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GC/MS Method for GC/MS Method for Determining the Occurrence and Determining the Occurrence and
Investigating Treatment Processes for Investigating Treatment Processes for Representative Representative EDCsEDCs and PPCPs in and PPCPs in Waters of Southeastern LouisianaWaters of Southeastern Louisiana
AWWA Annual Conference & Exposition, New Orleans, LAAWWA Annual Conference & Exposition, New Orleans, LA
June 18, 2002June 18, 2002
Glen R. Boyd, Ph.D., P.E. Helge Reemtsma
Dept. of Civil and Environmental Engineering
Deborah A. Grimm, Ph.D.Coordinated Instrumentation Facility
Tulane University, New Orleans, LA
AcknowledgementsAcknowledgementsSponsorsCenter for Bioenvironmental Research at
Tulane and Xavier UniversitiesTulane School of Engineering
Collaborators and Tech SupportSiddhartha Mitra – USGS (EEB) Jennifer Holland – CEE/TSPH-EHSReimers & Englande – TSPH-EHSRichard Campanella – CBRCraig Conard – CBR
Undergraduate StudentsSoren Eustis Kristen SmebyApryl Scott Sean ConnerRhonda Hattar Sarah RossRebekah Cohen Sarah PerksVictoria Nwosu Deante Preston
AcknowledgementsAcknowledgements
Wayne Wayne KoffskeyKoffskey, Jefferson Parish Water , Jefferson Parish Water Treatment PlantTreatment PlantRon Hoffman, Jefferson Parish Ron Hoffman, Jefferson Parish Wastewater Treatment PlantWastewater Treatment PlantSaadSaad JasimJasim, Windsor Utilities , Windsor Utilities CommissionCommissionSamarSamar MazloumMazloum, ENWIN Utilities, ENWIN Utilities
OutlineOutline
Target Compounds
Methods
Field Sampling
– WWTP effluent– Mississippi River water– Detroit River water– WTP processes
Conclusions
Target CompoundsTarget Compounds
Endocrine disrupting chemicalsLipid regulator, fungicides and disinfectantsAnti-inflammatory and analgesicsOthers
Endocrine disrupting Endocrine disrupting chemicalschemicals
CHO OH
CH3
CH3
CH3O
HOCH3
HO
OH
Bisphenol A 80-05-7228 g/mol
Estrone 53-16-7
270 g/mol
17β-Estradiol 50-28-2
272 g/mol
Lipid Regulator, Fungicides and Lipid Regulator, Fungicides and DisinfectantsDisinfectants
Clofibric Acid 882-09-7
214 g/mol
Chlorophene 120-32-1
218 g/mol
Triclosan 3380-34-5
288 g/mol
OH
Cl
CH2
Cl O
OHCl
Cl
Cl O COOH
CH3
CH3
AntiAnti--Inflammatory and AnalgesicsInflammatory and AnalgesicsNaproxen 22204-53-1
230 g/mol
(Naprosyn)
Ibuprofen 15687-27-1
206 g/mol
(Motrin, Advil)
Acetaminophen 103-90-2
151 g/mol
(Tylenol)
CH3O
CHCOOH
CH3
(CH3)2CHCH2 CHCOOH
CH3
OHCH3CNH
O
OthersOthers
O CHCH2CH2NHCH3F3C
N
NN
N
O
OH3C
CH3
CH3
ANTIDEPRESSANT
Fluoxetine 54910-89-3
309 g/mol
(Prozac)
HUMAN ACTIVITY MARKER
Caffeine 58-08-2
194 g/mol
MethodsMethodsSample Collection and Preparation
8L grab samples were taken. Canadian samples were acidified prior to shipment.Pre-filter samples with 1 µm and 0.2 µm glass fiber filtersIsolate PPCPs/EDCs using SPE disks (3M SDB-XC)Pre-condition with MeOH and DCMAcidify (pH 2) and add surrogate std.Vacuum extraction and air dry disk
MethodsMethods
Extraction and DerivatizationExtract with MeOH and DCM Dry samples (rapid vap w/N2)Dissolve in 1 mL BSTFA reagent Add 10 µL of internal std Derivatize at 80°C for 20 minAnalyze using GC/MS
MethodsMethodsGC/MS Setting
Injection: splitless2 µL injections @ 230°C onto DB5 column (25m w/0.25 µm film thickness and 0.25 mm ID)GC oven: 100°C (0 min), 5°C/min to 165°C (5min), 2°C/min to 175°C (0min) and 10°C/min to 320°C (5min), total run: 42.5 minMS is operated in +EI mode using SIM mode for sensitivity
MethodsMethods
Target Compounds and Detection LimitsTarget Compounds and Detection LimitsTarget
CompoundIDL
[ng/L]Average % Recov.
% RSD
Compl of Deriv (%)
MDL* [ng/L]
Clofibric acid 3 60.8 12.6 100 0.6Estrone 3 91.9 5.1 100 0.517β-Estradiol 1 90.5 9.1 100 0.1Ibuprofen 13 47.1 26.9 0 3.5Naproxen 3 87.9 2.8 0 0.4Acetaminophen 45 N.D. N.D. 100 N.D.Bisphenol-A 0.6 99.7 3.5 100 0.1Chlorophene 0.6 71.7 5.9 100 0.1Triclosan 1 53.8 24 100 0.2Fluoxetine 178 86.1 7 84.7 25.8Caffeine 24 2.8 3.6 100 107.1* Based on a 2µL injection from a 1mL extract of a 8L sample.
Field SamplingField Sampling
1 - Mississippi River2 - Lake Pontchartrain3 - Tulane University4 – Jeff. Parish WTP5 – Jeff. Parish WWTP
Field SamplingField SamplingJeff. Par. WWTP & Miss. River, LAJeff. Par. WWTP & Miss. River, LA
ClCl22
WWTP1WWTP1PrimaryPrimary
ClarificationClarification
AerationAeration
BasinBasin
SecondarySecondary
ClarificationClarificationSamplingSampling
SiteSite JP1JP1
MississippiMississippi
RiverRiver
Results Results Jeff. Par. WWTP & Miss. River, LAJeff. Par. WWTP & Miss. River, LA
Sampling Site
date 3/14/02 3/14/02 9/14/01 9/24/01Target Compound ng/L ng/L ng/L ng/LClofibric acid N.D. N.D. N.D. N.D.Ibuprofen N.D. N.D. N.D. N.D.Acetaminophen N.D. N.D. N.D. N.D.Caffeine N.D. N.D. N.D. N.D.Fluoxetine N.D. N.D. N.D. N.D.Chlorophene N.D. N.D. N.D. N.D.Naproxen 106 81 37 39Triclosan 21 10 N.D. N.D.Bisphenol-A N.D. N.D. N.D. N.D.Estrone N.D. N.D. N.D. N.D.17β -Estradiol N.D. N.D. N.D. N.D.Bisphenol-A-d14* 13.6% 13.9% 68.0% 75.0%Estrone-d4* 52.6% 28.9% 103.4% 119.4%Acetaminophen-d4* 1.1% 1.2% N.D. N.D.* surrogate std. recovery , N.D. not detected, N.Q. not quantifiable
Jeff. Par. WWTPeffluent (WWTP1)
Miss . Rivershore (JP1)
Observations Observations Jeff. Par. WWTP & Miss. River, LAJeff. Par. WWTP & Miss. River, LA
Low concentrations of Low concentrations of –– naproxen (81naproxen (81--106 106 ngng/L)/L)–– triclosan (10triclosan (10--21 21 ngng/L) /L) were detected in effluent at JPWWTP.were detected in effluent at JPWWTP.
Low concentrations of Low concentrations of –– naproxen (37naproxen (37--39 39 ngng/L) /L) were detected in raw Miss. River water were detected in raw Miss. River water
in New Orleans. in New Orleans.
Field SamplingField SamplingJefferson Parish WTP, LAJefferson Parish WTP, LA
MississippiMississippi
RiverRiver
JP1JP1Coag/FlocCoag/Floc
SedimentSediment
Filtration &Filtration &
StorageStorage
DistributionDistribution
SystemSystem
PACPAC ClCl22
JP2JP2 JP3JP3
NHNH22ClCl
ResultsResultsJefferson Parish WTP, LAJefferson Parish WTP, LA
2/14/02 2/28/02 2/14/02 2/28/02 2/14/02 3/28/02Target Compound ng/L ng/L ng/L ng/L ng/L ng/LClofibric acid N.D. N.D. N.D. N.D. N.D. N.D.Ibuprofen N.D. N.D. N.D. N.D. N.D. N.D.Acetaminophen N.D. N.D. N.D. N.D. N.D. N.D.Caffeine N.D. N.D. N.D. N.D. N.D. N.D.Fluoxetine N.D. N.D. N.D. N.D. N.D. N.D.Chlorophene N.D. N.D. N.D. N.D. N.D. N.D.Naproxen 64 65 63 68 N.D. N.D.Triclosan N.D. N.D. N.D. N.D. N.D. N.D.Bisphenol-A N.Q. N.Q. N.Q. N.Q. N.Q. N.D.Estrone N.D. N.D. N.D. N.D. N.D. N.D.17β−Estradiol N.D. N.D. N.D. N.D. N.D. N.D.Bisphenol-A-d14* 62.8% 65.2% 46.0% 81.3% 94.9% 18.6%Estrone-d4* 130.1% 68.3% 118.1% 99.3% 106.7% 17.7%Acetaminophen-d4* 0.2% 0.2% 0.2% N.D. 0.1% N.D.* surrogate std. recovery , N.D. not detected, N.Q. not quantifiable
Jefferson Parish WTP, LAraw water (JP1) post conv. treat. (JP2) finished water (JP3)
Observations Observations Jefferson Parish WTP, LAJefferson Parish WTP, LA
Naproxen was detected in raw Miss. Naproxen was detected in raw Miss. River water (64River water (64--65 65 ngng/L)./L).
NaxproxenNaxproxen persisted after PAC and persisted after PAC and coag/floc/sedcoag/floc/sed (63(63--68 68 ngng/L)./L).
Naproxen was reduced (N.D) by Naproxen was reduced (N.D) by chlorination/chlorination/chloraminationchloramination..
Naproxen byproducts (?) Naproxen byproducts (?) –– more more research.research.
Comparison to USGS StudyComparison to USGS Study
KolpinKolpin, , et.al.et.al., EST, , EST, 20022002, v. 36, , v. 36, 12021202--1211.
Compound (Methods) USGS ng/L Tulane ng/LClofibric acid -- NDIbuprofen (3) <18 3.5*Acetaminophen (3) <9 NACaffeine (3) 68 NACaffeine (4) E 80 NAFluoxetine (3) <18 25.8*Chlorophene -- NDNaproxen -- 50Triclosan (4) <40 0.2*Bisphenol-A (4) E 60 0.1*Estrone (5) <5 0.4*17β-Estradiol (5) <5 0.1**Tulane's estimated MDL, -- not attemptedNA not applicable, ND not detected
1211.
St. St. FrancisvilleFrancisville, LA, LA
(100 miles north of N.O.)(100 miles north of N.O.)
Comparison to USGS StudyComparison to USGS Study
St. St. FrancisvilleFrancisville (USGS) is about 100 miles upstream (USGS) is about 100 miles upstream from New Orleans (Tulane).from New Orleans (Tulane).Tulane and USGS agree (<DL): Tulane and USGS agree (<DL): –– IbuprofenIbuprofen–– FluoxetineFluoxetine–– TriclosanTriclosan–– EstroneEstrone–– 1717ββ--EstradiolEstradiol
For For BisphenolBisphenol--A,A,–– Tulane reported <0.1 Tulane reported <0.1 ngng/L/L–– USGS reported 60 USGS reported 60 ngng/L (estimated) /L (estimated)
USGS applied several analytical methods whereas USGS applied several analytical methods whereas Tulane applied one method.Tulane applied one method.
Field SamplingField SamplingA.H. Weeks WTP, ONA.H. Weeks WTP, ON
OO33 ClCl22
Coag/FlocCoag/Floc
SedimentSediment
Filtration &Filtration &
StorageStorageWO1WO1WO2WO2
DistributionDistribution
SystemSystemDetroitDetroit
RiverRiver
Results Results A.H. Weeks WTP, ONA.H. Weeks WTP, ON
Detroit River finished water(WO1) (WO2)
Target Compound ng/L ng/LClofibric acid 103 N.D.Ibuprofen N.D. N.D.Acetaminophen N.D. N.D.Caffeine N.D. N.D.Fluoxetine N.D. N.D.Chlorophene N.D. N.D.Naproxen 63 N.D.Triclosan N.D. N.D.Bisphenol-A N.Q. N.Q.Estrone N.D. N.D.17β -Estradiol N.D. N.D.Bisphenol-A-d14* 66.7% 93.6%Estrone-d4* 77.2% 90.7%Acetaminophen-d4* N.D. 0.2%* surrogate std. recovery , N.D. not detected, N.Q. not quantitated
A.H. Weeks WTP (2/14/2002)
Observations Observations A.H. Weeks WTP, ONA.H. Weeks WTP, ON
ClofibricClofibric acid (103 acid (103 ngng/L) and /L) and naproxen (63 naproxen (63 ngng/L) were detected /L) were detected in raw Detroit River water.in raw Detroit River water.
ClofibricClofibric acid (N.D.) and acid (N.D.) and naxproxennaxproxen(N.D.) were reduced by (N.D.) were reduced by ozonationozonation, , coag/floc/sedcoag/floc/sed, and chlorination., and chlorination.
ClofibricClofibric acid and naproxen acid and naproxen byproducts (?) byproducts (?) –– more research.more research.
Field SamplingField SamplingENWIN Pilot WTP, ONENWIN Pilot WTP, ON
DetroitDetroit
RiverRiver
WO1WO1
Coag/FlocCoag/FlocSedimentSediment
Dual Media Dual Media Filter 1Filter 1
OO33
Raw Raw Water Water
StorageStorage
EN1EN1
Coag/FlocCoag/FlocSedimentSediment
Dual Media Dual Media Filter 2Filter 2
EN2EN2
Results Results ENWIN Pilot WTP, ONENWIN Pilot WTP, ON
Raw Water Finished Finished(WO1) (EN1) (EN2)
Target Compound ng/L ng/L ng/LClofibric acid 103 N.D. N.D.Ibuprofen N.D. N.D. N.D.Acetaminophen N.D. N.D. N.D.Caffeine N.D. N.D. N.D.Fluoxetine N.D. N.D. N.D.Chlorophene N.D. N.D. N.D.Naproxen 63 N.D. N.D.Triclosan N.D. N.D. N.D.Bisphenol-A N.Q. N.Q. N.Q.Estrone N.D. N.D. N.D.17β -Estradiol N.D. N.D. N.D.Bisphenol-A-d14* 66.7% 80.2% 91.5%Estrone-d4* 77.2% 82.1% 74.6%Acetaminophen-d4* N.D. N.D. N.D.
ENWIN Pilot WTP (2/14/2002)
* surrogate std. recovery , N.D. not detected, N.Q. not quantitated
Observations Observations ENWIN Pilot WTP, ONENWIN Pilot WTP, ON
ClofibricClofibric acidacid (N.D.) and (N.D.) and naxproxennaxproxen (N.D.) were (N.D.) were reduced by dual media reduced by dual media filtrations.filtrations.
Removal Removal mechanismsmechanismsand and byproductsbyproducts for for clofibricclofibric acid and acid and naproxen (?) naproxen (?) –– more more research.research.
ConclusionsConclusionsMethods DevelopmentMethods Development
A method has been developed for detection of a range of low level PPCP/EDC contaminants in raw and treated water.
The method is reliable for 9 target compounds:
Clofibric Acid Chlorophene Bisphenol AIbuprofen Naproxen EstroneFluoxetine Triclosan 17B-Estradiol
ConclusionsConclusionsOccurrence of EDCs/PPCPsOccurrence of EDCs/PPCPs
ClofibricClofibric acidacid was detected in was detected in –– Detroit River (ON)Detroit River (ON)
NaproxenNaproxen was detected in was detected in –– WWTP effluent (LA)WWTP effluent (LA)–– Mississippi River (LA)Mississippi River (LA)–– Detroit River (ON)Detroit River (ON)
TriclosanTriclosan was detected in WWTP effluent (LA)was detected in WWTP effluent (LA)BisphenolBisphenol--AA was detected but nonwas detected but non--quantifiablequantifiable–– Mississippi River (LA)Mississippi River (LA)–– Detroit River (ON)Detroit River (ON)
ConclusionsConclusionsOccurrence of EDC/PPCPsOccurrence of EDC/PPCPs
NQNQE60E60NQNQNDNDBisphenolBisphenol--AA
NDND<40<40NDND1010--2121TriclosanTriclosan
6363NANA3737--68688181--106106NaproxenNaproxen
103103NANANDNDNDNDClofibricClofibric acidacid
USGSUSGSTulaneTulaneDetroit Detroit RiverRiver
Mississippi RiverMississippi RiverJPWWTP JPWWTP EffluentEffluent
Compound Compound ((ngng/L)/L)
ConclusionsConclusionsTreatment ProcessesTreatment Processes
NaproxenNaproxen and and clofibricclofibric acidacid werewereNOT removed by NOT removed by coag/floc/sedcoag/floc/sedREMOVED by oxidation (ClREMOVED by oxidation (Cl22 or Oor O33))REMOVED by dual media filtrationREMOVED by dual media filtration
ConclusionsConclusionsTreatment ProcessesTreatment Processes
NDNDNDNDEN2 (ON)EN2 (ON)
NDNDNDNDEN1 (ON)EN1 (ON)
NDNDNDNDWO2 (ON)WO2 (ON)
6363103103WO1 (ON)WO1 (ON)
NDNDNDNDJP3 (LA)JP3 (LA)
6363--6868NDNDJP2 (LA)JP2 (LA)
6464--6565NDNDJP1 (LA)JP1 (LA)
DMFDMFOO33ClCl22ConvConvNaproxen Naproxen
((ngng/L)/L)ClofibricClofibric
Acid (Acid (ngng/L)/L)Treatment Process*Treatment Process*Sampling Sampling
SiteSite
* * ConvConv –– Coag/Floc/SedCoag/Floc/Sed OO33 -- OzonationOzonation
ClCl22 –– ChlorinationChlorination DMF DMF –– Dual Media FiltrationDual Media Filtration
GC/MS Method for GC/MS Method for Determining the Occurrence and Determining the Occurrence and
Investigating Treatment Processes for Investigating Treatment Processes for Representative Representative EDCsEDCs and PPCPs in and PPCPs in Waters of Southeastern LouisianaWaters of Southeastern Louisiana
Glen R. Boyd, Ph.D., P.E. Helge Reemtsma
Dept. of Civil and Environmental Engineering
Deborah A. Grimm, Ph.D.Coordinated Instrumentation Facility
Tulane University, New Orleans, LA