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A Comparison of SPME Approaches for the Analysis of Alkylated PAHs in Pore Water Porewater: The Interaction between Sediment, Biota, and Water 2015 Fall Workshop Jim Occhialini Nathan Sorelle Alpha Analytical
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Overview ASTM D7363 Wrap up Topics for Discussion “A COMPARISON of SPME Approaches for the Analysis of Alkylated PAHs in Pore Water”
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2 EVALUATING ECOLOGICAL RISK TO INVERTEBRATE RECEPTORS FROM PAHS IN SEDIMENTS AT HAZARDOUS WASTE SITES EPA/600/R-06/162F ERASC-011F October 2009
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Sediment (& Tissue Analysis…) Difficult samples Great expectations –Sensitivity & quality
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Sampling Pore Water for Subsequent Analysis in the Laboratory Acquire pore water in the field –Direct sampling Piezometers, syringes Centrifuge in the lab –Assume ~1:4 pore water / sediment This ratio can vary, i.e. “sandy” sediments Both are generally volume-limited options Considering typical 1L extraction volumes… Relationship between extraction volume and sensitivity
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5 Championed by Dr. Steven Hawthorne, EERC, University of North Dakota EPA SW-846 Method 8272
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6 EVALUATING ECOLOGICAL RISK TO INVERTEBRATE RECEPTORS FROM PAHS IN SEDIMENTS AT HAZARDOUS WASTE SITES EPA/600/R-06/162F ERASC-011F October 2009 EMAP 34 List (EPA Monitoring & Assessment Program) 34 parent & alkylated PAHs (18 parent & 16 groups of alkyl PAHs listed for EPA’s equilibrium partitioning sediment benchmark (ESB) model [2003])
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Target Analyte List 10 parent and 14 alkylated groups – contribute 95% of the toxic units EMAP 34 list 7
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Colloids removed utilizing a flocculation procedure Direct measurement of truly dissolved fraction D7362 Procedure Minimal pore water volume required ~ 5 mLs –Generated by centrifugation in the lab –Temp control – 4 o C –7,400 RPM Direct measurement of truly dissolved fraction - Colloids removed utilizing a flocculation procedure
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D7362 Procedure Sample introduction technique –SPME (solid phase micro extraction) concentration equilibrium is established between the sample matrix and the extraction phase. PDMS (polydimethylsiloxane) coated fiber
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18 USEPA SAMS #3, Guidelines for using Passive Samplers to Monitor Organic Contaminants at Superfund Sediment Sites
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19 28 day hold time
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Different approach… Time consuming process –Every analytical run performed in duplicate Long equilibration, GC run times Typical analytical sequence –[CCV, CCV], [IB, IB], [MB, MB] Samp 1, Samp 1 IB, IB Samp 2, Samp 2 IB, IB Etc. ~ 3 field samples / day 20
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22 C1 – phenanthrenes / anthracenes
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D7363-13a Sensitivity 23 1
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24 Questions? Jim Occhialini jocchialini@alphalab.com (508) 380-8618
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