Urban Water Security Research Alliance Optimising Micropollutants - - PowerPoint PPT Presentation

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Urban Water Security Research Alliance Optimising Micropollutants - - PowerPoint PPT Presentation

Urban Water Security Research Alliance Optimising Micropollutants Extraction for Analysis of Water Samples: Comparison of Different Solid Phase Materials and Liquid-Liquid Extraction Frederic Leusch 1 , Erik Prochazka 1 , Benjamin Tan 2 ,


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Optimising Micropollutants Extraction for Analysis of Water Samples: Comparison of Different Solid Phase Materials and Liquid-Liquid Extraction

Frederic Leusch1, Erik Prochazka1, Benjamin Tan2, Stewart Carswell2, Peta Neale3 and Beate Escher3

1 Griffith University, Smart Water Research Centre 2 Queensland Health Forensic and Scientific Services 3 The University of Queensland – Entox

Bioassays and Risk Communication

20 June 2012

Urban Water Security Research Alliance

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CHEMICALS IN THE ENVIRONMENT

  • 63+ million chemicals with >100,000 in

commercial use + their transformation products

  • There are simply too many chemicals out

there to quantify them one by one …

Class Agric. Indust. Urban Natural Pesticides X Pharmaceuticals and personal care products (PPCPs) X X Hormones X X Industrial compounds X X Metals and inorganics X X X

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A ROLE FOR BIOANALYTICAL TOOLS

  • Toxicity testing, and bioanalytical tools in

particular, can overcome some of the challenges of environmental monitoring

  • Detect chemicals by their

effect, not their structure

– Non-target compounds – Transformation products – Mixture effects

  • “Is there a needle in the

haystack?”

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THE PROBLEM …

  • Similar to chemical analysis, bioanalytical

tools require a water sample to be processed prior to analysis

– Filtration followed by solid phase extraction (SPE) to concentrate organic compounds

  • Are there unintended consequences of

sample preparation?

– Are we losing important (toxic?) compounds?

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EXTRACTION: A NECESSARY EVIL

Vwater Vextract enrichment

Solid phase extraction

volume of extract added to assay total volume of assay

dilution

relative enrichment factor REF = enrichment factorSPE X dilution factorassay

enrichment dilution

REF = 1 “original sample” REF = 1 “original sample”

Macova, Toze, Hodgers, Mueller, Bartkow, Escher (2011). Bioanalytical tools for the evaluation of organic micropollutants during sewage treatment, water recycling and drinking water generation. Water Research 45: 4238-4247.

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EXTRACTION: A NECESSARY EVIL

Vwater Vextract enrichment

Solid phase extraction

volume of extract added to assay total volume of assay

dilution

relative enrichment factor REF = enrichment factorSPE X dilution factorassay

enrichment dilution

REF = 1 “original sample” REF = 1 “original sample”

Macova, Toze, Hodgers, Mueller, Bartkow, Escher (2011). Bioanalytical tools for the evaluation of organic micropollutants during sewage treatment, water recycling and drinking water generation. Water Research 45: 4238-4247.

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PROJECT AIM

  • Can we develop an extraction method that

minimizes chemical loss?

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EXPERIMENTAL DESIGN: STAGE 1

1L 1L Mix of 263 compounds Mix of 263 compounds

Oasis HLB Bond Elut PPL Supel HLB Strata X Bond Elut GC Supel CC

179 pesticides @ 1 ug/L 84 pharmaceuticals @ 20 ng/L

pH 2 pH 2 pH 7 pH 7

ultrapure water

LLE EthA LLE MTBE

Chemical analysis (LC-MS/MS, GC-MS/MS)

Elute (MeOH, acetone/hexane), Evaporate Elute (MeOH, acetone/hexane), Evaporate Rotovap Rotovap

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SPIKED COMPOUNDS

log Kow pKa

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RESULTS – STAGE 1

NA NA NA NA

Oasis HLB Bond Elut PPL Supel HLB Strata X Bond Elut GC Supel CC LLE EthA LLE MTBE Oasis HLB Bond Elut PPL Supel HLB Strata X Bond Elut GC Supel CC LLE EthA LLE MTBE

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CONCLUSIONS – STAGE 1

  • LLE performed well on average, but …

– High variability – Lots of solvent (60% of sample, vs 1% with SPE) – Contaminants even from high-grade solvent

  • SPE (HLB) was very effective

– Oasis HLB and Strata X performed best, but

  • ther options performed well too
  • SPE (carbon) poor overall, but …

– Fair recovery of a few compounds not well recovered by HLB

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ULTRAPURE VS RIVER WATER

  • Does organic matter (present in

environmental samples) interfere with extraction efficiency?

ultrapure water TOC = 0.15 mg/L tap water TOC = 2.05 mg/L river water TOC = 8.31 mg/L

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EXPERIMENTAL DESIGN – STAGE 2

1L 1L Mix of 315 compounds Mix of 315 compounds

215 pesticides @ 0.8 ug/L 88 pharmaceuticals @ 30 ng/L

pH 2 pH 2 pH 7 pH 7

tap water

Chemical analysis (LC-MS/MS, GC-MS/MS)

12 EDCs @ 50 ng/L river water (filtered)

1L 1L

Oasis HLB Supel CC

1L 1L 1L 1L Elute (MeOH, acetone/hexane), Evaporate Elute (MeOH, acetone/hexane), Evaporate

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RESULTS – STAGE 2

NA NA

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CONCLUSIONS – STAGE 2

  • With combined Oasis HLB and Supelco CC

– Excellent recovery of wide range of compounds in environmentally relevant matrices – Better recovery than with ultrapure water (keeper effect?)

  • However:

– 2x more solvent in stacked mode – More complex process

  • Make our own cartridges?
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RECOMMENDED PROTOCOL

pH 2 pH 2 SPE

HLB/CC

SPE

HLB/CC

Elute

(MeOH, acetone/hexane)

Elute

(MeOH, acetone/hexane)

Add keeper

(2 uL DMSO)

Add keeper

(2 uL DMSO)

Evaporate Evaporate 1L 1mL

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FUTURE WORK

  • Develop an empirical-based model to predict

the recovery of compounds on various SPE sorbents to predict recovery of untested compounds

  • Important variables include

– Sorbent – Kow – Ionised / unionised

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ACKNOWLEDGMENT

  • This project was supported by the Urban

Water Security Research Alliance

  • We thank Dr Nicole Knight, Steve Carter and

Vince Alberts for laboratory support

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Urban Water Security Research Alliance THANK YOU www.urbanwateralliance.org.au