Humic-like substances (HULIS) is a class of unresolved organic compounds in
atmospheric aerosols. HULIS is operationally defined by its isolation procedure in this work
to be the hydrophobic part of the water-soluble organic carbon (WSOC) fraction. HULIS
account for a significant fraction of PM
2.5. This thesis work aims to improve the scientific
understanding of HULIS in PM
2.5, focusing on source apportionment and molecular
characterization of HULIS in the atmosphere of the Pearl River Delta (PRD), China. The
main findings are summarized below:
Positive matrix factorization (PMF) analyses were used to investigate sources of HULIS
carbon (HULIS-C) at three sites in the Pearl River Delta (PRD): an urban site Guangzhou
(GZ) and a suburban site Nansha (NS) in the PRD, and an urban...[
Read more ]
Humic-like substances (HULIS) is a class of unresolved organic compounds in
atmospheric aerosols. HULIS is operationally defined by its isolation procedure in this work
to be the hydrophobic part of the water-soluble organic carbon (WSOC) fraction. HULIS
account for a significant fraction of PM
2.5. This thesis work aims to improve the scientific
understanding of HULIS in PM
2.5, focusing on source apportionment and molecular
characterization of HULIS in the atmosphere of the Pearl River Delta (PRD), China. The
main findings are summarized below:
Positive matrix factorization (PMF) analyses were used to investigate sources of HULIS
carbon (HULIS-C) at three sites in the Pearl River Delta (PRD): an urban site Guangzhou
(GZ) and a suburban site Nansha (NS) in the PRD, and an urban site Tsuen Wan (TW) in
Hong Kong, utilizing PM
2.5 chemical composition and source markers data. HULIS-C sources
were found to include secondary formation processes, biomass burning (BB), coal
combustion and ship emission which was identified for the first time as a significant source of
HULIS-C. Secondary formation processes contributed 42-79% (seasonal average) of ambient
HULIS-C in different seasons. BB emissions contributed 6-27% (seasonal average), with the
highest percentages in winter. Coal combustion could be apportioned at GZ and NS,
contributing 6-20% (seasonal average). Ship emission was revealed to be an important source
in summer (38% of HULIS-C at NS and 26% at TW). Vehicle emissions were found to
contribute little to HULIS-C.
Sources of HULIS were also investigated using radiocarbon (
14C) analysis for
unambiguous differentiation of fossil and contemporary carbon origins. A set of 8 samples in
winter and 9 samples in summer was selected from the 184 PM
2.5 samples based on PMF
results. The contemporary and fossil fractions of primary and secondary HULIS-C were
calculated by coupling
14C analysis and PMF results. On average, fossil carbon sources
contributed 60±15% to HULIS-C, and contemporary carbon sources contributed 40±15%. In
the winter samples, 81% of fossil source HULIS-C was borne from secondary processing, which is hypothesized as the precursors from fossil fuel burning transported in by the
northerly wind in winter. In the summer samples, 87% of contemporary HULIS-C was borne
from secondary processing mostly as biogenic secondary organic aerosol. This work
highlights the importance of both anthropogenic and biogenic precursor emissions for HULIS
in PM
2.5 in PRD.
The molecular composition of HULIS was characterized using Fourier Transform Ion
Cyclotron Resonance Mass Spectrometry (FT-ICR MS), an ultrahigh resolution mass
spectrometry (UHRMS). Based on the accurate mass measurements obtained with UHRMS,
molecular formulas were assigned and potential compound groups are identified. HULIS from
two BB source samples (rice straw and sugarcane leaves) and ten GZ and NS ambient
samples were analyzed. CHOS- and CHONS- formulas (possibly organosulfates (OS) and
nitrooxy-OS) dominated the ambient samples, while CHO- formulas dominated BB source
samples. CHN+ formulas (possibly alkaloids) were abundant in rice straw burning. Ambient
samples had significantly fewer CHN+ formulas. The differences between the ambient and
BB source samples highlight the importance of secondary formation of HULIS. OS
homologous series of different DBE values were discovered, indicating OS precursors from
saturated alkanes, biogenic VOCs and anthropogenic aromatic VOCs. Half of CHN+
formulas in ambient samples were also found in rice straw burning, indicating biomass
burning could be a source contributing to this group of compounds in ambient samples.
Size distribution of CHOS- and CHONS- (0.056-18 μm) in HULIS was investigated to
provide hints of formation pathways of OS. Size-segregated samples were analyzed by the
Orbitrap MS (also an UHRMS) coupled with negative ESI. OS derived from biogenic volatile
organic compounds (e.g. isoprene, α-/β-pinene, limonene) share a common characteristic with
sulfate in that the droplet mode dominated, peaking in either the 0.56-1.0 or 1.0-1.8 μm size
bin, reflecting sulfate as their common precursor. Most of these OSs have a minor coarse
mode, accounting for 0-45%. The presence of OSs on coarse particles is hypothesized to be a
result of OSs on small particle (<0.32 μm) coagulating with coarse particles.
Comparison of formulas identified by FT-ICR and Orbitrap MS was conducted by
analyzing BB HULIS samples and a GZ ambient HULIS sample on both instruments. Fewer
formulas were detected by Orbitrap than FT-ICR for the GZ ambient sample. It was revealed
that un-optimized mass detection sensitivity and inability to differentiate multiple formulas as
the causes for the smaller number of formulas obtained with Orbitrap.
Post a Comment