atmospheric pahs determination: influence of the air
TRANSCRIPT
ATMOSPHERIC PAHs DETERMINATION: ATMOSPHERIC PAHs DETERMINATION:
INFLUENCE OF THE AIR SAMPLING TIME INFLUENCE OF THE AIR SAMPLING TIME
PROGRAM IN THE OCCURRENCE OF PROGRAM IN THE OCCURRENCE OF
ARTIFACTSARTIFACTS
A&WMA International Specialty Conference: A&WMA International Specialty Conference:
Leapfrogging Opportunities for Air Quality ImprovementLeapfrogging Opportunities for Air Quality Improvement
CHINA, May 2010CHINA, May 2010
FRANCISCO CERECEDAFRANCISCO CERECEDA--BALICBALIC, V, Vííctor Vidal, ctor Vidal,
Juan Luis Guevara and NicolJuan Luis Guevara and Nicoláás Schiappacasse,s Schiappacasse,
LABORAT
ORIO DE QUIMIC
A AMBIENTA
L
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
INTRODUCTIONINTRODUCTION
PAHsPAHs ((PPolycyclic olycyclic AAromatic romatic HHydrocarbons )ydrocarbons )
Naftaleno
PirenoBenzo (c) fenantreno
Coroneno
S
Benzonaftotiofeno Benzo(a)pireno
One of the greatest challenges in air pollution research, especiOne of the greatest challenges in air pollution research, especially which is ally which is
focuses on the study of PAHs, is the development of systems and focuses on the study of PAHs, is the development of systems and sampling sampling
procedures to obtain more accurate, reliable and representative procedures to obtain more accurate, reliable and representative information about information about
concentrations of these compounds and their variation in timeconcentrations of these compounds and their variation in time
SAMPLING ARTIFACTSSAMPLING ARTIFACTS
PAHPAHPAHPAHPAHPAHPAHPAH’’’’’’’’s +s +s +s +s +s +s +s +
•• NONONONONONONONOXXXXXXXX
•• OOOOOOOO33333333
•• ACID GASES AND OACID GASES AND OACID GASES AND OACID GASES AND OACID GASES AND OACID GASES AND OACID GASES AND OACID GASES AND O33333333
NITRONITRONITRONITRONITRONITRONITRONITRO--------PAHPAHPAHPAHPAHPAHPAHPAH’’’’’’’’ssssssss
OXYOXYOXYOXYOXYOXYOXYOXY--------PAHPAHPAHPAHPAHPAHPAHPAH’’’’’’’’ssssssss
HIGHLY POLAR HIGHLY POLAR HIGHLY POLAR HIGHLY POLAR HIGHLY POLAR HIGHLY POLAR HIGHLY POLAR HIGHLY POLAR
COMPOUNDSCOMPOUNDSCOMPOUNDSCOMPOUNDSCOMPOUNDSCOMPOUNDSCOMPOUNDSCOMPOUNDS
Atmospheric Environment, 33, 4977-4986 (1999)Chemosphere, 62, 1889-1898 (2006)
J. Atmospheric Environment, 29(19), 2575-2584 (1995)
•• REACTIONS OF PAHREACTIONS OF PAHREACTIONS OF PAHREACTIONS OF PAHREACTIONS OF PAHREACTIONS OF PAHREACTIONS OF PAHREACTIONS OF PAH’’’’’’’’s WITH COMPOUNDS PRESENT IN s WITH COMPOUNDS PRESENT IN s WITH COMPOUNDS PRESENT IN s WITH COMPOUNDS PRESENT IN s WITH COMPOUNDS PRESENT IN s WITH COMPOUNDS PRESENT IN s WITH COMPOUNDS PRESENT IN s WITH COMPOUNDS PRESENT IN
THE AIRTHE AIRTHE AIRTHE AIRTHE AIRTHE AIRTHE AIRTHE AIR
PROBLEMS IN PROBLEMS IN SAMPLING PROCEDURES SAMPLING PROCEDURES
•• EXCHANGE OF PAHs BETWEEN GASEOUS AND EXCHANGE OF PAHs BETWEEN GASEOUS AND EXCHANGE OF PAHs BETWEEN GASEOUS AND EXCHANGE OF PAHs BETWEEN GASEOUS AND EXCHANGE OF PAHs BETWEEN GASEOUS AND EXCHANGE OF PAHs BETWEEN GASEOUS AND EXCHANGE OF PAHs BETWEEN GASEOUS AND EXCHANGE OF PAHs BETWEEN GASEOUS AND
PARTICULATE PHASESPARTICULATE PHASESPARTICULATE PHASESPARTICULATE PHASESPARTICULATE PHASESPARTICULATE PHASESPARTICULATE PHASESPARTICULATE PHASES
Atmospheric Environment, 33, 4977-4986 (1999)Chemosphere, 49(3), 331-340 (2002)
PAH’s
GASEOUS
PHASE
ADSORBED PAH’s
-
+
FILTER
SURFACE
PMPMPMPM
• Artifact negative: some of the particulate organic compounds
is volatilized
• Artifact positive: a portion of the
organic vapor phase is adsorbed onto the filter surface
or onto the deposited particulate matter
THE OBJECTIVE OF THIS WORK WAS: TO THE OBJECTIVE OF THIS WORK WAS: TO
DETERMINATE A SAMPLING TIME PROGRAM DETERMINATE A SAMPLING TIME PROGRAM
THAT SATISFIES THE FOLLOWING CONDITIONS:THAT SATISFIES THE FOLLOWING CONDITIONS:
GOALGOAL
�� Collect enough PAHs amount to be Collect enough PAHs amount to be
measurable by GCmeasurable by GC--FID and GCFID and GC--MSMS
�� Minimize the occurrence of sampling Minimize the occurrence of sampling
artifacts, and generate a representative artifacts, and generate a representative
sample for a 24 hour periodsample for a 24 hour period
SSampling site: Santiago de Chile, ampling site: Santiago de Chile,
Metropolitan RegionMetropolitan Region
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
Sampling MethodologySampling Methodology
Parque O'Higgins monitoring station is located in Parque O'Higgins monitoring station is located in
downtown Santiago. It is placed in a large park downtown Santiago. It is placed in a large park
about 2 km south of the city downtown and 1 km about 2 km south of the city downtown and 1 km
west of a major highway with traffic of about west of a major highway with traffic of about
60,000 vehicles per day60,000 vehicles per day
Sampling System OutlineSampling System Outline
Speciation Sampler Partisol 2300 (R&P)Speciation Sampler Partisol 2300 (R&P)
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
Inlet AirInlet AirOutlet AirOutlet Air
12
3
4
56
7
8
PAHs in PAHs in
Gaseous phaseGaseous phase
PUF PUF
PAHs absorbed/PAHs absorbed/
adsorbed onadsorbed on
particulate matterparticulate matter
FILTERFILTER
Sampling Times Program (STP)Sampling Times Program (STP)
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
Qualitative and quantitative determinationQualitative and quantitative determination
of PAHs (PM + gas phase)of PAHs (PM + gas phase)
SamplingSampling ExtractionExtraction Evaporation/ Evaporation/
concentrationconcentrationPurificationPurification
(clean(clean--up)up)
IdentificationIdentification
PM phasePM phase
Gaseous phaseGaseous phase
QuantificationQuantification
MultiMulti--step Environmental Analytical Process step Environmental Analytical Process
Real Samples ChromatogramsReal Samples Chromatograms
of PAHs, (Filter and PUF)of PAHs, (Filter and PUF)
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
PUFPUF(escale 20 a 200 mV)(escale 20 a 200 mV)
FilterFilter(escale 20 a 200 mV)(escale 20 a 200 mV)
Total PAH concentration obtained at Total PAH concentration obtained at
different Sampling Times Programdifferent Sampling Times Program
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
EQUIVALENT EQUIVALENT
SAMPLING SAMPLING
PROGRAMSPROGRAMS
SAMPLING SAMPLING
PROGRAMS WITH PROGRAMS WITH
MORE ARTIFACTSMORE ARTIFACTS
Regression analysisRegression analysis
RegressionRegression
analysisanalysis
Hypothetical Hypothetical
equivalence equivalence
case a = 1case a = 1
1.25381.2538
0.31290.3129= 4.04.0
•• Were made a concentration analysis of atmospherics Were made a concentration analysis of atmospherics
samples of HAPs, obtained in a urban sampling station and samples of HAPs, obtained in a urban sampling station and
performed with three different STPperformed with three different STP
•• A significant sampling artifact was found when sampler A significant sampling artifact was found when sampler
works continuously for 24 hoursworks continuously for 24 hours
•• Statistical analysis showed that concentrations of PAHs Statistical analysis showed that concentrations of PAHs
obtained with longer time sampling ( 24 chr) are 4 times obtained with longer time sampling ( 24 chr) are 4 times
lower than those found at 1hr/6hr or 10min/1hrlower than those found at 1hr/6hr or 10min/1hr
•• 1hr/6hr or 10min/1hr are equivalents; nevertheless to get a 1hr/6hr or 10min/1hr are equivalents; nevertheless to get a
wider picture of the variation of pollutants through the day wider picture of the variation of pollutants through the day
(eg PAHs) it is proposed that the program of 10min/1hr is (eg PAHs) it is proposed that the program of 10min/1hr is
the most appropriatethe most appropriate
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
ConclusionsConclusions
ACKNOWLEDGEMENTSACKNOWLEDGEMENTSCollaborators in this work Collaborators in this work •• Environmental Chemistry LaboratoryEnvironmental Chemistry Laboratory
Environmental Technology CentreEnvironmental Technology Centre
UTFSMUTFSM
•• School of Environmental Engineering, School of Environmental Engineering,
Catholic University of TemucoCatholic University of Temuco
FONDECYT project 1070500FONDECYT project 1070500
FONDEF project D02FONDEF project D02--II--10054 10054
Proyecto Interno DGIP UTFSM NProyecto Interno DGIP UTFSM Nºº 130625130625
Secretaria Regional Miniterial de Salud del la RegiSecretaria Regional Miniterial de Salud del la Regióón n MetropolitanaMetropolitana”” (SEREMI de Salud RM) of the Health (SEREMI de Salud RM) of the Health MinistryMinistry
VVííctor Vidalctor Vidal
Juan Luis GuevaraJuan Luis Guevara
NicolNicoláás Schiappacasse s Schiappacasse
PUF Cleaning comparison between AutoExtractPUF Cleaning comparison between AutoExtract--PUFPUF®®
and Soxhlet extraction (EPAand Soxhlet extraction (EPA--TO13A) with GCTO13A) with GC--FIDFID
AutoExtractAutoExtract--PUF BlankPUF Blank(escale 0 a 150 mV)(escale 0 a 150 mV)
Soxhlet Blank Soxhlet Blank (escale 0 a 150 mV)(escale 0 a 150 mV)
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
PUFPUF
Before cleaningBefore cleaning(escale (escale --15 a 700 mV)15 a 700 mV)
PUFPUF
After cleaningAfter cleaning(escale (escale --15 a 700 mV)15 a 700 mV)
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
Comparison between before and after PUF cleaningComparison between before and after PUF cleaning
procedure wit AutoExtractprocedure wit AutoExtract--PUFPUF®® (GC(GC--FID)FID)
Chromatogram of 1 Chromatogram of 1 µµll standard standard
of 16of 16--EPA HAPs (8 EPA HAPs (8 ng/ng/µµl)l)
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
Samples processing of PAHsSamples processing of PAHs
in gas phase and particulate matterin gas phase and particulate matter (MP(MP2,52,5))
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
Similar samples treatment Similar samples treatment
is made,is made,
but separately but separately
PUF extraction in a automatic PUF extraction in a automatic
pneumatic extraction systempneumatic extraction system
AutoExtract PUFAutoExtract PUF®®
PUFPUF
Polyurethane Polyurethane
foam filterfoam filter
PAHs ab/adsorbed on PAHs ab/adsorbed on
particulate matter particulate matter PAHsPAHs
in gas phasein gas phase
FILTERFILTER
teflon membraneteflon membrane
0,45 0,45 µµµµµµµµm m ∅∅∅∅∅∅∅∅ porepore
Filter extraction with Toluene Filter extraction with Toluene
during 1h using reflux systemduring 1h using reflux system
Extract filtration on specially Extract filtration on specially
designed vacuum systemdesigned vacuum system
®® Patent pendentPatent pendent
Laboratorio de QuLaboratorio de Quíímica Ambiental mica Ambiental -- UTFSMUTFSM Dr. Francisco CerecedaDr. Francisco Cereceda
Extract Concentration with rotary Extract Concentration with rotary
evaporatorevaporator
Evaporation under controlled Evaporation under controlled
nitrogen streamnitrogen stream
FILTERFILTER PUFPUF
Redisolution withRedisolution with
50 ul of Toluene50 ul of Toluene
Sample Clean Up on Sample Clean Up on
Silica Gel ColumnSilica Gel Column
chromatographicchromatographic
Identification Identification -- QuantificationQuantification
PAHs FractionPAHs Fraction
GCGC--FIDFIDGCGC--MSMS
Samples processing of PAHsSamples processing of PAHs
in gas phase and particulate matterin gas phase and particulate matter (MP(MP2,52,5))