Probing Legacy and Alternative Flame Retardants in the Air of Chinese Cities
China
Chemical Sciences not elsewhere classified
PM
Immunology
Chinese Cities
alternative flame retardants
PBDE
01 natural sciences
FR assessment
DP
North China Plain
alternative FRs
Environmental Sciences not elsewhere classified
Halogenated Diphenyl Ethers
DBDPE
FR patterns
Cities
12 organophosphate FRs
OA
Cancer
Flame Retardants
0105 earth and related environmental sciences
Ecology
novel brominated FRs
1 order
BDE 209
mass-normalized concentration
Organophosphates
polybrominated diphenyl ether
13. Climate action
NCP
Medicine
brominated FRs
Gas-particle partitioning analysis
Biotechnology
Developmental Biology
Biological Sciences not elsewhere classified
2018. OPFRs
NBFR
Environmental Monitoring
DOI:
10.1021/acs.est.0c07367
Publication Date:
2021-03-23T12:32:55Z
AUTHORS (11)
ABSTRACT
An increasing number of alternative flame retardants (FRs) are being introduced, following the international bans on the use of polybrominated diphenyl ether (PBDE) commercial mixtures. FRs' production capacity has shifted from developed countries to developing countries, with China being the world's largest producer and consumer of FRs. These chemicals are also imported with e-waste to China. Therefore, it is important to understand the current status of regulated brominated FRs, their phase-out in China, and their replacement by alternatives. In this study, a broad suite of legacy and alternative FRs, including eight PBDEs, six novel brominated FRs (NBFRs), two dechlorane plus variants (DPS), and 12 organophosphate FRs (OPFRs) were evaluated in the air of 10 large Chinese cities in 2018. OPFRs are the most prevalent FRs in China, exhibiting a wide range of 1-612 ng/m3, which is several orders of magnitude higher than PBDEs (1-1827 pg/m3) and NBFRs (1-1428 pg/m3). BDE 209 and DBDPE are the most abundant compounds in brominated FRs (>80%). The North China Plain (NCP, excluding Beijing), Guangzhou, and Lanzhou appear to be three hotspots, although with different FR patterns. From 2013/2014 to 2018, levels of PBDEs, NBFRs, and DPs have significantly decreased, while that of OPFRs has increased by 1 order of magnitude. Gas-particle partitioning analysis showed that FRs could have not reached equilibrium, and the steady-state model is better suited for FRs with a higher log KOA (>13). To facilitate a more accurate FR assessment in fine particles, we suggest that, in addition to the conventional volumetric concentration (pg/m3), the mass-normalized concentration (pg/g PM2.5) could also be used.
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