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Source Apportionment Using Radiocarbon and Organic Tracers for PM2.5 Carbonaceous Aerosols in Guangzhou, South China: Contrasting Local- and Regional-Scale Haze Events

TLDR
Investigation of the atmospheric behavior of carbonaceous aerosols during hazy and normal days using radiocarbon ((14)C) and biomass burning/secondary organic aerosol (SOA) tracers during winter in Guangzhou, China found that haze episodes were formed either abruptly by local emissions or through the accumulation of particles transported from other areas.
Abstract
We conducted a source apportionment and investigated the atmospheric behavior of carbonaceous aerosols during hazy and normal days using radiocarbon (14C) and biomass burning/secondary organic aero...

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1
Source Apportionment Using Radiocarbon and Organic
Tracers for PM
2.5
Carbonaceous Aerosols in Guangzhou, South
China: Contrasting Local- and Regional-Scale Haze Events
Junwen Liu
1,4
, Jun Li
1*
, Yanlin Zhang
2
, Di Liu
1
, Ping Ding
3
, Chengde Shen
3
,
Kaijun Shen
1,4
, Quanfu He
1,4
, Xiang Ding
1
, Xinming Wang
1
, Duohong Chen
1
,
Sönke Szidat
2
, Gan Zhang
1
1
State Key Laboratory of Organic Geochemistry, Guangzhou Institute of
Geochemistry, Chinese Academy of Sciences, Guangzhou, 510640, China
2
Department of Chemistry and Biochemistry & Oeschger Centre for Climate
Change Research, University of Bern, Berne, 3012, Switzerland
3
State Key Laboratory of Isotope Geochemistry, Guangzhou Institute of
Geochemistry, Chinese Academy of Sciences, Guangzhou, 510640, China
4
University of Chinese Academy of Sciences, Beijing, 100049, China
*
Corresponding author
Acceptedversion
Publishedin
EnvironmentalScienceandTechnology48(2014)1200212011
http://dx.doi.org/10.1021/es503102w

2
Abstract 1
We conducted a source apportionment and investigated the atmospheric 2
behavior of carbonaceous aerosols during hazy and normal days using 3
radiocarbon (
14
C) and biomass burning/secondary organic aerosol (SOA) 4
tracers during winter in Guangzhou, China. Haze episodes were formed either 5
abruptly by local emissions or through the accumulation of particles transported 6
from other areas. The average contributions of fossil carbon to elemental 7
carbon (EC), water-insoluble organic carbon, and water-soluble organic carbon 8
were 71 ± 10%, 40 ± 6% and 33 ± 3%, respectively. High contributions of fossil 9
carbon to EC (8090%) were observed for haze samples that were 10
substantially impacted by local emissions, as were the highest (lowest) ratios 11
for NO
3
/SO
4
2
(OC/EC), which indicates that these particles mainly came from 12
local vehicle exhaust. Low contributions of fossil carbon to EC (6070%) were 13
found for haze particles impacted by regional transport. Secondary organic 14
carbon (SOC) calculated using SOA tracers accounts for only 20% of the SOC 15
estimated by
14
C, which is probably because some important volatile organic 16
carbons are not taken into account in the SOA tracer calculation method and 17
because of the large discrepancy in ambient conditions between the 18
atmosphere and smog chambers. A total of 33 ± 11% of the SOC was of fossil 19
origin, a portion of which could be influenced by humidity. 20
Keywords: Haze,
14
C, organic tracer, secondary organic carbon, PM
2.5
21

3
22
TOC 23

4
1 Introduction
Haze episodes in China occur frequently, causing extensive public and
scientific concern.
1,2
Haze particles exert a severe influence on not only human
health and air quality,
2
but also the climatic system.
3
The main cause of this
haze is the rapid or persistent enhancement of fine particle (PM
2.5
, i.e., particles
with an aerodynamic diameter less than 2.5 μm) concentrations in the air,
accompanied by relatively stable synoptic conditions. These PM
2.5
particles can
either be emitted from local sources or transported from other regions through
atmospheric movement.
Carbonaceous aerosols account for a large fraction of PM
2.5
particles
(2090%)
4
and are considered to be a vital constituent controlling the
formation and evolution of haze episodes. Extremely high concentrations of
carbonaceous aerosols (100 μg C/m
3
) have been recorded during typical
haze days in northern China,
5
as well as in southern
6
and central China.
7
Generally, carbonaceous aerosols can be categorized into organic carbon (OC)
and elemental carbon (EC) based on their thermal, chemical, and optical
properties. EC is emitted directly from incomplete combustion (e.g., wood fire,
traffic, and industry emissions) and is frequently used as a primary tracer due
to its inert physiochemical properties in the atmosphere. OC includes primary
sources of emission (e.g., biogenic sources, biomass burning, traffic, cooking,
industry, soil, etc.) and secondary organic carbon (SOC), which is formed by
the atmospheric oxidation of gaseous precursors.
4,8
Water-soluble organic

5
carbon (WSOC) mainly comprises compounds with polar functional groups,
such as polyols, and (poly-)carboxylic acids;
9
these chemicals are mainly
derived from primary biomass burning and SOC.
10,11
For episodes with limited
biomass burning activity, WSOC is frequently used as an SOC tracer.
10,12
Water-insoluble organic carbon (WIOC) includes alkanes, polycyclic aromatic
hydrocarbons, plant debris, and bacteria. Although carbonaceous aerosols play
an important role in air pollution and haze formation, knowledge of their
emission sources and atmospheric behavior (including the characteristics of
biomass vs fossil fuel emissions and the differences between primary and
secondary sources) are still poorly understood.
Radiocarbon (
14
C) measurements allow unambiguous differentiation between
fossil and nonfossil sources. The underlying principle of
14
C measurements is
that this radioisotope has become extinct in fossil fuel carbon, while its
contemporary level is relatively constant.
13,14
With a combination of organic
tracers, detailed source apportionments of carbonaceous aerosols can be
achieved via
14
C analysis. These data are very helpful to understand the
evolution mechanisms of haze and SOC in the real atmosphere, with an aim of
controlling pollutant emissions. So far, such studies are still scarce and have
mainly been conducted in developed countries in Europe
1518
or the United
States.
19,20
Only a few studies have been performed in Chinese cities
21,22
or
rural sites.
23,24
Guangzhou (23.1°N, 113.3°E) is the largest city in the subtropical zone of

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Journal ArticleDOI

Review on recent progress in observations, source identifications and countermeasures of PM2.5.

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Journal ArticleDOI

Haze, public health and mitigation measures in China: A review of the current evidence for further policy response

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References
More filters
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Organic aerosol and global climate modelling: a review

TL;DR: In this article, the authors reviewed existing knowledge with regard to organic aerosol (OA) of importance for global climate modelling and defined critical gaps needed to reduce the involved uncertainties, and synthesized the information to provide a continuous analysis of the flow from the emitted material to the atmosphere up to the point of the climate impact of the produced organic aerosols.
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Atmospheric aerosols: composition, transformation, climate and health effects.

TL;DR: The current state of knowledge, major open questions, and research perspectives on the properties and interactions of atmospheric aerosols and their effects on climate and human health are outlined.
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Levoglucosan, a tracer for cellulose in biomass burning and atmospheric particles

TL;DR: The major organic components of smoke particles from biomass burning are monosaccharide derivatives from the breakdown of cellulose, accompanied by generally lesser amounts of straight-chain, aliphatic and oxygenated compounds and terpenoids from vegetation waxes, resins/gums, and other biopolymers.

Secondary Organic Aerosol Formation from Anthropogenic Air Pollution: Rapid and Higher than Expected

TL;DR: This paper showed that reactive anthropogenic VOCs (AVOCs) produce much larger amounts of SOA than these models predict, even shortly after sunrise, and a significant fraction of the excess SOA is formed from first-generation AVOC oxidation products.
Related Papers (5)
Frequently Asked Questions (19)
Q1. What have the authors contributed in "Source apportionment using radiocarbon and organic tracers for pm2.5 carbonaceous aerosols in guangzhou, south china: contrasting local- and regional-scale haze events" ?

Li et al. this paper used a combination of organic tracers, detailed source apportionments of carbonaceous aerosols can be achieved via 14C analysis, which is very helpful to understand the evolution mechanisms of haze and SOC in the real atmosphere, with an aim of controlling pollutant emissions. 

Approximately 60−80% of the VOCs emitted by biomass burning are alkanes and alkenes,50 whose contribution to SOC can approach ∼20%.51,53 

Carbonaceous aerosols account for a large fraction of PM2.5 particles (∼20−90%)4 and are considered to be a vital constituent controlling the formation and evolution of haze episodes. 

13,14 With a combination of organic tracers, detailed source apportionments of carbonaceous aerosols can be achieved via 14C analysis. 

Since particles directly come from biomass burning show a characteristic of both high values of OC/EC and Lev/OC16, impact of biomass burning is suspected on the samples collected during Dec. 26-27, Dec. 11-12 and Jan. 17-18). 

15,37 Because EC is formed only by primary emission, is inert in ambient air and originates from wood burning or fossil fuel combustion only, fm(EC) particularly tracks the change of these PM2.5 sources. 

This city often suffers severe air pollution episodes: it has been reported that ∼150 days per year may be governed by haze particles in Guangzhou. 

46 Because fossil-derived VOCs are less polar and appear to be more hydrophobic than biogenic VOCs, competing effects may exist between the20   formation of OCf_sec and OCbio_sec due to changes in relative humidity. 

This suggests that both the scavenging effect of rain and dilution effect of wind have clear positive elimination influences on PM2.5 concentrations, as well as indirectly reflecting the high intensity of local PM2.5 emissions in Guangzhou. 

27,28 Eight samples representing different atmospheric conditions were selected to further analyze the 14C content of WIOC, WSOC, and EC, as well as secondary organic aerosol (SOA) tracers that could directly reflect atmospheric reactions. 

The relative contribution of OCf_sec to total SOC is 33 ± 11%, and the corresponding value for OCbio_sec is 67 ± 11%, demonstrating that VOCs derived from biogenic/biomass burning emissions are the dominant contributor to SOC in Guangzhou, despite the importance of fossil emissions. 

The average fm values for WSOC, WIOC, and EC were 0.71 ± 0.03, 0.64 ± 0.06, and 0.31 ± 0.11, respectively, suggesting that fossil fuel has the largest impact on EC, whereas WIOC and WSOC are affected more by nonfossil sources. 

Remote particles generally have a high proportion of SOC43 due to the longer-range atmospheric transport they experience (Figure 1). 

toluene accounted for only ∼20% of the total aromatic VOCs emitted from vehicles during a tunnel study conducted in a southern Chinese city. 

Of which samples GIG02, GIG06, GIG07, and GIG08 were collected during typical haze episodes with PM2.5 concentrations >100 μg/m3. 

Because EC is derived from only biomass burning (bb) and fossil fuel combustion, the fraction of nonfossil fuel EC is expressed as ECbb here. 

Biomass burning OC (OCbb) is frequently calculated as the ratio (OC/Lev)bb in fresh biomass burning aerosols on the basis that Lev is an prominent tracer for biomass burning tracer to its high concentration and stable physiochemical properties in the atmosphere. 

Because SOC values derived from SOA tracers (SOCM+I+β plus SOCA) accounted for only 14 ± 6% of the OC in this study and because this proportion seems to be much lower than that observed in previous studies conducted in winter in southern and northern China (30−60%),48,49 the authors assumed that the SOC values based on these SOA tracers is underestimated. 

10 However, these values are lower than those observed in European and American cities (∼70−85%);10,15,37 this variation is likely because more15   SOC is derived from fossil fuels in Guangzhou, given that WSOC is a good tracer for SOC in urban regions.