ISPUB.com / IJFS/2/1/6781
  • Author/Editor Login
  • Registration
  • Facebook
  • Google Plus

ISPUB.com

Internet
Scientific
Publications

  • Home
  • Journals
  • Latest Articles
  • Disclaimers
  • Article Submissions
  • Contact
  • Help
  • The Internet Journal of Forensic Science
  • Volume 2
  • Number 1

Original Article

Forensic Detection Of Fire Accelerants Using A New Solid Phase Microextraction (SPME) Fiber

U Ahmad, G Selvaraju

Keywords

accelerants, arson, fire debris, hs-spme, lab-made c8-coated fiber, n-alkane hydrocarbons

Citation

U Ahmad, G Selvaraju. Forensic Detection Of Fire Accelerants Using A New Solid Phase Microextraction (SPME) Fiber. The Internet Journal of Forensic Science. 2006 Volume 2 Number 1.

Abstract

An important aspect of an investigation of a suspected arson case involves the chemical analysis of the debris remaining after the fire. Currently, accelerant extraction and analytical techniques have been refined to improve sample turnover and to reduce the number of inconclusive findings. For this purpose, solid-phase micro extraction (SPME) have been introduced. SPME relies upon the concentration of headspace vapors onto an adsorbent medium. A new lab-made fiber prepared by sol-gel method, containing 1:1 molar ratio of octyltriethoxysilane (C8-TEOS): methyltrimethoxysilane (MTMOS) was employed in this technique. The fiber was evaluated for the analysis of n-alkane standard hydrocarbon compounds and common petroleum based accelerants. Compared with commercial PDMS/DVB fibre, the new lab-made fibre exhibited higher extraction capability for n-alkane hydrocarbon compounds and accelerants, higher thermal stability (up to 300 °C) and longer lifetime (~ 200 times usage). Electron microscopy experiments revealed that the surface of the fiber coating was well-distributed and a porous structure was suggested for the sol-gel derived C8 coating with an approximate thickness of (3-4) µm. The developed HS-SPME method using C8-coated fiber showed satisfactory reproducibility (RSD < 6 %), detection limits for accelerants (0.7-1.0 µL) and linearity ((r > 0.9869) under the optimum experimental conditions.

 

1. Introduction

The forensic discipline of ignitable liquid and fire debris analysis is rapidly changing. Modifications to traditional ignitable liquid extraction methods and research into new applications of existing extraction techniques continue to improve the quality of arson analysis. The earliest methods of identification relied upon simple identification of the headspace odor-often referred to as a “nasal appraisal”. With improvements in analytical instrumentation, vapor samples were taken and subjected to instrumental analysis, usually gas chromatography. A significant improvement came with the application of steam distillation to fire debris analysis and this was followed by passive and dynamic headspace method [1, 2].

In addition to optimizing existing extraction techniques, the field of forensic science has also introduced a new extraction technique for application to arson analysis: solid-phase microextraction (SPME). The major advantage of this technique is that it uses no solvents and can be used for either direct sampling or sample clean-up. It is fairly economical and is a relatively simple and sensitive technique. The extraction is based on the enrichment of components on a polymer or adsorbent coated fused silica fiber [3,4,5,6].

SPME is predominantly performed on commercial SPME fibers; however the extent of selectivity obtainable using conventional fibers is limited. Generally accepted drawbacks of conventional adsorbents are a relatively low thermal stability (200-270) ° C which leads to incomplete sample desorption and sample carry-over problem, short lifetime (40-100) times, poor solvent stability and expensive [7,8,9,10,11,12,13,14,15,16,17,18,19,20,21,22,23,24,25].

Recently, many novel coatings have been developed using different techniques and technology for use in SPME. Compared with commercially available SPME adsorbents, the new materials exhibited higher thermal stability (350 ° C), solvent stability, extraction capability and longer lifetime [7,8,9,10,11,12,13,14,15,16,17,18,19,20,21,22,23,24,25]. However, up to now, none of the novel fibers have been evaluated for the determination of accelerants in arson analysis. This paper presents a recent development in the forensic aspects of fire investigation. As a preliminary study, a new SPME adsorbent comprising of sol-gel derived C8-coating was developed and evaluated for the determination of accelerants in arson samples, with the aim of improving the quality of ignitable liquid residue analysis.

2. Experimental

2.1. Chemicals and Materials

Individual standards of n-alkanes (C8, C10, C12, C14 and C16) were purchased from Fluka Chemika. Samples of diesel and unleaded gasoline were purchased from a petrol station in Skudai, Johor while kerosene was obtained from a grocery shop at Taman Universiti, Skudai, Johor. Samples of carpet were purchased from a carpet retail shop in Taman Ungku Tun Aminah, Skudai, Johor, Malaysia.

2.2. Apparatus

Two glass apparatus (400 cm 3 and 125 cm 3 ) for sample preparation step of HS-SPME was specially designed [26]. A Supelco SPME holder, commercially available PDMS/DVB fiber (Bellefonte, Pennsylvania, U.S.A.) and a used SPME fibre with a burnt off tip, coated with sol-gel derived C8-coated fiber containing (1:1, C8-TEOS:MTMOS) [27] were employed for the extraction of n-alkanes and accelerants.

2.3. Instrumentation

Gas chromatography analyses were conducted using a Hewlett-Packard 6890 GC (Wilmington, Delaware, U.S.A.). The HP 6890 gas chromatograph was equipped with FID and a HP ChemStation for data processing. An Ultra-1 capillary column (Agilent) of dimensions 25 m x 0.20 mm x 0.11 µm film thickness was used. Helium was used as the carrier gas at a flow rate of 1.2 mL/min. The injection port temperature was set at 250 °C and FID temperature at 310 °C. SPME injections were performed using a split mode injection (5:1).

Studies of fiber coating structure and thickness were made by means of Philips Scanning Electron Microscope model XL 30 SEM (Philips Electronic Instruments Company, Mahwah, New Jersey) equipped with a ThermoNoran energy dispersive X-ray detection system (EDX).

2.4. Procedures for Headspace SPME

30 µL from the prepared standard solution of n-alkanes (C8, C10, C12, C14, and C16) was placed in the sample preparation apparatus which was immersed in a hot water bath and heated for 20 min at 100 ° C. The C8-coated fiber was exposed in the headspace and the fiber extracts were analyzed using GC-FID. The oven temperature was initially set at 40 ° C, programmed at a rate of 10 ° C/min until a final temperature of 270 ° C. The headspace SPME procedure was repeated using PDMS/DVB fiber for comparison. The same HS-SPME procedure was carried out again using spiked fire debris sample for the determination of accelerants in simulated arson samples.

2.5. Preparation of Fire Debris sample

A sample of carpet (20 cm x 13 cm) placed on a sheet of aluminium foil was ignited with a fire starter and left to burn until about one-third remained on the aluminium foil. Fire was extinguished by cutting off the oxygen supply. The partially burnt carpet was then exposed to the surrounding air for 30 minutes to let it cool down.

3. Results and Discussion

3.1. Characterization of the C-coated Fiber

3.1.1. Selectivity for n-alkane Standard Hydrocarbons

In order to examine selectivity of the lab-made SPME fiber towards hydrocarbon compounds, a mixture of n-alkanes (C8, C10, C12, C14 and C16 ) were subjected to HS- SPME using C8-coated fiber and the GC profiles were compared with that from direct injection. The GC profiles obtained from headspace SPME using C8-coated fiber was comparable with the profiles of hydrocarbon standards from direct injection. All the n-alkane hydrocarbon components were well separated as shown in Figure 1.

Figure 1
Figure 1: SPME-GC analysis of hydrocarbon compounds using C-coated fibers Peaks: (1) C, (2) C, (3) C, (4) C and (5) C n-alkanes

3.1.2. Extraction Capability for n-alkane Standard Hydrocarbons

The extraction capability of the C8-coated fiber for hydrocarbons was determined by comparing it with the extraction capability of commercially available PDMS/DVB fiber. PDMS/DVB fiber was selected for comparison because previous work done in this lab [26] proved that the fiber has the highest sensitivity towards hydrocarbon compounds. As can be seen from Figure 2, the C8-coated fiber exhibited a slightly higher extraction capability for all the hydrocarbon compounds by contrast with conventional PDMS/DVB fiber. A higher extraction capability yielded by C8-coated fiber could be due to the existence of higher surface area for the C8-coated fibers [13].

Figure 2
Figure 2: Comparison of extraction capability between C-coated fiber and PDMS/DVB fiber

3.1.3. Lifetime of the C-coated Fiber

The long lastingness of the C8-coated fiber was determined by 200 continued operations carried out with the same fiber and oven temperature program. The C8-coated fiber have been used for hydrocarbon extractions (C9, C13, and C15) and subjected to GC for more than 200 times. There was no significant differences of hydrocarbon peaks obtained in each operation. All the hydrocarbon compounds gave a low relative standard deviation (RSD) value ranging from 3.8 %-5.4 % which shows an acceptable reproducibility. This proves that the coated surface of the fiber was not partially depleted during the continued operation. It was still stable and reusable. Such a long service life are possibly due to the strong chemical bonding between the sol-gel generated C8-coated composite coating and the silica surface [7,12,13, 15].

3.1.4. Thermal Stability of the C-coated Fiber

The effect of conditioning temperature on the stability of the C8-coated fiber was determined by conditioning the fiber at high temperatures (270 and 300) ° C for 1 hour prior to extraction. High temperature conditioning lead to consistent improvement in peak area repeatability for SPME-GC analysis. The RSD value of < 4.6 % can be routinely obtained for hydrocarbons on C8-coated fibers conditioned at 270 ° C and 300 ° C. The C8-coated fiber can be routinely used at 300 ° C without any sign of bleeding, whereas for commercial PDMS/DVB fiber, the highest temperature the coating layer can endure is less than 280 ° C, and thus the range of analyte molecular weights that can be handled by SPME-GC is limited. Enhanced thermal stability of C8-coated fiber might be due to the strong chemical bonding between the sol-gel generated composite coating and the silica surface [8, 11, 16, 17,18,19, 24, 25].

3.1.5. Scanning Electron Microscopy (SEM) Analysis

The morphology of the lab-made fiber was investigated using the scanning electron microscope. As can be seen from Figure 3, it is obvious that the surface of the fiber coating was well-distributed. A homogeneous porous structure was suggested for sol-gel C8-coating (Figure 4). Chong et al. [7] and Yu et al. [10] have reported that porous structure of the sol-gel coating should significantly increase the surface area on the fiber. Consequently, with such a porous coating structure, even an apparently thinner coating will be able to provide enhanced stationary-phase loadings and therefore, high fiber sample capacity. Figure 5 reveals that the fiber was not uniformly coated. This suggestion is agreeable to those reported by Gbatu et al. [13].

The average thickness of the C8 coating was estimated as being ~ 3-4 µm, which is considerably thinner than most conventional SPME fibers (65 µm for PDMS/DVB). The reproducibility of the coating thickness obtained in this study is rather promising. The volume of extracting phase on the lab-made C8-coated fiber is ~ 0.011-0.014 mm 3 whereas a 65 µm PDMS/DVB commercial fiber has an extracting phase volume of 0.357 mm 3 . It is apparent that the volume of extracting phase on the lab-made C8-coated fiber is considerably less than that of commercial PDMS/DVB fiber. Therefore the C8 coating has a larger affinity towards the analytes than regular PDMS/DVB.

Figure 3
Figure 3: The surface view of C fiber at 150 fold-magnification obtained by SEM

Figure 4
Figure 4: The surface view of C fiber at 150 fold-magnification obtained by SEM

Figure 5
Figure 5: The cross-sectional view of C fiber at 4000 fold-magnification obtained by SEM

3.2. Method Validation

3.2.1. Accuracy of HS-SPME Method using C-coated Fiber

The accuracy of the developed method for three replicate analyses was determined by calculating the relative standard deviations (RSD) of the peak areas for all standard hydrocarbons (C8, C10, C12, C14 and C16) in burnt carpet sample spiked at the same concentration level.

All the hydrocarbon compounds gave a low relative standard deviation (RSD) value ranging from 3.9 %-5.5 % which shows an acceptable reproducibility. These results indicated that quantitative analysis of hydrocarbons was possible using the external standard method and the applicability of lab-made C8-coated fiber for routine analysis.

3.2.2. Detection Limits of Accelerants

Detection limits of accelerants (lowest detectable amount determined based on three times the baseline noise) were evaluated in order to access the performance of the proposed method. The lab-made C8-coated fiber was employed for extractions of gasoline, kerosene and diesel in spiked burnt carpet sample under optimum HS-SPME conditions.

For all the common accelerants, the LODs were between 0.7 to 1.0 µL. These values are indicative of good performance of the lab-made C8-coated fiber. The detection limits of common accelerants obtained is this study using C8-fiber is comparable to those reported by Yong [26] using commercial PDMS/DVB fiber.

3.2.3. Linearity

Calibration curves consisting of five different concentration of n-alkane hydrocarbons were generated as regression lines and the correlation coefficients were obtained. The analytes were extracted using lab-made C8-coated fiber under the optimum HS-SPME conditions. The

HS-SPME procedure with C8-coated fiber yielded an excellent linear relationship between the peak area counts and analyte concentration in the range of 2.00-10.00 % v/v. Good correlations with R 2 value between 0.9869-0.9958 (R 2 ~ 1) were obtained. It is apparent that there were almost no factors in the HS-SPME extractions of n-alkane hydrocarbons using lab-made C8-coated fiber that might cause the concentration characteristics to deviate from linearity.

3.3. Analysis of Simulated Arson Samples using C-coated Fiber

3.3.1. Selectivity for Petroleum Based Accelerants

In order to examine selectivity of the C8-coated fiber towards petroleum based accelerants, burnt carpet sample were individually spiked with known amount of gasoline, kerosene and diesel. The samples were subjected to headspace SPME using C8-coated fiber and the GC profiles were compared with that from direct injection. As seen in Figure 6 (b), all the hydrocarbon components in gasoline spiked burnt carpet sample were recovered by using C8-coated fiber and the chromatogram was comparable with the profile of gasoline from direct injection [Figure 6 (a)]. The hydrocarbon components in kerosene (Figure 7) and diesel (Figure 8) spiked burnt carpet sample were also effectively extracted using the C8-coated fiber and similar comparisons were obtained with direct injection of the respective accelerants. This indicated that the C8-coated fiber favored the extraction of hydrocarbons, thus providing a good selectivity towards accelerants. The GC profiles of gasoline, kerosene and diesel spiked samples obtained in this study were in good agreement with those obtained by Borusiewicz [1] using Tenax as adsorbent and Yong [26] using commercially available fibers. Figure 6: GC profiles of direct injection of gasoline

Figure 6
Figure 6: GC profiles of (b) gasoline spiked burnt carpet sample and (c) the blank burnt carpet sample using C-coated fibers. Peak identities: (1) methylbenzene, (2) ethylbenzene, (3) 1, 3-dimethylbenzene, (4) 1, 2- dimethylbenzene, (5) 1-ethyl-2-methylbenzene, (6) 1, 2, 4-trimethylbenzene, (7) 1, 2, 3- trimethylbenzene

Figure 7
Figure 7: GC profiles of (a) direct injection of kerosene and (b) kerosene spiked burnt carpet sample using C-coated fibers.Peak identities: (1) C, (2) C, (3) C, (4) C, (5) C, (6) C, (7) 2, 6-dimethylnapthalene, (8) C

Figure 8
Figure 8: GC profiles of direct injection of diesel spiked burnt carpet sample using C-coated fibers. Peak identities: (1) C, (2) C, (3) C, (4) C, (5) C, (6) C, C, (7) C

3.3.2 Extraction Capability for Petroleum Based Accelerants

The extraction capability of the sol-gel derived C8-coated fiber was determined by comparing it with the commercially available PDMS/DVB fiber. Both C8-coated fiber and PDMS/DVB fiber were capable of extracting early, middle and late eluting hydrocarbon compounds sufficiently. However, the C8-coated fiber showed a slightly higher extraction capability by contrast with conventional PDMS/DVB fiber for all the accelerants as shown in Figure 9. This result was comparable to that reported by Gbatu [13]. A higher extraction capability could be due to the existence of higher surface area for the C8-coated fibers [9, 13, 14, 20,21,22,23].

Figure 9
Figure 9: Comparison of sol-gel derived C-coated fiber and commercially available PDMS/DVB fiber in extracting hydrocarbon compounds from (a) gasoline, (b) kerosene and (c) diesel spiked burnt carpet

3. Conclusions

A new SPME fiber (lab-made C8-coated fiber) has been successfully developed and evaluated for the determination of common petroleum based accelerants in arson samples. The C8-coated fiber has a good selectivity towards hydrocarbon compounds and accelerants as it was capable of effectively extracting all the tested n-alkane hydrocarbon compounds and hydrocarbon components in gasoline, kerosene and diesel spiked burnt carpet samples. The lab-made fibre gave superior characteristics when compared to commercially available PDMS/DVB fibre. Compared with commercial PDMS/DVB fibre, the new lab-made fibre exhibited higher extraction capability for n-alkane hydrocarbon compounds and accelerants, higher thermal stability (up to 300 ° C) and longer lifetime (~ 200 times usage). Electron microscopy experiments revealed that the surface of the fibre coating was well-distributed but not uniformly coated and a porous structure was suggested for the sol-gel derived C8 coating with an approximate thickness of (3-4) µm. The developed HS-SPME method using C8-coated fiber exhibited a high degree of accuracy under the optimum experimental conditions. The limits of detection for the common accelerants were in the range of 0.7 to 1.0 µL. The linearity of the calibration graphs for all the tested n-alkane hydrocarbons was excellent (r > 0.9869). The experimental results clearly demonstrate the potential of C8-coated fiber in SPME for the detection of arson accelerants.

Acknowledgements

The authors would like to express their deepest gratitude to the Ministry of Science, Technology and Innovation, Malaysia (MOSTI) for the financial support under IRPA RM8 mechanism vote No. 74090.

References

1. Borusiewicz R., Zadora G.and Palus J. Z. 2004. "Application of headspace analysis with passive adsorption for forensic purposes in the automated thermal desorption GC-MS system". Chromatographia Supplement. 60: S113-S142.
2. Dolan J. (2003). "Recent advances in the applications of forensic science to fire debris analysis." Anal. Bioanal. Chem. 376. 1168-1171.
3. Almirall J. S., Furton K. G. and. Bruna J. C (1996). "A novel method for the analysis of gasoline from fire debris using headspace solid-phase microextraction". J. Forensic. Sci. 71. 12-22.
4. Lord, H. and Pawliszyn, J. 2000. Evolution of Solid phase Microextraction Technology. J. Chromatogr. A.. 885: 153-193.
5. Almirall, J. S., Bruna, J. C. and Furton, K. G. 1996. "Recovery of Accelerants in Aqueous Samples Using SPME". Science & Justice. 36: 283-287.
6. Lloyd, J. A. and Edmiston, P. L. 2003. "Preferential Extraction of Hydrocarbons from Fire Debris Samples by Solid phase Microextraction" J. Forensic. Sci. 48: 130-134.
7. Chong , S. L., Wang, D., Hayes, J. D., Wilhite, B. W. and Malik, A. 1997. "Sol-gel Coating Technology for the Preparation of Solid-phase Microextraction Fibers of Enhanced Thermal Stability". Anal Chem. 69: 3889-3898.
8. Lopes, A. L. and Augusto, F. 2004. "Preparation and Characterization of Polydimethylsiloxane / Poly(vinylalcohol) Coated SPME Fibers using Sol-Gel Technology". J. Chromatogr. A. 1056: 13-19.
9. Li, X., Zeng, Z. and Zhou, J. 2004. "High Thermal-Stable Sol-gel Coated Calix4. arene Fiber for SPME of Chlorophenols". Anal Chim Acta. 509: 27-37.
10. Yu, J., Wu, C. and Xing, J. 2004. "Development of New SPME Fibers By Sol-gel Technology for The Determination of Organophosphorus Pesticide Multiresidues in Food". J. Chromatogr. A. 1036: 101-111.
11. Wang, Z., Xiao, C., Wu, C. and Han, H. 2000. "High-performance Polyethylene Glycol Coated Solid-phase Microextraction Fibers Using Sol-gel Technology". J. Chromatogr. A. 893: 157-168.
12. Zeng, Z., Qiu, W., Wei, X, Yang, M., Huang, Z. and Li, F. (2001). "Solid-phase Microextraction of Monocyclic Aromatic Amines using Novel Fibers Coated with Crown Ether". J. Chromatogr. A. 934: 51-57.
13. Gbatu, T. P., Sutton, K. L. and Caruso, J. A. 1999. "Development of New SPME Fiber by Sol-gel Technology for SPME-HPLC Determination of Organometals". Anal Chim Acta. 402: 67-79.
14. Azenha, M., Malheiro, C. and Silva, A. F. 2005. "Ultrathin Phenyl-functionalized Solid-phase Microextraction Fiber Coating Developed by Sol-gel Deposition". J. Chromatogr. A. 1069: 163-172.
15. Cai, L., Gong, S., Chen, M. and Wu, C. 2006. "Vinyl Crown Ether as a Novel Radical Crosslinked Sol-gel SPME Fiber for Determination of Organophosphorus Pesticides in Food Samples". Anal Chim Acta. 559: 89-96.
16. Hu, Y. L., Fu, Y. L. and Li, G. K. 2006. "Preparation of Anilinemethyltriethoxysilane / polydimethylsiloxane Sol-gel Coatings for Solid-phase Microextraction of Aromatic Compounds". Anal Chim Acta. 567: 211-217.
17. Liu, M. M., Zeng, Z. R., Wang, C. L., Tan Y. J. and Liu H. 2003. "Solid-phase Microextraction of Phosphate and Methylphosphonate Using Novel Fibers Coated with Sol-gel Derived Silicone-divinylbenzene Co-polymer". Chromatographia. 58: 597-605.
18. Liu, M., Zeng, Z. and Fang, H. 2005. "Preparation and Application of the Sol-gel Derived Acrylate/silicone Co-polymer Coatings for Headspace Solid-phase Microextraction of 2-chloroethyl Ethyl Sulfide in Soil". J. Chromatogr. A. 1076: 16-26.
19. Wang, D., Xing, J., Peng, J. and Wu, C. 2003. "Novel Benzo-15-crown-5 Sol-gel Coating for Solid-phase Microextraction". J. Chromatogr. A. 1005: 1-12.
20. Yu, J., Dong, L., Wu, C., Wu, L. and Xing, J. 2002. "Hydroxyfullerene as a Novel Coating for Solid-phase Microextraction Fiber with Sol-gel Technology". J. Chromatogr. A. 978: 37-48.
21. Zhou, F., Li, X. and Zeng, Z. 2005. "Determination of Phenolic Compounds in Wastewater Samples using a Novel Fiber by Solid-phase Microextraction Coupled to Gas-chromatography". Anal. Chim. Acta. 538: 63-70.
22. Zuin, V. G., Lopes, A. L., Yariwake, J. H., and Augusto. F. 2004. "Application of a Novel Sol-gel Polydimethylsiloxane-Poly(vinyl alcohol) SPME Fiber for Gas Chromatographic Determination of Pesticide Residues in Herbal Infusions". J. Chromatogr. A. 1056: 21-26.
23. Yun, L. (2003). "High Extraction Efficiency Soild-phase Microextraction Fibers Coated with Open Crown Ether Stationary Phase using Sol-gel Technique". Anal Chim Acta. 486: 63-72.
24. Liu, M., Zeng, Z. and Xiong, B. (2005). "Preparation of Novel Solid-phase Microextraction Fibers by Sol-gel Technology for Headspace Solid-phase Microextraction - Gas Chromatographic Analysis of Aroma Compounds in Beer". J. Chromatogr. A. 1065: 287-299.
25. Bagheri, H., Es-Hagli, A and Rouini, M. R. (2005). "Sol-gel Based Solid-phase Microextraction and Gas Chromatography-Mass Spectrometry Determination of Dextromethorphan and Dextrorphan in Human Plasma". J. Chromatogr. B. 818: 147-157.
26. Yong, Y. T. 2004. "Development of Headspace SPME-GC Technique for the Forensic Analysis of Ignitable Liquid Residues in Fire Debris". M. Sc. Thesis. Universiti Teknologi Malaysia.
27. Ahmad U. K., Yacob A. R. and Selvaraju G. 2005. "A New SPME Adsorbent for the Forensic Analysis of Accelerant Residues". Ibnu Sina Institute, Universiti Teknologi Malaysia: Proceedings of the Annual Fundamental Science Seminar.

Author Information

Umi K. Ahmad, Ph.D., UTM
Department of Chemistry, Faculty of Science, Universiti Teknologi Malaysia

Geetha Selvaraju, M.Sc., UTM
Department of Chemistry, Faculty of Science, Universiti Teknologi Malaysia

Download PDF

Your free access to ISPUB is funded by the following advertisements:

 

BACK TO TOP
  • Facebook
  • Google Plus

© 2013 Internet Scientific Publications, LLC. All rights reserved.    UBM Medica Network Privacy Policy