CN112798698B - Oil fingerprint identification method for selecting biomarkers based on difference degree of main components - Google Patents

Oil fingerprint identification method for selecting biomarkers based on difference degree of main components Download PDF

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CN112798698B
CN112798698B CN202011376665.4A CN202011376665A CN112798698B CN 112798698 B CN112798698 B CN 112798698B CN 202011376665 A CN202011376665 A CN 202011376665A CN 112798698 B CN112798698 B CN 112798698B
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张鲁筠
王春艳
黄小东
王岩
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Abstract

The invention provides an oil fingerprint identification method for selecting biomarkers based on principal component difference, which comprises the steps of obtaining the information of a whole set of biomarkers, calculating an original principal component matrix, calculating a new principal component matrix after removing the biomarkers one by one, calculating the difference and selecting important biomarkers. The reliability and the accuracy of the oil fingerprint identification method for classifying and identifying the oil spilling sample by the selected few biomarkers can completely be compared with the results of a whole set of biomarkers, and even better. The oil fingerprint identification method provided by the invention allows a faster elution procedure to be developed, simplifies original complicated chemical explanations which may even cause contradictions, and helps to obtain a more accurate identification result. Meanwhile, the biomarker set selected by the method can be compared with the results of a chemical separation method based on knowledge and experience, and the method provides possibility for searching new useful biomarkers and exploring the chemical and geological significance of the biomarkers.

Description

Oil fingerprint identification method for selecting biomarkers based on difference degree of main components
Technical Field
The invention relates to an oil fingerprint identification method for selecting gas chromatography/mass spectrum biomarkers based on the difference degree of main components, and belongs to the technical field of oil fingerprint identification.
Background
The frequent occurrence of marine oil spill accidents and their serious harm to marine environmental safety and human health will suggest one of the focuses of global environmental issues for marine oil spill research. Due to high oil spill incidence and high risk, the exact source of oil spill is determined, and monitoring of chemical changes in the weathering migration process of crude oil is necessary. Therefore, a set of oil fingerprint identification technology which is fast, economical, simple and easy to popularize is established, and the method has important practical value for the most developed Chinese furniture in the world with increasingly severe environmental pressure in China.
Oil fingerprinting involves a series of analytical and statistical techniques to objectively identify the most likely source of a hydrocarbon leak by matching the hydrocarbons in the oil spill to a set of potential candidate sources. Gas chromatography-mass spectrometry (GC-MS) is recognized as the cornerstone of modern oil spill fingerprints. Gas chromatography-mass spectrometry (GC-MS) is rapidly applied to detection of water, air, soil, ocean and other environments, agricultural supervision, food safety and discovery and production of medical products due to strong and effective separation, separation and identification capabilities of compounds. In recent decades, a great deal of application of GC-MS has been developed in the field of oil spill identification, and on the one hand, the effectiveness of GC-MS is shown. On the other hand, GC-MS related oil spill studies and articles are continually being explored and updated, suggesting that GC-MS has not been able to completely solve the oil spill identification problem, which is consistent with the widely accepted view that no single approach is available to solve this problem due to the complex nature of crude oil and the low concentration of biomarkers.
Some of the bottlenecks in gas chromatography-mass spectrometry are responsible for this problem, one of the major bottlenecks is that almost all oil fingerprinting studies use a full set of biomarkers measured in chromatography, typically including terpenes, regular and rearranged stanols, monoaromatics and triarylsteroids, bicyclic sesquiterpenes and adamantanes, etc. The detection and analysis of such large amounts of compounds requires highly skilled personnel and careful examination and is therefore quite time consuming and costly. Meanwhile, fuzzy and even contradictory behaviors may exist among the variables, so that the interpretation of the result is complex and the decision is difficult to make. Researchers have come to appreciate that the chromatographic ratios or abundances of certain biomarkers may be more informative than others, and that certain variables, if stored in an identification dataset, may even lead to incorrect recognition results. Therefore, proper variable selection is critical to minimize uncertainty and produce reliable results.
Currently, most of the research for sorting biomarkers is based on the knowledge and experience of researchers on petroleum analysis, and a chemical separation method is directly adopted to extract and analyze a specific biomarker set. However, this method is generally only effective for one or a few types of oil samples and is likely to fail for new oil samples. In addition, this method may also produce some subjective bias.
Disclosure of Invention
Aiming at the defects in the prior art, the invention provides an oil fingerprint identification method for selecting biomarkers based on the difference degree of main components, wherein a group of simplified biomarker parameters are found in a GC-MS complete set of biomarker parameters by a chemometrics and data analysis method, and are used for representing main information in the whole data set, so that the classification identification capability almost identical to that of the complete set of biomarker parameters is generated under the condition of not losing important information.
In order to solve the technical problem, the invention adopts the following technical scheme:
an oil fingerprint identification method for selecting biomarkers based on principal component difference degree comprises the steps of obtaining complete set of biomarker information, calculating an original principal component matrix, calculating a new principal component matrix after removing the biomarkers one by one, calculating the difference degree and selecting important biomarkers.
The following is a further improvement of the above technical solution:
step 1: and (3) obtaining the detection distribution results of the whole set of biomarkers (m) of the petroleum oil spill sample through GC-MS analysis.
Step 2: forming a matrix X by using the detection values of the whole set of biomarkers of all samples (n samples) as observation values m×n PCA analysis is carried out on the principal component matrix PC, and the first p principal components (representing the most important main information) with the cumulative contribution rate of more than 95 percent are selected according to the principal component contribution rate, so that the principal component matrix PC is obtained p×n
And step 3: removing the biomarkers one by one from the first biomarker to obtain a new matrix
Figure BDA0002807302810000021
(k denotes the number of removed biomarkers, ranging from 1 to m), and the PCA analysis is repeated to obtain a new principal component matrix
Figure BDA0002807302810000022
And 4, step 4: calculate new
Figure BDA0002807302810000023
With the original PC p×n Difference between them k
And 5: all Difference k (k is from 1 to m)And (4) comparing, selecting the first p biomarkers with the maximum difference degree, namely the biomarkers which are the most important and most information quantity to be selected and used as the basis for oil fingerprint identification.
The Principal Component Analysis (PCA) method can realize data dimension reduction and classification identification based on principal components by extracting the principal components of the original variables. PCA uses orthogonal transformation to transform a set of observations of possibly relevant variables (in the present invention, the original full set of biomarker parameters) into a set of linearly uncorrelated variable values called principal components. This transformation is defined in such a way that the first principal component has the largest variance and the variance of each subsequent principal component decreases in turn, while being orthogonal to the preceding principal component. The first few principal components with larger variance (larger contribution rate) represent the main information of the original variable. Can be expressed by a formula: PC (personal computer) p×n =Loading p×m X m×n Wherein n represents the number of samples, m represents the number of observed values of each sample, and X is a matrix formed by all the observed values of the samples; p represents the number of principal components, PC is a principal component matrix, and each sample reserves p principal components; the Loading is a weighting coefficient matrix, and the Loading is i,j The weighting factor for the jth observed value in the sample to the ith principal component is also equivalent to the weight of the jth observed value in the ith principal component.
As can be seen from the formula, each observation contributes to the principal component result, but the contribution is small or large. If one observation value (one biomarker) is removed from all observation values (the whole set of biomarkers) and the principal component calculation is carried out again, the obtained new principal component result can be marked as the new principal component result
Figure BDA0002807302810000031
The contribution of this observation is not necessarily included anymore. At this time, it is possible to calculate
Figure BDA0002807302810000032
And the original PC p×n The degree of difference between them to determine whether the contribution of the observation value to the principal component is important. Is obvious, e.g.The difference degree of the fruits is small, which indicates that the observation value has little effect on the main component and can be discarded; otherwise, the information of the observed value plays an important role and must be preserved. Thus, the observation values can be removed one by adopting a cross-check method, all the differences are compared, and the first p observation values (the number of the selected observation values is the same as that of the main component) with the largest difference are the most important biomarkers to be selected. The difference calculation method adopts a classical mean square error form, and the specific formula is as follows:
Figure BDA0002807302810000034
compared with the prior art, the invention has the following technical effects:
according to the oil fingerprint identification method, the reliability and the accuracy of classifying and identifying the oil spilling sample by the selected few biomarkers are high. Experiments on the examples show that the results of biomarker selection, whether PCA spatial (three-dimensional and two-dimensional) clustering or hierarchical clustering, can completely match the results of a full set of biomarkers, even better. When the selected biomarkers are used as classification bases and artificial neural network oil sample classification is carried out through GRNN, the correct recognition rate is higher than that when the original complete set of biomarkers is used.
The oil fingerprinting method according to the invention, which allows a significant reduction in the number of key variables (biomarkers) used to identify the sample, will allow the development of faster elution procedures, since only some compounds have to be carefully analyzed, with a corresponding reduction in the pre-treatment time; the simplified key variables also simplify the original complicated and possibly contradictory chemical explanations, and help to obtain a more accurate identification result.
Meanwhile, the method for selecting the biomarker set based on data analysis is a completely objective analysis method which is separated from subjective experience.
The biomarker set selected by the method can be compared with the results of a chemical separation method based on knowledge and experience, so that the method provides possibility for searching new useful biomarkers and exploring the chemical and geological significance of the biomarkers, and provides new ideas and prospects for petrochemical and geological analysis.
Drawings
FIG. 1 is a graph of GC-MS detection of 61 biomarkers from oil-like LD 1;
FIG. 2 is a graph of GC-MS detection of 61 biomarkers from oil-like LD 2;
FIG. 3 is a graph of GC-MS detection of 61 biomarkers from oil-like LD 3;
FIG. 4 is a graph of GC-MS detection of 61 biomarkers from an oil sample BZ 1;
FIG. 5 is a graph of GC-MS detection of 61 biomarkers from an oil sample BZ 2;
FIG. 6 is a graph of GC-MS detection of 61 biomarkers of oil-like NH;
FIG. 7 is a graph of GC-MS detection of 61 biomarkers from oil-like WC;
FIG. 8 is a graph of GC-MS detection of 61 biomarkers from oil-like NB;
FIG. 9 is a graph of GC-MS detection of 61 biomarkers for oil-like CB;
FIG. 10 is a graph showing the GC-MS detection of 61 biomarkers for SZ of oil sample;
FIG. 11 is a graph of the principle component differential scores of 61 biomarkers;
FIG. 12 is a graph comparing the distribution of selected biomarkers (5) in oil sample LD 1;
FIG. 13 is a graph comparing the distribution of selected biomarkers (5) in an oil sample LD 2;
FIG. 14 is a graph comparing the distribution of selected biomarkers (5) in an oil sample LD 3;
FIG. 15 is a graph comparing the distribution of selected biomarkers (5) in the oil sample BZ 1;
FIG. 16 is a graph comparing the distribution of selected biomarkers (5) in the oil sample BZ 2;
FIG. 17 is a graph comparing the distribution of selected biomarkers (5) in oil-like NH;
FIG. 18 is a graph comparing the distribution of selected biomarkers (5) in oil-like WC;
FIG. 19 is a comparison of the distribution of selected biomarkers (5) in the oil sample NB;
FIG. 20 is a graph comparing the distribution of selected biomarkers (5) in oil sample CB;
FIG. 21 is a graph comparing the distribution of selected biomarkers (5) in the oil sample SZ;
FIG. 22 is a three-dimensional PCA spatial clustering distribution plot of PC1-PC2-PC3 based on a full set of biomarkers;
FIG. 23 is a three-dimensional PCA spatial clustering distribution plot of PC1-PC2-PC3 based on selected biomarkers;
FIG. 24 is a two-dimensional PCA spatial clustering distribution plot of PC1-PC2 based on a full set of biomarkers;
FIG. 25 is a two-dimensional PCA spatial clustering distribution plot of PC1-PC2 based on selected biomarkers;
FIG. 26 is a hierarchical clustering tree diagram based on a full set of biomarkers;
FIG. 27 is a hierarchical clustering tree based on selected biomarkers;
FIG. 28 is a graph of GRNN classification recognition results based on a full set of biomarkers;
fig. 29 is a graph of GRNN classification recognition results based on selected biomarkers.
Detailed Description
Example (b):
1. petroleum samples and treatments
The sample selects ten crude oil samples of four types (A type) belonging to the Luda LD-A11# (LD1), LD-A16# (LD2), LD-A12# (LD3), (B type) belonging to the BZ26-2(BZ1), BZ28-1(BZ2), (C type) belonging to the south sea oil (NH) and Wenchang oil (WC) of the Bohai oil field, and (D type) belonging to the A12# (NB) and North Welsh oil (CB) of the NB-CEP platform, and 36-1# (SZ) of the Welsh Sulski oil field to carry out GC-MS test.
Sample treatment for GC-MS: a crude oil sample of 800mg was taken and dissolved in 10mL of n-hexane to prepare a crude oil stock solution of 80 mg/mL. 200. mu.L of the eluate was put on a 10mm column packed with 3g of activated silica gel (1.0 cm of anhydrous sodium sulfate placed on the top), and the saturated hydrocarbon fraction F1 was eluted with 12mL of n-hexane, and the eluate F1 was concentrated to about 0.9mL on a nitrogen blower.Add 100. mu.L of internal standard (containing d) 18 -Decahydronaphthalene,d 16 -Adamantane,C 30 17 β (H),21 β (H) -hopane) to yield 1.0mL of concentrate for GC-MS analysis.
2. GC-MS experiment
GC-MS measurements were performed using an Agilent HP 6890 instrument (Agilent Technologies, Palo Alto, Calif., USA) with a pulsed splitless sample injector, HP 5973 mass spectrometer and HP-5MS fused silica capillary column (J & W Scientific, Folsom, Calif., USA). The operating conditions were: the initial temperature is 50 ℃, the temperature is kept isothermal for 2 minutes, the temperature is increased to 300 ℃ at the speed of 6 ℃/min, and the temperature is kept isothermal for 16 minutes. Carrier gas: helium gas; the injection was carried out in a pulsed no-split mode with a sample injection rate of 1.0mL/min and sample inlet and detector temperatures of 290 and 300 ℃ respectively. Ionization voltage: 70eV, and the ion source temperature 230 ℃. The m/z range of MS analysis is 40-400.
3. Selecting the GC-MS biomarkers according to the specific scheme of the invention:
step 1: for 10 petroleum oil spill samples, detection values of a full set of 61 biomarkers are obtained through GC-MS detection and analysis, and the biomarkers are common biomarkers measured in oil fingerprint chromatography and comprise p-menthane, regular and rearranged stane, monoaryl and triaryl steroid, bicyclic sesquiterpene, adamantane and the like. The detection distribution diagram is shown in the attached figures 1-10, and the detailed information of 61 biomarkers is shown in the table 1.
TABLE 1 61 biomarkers for GC-MS detection
Figure BDA0002807302810000061
Figure BDA0002807302810000071
Figure BDA0002807302810000081
Step 2: examining the full set of biomarkers from all samplesMeasured values as observed values forming a matrix X 61×10 PCA analysis is carried out on the mixture, and the first 5 principal components are selected according to the requirement that the accumulated contribution rate reaches 98 percent, so that a principal component matrix PC is obtained 5×10
And step 3: starting from the first biomarker, the biomarkers are removed one by one to obtain a new matrix
Figure BDA0002807302810000082
(k denotes the number of removed biomarkers, ranging from 1 to 61), and the PCA analysis is repeated to obtain a new principal component matrix
Figure BDA0002807302810000083
And 4, step 4: calculate new
Figure BDA0002807302810000084
With the original PC 5×10 Difference between them k See fig. 11.
And 5: all differences are described k And (k is from 1 to 61), comparing, and selecting the first 5 biomarkers with the largest difference as the biomarkers with the most important and most information quantity to be selected and as the basis for the next oil fingerprint identification.
4. Analyzing and verifying the Classification-recognition Capacity of selected biomarkers
FIG. 11 shows principal component Difference k The distribution of C can be seen by comparison 29 (k=6),C 30 (k-7), G (k-20), SQT3 (k-54), and SQT4 (k-55) gave a large degree of difference and were therefore selected as a simplified biomarker combination.
FIGS. 12-21 show the profiles of these five selected biomarkers in 10 samples. It can be seen that with only these 5 biomarker parameters, already significant differences between the petroleum samples of different classifications have been shown, and are therefore fully feasible as a basis for classification identification.
To further verify the biomarker selection on oil spillReliability and accuracy of classification and identification of samples are respectively determined by PCA (principal component analysis) space clustering (front three-dimensional principal component matrix PC) 3×10 Spatial clustering, first two-dimensional principal component matrix PC 2×10 Spatial clustering), hierarchical clustering, and Generalized Regression Neural Network (GRNN) to verify the classification of the original set of biomarkers and the selected biomarkers, as shown in fig. 22-29.
Whether PCA space (three-dimensional and two-dimensional) clustering or hierarchical clustering, the result of selecting the biomarkers can be completely similar to the result of the whole set of biomarkers, and even better.
When the selected biomarkers are used as classification bases, the correct recognition rate can reach 100% when the artificial neural network oil sample classification is carried out through GRNN, the correct recognition rate can only reach 90% by adopting the whole set of biomarkers, and the BZ1 sample is wrongly recognized as the LD sample. This indicates that fuzzy and even error-causing information exists in the whole set of original biomarkers, and rather, the information is more definite than the selected biomarkers. These verification experiments all prove that the biomarkers selected by the method of the invention are used as classification bases, and have good reliability and accuracy. According to the method provided by the invention, a faster elution procedure can be completely developed, the tedious and possibly contradictory chemical explanation is simplified, and a more efficient and more accurate oil fingerprint identification result is obtained.

Claims (1)

1. An oil fingerprint identification method for selecting biomarkers based on principal component difference degree is characterized in that: the method comprises the steps of obtaining the information of a whole set of biomarkers, calculating an original principal component matrix, calculating a new principal component matrix after removing the biomarkers one by one, calculating the difference degree, and selecting important biomarkers;
calculating an original principal component matrix, and forming a matrix by using the detection values of m complete sets of biomarkers of n samples as observation values
Figure DEST_PATH_IMAGE001
Carrying out PCA analysis on the mixture, calculating the contribution rate of the principal component, and selecting the cumulative contribution rate to 9More than 5% of the total weight of the powder
Figure 749244DEST_PATH_IMAGE002
A principal component to obtain an original principal component matrix
Figure DEST_PATH_IMAGE003
Calculating a new principal component matrix, and removing the biomarkers one by one from the first biomarker to obtain a new matrix
Figure 634024DEST_PATH_IMAGE004
And PCA analysis is performed again to obtain a new principal component matrix
Figure DEST_PATH_IMAGE005
The calculated difference degree is calculated
Figure 714106DEST_PATH_IMAGE005
And the original
Figure 240902DEST_PATH_IMAGE003
Degree of difference therebetween
Figure 113043DEST_PATH_IMAGE006
The important biomarkers are selected, and all the biomarkers are
Figure 949150DEST_PATH_IMAGE006
Comparing, and selecting the front part with the maximum difference
Figure 172321DEST_PATH_IMAGE002
The biological markers are selected important biological markers;
k is from 1 to
Figure DEST_PATH_IMAGE007
The biomarker number of (a);
obtaining the detection distribution result of the whole set of biomarkers of the petroleum oil spill sample through GC-MS analysis;
before the GC-MS analysis, a petroleum oil spill sample needs to be subjected to sample treatment;
the sample treatment method comprises the following steps: taking a 800mg crude oil sample, dissolving the crude oil sample in 10mL normal hexane, and preparing a crude oil stock solution of 80 mg/mL; adding 200 mu L of crude oil stock solution into a 10mm chromatographic column filled with 3g of activated silica gel, washing out a saturated hydrocarbon component F1 by using 12mL of n-hexane, concentrating the F1 eluate to 0.9mL on a nitrogen blowing instrument, and adding 100 mu L of internal standard to obtain 1.0mL of concentrated solution for GC-MS analysis;
1.0cm of anhydrous sodium sulfate is placed at the top of the chromatographic column;
d is contained in the internal standard 18 -Decahydronaphthalene, d 16 -Adamantane, C 30 17β(H),21β(H)-hopane;
The GC-MS analysis adopts an HP-5MS fused quartz capillary column as a chromatographic column;
the operating conditions for the GC-MS analysis were: the initial temperature is 50 ℃, the isothermal holding is carried out for 2 minutes, the temperature is increased to 300 ℃ at the speed of 6 ℃/min, and the isothermal holding is carried out for 16 minutes; the carrier gas is helium; detecting in a pulse non-shunting mode, wherein the sample introduction speed is 1.0mL/min, and the temperatures of a sample introduction port and a detector are 290 ℃ and 300 ℃ respectively; the ionization voltage is 70eV, and the ion source temperature is 230 ℃; the m/z range of MS analysis is 40-400.
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