A Holding Time Evaluation Study for the Analysis of PFAS in Aqueous Samples Charles Neslund, Scientific Officer, Eurofins Lancaster Laboratories Environmental,

Slides:



Advertisements
Similar presentations
Activity 48 Follow-up Discuss in your groups the difference in results for each neutralization between pairs. Lack of consistency in drop size Error in.
Advertisements

Activity 10 Follow-up Were there differences in your results from one group to another? Why did we use the average to compare to table 3 in activity 9?
Quality Decisions Today’s Goal: To learn about nonpoint source pollution. To understand how decisions we make impact the environment around us.
Result validation. Exercise 1 You’ve done an analysis to the best of your ability using the correct procedure. Is your answer correct? possibly, hopefully.
Titremetric analysis Dr. Mohammad Khanfar. Concept of Titremetric analysis In general, we utilize certain property of a substance to be analyzed in order.
Emily Young Carr Grade 9 Academy of Notre Dame de Namur Levels of Pollutants in Local Waters.
AXYS developed a method for direct injection analysis of 9 perfluoroalkyl carboxylates (PFCA), 3 perfluoroalkyl sulfonates (PFSA) and perfluorooctane sulfonamide.
Understanding and Implementing SWAMP Comparability: Quality Assurance SWAMP Quality Assurance Help Desk Quality Assurance Research.
problem solved Preservation of Samples for RETS, REMP and RW Bob Litman Radiochemistry Laboratory Basics Presented in coordination with GEL.
New York City Department of Environmental Protection Bureau of Water Supply Water Quality Bio-Stability of New York City’s Distribution Water Authors:
Rapid and Accurate Analysis of Microcystins Using UPLC/MS/MS Yongtao (Bruce) Li, Ph.D. Joshua S. Whitaker Eurofins Eaton Analytical,
HOLD TIME, STORAGE, AND SAMPLE CONTAINER CONSIDERATIONS FOR ANALYTICAL METHODS TO DETERMINE HIGHLY FLUORINATED COMPOUNDS IN ENVIRONMNTAL MATRICES Mary.
Introduction The past, the present and the future.
Copyright 2008 © Silliker, All Rights Reserved Collection of Samples for Chemical Analysis.
Level (3.1) - Carry out an extended practical investigation involving quantitative analysis (Version 2) Exemplars of Student Work.
Providing comprehensive scientific resources to environmental clients worldwide. Dissolved Gas Analysis: A Review and Comparison.
(2) Scientific processes. The student uses scientific methods during field and laboratory investigations. The student is expected to: (A) plan and implement.
Making Molar Solutions From Liquids (More accurately, from stock solutions)
PERFLUORINATED CARBOXYLIC ACIDS AND SULFONIC ACIDS IN WASTE SAMPLES Katsuya Y 1 *,Takemine S 1, Matsumura C 1, Tsurukawa M 1, Haga Y 1, Fujimori K 1, Nakano.
Dieldrin in Cyprinus Carpio from the Des Moines River: The Des Moines River Water Quality Network (DMRWQN) is a long-term monitoring project.
1 of 48 The EPA 7-Step DQO Process Step 6 - Specify Error Tolerances 3:00 PM - 3:30 PM (30 minutes) Presenter: Sebastian Tindall Day 2 DQO Training Course.
Alternative Evaluation Framework for Managing Dioxins/Furans in Dredged Material Proposed for Open-Water Disposal Tad Deshler Windward Environmental LLC.
OBJECTIVES To measure ascorbic acid level in food products Identify the sources of ascorbic acid Master of extraction and determination of ascorbic.
Objective  To develop methods for analysis of compounds in organic aerosol particles Why is this important?  Environmental impact  Alternative fuels.
Abstract Quantitative Comparative Analysis of Proteins in three types of Beans: Green Beans, Lima Beans, and Soy Beans By, Ashley Rowles Bean: Correction.
John D. Vargo 1 ; Michael Schueller 1 ; Mary Skopec 2 1 State Hygienic Laboratory at the University of Iowa, Coralville, IA; 2 Iowa Department of Natural.
이 장 우. 1. Introduction  HPLC-MS/MS methodology achieved its preferred status -Highly selective and effectively eliminated interference -Without.
Navigating the Challenges for the Analysis of PFAS in Environmental Matrices to Meet TRRP Requirements Charles Neslund, Technical Director TCEQ Environmental.
Determinations and Interpretations of FTIR Detection Limits
Thomas Bruton, David Sedlak
Clean Water Act Methods Overview of EPA’s CWA Method Activities
A Technique for Determining Total Oxidizable Precursors (TOP) of Perfluoroalkyl Compounds Chuck Neslund, Technical Director, Eurofins Lancaster Laboratories.
Jøran Solnes Skaar1,2, Erik Magnus Ræder3, Lutz Ahrens 4, Roland Kallenborn1,5, Jan Ludvig Lyche3.   1 Faculty of Biotechnology and Food Science (KBM),
Outdoor Water Sediment Study – Adding Effects of Sunlight to Aquatic System Exposure Assessment Cecilia Mucha Hirata (DuPont Crop Protection, Newark DE,
EPA Method Equivalency
Janice L. Willey Senior Chemist
Classifying Matter: Physical and Chemical Properties
Activity 12 First Activity of Unit B
Risk governance of emerging contaminants in drinking water and its resources Comparing practices in the Netherlands, Germany, Switzerland and the State.
Evaluation and Application of SPME Arrows
Added Monrovia and South Bend to the slide.
ASTSWMO Annual Meeting
The Use of Advanced Instrumental Techniques to Address Emerging and Unique Circumstance Contaminants Charles Neslund, Scientific Officer, Eurofins Lancaster.
Have Instrument, make method; How new methods are made and validated
Protein Production Jackpot!
PFAS Dark Matter: Per- and polyfluorinated precursors in soil and water Pat Benvenuto, Heather Lord, Terry Obal, Maxxam Analytics, Mississauga, ON Canada.
Russ Wolff and Craig Caselton,
EPA method 521 by direct-inject LC-MS/MS
Mercury Speciation in Tank Waste at the Savannah River Site
Michela Powell-Hernandez Senior Environmental Scientist, EcoChem, Inc.
A Field Analysis Technique for the Determination of PFAS Compounds
Increasing TKN Sample Determinations Through Automation
The Practicality (Necessity) of Use of Clean-up Techniques for the Analysis of D/F and PCB Congeners Charles Neslund, Scientific Officer, Eurofins Lancaster.
Health Effects of PFAS 7th June 2018
Remediation & Restoration
Organic solvent extraction
Health Effects of PFAS 7th June 2018
Groundwater Watch list «draft concept report»
Best Practices for Identification and Quantitation
PFC-Template and Questionnaire for the pilot study on PFC (2017)
NJ DWQI Testing Subcommittee
Very special case/scenario David Schiessel, Senior Chemist
Groundwater Watch List GWWL «Draft Concept Report»
Aroclors, Homologs and Congeners – An Evaluation of the Options for PCB Analysis and a Comparison of the Interpretive Value Charles Neslund, Scientific.
Solutions Part II: Units of Concentration (loosely from Jespersen Chap
Groundwater Watch List Meeting - Group of Volunteers –
PFC-Template and Questionnaire for the pilot study on PFC (2017)
EPA/OAQPS Pollutant Emissions Measurement Update 2019
Emerging Contaminants
Per- and Polyfluoroalkyl Substances (PFAS)
Presentation transcript:

A Holding Time Evaluation Study for the Analysis of PFAS in Aqueous Samples Charles Neslund, Scientific Officer, Eurofins Lancaster Laboratories Environmental, LLC National Environmental Monitoring Conference, New Orleans, LA August 6-10, 2018 Providing comprehensive scientific resources to environmental clients worldwide.

Per/Polyfluorinated Compounds Per/Polyfluorinated Alkyl Substances (PFAS) are a class of compounds that have been in use since the late 1940’s, early 1950’s. PFAS compounds, in general, are persistent in the environment and bioaccumulative. Because of that we might expect that persistence and stability to impact holding times referenced in analytical methods. Persistent organic pollutants (POPs) like PCBs and Dioxins/furans reference holding times of 1 year. 2 2

PFAS Holding Times EPA Method 537 ver 1.1 stipulates a 14 day holding time, when using polypropylene containers and Trizma as a preservative ISO 25101 uses a 14 day holding time with polypropylene and sodium thiosulfate as preservative ASTM D7979-17 uses a 28 day holding time with a polypropylene tube and dilution with methanol DoD/QSM 5.1.1 using a 14 day holding time with high density polyethylene (HDPE) containers 3 3

PFAS Holding Time Study Decided to look at three different variables that are suspected of impacting the stability and integrity of a water sample and therefore the holding time; Container Type (HDPE vs Glass) Amount of sample used (Entire container vs subsample) Use of a preservative (Trizma vs no-Trizma/preservative Spiked laboratory grade water, in duplicate, at 200 ng/l and collected data at 10 points over 70 days 4 4

PFAS Holding Time Study Spiking groups were Group 1 – HDPE / 250 mls / No Trizma Group 2 – HDPE / 250 mls / Trizma Group 3 – HDPE / 100 mls / No Trizma Group 4 – HDPE / 100 mls / Trizma Group 5 – Glass / 250 mls / No Trizma Group 6 – Glass / 250 mls / Trizma Group 7 – Glass / 100 mls / No Trizma Group 8 – Glass / 100 mls / Trizma Samples pulled from refrigerated storage on a weekly basis starting from Day 0 up until Day 70. 5 5

Compounds Studied Perfluorobutanoic acid Perfluorobutanesulfonate Perfluoropentanoic acid Perfluoropentanesulfonate Perfluorohexanoic acid Perfluorohexanesulfonate Perfluoroheptanoic acid Perfluoroheptanesulfonate Perfluorooctanoic acid Perfluorooctanesulfonate Perfluorononanoic acid Perfluorononanesulfonate Perfluorodecanoic acid Perfluorodecanesulfonate Perfluoroundecanoic acid Perfluorododecanesulfonate Perfluorododecanoic acid 4:2 Fluorotelomer sulfonate Perfluorotridecanoic acid 6:2 Fluorotelomer sulfonate Perfluorotetradecanoic acid 8:2 Fluorotelomer sulfonate Perfluorohexadecanoic acid 10:2 Fluorotelomer sulfonate Perfluorooctadecanoic acid N-methylperfluoro-1-octanesulfonamidoacetic acid N-ethylperfluoro-1-octanesulfonamidoacetic acid Compounds in red are the ones listed in EPA 537 ver 1.1 6 6

No-Trizma vs Trizma 7 7

Observations Little to no difference observed between Trizma preserved and unpreserved containers Performance of longest chain length carboxylic acids (C16 and C18) not as solid as shorter chain Sulfonates, overall, don’t perform as well as carboxylates Reasonable good performance for both unpreserved and Trizma preserved out to 70 days 8 8

Entire Container vs Subsample 9 9

Entire Container vs Subsample 10 10

Observations Presence of Trizma has significant impact on subsampled aliquot for anything past C10 carboxylate and C9 sulfonate In unpreserved HDPE container, little impact over 70 day period until C13 carboxylate and C10 sulfonate. Implications for evaluation of results from analysis of very high level samples. 11 11

HDPE vs Glass 12 12

HDPE vs Glass 13 13

Observations Glass performed surprisingly well in the unpreserved container as compared to HDPE. For the 537 ver 1.1 list of compounds glass looked to perform as well as HDPE. Longer chain acids and sulfonates fell off between day 56 and day 70 Trizma preserved did not seem to contribute any advantage to performance and recovery 14 14

HDPE/Full Container vs Glass/Subsample 15 15

HDPE/Full Container vs Glass/Subsample 16 16

Observations Not much difference between unpreserved and Trizma preserved, HDPE and glass Unexplained contamination for longer chain carboxylates (C11-C14) in both unpreserved and Trizma preserved containers from day 35 and later extractions C16 and C18 carboxylates significantly impacted in both 17 17

Conclusions The use of Trizma does not appear to provide any advantages (buffering) to the holding time stability. Under certain conditions, glass containers appear to demonstrate reasonable performance. Lid liner would be a concern. Whole sample container should be used, except where expected concentrations would be high and impact on overall results negligible. Holding times well in excess of 14 days, even for an expanded list of compounds could be used.

Thank you Charles Neslund charlesneslund@eurofinsus.com 717-799-0439