CN1164941C - Determination method of trace organic chlorine pesticide and polychlorobiphenyl residual amount - Google Patents
Determination method of trace organic chlorine pesticide and polychlorobiphenyl residual amount Download PDFInfo
- Publication number
- CN1164941C CN1164941C CNB01127140XA CN01127140A CN1164941C CN 1164941 C CN1164941 C CN 1164941C CN B01127140X A CNB01127140X A CN B01127140XA CN 01127140 A CN01127140 A CN 01127140A CN 1164941 C CN1164941 C CN 1164941C
- Authority
- CN
- China
- Prior art keywords
- pcb
- calibration curve
- mark
- working fluid
- polychlorinated biphenyl
- 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
Links
Images
Landscapes
- Other Investigation Or Analysis Of Materials By Electrical Means (AREA)
- Sampling And Sample Adjustment (AREA)
Abstract
The present invention discloses a gas chromatographic method for measuring residual quantities of trace organochlorine pesticides and polychlorinated biphenyl by using PCB2 and PCB209 as internal standards in an n-hexane oscillation extraction mode. Compared with the traditional Soxhlet extraction method, on the premise that the accuracy, the precision and the sensitivity are sufficiently ensured, the method of the present invention has the characteristics of simple pretreatment, low measuring cost and small amount of use specimens, can be used for simultaneously measuring residual quantities of organochlorine pesticides and typical compounds in the polychlorinated biphenyl class, and is especially suitable for measuring trace organic pollutants in food.
Description
Technical field
The present invention relates to the gas Chromatographic Determination method of trace organic chlorine pesticide and polychlorinated biphenyl in the assay method of persticide residue in the agricultural byproducts, particularly birds, beasts and eggs (polychlorinated biphenyl is called for short PCBs) residual quantity.
Background technology
Organo-chlorine pesticide once had been used for agricultural production in a large number since 20 beginnings of the century are synthetic, promoted the significantly raising of agricultural output.But because organo-chlorine pesticide holds property stayed and the height cumulative bad in fat thereof by force in environment, developed country forbids in succession, and China stops to produce and completely forbade on agricultural in 1986 in nineteen eighty-three and uses.In forbidding today after nearly 20 years, still can from various surrounding medium samples, detect the residue of organo-chlorine pesticide, the detected level in the sample segment is also quite high.Not only China's situation is like this, and in the much longer developed country of forbidding time ratio China, still can detect the residue of organo-chlorine pesticide so far from environment.
Micropollutant such as organic chloro pesticide residue, polychlorinated biphenyl transmission, rich the amassing in the process in the bird food chain such as (abbreviating PCBs down as), might enter birds, beasts and eggs and accumulate in wherein, the detection method of therefore establishing and improve trace organic chlorine pollutant in the birds, beasts and eggs is crucial for the control of agricultural byproducts quality.Yet the domestic special method of testing that does not also have contamination with chlorinated organics in the birds, beasts and eggs at present, and the method for testing of external relevant organochlorine residue thing in the environmental sample mostly with organo-chlorine pesticide such as benzene hexachloride and D.D.T. (dichloro-diphenyl-trichloroethane) (all abbreviating HCH and DDT down as) with measure respectively after PCBs separates, to get rid of the qualitative and quantitative of organo-chlorine pesticide and residual polychlorinated biphenyl thing mutual disturbing effect determinand in chromatographic determination.This type of method of testing, not only sample pre-treatments is tediously long, and workload and labour intensity are big, and the adsorbent of costliness that need to adopt import is as cleanser, thereby testing cost is too high.
In addition, American-European many during polychlorinated biphenyl in the testing environment sample be reference material with Aroclor1254 or Aroclor1260, majority of compounds is a perchloride in these two kinds of potpourris, be that amount of chlorine atom is higher in the molecule, as 61.78% of the ingredients constitute total amount of amount of chlorine atom among the Aroclor1254 〉=6,89.70% of the ingredients constitute total amount of amount of chlorine atom among the Aroclor1260 〉=6.Polychlorinated biphenyl according to China's production and use mostly is the characteristics of hanging down chlorine compound, and should select chloride low PCBs for use is reference material, and emphasis detects and contains the PCBs that amount of chlorine atom is 3-6, to meet the actual conditions of China.
Summary of the invention
The purpose of this invention is to provide the assay method of trace organic chlorine pesticide and residual polychlorinated biphenyl amount in a kind of birds, beasts and eggs, it chooses PCB
2And PCB
209Be internal standard compound, behind normal hexane (heavily steaming normal hexane) or sherwood oil vibration extraction, purification, constant volume, carry out gas Chromatographic Determination.
Assay method of the present invention comprises selects suitable interior mark to be mixed with interior mark annex solution as object of reference, will be mixed with corresponding calibration curve working fluid in the interior mark annex solution adding determinand standard mixed liquor then; The testing sample sampling in purifying, add, vibration extraction, acidity is obtained sample liquid to be measured behind mark annex solution, the constant volume, carry out chromatographic determination with the gas chromatograph of being furnished with electron capture detector (ECD) at last, it is characterized in that: in the suitable interior mark of above-mentioned selection is configured to as object of reference, in the step of mark annex solution, choose the PCB of polychlorinated biphenyl
2And PCB
209Be interior mark.
The concrete steps of this assay method are:
A) take by weighing internal standard compound PCB
2And PCB
209, dissolve mark storing solution in the standard that obtains with heavily steaming benzene respectively, it is an amount of to get the interior mark of above-mentioned standard storing solution respectively, is diluted to mark annex solution in the mixing heavily to steam normal hexane or sherwood oil again;
B) get and contain α-HCH, β-HCH, γ-HCH, δ-HCH, p, p '-DDE, p, p '-DDD, p, the standard blended liquid of p '-DDT, heptachlor, nine kinds of pesticide compositions to be measured of drinox, add in the mixing in the step a) with normal hexane or sherwood oil dilution back and to mark annex solution, be mixed with the calibration curve working fluid that contains nine kinds of pesticide compositions to be measured, HCH be benzene hexachloride, DDE for drip according to, DDD for dichloro-diphenyl-dichlorothane, DDT is D.D.T. (dichloro-diphenyl-trichloroethane);
C) 15 kinds of PCBs homolog reference materials, PCB
sBe polychlorinated biphenyl, be respectively PCB by the IUPAC name
28, PCB
52, PCB
70, PCB
74, PCB
66, PCB
87, PCB
99, PCB
101, PCB
118, PCB
153, PCB
141, PCB
138, PCB
185, PCB
180, PCB
194Each accurately takes by weighing in right amount, heavily to steam the hybrid standard storing solution that benzene dissolving constant volume becomes to contain 15 kinds of polychlorinated biphenyl components, get above-mentioned hybrid standard storing solution, add mark annex solution in the mixing in the step a), to be mixed with the calibration curve working fluid that contains 15 kinds of polychlorinated biphenyl components to be measured behind normal hexane or the sherwood oil dilution constant volume;
D) get egg white, yolk mixing, be lower than 60 ℃ and dry, grind to constant weight;
E) get anhydrous sodium sulfate and mix, grind powdering, place in the centrifuge tube and add mark annex solution in the mixing of step a), shake up with the result of step d);
F) add and heavily to steam normal hexane or sherwood oil, in vibrating machine, extract, after placing hydro-extractor centrifugal then extract;
G) add the concentrated sulphuric acid in extract, lower floor's acid solution is shifted out in vibration, centrifugal, abandons it, repeat for several times, and be colourless until lower floor's concentrated sulphuric acid eluate;
H) The above results is placed water-bath, under the protection of nitrogen stream, dry up, heavily to steam normal hexane or petroleum ether dissolution dried extract constant volume, get testing sample solution again;
I) get step b), c respectively) in the calibration curve working fluid and the step h that obtain) in the testing sample solution that obtains, with being equipped with the gas chromatograph (can abbreviate GC-ECD as) of electron capture detector (ECD) to carry out chromatographic determination.
Above-mentioned:
In the step a), mark storing solution concentration respectively is 2000 μ g/ml in the gained standard, PCB in the mark annex solution in mixing
2And PCB
209Concentration be respectively 10.0 μ g/ml and 0.5 μ g/ml;
In the step b), the concentration of each pesticide composition to be measured is 2000 μ g/ml, get the standard blended liquid of different volumes, quantitatively add mark annex solution in the mixing in the step a), behind normal hexane or sherwood oil dilution constant volume, be mixed with the calibration curve working fluid that contains nine kinds of pesticide compositions to be measured of a series of variable concentrations; In the above-mentioned calibration curve working fluid, the concentration of pesticide composition to be measured is respectively 0,8.0, and 16.0,32.0,64.0 and 100ng/ml, mark PCB in each
2And PCB
209Concentration be respectively 1000 and 50ng/ml;
In the step c), the PCB in described 15 kinds of polychlorinated biphenyl components
153, PCB
141, PCB
138, PCB
185, PCB
180, PCB
194Concentration be 300 μ g/ml, all the other nine kinds of component concentrations are 400 μ g/ml, get the hybrid standard liquid of containing of different volumes of above-mentioned 15 kinds of polychlorinated biphenyl components, quantitatively add mark annex solution in the mixing in the step a), behind normal hexane or sherwood oil dilution constant volume, be mixed with the calibration curve working fluid that contains 15 kinds of polychlorinated biphenyl components of a series of variable concentrations; In the above-mentioned calibration curve working fluid, polychlorinated biphenyl component concentrations scope is 2.5-400ng/ml, interior mark PCB
2And PCB
209Concentration be respectively 1000 and 50ng/ml;
In the step e), anhydrous sodium sulfate is used after toasting;
In the step f), vibration, centrifugal leaching process are 3 times, merge extract;
Step h) in, bath temperature is 40 ℃;
Step I) in, before beginning chromatographic determination with the gas chromatograph that is equipped with electron capture detector (ECD), measure the calibration curve working fluid earlier, after the chromatogram response of respective components is stablized, begin into the calibration curve working fluid and make calibration curve, carrying out testing sample solution afterwards measures, with peak height inner mark method ration or peak height single-point inner mark method ration, when implementing the single-point inner mark method ration, the calibration curve working fluid of looking sample concentration scope selection suitable concn is quantitative object of reference, and try to achieve correction factor with the mean value of 3-5 chromatogram peak height of this calibration curve working fluid, no matter be calibration curve or single-point sizing technique, in a large amount of sample test processes, all need get calibration curve working fluid sample introduction again, obtain the chromatogram response, calibration curve or correction factor are revised, to guarantee the test result accuracy.
Chromatogram test job condition is: carrier gas is high purity nitrogen, presses 55.16kPa before the post, and tail blows 60ml/min, sample size 1 μ l, split sampling not, 210 ℃ of the temperature of injection port, 310 ℃ of detector temperatures, 140 ℃ of column temperatures, keep 2min, be warming up to 270 ℃, keep 3min with the speed of 2 ℃/min.
Description of drawings
Fig. 1 is organo-chlorine pesticide and polychlorinated biphenyl homolog calibration curve working fluid chromatogram;
Fig. 2 is the gas chromatogram of the extract of certain commercially available egg in city.
Embodiment
The invention will be further described for the concrete mensuration embodiment that just provides below.
1. test material and equipment
Anhydrous sodium sulfate is analyzed purely, and 650 ℃ of bakings 4 hours after waiting to be chilled to room temperature, place the sealing of full glass container to store, and are stand-by;
The concentrated sulphuric acid (98%) is analyzed pure;
Normal hexane is analyzed purely, and redistillation is collected 68 ℃ of cuts in full glass container, and sealing is stored, and is stand-by;
Sherwood oil is analyzed purely, and redistillation is collected 68-72 ℃ of cut in full glass container, and sealing is stored, and is stand-by;
Benzene is analyzed purely, and redistillation is collected 72 ℃ of cuts in full glass container, and sealing is stored, and is stand-by;
7% aqueous sodium persulfate solution;
Reciprocating type concussion machine;
Hydro-extractor (changeing scooter 4500/min);
20ml spiral mouth centrifuge tube, screw top, polytetrafluoroethyllining lining pad, good airproof performance;
2ml spiral mouth sample bottle, screw top, inner liner polytetrafluoroethylene film, good airproof performance;
60ml extracting fat device;
The 200ml separating funnel.
2. instrument
Gas chromatograph: HEWLETT5890-II, distribution muon capture detecting device (GC/ECD), HW-2000 type chromatographic work station, capillary column HP-5, internal diameter 0.32um, long 30m.
3. calibration curve working fluid
Dried whole-egg, object of reference 8415, Canadian national standard and technical institute's development.
Interior mark: PCB
2, PCB
209, accurately take by weighing internal standard compound respectively with heavily steaming the benzene dissolving, being mixed with concentration is the standard reserving solution of 2000 μ g/ml respectively, gets this standard reserving solution and is diluted to mark annex solution, wherein PCB in the mixing with normal hexane
2And PCB
209Concentration be respectively 10.0 and 0.5 μ g/ml.
Organo-chlorine pesticide: contain α-HCH, β-HCH, γ-HCH, δ-HCH, p, p '-DDE, p, p '-DDD, p, the agricultural chemicals hybrid standard liquid of 9 kinds of reference materials such as p '-DDT, heptachlor, drinox, various pesticide concentrations all are about 2000 μ g/ml, solvent is 1: 1 normal hexane/methanol solution, purchases the company in Supelco.Get this hybrid standard liquid and progressively dilute with normal hexane, be mixed with the calibration curve working fluid, its concentration is respectively: 0,8.0,16.0,32.0,64.0 and 100.0ng/ml, in each calibration curve working fluid in mark PCB
2And PCB
209Concentration be respectively 1000ng/ml and 50ng/ml.
Polychlorinated biphenyl: be respectively PCB by the IUPAC name
28, PCB
52, PCB
70, PCB
74, PCB
66, PCB
87, PCB
99, PCB
101, PCB
118, PCB
153, PCB
141, PCB
138, PCB
185, PCB
180, PCB
194Totally 15 kinds of PCBs homologs (congener) reference material is purchased the company in Chem Seveic.Accurately take by weighing various reference materials respectively with the dissolving of redistillation benzene, compound concentration is the standard reserving solution of 2000 μ g/ml respectively, and it is an amount of to get various storing solutions, is diluted to hybrid standard mother liquor, wherein PCB with normal hexane
153, PCB
141, PCB
138, PCB
185, PCB
180, PCB
194Concentration be 300 μ g/ml, all the other concentration of component respectively are 400 μ g/ml.Get the hybrid standard mother liquor and progressively dilute with normal hexane, be mixed with the calibration curve working fluid, its concentration range is 2.5-400ng/ml, interior mark PCB in each calibration curve working fluid
2And PCB
209Concentration be respectively 1000ng/ml and 50ng/ml.
4. test method
Birds, beasts and eggs are abandoned shell, and the yellow and white mixing places the opening glass container to dry to constant weight for 45 ℃, grinds in mortar, is collected in the container, and is stand-by.
(1). the vibration extraction method
Take by weighing anhydrous sodium sulfate 2.0 gram, place small-sized mortar, accurately take by weighing birds, beasts and eggs powder 0.200-0.500 gram and put into anhydrous sodium sulfate and be ground into powder through baking, change in the 20ml centrifuge tube through funnel, mark annex solution 50ul in adding with microsyringe, treat that solvent evaporates is done after, shake all;
Extract: increase the weight of to steam normal hexane 4.0ml, screw screw top, 3min is extracted in vibration on the sample earthquake machine, places the centrifugal 3min of hydro-extractor, rotating speed 4200 commentaries on classics/min.With disposable dropper extract is gone in another 20ml spiral mouth centrifuge tube, powdered egg extracts and repeats said process twice again, merges extract, gets the about 12ml of extract.
The acid purification: add concentrated sulphuric acid 1ml to extract, screw screw top, vibration 3min, centrifugal, will become the concentrated sulphuric acid sucking-off of tan lower floor with disposable dropper, discard this spent acid solution.This process repeats for several times, till lower floor's concentrated sulphuric acid eluate is colourless.
Concentrate constant volume: change the extract after purified treatment over to a clean tube, place about 40 ℃ of water-baths, under the protection of nitrogen stream, dry up.Accurately add 0.5ml and heavily steam normal hexane, with solution mixing (0.5min) in the test tube, draw mixing solution with disposable dropper and insert in the 2ml sample bottle with the vortex vortex mixer, screw bottle cap, place the refrigerator low-temperature dark to preserve, treat chromatographic determination, finish the test of sample in the week.
5. measure
Before beginning sample GC-ECD test, first metric works liquid after respective components chromatogram response is stable, begins into calibration curve working fluid making calibration curve, carries out sample determination afterwards.With the peak height inner mark method ration, or peak height single-point inner mark method ration.When implementing the single-point inner mark method ration, the calibration curve working fluid that visual sample concentration scope is got suitable concn is quantitative object of reference, and tries to achieve correction factor with the mean value of 3-5 chromatogram peak height of this calibration curve working fluid.No matter be calibration curve or single-point sizing technique, in the process of a large amount of sample tests, all need get standard operation liquid sample introduction again, obtain the chromatogram response, calibration curve or correction factor are carried out necessary revision, to guarantee precision of test result.
Condition of work: carrier gas, press 55.16kPa before the high purity nitrogen, post, tail blows 60ml/min; Sample size: 1ul, not split sampling.210 ℃ of injector temperatures, 310 ℃ of detector temperatures, 140 ℃ of column temperatures keep 2min, are warming up to 270 ℃ with the speed of 2 ℃/min, keep 3min.
Result and discussion
One. the recovery of method and influence factor thereof
Add organo-chlorine pesticide standard operation liquid and each 0.5ml of PCBs standard operation liquid (the accurate concentration value of each component sees Table 1) with the 0.5g dried whole-egg, after treating that solvent evaporates is done, mark annex solution 50ul in adding, mixing, the vibration extraction method of extracting with the 50ml normal hexane with soxhlet extraction respectively and introducing according to this paper is extracted, purifies, is concentrated constant volume and GC/ECD measures determinand.Gained adds the recovery (three repetition mean value) and lists in table 1
Table 1 organo-chlorine pesticide machine polychlorinated biphenyl adds the recovery (%, the mean value of three repetitions)
| Determinand | Amount of chlorine atom among the PCBs | Add concentration (ng/g) | Soxhlet extraction | The vibration extraction method |
| α-HCH | 8.0 | 94.81 | 98.38 | |
| β-HCH | 8.0 | 108.58 | 98.38 | |
| ν-HCH | 8.0 | 107.41 | 103.50 | |
| δ-HCH | 8.0 | 85.03 | 84.31 | |
| | 3 | 6.25 | 106.24 | 110.32 |
| Heptachlor heptachlor | 8.0 | 106.81 | 102.94 | |
| | 4 | 6.25 | 108.22 | 103.36 |
| Drinox aldrine | 8.0 | 97.09 | 88.25 | |
| | 4 | 4.75 | 111.18 | 107.58 |
| | 4 | 4.50 | 112.53 | 119.16 |
| | 4 | 5.38 | 98.98 | 108.46 |
| | 5 | 3.75 | 98.83 | 89.55 |
| | 5 | 6.13 | 108.08 | 104.98 |
| | 5 | 5.5 | 103.96 | 86.03 |
| p，p’- | 8 | 112.4 | 112.5 | |
| | 5 | 5.13 | 122.28 | 109.06 |
| p，p’- | 8 | 98.24 | 99.06 | |
| PCB 153 | 6 | 2.50 | 108.00 | 103.60 |
| PCB 141 | 6 | 3.25 | 115.58 | 116.77 |
| p，p’- | 8 | 97.74 | 95.88 |
| PCB 138 | 6 | 2.50 | 104.44 | 111.88 |
| | 7 | 2.75 | 113.11 | 107.67 |
| | 7 | 2.50 | 98.20 | 96.80 |
| | 8 | 3.13 | 120.02 | 108.15 |
Table 2 vibration extraction time adds the influence of the recovery (%) to part for the examination thing
| Determinand | Extract once | Extract secondary | Extract three times |
| α-HCH | 49.67 | 76.23 | 84.74 |
| β-HCH | 57.77 | 79.55 | 89.23 |
| ν-HCH | 54.16 | 80.03 | 90.27 |
| Heptachlor heptachlor | 80.69 | 100.14 | 103.38 |
| p，p’-DDE | 88.20 | 109.31 | |
| p，p’-DDD | 74.89 | 90.27 | 94..62 |
| p，p’-DDT | 99.34 | 125.13 | 121.59 |
| PCB 153 | 103.17 | 108.44 | 109.42 |
| PCB 138 | 97.98 | 107.50 | 109.04 |
| PCB 180 | 93.29 | 93.99 | 92.15 |
As can be seen from Table 1,9 kinds of organo-chlorine pesticides selecting and 15 kinds of polychlorinated biphenyl that supply examination extract with the extraction of vibrating with Soxhlet all can obtain the good recovery.In view of Soxhlet extraction time longer, reagent dosage is big, and needs specific extraction element, and the vibration extraction is simple to the requirement of facility, extraction time is short, and recovery height can satisfy the requirement that this method is measured micro quantity organic pollutant in the Poultry and Eggs fully so vibration is extracted.
Test findings shows that also the number of times of vibration extraction is outstanding to the recovery influence of polychlorinated biphenyl, but the recovery of organo-chlorine pesticide residue is had tangible influence (table 2).All＜60% extract recovery side, back near 90% as three kinds of HCH recovery when extracting for the first time at three times.Therefore it is good extracting 3 times with vibration when measuring Residual Levels of Organochlorine Pesticides.
Two. the separation case of chromatogram
As seen under selected chromatogram condition of work, component to be measured obtains good separation from Fig. 1 Fig. 2, and the degree of separation R at each peak is shown in Table 3.R is a nondimensional number, peak height two component Quantitative Separation such as when R is 1, and peak height two components are quantitatively separated fully when R is 1.5 etc., and R value is big more, and the separation of two peaks is good more.This shows that under the chromatogram condition of work that this method is selected, component situation to be measured satisfies the needs that actual sample is measured fully.1:PCB among Fig. 1, Fig. 2
2(interior mark) 2: α-HCH 3:r-HCH 4: β-HCH 5: δ-HCH 6:PCB
287: heptachlor 8:PCB
529: drinox 10: Heptachlor epoxide 11:PCB
7412:PCB
7013:PCB
6614:PCB
10115:PCB
9916:PCB
8717:p, p '-DDE 18: different Di Shi agent 19: Huo Shi agent aldehyde 20:PCB
11821:p, p '-DDD 22: 5a,6,9,9a-hexahydro-6,9-methano-2,4-β 23:PCB
15324:PCB
14125: 5a,6,9,9a-hexahydro-6,9-methano-2,4 sulfate 26:p, p '-DDT 27:PCB
13828:PCB
18529:PCB
18030:PCB
19431:PCB
209(interior mark).
Three, the coefficient of variation and minimum detect concentration
Detect the computing formula of concentration according to minimum:
The minimum that calculates each component to be measured detects concentration C
Mix, list table 3 in.
C in the formula
Mix: minimum detects concentration, C: calibration curve working fluid concentration (ng/ml), N: noise of instrument (uv), h: calibration curve working fluid peak height (uv).
As seen from Table 3: the minimum of each component to be measured detect concentration all≤0.35ng/g, this foot has satisfied detection needs of trace organic chlorine pollutant in the birds, beasts and eggs.With regard to the coefficient of variation (CV), although interpolation concentration is lower, method all can obtain good degree of accuracy to all components, and the CV value of majority of compounds is about 10%, and only the CV value of a few component is slightly high, but still less than 20%.
Four. the distribution situation of micro quantity organic pollutant in egg white and yolk
Because all determinands mostly are the lipophilicity organism in this method, differ so distribute in the different sample of lipid content.Table 4 is depicted as the distribution situation of pollutant in the commercially available egg in certain city, institute's column data as can be seen from table, the content of all contaminations has very big-difference in the interior egg white of same egg, the yolk, and except that α-HCH, the content of most determinands in yolk is higher than its value of detecting in egg white far away.In addition, because the amount of dry matter of egg white is low, the amount of dry matter of powdered egg depends primarily on yolk, therefore can think roughly that pollutant mainly is distributed in the yolk.Simultaneously, when needs are measured the content of pollutant in the dried whole-egg, powdered egg fully must be ground mixing, otherwise, may cause the inaccurate of test result because of sampling inhomogeneous.
Table 3 this method detects concentration and detects the coefficient of variation (seven repetition mean value) the minimum of different determinands
Serial number name peak, peak degree of separation concentration limit (ng/g) coefficient of variation (CV, %)
*
2 α-HCH 5.0 0.35 8％
3 r-HCH 1.2 0.30 13％
4 β-HCH 5.5 0.25 17％
5 -HCH 8.0 0.27 10％
6 PCB28 3.2 0.30 15％
7 heptachlor heptachlor 5.6 0.29 8%
8 PCB
52 3.1 0.19 8％
9 drinox aldrin 11.8 0.21 18%
11 PCB
74 1.4 0.19 12％
12 PCB
70 1.2 0.28 13％
13 PCB
66 8.4 0.19 14％
14 PCB
101 1.7 0.04 9％
15 PCB
99 7.4 0.20 9％
16 PCB
87 1.3 0.1 0 18％
17 PP′-DDE 6.6 0.19 15％
20 PCB
118 3.4 0.18 8％
21 PP′-DDD 2.2 0.31 17％
23 PCB
153 4.5 0.07 8％
24 PCB
141 1.4 0.16 7％
26 PP′-DDT 1.7 1.11 8％
27 PCB
138 11.4 0.09 6％
28 PCB
185 12.5 0.11 16％
29 PCB
180 32.9 0.09 13％
30 PCB
194 22.7 0.35 12％
The distribution situation (ng/g, dry weight) of table 4 contamination with chlorinated organics in egg
| Determinand | Yolk | Egg white | Shell egg |
| α-HCH | 0.6 | 1.1 | 0.6 |
| β-HCH | 5.97 | 1.23 | 7.28 |
| PCB 28 | 73.0 | 7.46 | 57.0 |
| PCB 52 | 3.2 | 1.1 | 3.3 |
| PCB 74 | 14.9 | 1.9 | 12.3 |
| PCB 70 | 4.4 | 1.0 | 4.3 |
| PCB 56 | 25.3 | 2.9 | 20.3 |
| PCB 101 | 1.1 | 0.5 | 1.6 |
| PCB 99 | 6.4 | 1.4 | 6.8 |
| PCB 87 | 1.3 | 0.5 | 2.0 |
| p，p’-DDE | 12.9 | 2.3 | 12.2 |
| PCB 118 | 6.8 | 0.7 | 7.6 |
| PCB 153 | 2.6 | 0.3 | 2.6 |
| PCB 141 | 0.7 | 0.1 | 1.6 |
| PCB 138 | 10.6 | 1.2 | 8.9 |
The inventive method is compared with traditional soxhlet extraction, guaranteeing under enough accuracy, degree of accuracy and the sensitivity prerequisite, have the advantages that pre-treatment is simple, testing cost is low, the sample consumption is few, and can measure the residual quantity of organo-chlorine pesticide and typical polychlorinated biphenyl simultaneously, be particularly suitable for detecting micro quantity organic pollutant in the food.This method test result shows that when adding ng/g level concentration determinand with the standard dried whole-egg, the recovery of various determinands is 84.31%-116.77% (three mensuration mean value); The coefficient of variation is 6%-18% (seven mensuration mean value); Concentration limit is 0.07-0.35ng/g.In addition, we use this method China's commercially available egg in part city are detected, and organo-chlorine pesticide is with p, and the recall rate of p '-DDE is the highest, reaches 100%, and detecting concentration range is 2.2-696ng/g; Secondly be p, p '-DDT, recall rate is 89.5%, detecting concentration range is n.d.-501.8ng/g.The recall rate of polychlorinated biphenyl is very high, but detected level is very low, and total detected level of polychlorinated biphenyl is lower than 10ng/g in most of samples.In the polychlorinated biphenyl that is detected, the overwhelming majority is the chloride of chloride low (amount of chlorine atom is 2-5).
Claims (3)
1, the assay method of trace organic chlorine pesticide and residual polychlorinated biphenyl amount in the birds, beasts and eggs, comprise and select suitable interior mark to be configured to interior mark annex solution, will be mixed with corresponding calibration curve working fluid in the interior mark annex solution adding determinand standard mixed liquor then as object of reference; Again the testing sample sampling is obtained chromatogram liquid to be measured behind vibration extraction, acid purification, constant volume, carry out chromatographic determination with the gas chromatograph of being furnished with electron capture detector (ECD) at last, it is characterized in that: in the suitable interior mark of above-mentioned selection is configured to as object of reference, in the step of mark annex solution, choose the PCB of polychlorinated biphenyl
2And PCB
209Be interior mark, the concrete steps of this assay method are:
A) take by weighing internal standard compound PCB
2And PCB
209, dissolve mark storing solution in the standard that obtains with heavily steaming benzene respectively, it is an amount of to get the interior mark of above-mentioned standard storing solution respectively, is diluted to mark annex solution in the mixing heavily to steam normal hexane or sherwood oil again;
B) get and contain α-HCH, β-HCH, γ-HCH, δ-HCH, p, p '-DDE, p, p '-DDD, p, the standard blended liquid of p '-DDT, heptachlor, nine kinds of pesticide compositions to be measured of drinox, to mark annex solution in the mixing in normal hexane or the sherwood oil dilution back adding step a), be mixed with the calibration curve working fluid that contains nine kinds of pesticide compositions to be measured, HCH be benzene hexachloride, DDE for drip according to, DDD for dichloro-diphenyl-dichlorothane, DDT is D.D.T. (dichloro-diphenyl-trichloroethane);
C) 15 kinds of PCBs homolog reference materials, PCB
sBe polychlorinated biphenyl, be respectively PCB by the IUPAC name
28, PCB
52, PCB
70, PCB
74, PCB
66, PCB
87, PCB
99, PCB
101, PCB
118, PCB
153, PCB
141, PCB
138, PCB
185, PCB
180, PCB
194Each accurately takes by weighing in right amount, be mixed with the hybrid standard storing solution that contains above-mentioned 15 kinds of polychlorinated biphenyl components heavily to steam the benzene dissolving, get above-mentioned hybrid standard storing solution, add mark annex solution in the mixing in the step a), to be mixed with the calibration curve working fluid that contains 15 kinds of polychlorinated biphenyl components to be measured behind normal hexane or the sherwood oil dilution constant volume;
D) get egg white, yolk mixing, be lower than 60 ℃ and dry, grind to constant weight;
E) get anhydrous sodium sulfate and mix, grind powdering, place in the centrifuge tube and add mark annex solution in the mixing of step a), shake up with the result of step d);
F) add and heavily to steam normal hexane or sherwood oil, in vibrating machine, extract, after placing hydro-extractor centrifugal then extract;
G) add the concentrated sulphuric acid in extract, lower floor's acid solution is shifted out in vibration, centrifugal, abandons it, repeat for several times, and be colourless until lower floor's concentrated sulphuric acid eluate;
H) The above results is placed water-bath, under the protection of nitrogen stream, dry up, heavily to steam normal hexane or petroleum ether dissolution dried extract constant volume, get testing sample solution again;
I) get step b), c respectively) in the calibration curve working fluid and the step h that obtain) in the testing sample solution that obtains, with being equipped with the gas chromatograph of electron capture detector (ECD) to carry out chromatographic determination.
2, the assay method of trace organic chlorine pesticide and residual polychlorinated biphenyl amount in the birds, beasts and eggs according to claim 1 is characterized in that:
In the step a), the concentration of mark storing solution respectively is 2000 μ g/ml in the gained standard, PCB in the mark annex solution in mixing
2And PCB
209Concentration be respectively 10.0 μ g/ml and 0.5 g/ml;
In the step b), the concentration of each pesticide composition to be measured is 2000 μ g/ml, get the standard blended liquid of different volumes, quantitatively add mark annex solution in the mixing in the step a), behind normal hexane or sherwood oil dilution constant volume, be mixed with the calibration curve working fluid that contains nine kinds of pesticide compositions to be measured of a series of variable concentrations; In the above-mentioned calibration curve working fluid, the concentration of pesticide composition to be measured is respectively 0,8.0, and 16.0,32.0,64.0 and 100ng/ml, interior mark PCB
2And PCB
209Concentration be respectively 1000 and 50ng/ml;
In the step c), the PCB in described 15 kinds of polychlorinated biphenyl components
153, PCB
141, PCB
138, PCB
185, PCB
180, PCB
194Concentration be 300 μ g/ml, all the other nine kinds of component concentrations are 400 μ g/ml, get the hybrid standard liquid of containing of different volumes of above-mentioned 15 kinds of polychlorinated biphenyl components, quantitatively add mark annex solution in the mixing in the step a), behind normal hexane or sherwood oil dilution constant volume, be mixed with the calibration curve working fluid that contains 15 kinds of polychlorinated biphenyl components of a series of variable concentrations; In the above-mentioned calibration curve working fluid, polychlorinated biphenyl component concentrations scope is 2.5-400ng/ml, interior mark PCB
2And PCB
209Concentration be respectively 1000 and 50ng/ml;
In the step e), anhydrous sodium sulfate is used after toasting;
In the step f), vibration, centrifugal leaching process are 3 times, merge extract;
Step h) in, bath temperature is 40 ℃;
Step I) in, before beginning chromatographic determination with the gas chromatograph that is equipped with electron capture detector (ECD), measure the calibration curve working fluid earlier, after the chromatogram response of respective components is stablized, begin into the calibration curve working fluid and make calibration curve, carrying out testing sample solution afterwards measures, with peak height inner mark method ration or peak height single-point inner mark method ration, when implementing the single-point inner mark method ration, the calibration curve working fluid of looking sample concentration scope selection suitable concn is quantitative object of reference, and try to achieve correction factor with the mean value of 3-5 chromatogram peak height of this calibration curve working fluid, no matter be calibration curve or single-point sizing technique, in a large amount of sample test processes, all need get calibration curve working fluid sample introduction again, obtain the chromatogram response, calibration curve or correction factor are revised, to guarantee the test result accuracy.
3, the assay method of trace organic chlorine pesticide and residual polychlorinated biphenyl amount in the birds, beasts and eggs according to claim 1 and 2, it is characterized in that chromatogram test job condition is: carrier gas is high purity nitrogen, presses 55.16kPa before the post, and tail blows 60ml/min, sample size 1 μ l, split sampling not, 210 ℃ of the temperature of injection port, 310 ℃ of detector temperatures, 140 ℃ of column temperatures, keep 2min, be warming up to 270 ℃, keep 3min with the speed of 2 ℃/min.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB01127140XA CN1164941C (en) | 2001-08-23 | 2001-08-23 | Determination method of trace organic chlorine pesticide and polychlorobiphenyl residual amount |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB01127140XA CN1164941C (en) | 2001-08-23 | 2001-08-23 | Determination method of trace organic chlorine pesticide and polychlorobiphenyl residual amount |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN1341855A CN1341855A (en) | 2002-03-27 |
| CN1164941C true CN1164941C (en) | 2004-09-01 |
Family
ID=4667129
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB01127140XA Expired - Fee Related CN1164941C (en) | 2001-08-23 | 2001-08-23 | Determination method of trace organic chlorine pesticide and polychlorobiphenyl residual amount |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN1164941C (en) |
Families Citing this family (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101105477B (en) * | 2007-07-24 | 2010-11-10 | 南京大学 | Method for detecting atmosphere granule trace polychlorinated biphenyls by ion trap tandem mass spectrometry |
| CN101126751B (en) * | 2007-09-11 | 2011-05-04 | 南京大学 | Gas phase chromatogram- ion trap tandem mass spectrometry method for detecting organochlorine pesticide |
| CN101462720B (en) * | 2009-01-16 | 2011-06-08 | 国家海洋环境监测中心 | Preparation of modified active carbon glass chromatography column |
| CN101813677B (en) * | 2010-04-29 | 2013-06-05 | 同济大学 | Method for analyzing and determining organics persistently containing chlorine in aquatic product |
| CN102495016B (en) * | 2011-12-12 | 2013-03-27 | 厦门大学 | Method for detecting polychlorinated biphenyl (PCB) pollutants in soil |
| CN105738494A (en) * | 2014-12-11 | 2016-07-06 | 中国科学院大连化学物理研究所 | Isotope dilution high resolution chromaticness combination method for simultaneously detecting organic chlorine pesticides and polychlorinated biphenyl in biological sample, and application |
| CN106018592B (en) * | 2016-05-16 | 2018-08-31 | 江苏中烟工业有限责任公司 | A kind of method of Polychlorinated biphenyls in quantitative analysis dry food wrapping paper |
| CN106546584A (en) * | 2016-11-09 | 2017-03-29 | 百奥森（江苏）食品安全科技有限公司 | The quick detection kit and using method of organochlorine residue in a kind of agricultural product |
| CN106872615B (en) * | 2017-03-06 | 2019-06-04 | 杭州普洛赛斯检测科技有限公司 | Methylation processing vapor detection analysis method |
| CN108459112B (en) * | 2018-05-18 | 2020-12-29 | 中国水产科学研究院淡水渔业研究中心 | Method for detecting content of organochlorine pesticide in crab cream of Eriocheir sinensis |
| CN109270033A (en) * | 2018-09-10 | 2019-01-25 | 南京市产品质量监督检验院 | The rapid detection method of Hazard factor in a kind of food |
| CN109765307B (en) * | 2018-12-24 | 2021-06-29 | 山东省科学院海洋仪器仪表研究所 | Method for measuring hexachlorocyclohexane in water body |
| CN111650325A (en) * | 2020-03-02 | 2020-09-11 | 台州学院 | Method for detecting soil organochlorine pesticide |
-
2001
- 2001-08-23 CN CNB01127140XA patent/CN1164941C/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| CN1341855A (en) | 2002-03-27 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN1164941C (en) | Determination method of trace organic chlorine pesticide and polychlorobiphenyl residual amount | |
| CN100346162C (en) | Method for detecting citrinin content in red koji fermentation product | |
| CN102636603B (en) | Method for detecting organochlorine pesticide residue in soil | |
| CN107817305B (en) | Method for detecting dioxin and dioxin polychlorinated biphenyl in poultry eggs | |
| CN1803242A (en) | Solid phase dispersion microwave extraction method of sample residues matrix and extraction stuffing and solvent | |
| CN104597194B (en) | The high performance liquid chromatography-fluorescence method of 3-chlorine-1,2-propylene glycol | |
| CN101813677B (en) | Method for analyzing and determining organics persistently containing chlorine in aquatic product | |
| CN103995074B (en) | Method for detecting residual quantity of organochlorine pesticides in raw milk | |
| CN105572239A (en) | Method for simultaneously and rapidly determining contents of various organic chlorine pesticides in water | |
| CN211462173U (en) | Solid phase extraction column | |
| CN107167545A (en) | A kind of method of total content of organic carbon in measure water | |
| CN110108809A (en) | A kind of measuring method of essence crudefiber crop drug | |
| CN106770725B (en) | A kind of method of dinocap residual quantity in quick measurement vegetable and fruit | |
| CN1899283A (en) | Quality control method for medicinal composition containing artemisine | |
| CN110749676B (en) | Method for detecting migration quantity of ethylenediamine and hexamethylenediamine in food contact material and product | |
| CN108445128A (en) | A kind of method of carbamates determination of drug residues in birds, beasts and eggs | |
| CN104353441A (en) | Ionic imprinting material for enriching ultratrace methyl mercury in water body | |
| CN1785219A (en) | Quality control method of composite prepn. of dry mango tree leaves extract | |
| Liu et al. | On-site solid phase extraction and HPLC determination of chloramphenicol in surface water and sewage | |
| CN103962114A (en) | Preparation method of conducting polymer coating silica gel and application of conducting polymer coating silica gel to solid phase extraction | |
| CN104991012B (en) | Sample purifying device capable of separating HBCDs and TBBPA simultaneously | |
| CN101051027A (en) | Method for water phase detecting micro mercury in water or waste water by spectrophotometry | |
| CN1595127A (en) | Method for measuring thermodynamic data by utilizing phase balance | |
| CN1947740A (en) | Fingerprint spectrum quality detection method for lamiophlomis rotata medicinal material, intermediate and injection thereof | |
| CN109470780B (en) | Method for determining residues of eight antidepressant drugs in aquatic product |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C06 | Publication | ||
| PB01 | Publication | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| C19 | Lapse of patent right due to non-payment of the annual fee | ||
| CF01 | Termination of patent right due to non-payment of annual fee |