| Literature DB >> 28243268 |
Slobodan B Gadžurić1, Sanja O Podunavac Kuzmanović2, Milan B Vraneš1, Marija Petrin3, Tatjana Bugarski4, Strahinja Z Kovačević2.
Abstract
The purpose of this work is to promote and facilitate forensic profiling and chemical analysis of illicit drug samples in order to determine their origin, methods of production and transfer through the country. The article is based on the gas chromatography analysis of heroin samples seized from three different locations in Serbia. Chemometric approach with appropriate statistical tools (multiple-linear regression (MLR), hierarchical cluster analysis (HCA) and Wald-Wolfowitz run (WWR) test) were applied on chromatographic data of heroin samples in order to correlate and examine the geographic origin of seized heroin samples. The best MLR models were further validated by leave-one-out technique as well as by the calculation of basic statistical parameters for the established models. To confirm the predictive power of the models, external set of heroin samples was used. High agreement between experimental and predicted values of acetyl thebaol and diacetyl morphine peak ratio, obtained in the validation procedure, indicated the good quality of derived MLR models. WWR test showed which examined heroin samples come from the same population, and HCA was applied in order to overview the similarities among the studied heroine samples.Entities:
Keywords: Forensic profiling; Heroin; Illicit drug; Multiple linear regression; Wald-Wolfowitz runs test
Year: 2016 PMID: 28243268 PMCID: PMC5316250
Source DB: PubMed Journal: Iran J Pharm Res ISSN: 1726-6882 Impact factor: 1.696
Peak ratio of TEB/DAM, MAM/DAM, PAP/DAM and NOS/DAM for all investigated heroin samples
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| 1 | 0.1269 | 0.0062 | 0.0424 | 0.1157 | 0.0367 | 0.1433 | 0.0479 | 0.0902 | 0.0267 | 0.1233 | 0.0379 | 0.0802 |
| 2 | 0.1562 | 0.0068 | 0.0568 | 0.1283 | 0.0411 | 0.1488 | 0.0481 | 0.1462 | 0.0311 | 0.1388 | 0.0381 | 0.1362 |
| 3 | 0.1269 | 0.0062 | 0.0424 | 0.1157 | 0.0141 | 0.1104 | 0.0246 | 0.1368 | 0.0241 | 0.1204 | 0.0346 | 0.1468 |
| 4 | 0.1562 | 0.0068 | 0.0568 | 0.1283 | 2.5076 | 6.7521 | 0.4682 | 0.0076 | 2.5276 | 6.7721 | 0.4482 | 0.0276 |
| 5 | 0.1873 | 0.0073 | 0.0492 | 0.1909 | 2.7672 | 7.1083 | 0.4746 | 0.0374 | 2.7672 | 7.1083 | 0.4746 | 0.0374 |
| 6 | 0.1524 | 0.0062 | 0.0441 | 0.1790 | 0.0135 | 0.0657 | 0.0219 | 0.0524 | 0.0135 | 0.0657 | 0.0219 | 0.0524 |
| 7 | 0.1590 | 0.0062 | 0.0452 | 0.1828 | 0.0147 | 0.2456 | 0.0327 | 0.0049 | 0.0147 | 0.2456 | 0.0327 | 0.0049 |
| 8 | 0.1566 | 0.0059 | 0.0439 | 0.1764 | 0.1103 | 0.1463 | 0.4271 | 0.1045 | 0.0103 | 0.0463 | 0.3271 | 0.0045 |
| 9 | 0.3945 | 0.0276 | 0.0474 | 0.1248 | 0.2208 | 0.2293 | 0.2335 | 0.3083 | 0.0208 | 0.0930 | 0.0335 | 0.1083 |
| 10 | 0.3652 | 0.0284 | 0.0452 | 0.1192 | 0.0248 | 0.0965 | 0.0393 | 0.1099 | 0.0208 | 0.0925 | 0.0363 | 0.1055 |
| 11 | 0.3525 | 0.0284 | 0.0455 | 0.1416 | 0.0209 | 0.1307 | 0.0303 | 0.1001 | 0.0229 | 0.1337 | 0.0363 | 0.1021 |
| 12 | 0.3577 | 0.0242 | 0.0393 | 0.1211 | 0.1143 | 0.2137 | 0.1232 | 0.1052 | 0.0143 | 0.1137 | 0.0232 | 0.0049 |
| 13 | 0.3519 | 0.0287 | 0.0465 | 0.1407 | 0.2096 | 0.2589 | 0.2229 | 0.2029 | 0.0096 | 0.0888 | 0.0229 | 0.0029 |
| 14 | 0.3449 | 0.0287 | 0.0459 | 0.1442 | 0.3101 | 0.4474 | 0.3364 | 0.4564 | 0.0101 | 0.1474 | 0.0364 | 0.1564 |
| 15 | 0.4303 | 0.0284 | 0.0485 | 0.1288 | 0.0100 | 0.0732 | 0.0279 | 0.1036 | 0.0100 | 0.0732 | 0.0279 | 0.1036 |
| 16 | 0.3261 | 0.0253 | 0.0391 | 0.1136 | 0.0243 | 0.1208 | 0.0342 | 0.1472 | 0.0243 | 0.1208 | 0.0342 | 0.1472 |
| 17 | 0.3360 | 0.0288 | 0.4460 | 0.1353 | 2.5288 | 6.7730 | 0.4499 | 0.0279 | 2.5279 | 6.7730 | 0.4489 | 0.0279 |
| 18 | 0.3378 | 0.0288 | 0.0449 | 0.1345 | 0.1140 | 0.1135 | 0.0239 | 0.1045 | 0.0140 | 0.1134 | 0.0229 | 0.0045 |
| 19 | 0.3737 | 0.0272 | 0.0454 | 0.1110 | 0.0094 | 0.0883 | 0.0225 | 0.0023 | 0.0094 | 0.0883 | 0.0225 | 0.0023 |
| 20 | 0.3432 | 0.0251 | 0.0393 | 0.1196 | 0.2150 | 0.2460 | 0.2330 | 0.0052 | 0.0150 | 0.2460 | 0.0330 | 0.0052 |
| 21 | 0.3350 | 0.0290 | 0.0459 | 0.1363 | 0.1110 | 0.0487 | 0.3276 | 0.1049 | 0.0110 | 0.0467 | 0.3276 | 0.0049 |
| 22 | 0.3149 | 0.0284 | 0.0449 | 0.1392 | 0.2470 | 0.1297 | 0.2583 | 0.0817 | 0.0270 | 0.1237 | 0.0383 | 0.0807 |
| 23 | 0.3065 | 0.0277 | 0.0445 | 0.1384 | 0.1315 | 0.1392 | 0.0386 | 0.1364 | 0.0315 | 0.1392 | 0.0386 | 0.1364 |
| 24 | 0.3261 | 0.0283 | 0.0449 | 0.1385 | 0.0292 | 0.0920 | 0.0360 | 0.1050 | 0.0202 | 0.0920 | 0.0360 | 0.1050 |
| 25 | 0.2551 | 0.0277 | 0.0453 | 0.1384 | 0.4220 | 0.1330 | 0.0360 | 0.1017 | 0.0220 | 0.1330 | 0.0360 | 0.1017 |
| 26 | 0.2719 | 0.0286 | 0.0460 | 0.1411 | 2.7975 | 7.1087 | 0.4749 | 0.0378 | 2.7675 | 7.1087 | 0.4749 | 0.0378 |
| 27 | 0.3806 | 0.0290 | 0.0478 | 0.1192 | 0.1414 | 0.0660 | 0.0224 | 0.0528 | 0.0139 | 0.0660 | 0.0224 | 0.0528 |
| 28 | 0.3496 | 0.0280 | 0.0447 | 0.1435 | 0.0299 | 0.0901 | 0.0330 | 0.1080 | 0.0200 | 0.0900 | 0.0330 | 0.1080 |
| 29 | 0.3812 | 0.0288 | 0.0463 | 0.1374 | 0.0909 | 0.0557 | 0.0215 | 0.0424 | 0.0015 | 0.0857 | 0.0319 | 0.0528 |
| 30 | 0.4047 | 0.0386 | 0.0470 | 0.1401 | 0.0296 | 0.0810 | 0.0330 | 0.1100 | 0.0772 | 0.2876 | 0.0427 | 0.0104 |
| 31 | 0.3305 | 0.0284 | 0.0488 | 0.1162 | 0.0417 | 0.1492 | 0.0376 | 0.1264 | 0.0182 | 0.0482 | 0.3071 | 0.0145 |
| 32 | 0.3621 | 0.0279 | 0.0458 | 0.1415 | 0.1003 | 0.1004 | 0.0255 | 0.1377 | 0.0072 | 0.1237 | 0.0245 | 0.0070 |
| 33 | 0.3685 | 0.0267 | 0.0466 | 0.1417 | 0.0792 | 0.1138 | 0.0342 | 0.1462 | 0.0013 | 0.0878 | 0.0329 | 0.0429 |
| 34 | 0.2921 | 0.0254 | 0.0455 | 0.1432 | 0.0713 | 0.1317 | 0.0313 | 0.1021 | 0.0368 | 0.1574 | 0.0264 | 0.1364 |
| 35 | 0.3289 | 0.0284 | 0.0465 | 0.1299 | 0.0690 | 0.1235 | 0.0339 | 0.1065 | 0.0196 | 0.1247 | 0.0483 | 0.0707 |
| 36 | 0.3063 | 0.0263 | 0.0401 | 0.1176 | 0.0710 | 0.0760 | 0.0324 | 0.0528 | 0.0288 | 0.1192 | 0.0346 | 0.1324 |
| 37 | 0.3557 | 0.0277 | 0.4360 | 0.1383 | 0.0591 | 0.0865 | 0.0393 | 0.1189 | 0.0050 | 0.0920 | 0.0440 | 0.1050 |
| 38 | 0.3666 | 0.0282 | 0.0454 | 0.1251 | 0.0768 | 0.1340 | 0.0360 | 0.1019 | 0.0109 | 0.0825 | 0.0353 | 0.1057 |
Best MLR models for the prediction of heroin geographical origin
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| NOS/DAM | 0.1449 | ||||||
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| TEB/DAM | Intercept | 0.1274 | 28 | 0.9270 | 0.0334 | 48.8618 |
| MAM/DAM | 8.6544 | ||||||
| PAP/DAM | -0.0353 | ||||||
| NOS/DAM | -0.1806 | ||||||
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| TEB/DAM | Intercept | 0.0073 | 28 | 0.9919 | 0.0922 | 873.29 |
| MAM/DAM | 0.3627 | ||||||
| PAP/DAM | 0.2680 | ||||||
| NOS/DAM | 0.1453 | ||||||
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| TEB/DAM | Intercept | -0.0419 | 28 | 0.9996 | 0.0273 | 106.23 |
| MAM/DAM | 0.3798 | ||||||
| PAP/DAM | 0.1073 | ||||||
The cross-validation parameters
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| (3) | 0.0288 | 23.7616 | 0.0012 | 0.0321 | 0.9988 | 0.9992 |
| (1) | 0.0794 | 0.2380 | 0.3336 | 0.0532 | 0.6664 | 0.8417 |
| (2) | 0.2601 | 22.4969 | 0.0116 | 0.0964 | 0.9884 | 0.9898 |
Predicted TEB/DAM peak ratio of test set with the residual values
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| 10 | 0.3472 | 0.0664 | 0.0085 | 0.0194 | 0.0104 | 0.0024 |
| 1 | 0.3502 | 0.0799 | 0.0017 | 0.0310 | 0.0110 | -0.0002 |
| 2 | 0.4345 | 0.0394 | 0.0734 | -0.0298 | -0.0098 | 0.0038 |
| 3 | 0.3505 | 0.0615 | 0.0114 | -0.0199 | -0.0198 | 0.0068 |
| 4 | 0.3417 | 0.0898 | 0.0087 | 0.0205 | 0.0105 | -0.0015 |
| 5 | 0.3312 | 0.0705 | 0.0012 | 0.0373 | 0.0087 | 0.0001 |
| 6 | 0.3198 | 0.0789 | 0.0404 | -0.0276 | -0.0076 | -0.0036 |
| 7 | 0.3481 | 0.0782 | 0.0208 | -0.0192 | -0.0092 | -0.0012 |
| 8 | 0.3324 | 0.0766 | 0.0262 | -0.0260 | -0.0056 | 0.0026 |
| 9 | 0.3268 | 0.0512 | 0.0129 | 0.0290 | 0.0079 | -0.0079 |
Figure 1a, b, c) Plots of predicted versus experimentally observed TEB/DAM ratio
Figure 2a, b, c) Plots of the residual values against the experimentally observed TEB/DAM ratio
Figure 3Dendrogram of HCA as a result of classification of analyzed heroin samples
The results of Wald-Wolfowitz run test for comparison of heroin samples taking into account TEB/DAM, MAM/DAM, PAP/DAM and NOS/DAM ratios together
| rcr = 135.94 |
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| - | H0 rejected (r = 65) | H0 rejected (r = 67) |
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| H0 rejected (r = 65) | - | H0 accepted (r = 149) |
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| H0 rejected (r = 67) | H0 accepted (r = 149) | - |
The results of Wald-Wolfowitz run test for comparison of heroin samples taking into account TEB/DAM, MAM/DAM, PAP/DAM and NOS/DAM ratios separately
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| rcr = 30.51 | ||
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| - | H0 rejected (r = 11) | H0 rejected (r = 3) |
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| H0 rejected (r = 11) | - | H0 rejected (r = 28) |
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| H0 rejected (r = 3) | H0 rejected (r = 28) | - |
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| rcr = 30.51 | ||
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| - | H0 rejected (r = 2) | H0 rejected (r = 2) |
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| H0 rejected (r = 2) | - | H0 accepted (r = 48) |
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| H0 accepted (r = 48) | H0 rejected (r = 2) | - |
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| rcr = 30.51 | ||
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| - | H0 rejected (r = 9) | H0 rejected (r = 11) |
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| H0 rejected (r = 9) | - | H0 accepted (r = 40) |
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| H0 rejected (r = 11) | H0 accepted (r = 40) | - |
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| rcr = 30.51 | ||
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| - | H0 rejected (r = 13) | H0 rejected (r = 10) |
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| H0 rejected (r = 13) | - | H0 accepted (r = 41) |
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| H0 rejected (r = 10) | H0 accepted(r = 41) | - |