurately pipetted, it is dilute with n-hexane It releases to required concentration, 2-8 DEG C is kept in dark place.
N-alkane hybrid standard working solution: appropriate mixing intermediate solution, rate of recovery instruction solution are accurately pipetted and is fitted Amount internal standard is dissolved in suitable n-hexane solvent using solution (HMB) is prepared into polycyclic aromatic hydrocarbon concentration as 0.05 μ g/mL, 0.1 μ G/mL, 0.5 μ g/mL, 1 μ g/mL, 2 μ g/mL, 5 μ g/mL and containing the internal standard object concentration are the hybrid standard working solution of 1 μ g/mL, 2-8 DEG C is kept in dark place.
Three, instrument and equipment
Gas chromatography-mass spectrometry;Chromatographic column: J&WDB-5MS quartz capillary chromatograph (30m*0.25mm*0.25 μ m);Muffle furnace;Constant temperature oven;Rotary Evaporators;Glass chromatography column;Supersonic cleaning machine;Accelerate solvent extraction instrument;Nitrogen evaporator;It is cold Lyophilizer;Ten thousand grades of balances;Common laboratory common instrument and equipment.
Four, in the Gas Chromatography-Mass Spectrometry deposit organic matter method the following steps are included:
1, sample preparation
Sample be placed in advance clean drying and 450 DEG C of calcination 4h wide-mouth sampling bottle in or with equally processed aluminium Foil package, sample contain a large amount of moisture, to pay special attention to the sealing of container, refrigerate under the conditions of being placed in -20 DEG C to -40 DEG C.Sample After being sent to laboratory after product acquisition, it should handle and analyze as early as possible.
Contain large quantity of moisture in deposit, it is necessary to be removed, be not directly exposed to the sun in the sun or high with method appropriate Temperature drying, the method that vacuum freeze drying can be used, dry 3-7 days (depending on the sample size) in freeze drier.It will Dry sample is after agate mortar is ground by spare after the sieve of 100 mesh after dehydration.
2, sample extraction
10g sample is weighed, rate of recovery indicator is added and is fitted into ASE abstraction pool by step, after installing sample, placed Loading after night carries out ASE extraction, and solvent is methylene chloride, takes out receiving bottle after extraction, is added in receiving bottle appropriate The copper powder sulphur removal activated is non-discolouring to copper powder, and the liquid in receiving bottle is transferred in pear shape bottle.
ASE condition:
System pressure 10.3MPa, 100 DEG C of extraction temperature, heating time 5min, quiet hour 5min, flush volume is extraction The 60% of pond body product is taken, is recycled 2 times.
3, sample purification
Pending chromatography post separation is concentrated by Rotary Evaporators in liquid in pear shape bottle.It is chromatographed in the glass of 8mm internal diameter Column successively fills out the deactivation neutral alumina of 3cm, the deactivation neutral silica gel of 3cm, the anhydrous sodium sulfate of 1cm from top to bottom.First with two Chloromethanes is washed pillar 2 times (10mL), then is washed pillar 2 times (10mL) with n-hexane, just drops to anhydrous sodium sulfate circle to liquid level When face, concentrate is added drop-wise in chromatographic column, fills the pear shape bottle of concentrate, rinse liquid three times with n-hexane/methylene chloride rinse Also upper chromatographic column.When sample drops to anhydrous sodium sulfate interface, successively with 10mL n-hexane, 20mL n-hexane/methylene chloride, 10mL methylene chloride/methanol elutes extraction column, collects eluent respectively.N-hexane affords non-polar component (F1), just oneself Alkane/dichloromethane eluent obtains middle polarity component (F2), and methylene chloride/methanol elutes to obtain polar compound (F3).Deposition PCBs, HCHs, DDTs, n-alkane are present in F1 component in object, and PAHs is present in F2 component.Through rotary evaporation and nitrogen After blowing, F1 component adds inner mark solution each 1000ng of PCNB and HMB, and F2 component adds internal standard HMB1000ng, fixed with n-hexane constant volume Hold to 1ml, is placed in -20 DEG C of refrigerators and saves, it is to be analyzed.
4, sample measures
(1) GC condition:
J&W DB-5MS quartz capillary chromatograph (30m × 0.25mm × 0.25 μm);280 DEG C of temperature of vaporization chamber;Carrier gas is High-purity He (99.999%);Flow velocity 1.0mL/min;1 μ L of sample volume;Splitless injecting samples.
Temperature program:
1) 60 DEG C (keeping 1min), 280 DEG C (keeping 15min) polycyclic aromatic hydrocarbon: are risen to 5 DEG C/min;
2) Polychlorinated biphenyls, six six six, DDT: 80 DEG C, 180 DEG C are risen to 30 DEG C/min, then rise to 205 with 3 DEG C/min DEG C (keep 2min), then 290 DEG C (keeping 4min) are risen to 5 DEG C/min;
3) n-alkane: 60 DEG C (keeping 1min), 170 DEG C (keeping 1min) are risen to 12 DEG C/min, then with 8 DEG C/min Rise to 300 DEG C (keeping 0.5min);320 DEG C (keeping 10min) are risen to 12 DEG C/min again:
(2) MS condition:
Electron bombardment (EI) ion source;Electron energy 70eV;280 DEG C of transmission line temperature;230 DEG C of ion source temperature;Quadrupole 150 DEG C of bar temperature;Solvent delay time 4min;Quantitative analysis using Salbutamol Selected Ion Monitoring (SIM) type collection polycyclic aromatic hydrocarbon, Polychlorinated biphenyls, six six six and DDT, using full scan type collection n-alkane.28 kinds of PCBs and 8 kinds of organo-chlorine pesticides The quantitation curves dependent linearity coefficients R of HCHs, DDTs2It is 0.990~0.998;The quantitation curves phase of 16 kinds of PAHs Close coefficients R2It is 0.995~0.999;The quantitation curves coefficient R of n-alkane2It is 0.992~0.999.
Five, record and calculating
1, qualitative analysis
(1) qualitative analysis of polycyclic aromatic hydrocarbon
It uses SIM method (table 1).Fig. 1 is the total ion chromatogram of polycyclic aromatic hydrocarbon.
1 SIM method characteristic ion in different time periods of table
Retention time refers to (table 2).
The different the retention time of the compound of table 2
(2) qualitative analysis of Polychlorinated biphenyls, six six six, DDT
It uses SIM method (table 3).Fig. 2 is Polychlorinated biphenyls, six six six, the total ion chromatogram of DDT.
3 SIM method characteristic ion in different time periods of table
Retention time refers to (table 4).
The different the retention time of the compound of table 4, characteristic ion and calibration curve
(3) qualitative analysis of n-alkane
Use full scan method, scanning range: (50-500) m/z.Fig. 3 is the total ion chromatogram of n-alkane.It protects Stay time reference table 5.
The different the retention time of the compound of table 5, characteristic ion and calibration curve
2, the calculating of response factor
The relatively corresponding factor R Fi of standard series the i-th point target compound is calculated according to formula (1).
In formula: RFi-- the relative response factor of the i-th point target compound in standard series;
Ai-- the response of the i-th point target compound quota ion in standard series;
AISi-- the response of i-th point of internal standard quota ion corresponding with target compound in standard series;
cISi-- the mass concentration of internal standard compound in standard series, μ g/mL;
ci-- the mass concentration of the i-th point target compound, μ g/mL in standard series.
3, the result of sediment sample calculates
Target compound content w (mg/kg) in sediment sample dry sample, according to following calculation.
In formula: the object content in w-- sample, mg/kg;
Ax-- the peak area of target compound quota ion in test fluid;
AIS-- the peak area of internal standard compound quota ion in test fluid;
cIS-- interior target concentration, μ g/mL in test fluid;
RFi-- the average relative response factor of calibration curve;
Vx-- concentration constant volume, mL;
M-- sample size, g;
Six, precision and accuracy
1, precision
It is respectively 1 μ g/mL polycyclic aromatic hydrocarbon, 0.1 μ g/mL Polychlorinated biphenyls, six six six, DDT, 1 μ g/mL to spiked levels The hybrid standard of n-alkane is unified sample and is determined.Relative standard deviation is respectively 0.9%-4.6%, 1.4%- 7.9% and 1.5%-7.1%.
2, accuracy
Recovery of standard addition measurement carried out to 10g sediment sample respectively, spiked levels are 1 μ g/mL polycyclic aromatic hydrocarbon, 0.1 μ g/mL Polychlorinated biphenyls, six six six, DDT, 1 μ g/mL n-alkane.Recovery of standard addition average value ranges are respectively as follows: polycyclic virtue Hydrocarbon is 75-112%, Polychlorinated biphenyls, six six six, DDT 84%-105%, n-alkane 85-102%.
3, detection limit and quantitative limit
It is 2-5 times of the sample that estimation method detects limit value to concentration value or content according to the Overall Steps of sample analysis N >=7 time are carried out to be measured in parallel.The standard deviation that n times are measured in parallel is calculated, method detection limit is calculated by formula.Detection limit difference Are as follows: polycyclic aromatic hydrocarbon 0.06-0.76ng/g, Polychlorinated biphenyls, six six six, DDT 0.04-0.26ng/g, n-alkane are 0.04-0.82ng/g;It is 0.20-2.53ng/g that quantitative limit, which is respectively as follows: polycyclic aromatic hydrocarbon, and Polychlorinated biphenyls, six six six, DDT are 0.13-0.87ng/g, n-alkane 0.13-2.74ng/g.It is shown in Table 6.
The detection limit and quantitative limit of the different compounds of table 6
Seven, quality controls
1, solvent blank is tested
It after experiment solvent hexane and methylene chloride are concentrated 60 times, is detected into GC-MS, the blank result of analysis is answered Lower than method detection limit.
2, analysis margin is tested
Every batch of sample (being no more than 20) must do a blank test, the target concentration side of being not to be exceeded in measurement result Method detection limit.Otherwise, reagent blank, instrument system and pretreatment process should be checked.
3, mark-on reclaims
Standard is added in blank sample kind and uses solution, remaining step is executed according to 5, and one batch sample of every analysis is to whole A analytic process carries out 10% recovery testu.The sample analysis rate of recovery is preferably controlled in 60-130%.
4, Duplicate Samples and Quality Control sample
Every 12 samples add a Duplicate Samples, and every 24 samples add a Quality Control sample.The test knot of Duplicate Samples and Quality Control sample Fruit relative deviation should be less than 30%.
Eight, points for attention
Acquisition, storage and the transport of sample should meet the regulation of GBT12763.8-2007.
Reagent used in experiment and standard liquid have certain toxicity, Ying Caiyong safeguard procedures.
For the pollution for avoiding organic substance, sediment sample should be placed in the wide mouth glass bottle of calcination or calcination Aluminium foil package.
All vessel used in experiment need rinse or calcination by organic reagent.
All waste liquids and waste (including the raffinate after detection) generated in test, which should be placed in closed container, to be saved, and is entrusted Hold in the palm qualified processed in units.
The above embodiments are merely illustrative of the technical solutions of the present invention, rather than is limited;Although referring to aforementioned reality Applying example, invention is explained in detail, for those of ordinary skill in the art, still can be to aforementioned implementation Technical solution documented by example is modified or equivalent replacement of some of the technical features;And these are modified or replace It changes, the spirit and scope for claimed technical solution of the invention that it does not separate the essence of the corresponding technical solution.

Claims (10)

1. a kind of method of organic matter in Gas Chromatography-Mass Spectrometry deposit, it is characterised in that: the method includes following Step:
(1) it prepares: deposit being dehydrated, is ground up, sieved, sample is made;
(2) it extracts: sample is subjected to ASE extraction, the solvent used is methylene chloride, obtains extract liquor;
(3) it purifies: extract liquor being concentrated, concentrate is separated using chromatographic column, collects eluent respectively;The chromatographic column Fill method are as follows: successively fill out the deactivation neutral alumina of 3 ~ 4cm from top to bottom, the deactivation neutral silica gel of 3 ~ 4cm, 1 ~ 2cm's Anhydrous sodium sulfate;
(4) it measures: the organic matter in eluent being subjected to qualitative and quantitative analysis with gas chromatography-mass spectrography, wherein according to color The characteristic ion of spectral peak retention time and object is qualitative, inner mark method ration.
2. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: The organic matter is polycyclic aromatic hydrocarbon, Polychlorinated biphenyls, six six six, DDT and n-alkane.
3. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: The method dehydrated in the step (1) is to use freeze drier vacuum freeze drying 3-7 days.
4. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: ASE extraction conditions is 10 ~ 11MPa of system pressure in the step (2), and 90 ~ 110 DEG C of extraction temperature, 3 ~ 7min of heating time is quiet 5 ~ 10min of state time, flush volume are the 60 ~ 70% of abstraction pool volume, are recycled 2 ~ 3 times.
5. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: After the step (2) further includes ASE extraction, the copper powder that addition has activated is non-discolouring to copper powder, obtains extract liquor.
6. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: The diameter of chromatographic column is 8mm in the step (3).
7. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: The specific steps separated in the step (3) are as follows:
Concentrate is added drop-wise in chromatographic column, successively elutes layer with n-hexane, n-hexane and methylene chloride, methylene chloride and methanol Column is analysed, non-polar component, middle polarity component and polar compound are respectively obtained;
After rotary evaporation and nitrogen are blown, non-polar component adds inner mark solution PCNB and HMB, and middle polarity component adds internal standard HMB, uses N-hexane constant volume.
8. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: The condition of gas-chromatography in the step (4) are as follows:
Chromatographic column: column length 30m, diameter 0.25mm, 0.25 μm of film thickness;250 ~ 300 DEG C of temperature of vaporization chamber;Carrier gas is high-purity He;Stream 0.9 ~ 1.2mL/min of speed;1 μ L of sample volume;Input mode is Splitless injecting samples.
9. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 8, it is characterised in that: The temperature program of the condition of gas-chromatography in the step (4) are as follows:
Polycyclic aromatic hydrocarbon:, keeping 1 ~ 2min by 50 ~ 70 DEG C, rises to 250 ~ 300 DEG C with 5 DEG C/min, keeps 15 ~ 20min;
Polychlorinated biphenyls, six six six, DDT: 80 ~ 100 DEG C, 180 ~ 200 DEG C are risen to 30 DEG C/min, then rise to 3 DEG C/min 200 ~ 210 DEG C, 2 ~ 5min is kept, then rise to 250 ~ 300 DEG C with 5 DEG C/min, keep 3 ~ 6min;
N-alkane:, keeping 1 ~ 2min by 50 ~ 80 DEG C, rises to 150 ~ 200 DEG C with 12 DEG C/min, keeps 1 ~ 2min, then with 8 DEG C/ Min rises to 270 ~ 310 DEG C, keeps 0.5 ~ 1min;300 ~ 350 DEG C are risen to 12 DEG C/min again, keeps 10 ~ 15min.
10. the method for organic matter in Gas Chromatography-Mass Spectrometry deposit according to claim 1, it is characterised in that: Mass Spectrometry Conditions in the step (4) are as follows: electron impact ion source;Electron energy 70eV;280 ~ 300 DEG C of transmission line temperature;Ion 230 ~ 250 DEG C of source temperature;130 ~ 170 DEG C of quadrupole rod temperature;3 ~ 6min of solvent delay time.
CN201910614696.XA 2019-07-09 2019-07-09 A kind of method of organic matter in Gas Chromatography-Mass Spectrometry deposit Pending CN110346472A (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112051347A (en) * 2020-09-30 2020-12-08 浙江大学 GC-MS quantitative method capable of simultaneously and rapidly analyzing 41 persistent organic matters in soil
CN114264758A (en) * 2020-09-16 2022-04-01 南京理工大学 Pretreatment method for detecting PCBs, PBDEs and EHFRs in sediment

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101458236A (en) * 2008-12-30 2009-06-17 重庆市计量质量检测研究院 Method for detecting polycyclic aromatic hydrocarbon in plastic product
CN101726558A (en) * 2009-12-10 2010-06-09 清华大学 Method for detecting polycyclic aromatic hydrocarbon component in coking wastewater processing system
CN103592399A (en) * 2013-12-04 2014-02-19 上海大学 Method capable of simultaneously measuring organochlorine pesticide concentration and synthetic musk concentration in human serum
CN104237436A (en) * 2014-09-03 2014-12-24 上海大学 Qualitative screening method of semi-volatile halogenated organic pollutants in sediments
CN105092748A (en) * 2014-05-07 2015-11-25 中国科学院生态环境研究中心 Method for screening organic pollutants in sludge
CN106841490A (en) * 2017-03-10 2017-06-13 环境保护部华南环境科学研究所 A kind of method of contained polycyclic aromatic hydrocarbon in detection surrounding air
CN108680681A (en) * 2018-07-09 2018-10-19 江苏理工学院 Method that is a kind of while measuring polycyclic aromatic hydrocarbons on atmospheric particles and n-alkane
CN109604317A (en) * 2018-12-05 2019-04-12 兰州大学 A kind of charcoal and its purposes for handling Pollution of Polycyclic Aromatic Hydrocarbons in Soil

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101458236A (en) * 2008-12-30 2009-06-17 重庆市计量质量检测研究院 Method for detecting polycyclic aromatic hydrocarbon in plastic product
CN101726558A (en) * 2009-12-10 2010-06-09 清华大学 Method for detecting polycyclic aromatic hydrocarbon component in coking wastewater processing system
CN103592399A (en) * 2013-12-04 2014-02-19 上海大学 Method capable of simultaneously measuring organochlorine pesticide concentration and synthetic musk concentration in human serum
CN105092748A (en) * 2014-05-07 2015-11-25 中国科学院生态环境研究中心 Method for screening organic pollutants in sludge
CN104237436A (en) * 2014-09-03 2014-12-24 上海大学 Qualitative screening method of semi-volatile halogenated organic pollutants in sediments
CN106841490A (en) * 2017-03-10 2017-06-13 环境保护部华南环境科学研究所 A kind of method of contained polycyclic aromatic hydrocarbon in detection surrounding air
CN108680681A (en) * 2018-07-09 2018-10-19 江苏理工学院 Method that is a kind of while measuring polycyclic aromatic hydrocarbons on atmospheric particles and n-alkane
CN109604317A (en) * 2018-12-05 2019-04-12 兰州大学 A kind of charcoal and its purposes for handling Pollution of Polycyclic Aromatic Hydrocarbons in Soil

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
胡利民: "大河控制性影响下的陆架海沉积有机质的"源-汇"作用", 《中国博士学位论文全文数据库 工程科技Ⅰ辑》 *
郑亚楠: "沉积物中持久性有机污染物的检测", 《中国优秀硕士学位论文全文数据库 工程科技I辑》 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114264758A (en) * 2020-09-16 2022-04-01 南京理工大学 Pretreatment method for detecting PCBs, PBDEs and EHFRs in sediment
CN114264758B (en) * 2020-09-16 2023-04-07 南京理工大学 Pretreatment method for detecting PCBs, PBDEs and EHFRs in sediment
CN112051347A (en) * 2020-09-30 2020-12-08 浙江大学 GC-MS quantitative method capable of simultaneously and rapidly analyzing 41 persistent organic matters in soil

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