Fully Automated, Trace-Level Determination of Parent and Alkylated PAHs in Environmental Waters by Online SPE-LC-APPI-MS/MS
Applications | 2014 | Thermo Fisher ScientificInstrumentation
Polycyclic aromatic hydrocarbons (PAHs) and their alkylated homologues are persistent organic pollutants with toxic, mutagenic, and carcinogenic properties. Monitoring trace levels of these compounds in environmental waters is essential for source identification, regulatory compliance, and protection of public health and ecosystems.
This study aimed to develop and validate a rapid, fully automated method for trace‐level determination of 28 parent and alkylated PAHs in environmental waters using online solid‐phase extraction (SPE) coupled with liquid chromatography and tandem mass spectrometry (LC‐MS/MS) with atmospheric pressure photoionization (APPI). The method was compared with conventional liquid–liquid extraction (LLE) followed by GC‐MS.
Environmental water samples (seawater, reclaimed water, rainwater runoff) were collected in pre-cleaned amber glassware, fortified with isotopically labeled internal standards, and directly injected (10 mL) into an automated online SPE system. Optimized chromatographic gradients combined methanol/water and acetonitrile/methanol to resolve isobaric and alkylated PAHs on a Hypersil Green PAH column. Dopant‐assisted APPI (chlorobenzene) enhanced ionization, enabling sensitive SRM detection on a TSQ Quantum Access triple quadrupole MS.
The method achieved linear calibration (5–500 ng/L, R²>0.99) and method detection limits of 7.9–34 ng/L for priority PAHs, approximately one order of magnitude lower than LLE‐GC‐MS. Alkylated isomers (e.g., C1‐naphthalenes, C1‐phenanthrenes) were partially resolved using the dual‐gradient flow strategy. Automated SPE prevented salt carryover and minimized sample preparation time. Application to field samples detected naphthalenes and alkylated PAHs in boating areas, parent and alkylated PAHs in rainwater runoff from a partially flooded parking lot, and trace C2‐PAHs in reclaimed water.
Further integration with high‐resolution mass spectrometry and expanded compound libraries could enable comprehensive fingerprinting of complex PAH mixtures. Real‐time monitoring platforms and miniaturized extraction modules may facilitate continuous surveillance of industrial effluents, runoff, and drinking water. Advancements in column chemistry may improve separation of closely related isomers and alkyl homologues.
The fully automated online SPE‐LC‐APPI‐MS/MS method offers a rapid, sensitive, and environmentally friendly alternative to traditional LLE‐GC‐MS for routine monitoring of parent and alkylated PAHs in environmental waters. Its high throughput and low solvent consumption make it well suited for regulatory laboratories, environmental research, and quality assurance in water analysis.
Sample Preparation, LC/MS, LC/MS/MS, LC/QQQ
IndustriesEnvironmental
ManufacturerThermo Fisher Scientific
Summary
Significance of the topic
Polycyclic aromatic hydrocarbons (PAHs) and their alkylated homologues are persistent organic pollutants with toxic, mutagenic, and carcinogenic properties. Monitoring trace levels of these compounds in environmental waters is essential for source identification, regulatory compliance, and protection of public health and ecosystems.
Objectives and Overview of the Study
This study aimed to develop and validate a rapid, fully automated method for trace‐level determination of 28 parent and alkylated PAHs in environmental waters using online solid‐phase extraction (SPE) coupled with liquid chromatography and tandem mass spectrometry (LC‐MS/MS) with atmospheric pressure photoionization (APPI). The method was compared with conventional liquid–liquid extraction (LLE) followed by GC‐MS.
Methodology and Instrumentation
Environmental water samples (seawater, reclaimed water, rainwater runoff) were collected in pre-cleaned amber glassware, fortified with isotopically labeled internal standards, and directly injected (10 mL) into an automated online SPE system. Optimized chromatographic gradients combined methanol/water and acetonitrile/methanol to resolve isobaric and alkylated PAHs on a Hypersil Green PAH column. Dopant‐assisted APPI (chlorobenzene) enhanced ionization, enabling sensitive SRM detection on a TSQ Quantum Access triple quadrupole MS.
Used Instrumentation
- Thermo Scientific EQuan online SPE system with HTC‐PAL autosampler
- Accela 1000 and Accela 600 liquid chromatography pumps
- Thermo Scientific Hypersil GOLD aQ SPE column (20×2.1 mm, 12 µm)
- Hypersil Green PAH analytical column (150×2.1 mm, 3 µm) with guard column
- Thermo Scientific TSQ Quantum Access triple-quadrupole MS with IonMax APPI source
- Chlorobenzene dopant delivery via programmable syringe pumps
Main Results and Discussion
The method achieved linear calibration (5–500 ng/L, R²>0.99) and method detection limits of 7.9–34 ng/L for priority PAHs, approximately one order of magnitude lower than LLE‐GC‐MS. Alkylated isomers (e.g., C1‐naphthalenes, C1‐phenanthrenes) were partially resolved using the dual‐gradient flow strategy. Automated SPE prevented salt carryover and minimized sample preparation time. Application to field samples detected naphthalenes and alkylated PAHs in boating areas, parent and alkylated PAHs in rainwater runoff from a partially flooded parking lot, and trace C2‐PAHs in reclaimed water.
Benefits and Practical Applications
- High sample throughput (28 min/run) with minimal manual preparation
- Improved sensitivity per volume (1 ng on column) and lower solvent use
- Reduced toxic waste generation and environmental impact
- Capability to screen for localized contamination events
- Robust quantitation in diverse matrices without filtration or cleanup
Future Trends and Applications
Further integration with high‐resolution mass spectrometry and expanded compound libraries could enable comprehensive fingerprinting of complex PAH mixtures. Real‐time monitoring platforms and miniaturized extraction modules may facilitate continuous surveillance of industrial effluents, runoff, and drinking water. Advancements in column chemistry may improve separation of closely related isomers and alkyl homologues.
Conclusion
The fully automated online SPE‐LC‐APPI‐MS/MS method offers a rapid, sensitive, and environmentally friendly alternative to traditional LLE‐GC‐MS for routine monitoring of parent and alkylated PAHs in environmental waters. Its high throughput and low solvent consumption make it well suited for regulatory laboratories, environmental research, and quality assurance in water analysis.
Reference
- Manoli E., Samara C. Polycyclic aromatic hydrocarbons in natural waters: sources, occurrence and analysis. Trac-Trends Anal Chem. 1999;18:417–428.
- Wolska L., Mechlińska A., Rogowska J., Namieśnik J. Sources and fate of PAHs and PCBs in the marine environment. Crit Rev Environ Sci Technol. 2012;42:1172–1189.
- Wang Z., Stout S.A., Fingas M. Forensic fingerprinting of biomarkers for oil spill characterization and source identification. Environ Forensic. 2006;7:105–146.
- Boehm P.D., Douglas G.S., Burns W.A., Mankiewicz P.J., Page D.S., Bence A.E. Application of petroleum hydrocarbon chemical fingerprinting after the Exxon Valdez oil spill. Mar Pollut Bull. 1997;34:599–613.
- Boehm P.D., Neff J.M., Page D.S. Assessment of PAH exposure in Prince William Sound after Exxon Valdez. Mar Pollut Bull. 2007;54:339–356.
- ATSDR. Toxicological profile for polycyclic aromatic hydrocarbons. U.S. Dept of Health and Human Services; 1995.
- Manzetti S. Ecotoxicity of PAHs, aromatic amines, and nitroarenes through molecular properties. Environ Chem Lett. 2012;10:349–361.
- US EPA. Priority pollutant list; 1998.
- US EPA. Definition and procedures for the determination of the method detection limit. 40 CFR Part 136 App. B; 2010.
- US EPA. Method 3510C: Separatory funnel liquid–liquid extraction. SW-846; 1996.
- US EPA. Method 3630C: Silica gel cleanup. SW-846; 1996.
- Denoux G.J., Gardinali P., Wade T.L. Quantitative determination of PAHs by GC/MS-SIM. NOAA; 1998.
- Rawa-Adkonis M., Wolska L., Namieśnik J. Analytical procedures for PAH and PCB determination in water samples. Crit Rev Anal Chem. 2006.
- Smith R.M. Modern methods of sample preparation. J Chromatogr A. 2003;1000:3–27.
- Garcia-Ac A., Segura P.A., Viglino L., et al. On-line SPE-LC-MS/MS for drinking and surface water. J Chromatogr A. 2009;1216:8518–8527.
- Wang C.T., Gardinali P.R. Comparison of API techniques for detection of microconstituents by SPE-LC-MS/MS. J Mass Spectrom. 2012;47:1255–1268.
- Busetti F., Backe W.J., Bendixen N., et al. Trace analysis by large-volume injection LC-MS. Anal Bioanal Chem. 2012;402:175–186.
- Ramirez C.E., Wang C., Gardinali P.R. Automated trace PAH determination by online SPE-LC-APPI-MS/MS. Anal Bioanal Chem. 2014;406:329–344.
- Smith D.R., Robb D.B., Blades M.W. Comparison of dopants for ionization of PAHs by LC-APPI-MS. J Am Soc Mass Spectrom. 2009;20:73–79.
- Cai S.S., Syage J.A., Hanold K.A., Balogh M.P. UPLC-APPI-MS/MS of PAHs. Anal Chem. 2009;81:2123–2128.
- Sander L.C., Pursch M., Wise S.A. Shape selectivity in reversed-phase LC. Anal Chem. 1999;71:4821–4830.
- Rimmer C., Sander L., Wise S. Selectivity of long chain phases in RP-LC. Anal Bioanal Chem. 2005;382:698–707.
- Horak J., Lindner W. Sulfonyl-embedded reversed phase materials. J Chromatogr A. 2008;1191:141–156.
- Wang Z.D., Fingas M., Page D.S. Oil spill identification. J Chromatogr A. 1999;843:369–411.
- Mahler B.J., Van Metre P.C., Crane J.L., et al. Coal-tar-based sealcoat and PAHs. Environ Sci Technol. 2012;46:3039–3045.
- Watts A.W., Ballestero T.P., Roseen R.M., Houle J.P. PAHs in stormwater runoff from sealcoated pavements. Environ Sci Technol. 2010;44:8849–8854.
- Mahler B.J., Van Metre P.C., Bashara T.J., et al. Parking lot sealcoat: source of urban PAHs. Environ Sci Technol. 2005;39:5560–5566.
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