中国环境科学
中國環境科學
중국배경과학
CHINA ENVIRONMENTAL SCIENCE
2014年
1期
219-224
,共6页
于英鹏%杨毅%刘敏%汪青%郑鑫%刘营
于英鵬%楊毅%劉敏%汪青%鄭鑫%劉營
우영붕%양의%류민%왕청%정흠%류영
上海%工业区%玻璃表面%多环芳烃%源解析
上海%工業區%玻璃錶麵%多環芳烴%源解析
상해%공업구%파리표면%다배방경%원해석
Shanghai%industrial zone%glass surface%polycyclic aromatic hydrocarbons (PAHs)%source apportionment
利用GC-MS对上海工业区玻璃表面16种优控多环芳烃(PAHs)进行了定量分析.结果表明,宝山工业区、吴泾化工区和金山化工区玻璃表面PAHs平均含量分别为10.66,16.48,31.94μg/m2,工业区附近对照点PAHs平均含量分别为2.7,8.86,4.18μg/m2.各采样点玻璃表面不同环数PAHs分布特征相似,以3环和4环PAHs为主,平均含量分别占∑16PAHs的25%和47%;其次为5环和6环PAHs,分别占∑16PAHs的14%和9%,最低为2环PAHs,仅占5%.单体PAH以Phe、Fluo、Py和Chry为主.源解析表明,玻璃表面PAHs主要来源于煤和焦炭燃烧,部分来源于石油燃烧.质量标准化毒性当量浓度范围在0.07~3.23μg/g之间,对毒性当量贡献最大的单体PAH分别是BaP,BbF,BkF,DahA.
利用GC-MS對上海工業區玻璃錶麵16種優控多環芳烴(PAHs)進行瞭定量分析.結果錶明,寶山工業區、吳涇化工區和金山化工區玻璃錶麵PAHs平均含量分彆為10.66,16.48,31.94μg/m2,工業區附近對照點PAHs平均含量分彆為2.7,8.86,4.18μg/m2.各採樣點玻璃錶麵不同環數PAHs分佈特徵相似,以3環和4環PAHs為主,平均含量分彆佔∑16PAHs的25%和47%;其次為5環和6環PAHs,分彆佔∑16PAHs的14%和9%,最低為2環PAHs,僅佔5%.單體PAH以Phe、Fluo、Py和Chry為主.源解析錶明,玻璃錶麵PAHs主要來源于煤和焦炭燃燒,部分來源于石油燃燒.質量標準化毒性噹量濃度範圍在0.07~3.23μg/g之間,對毒性噹量貢獻最大的單體PAH分彆是BaP,BbF,BkF,DahA.
이용GC-MS대상해공업구파리표면16충우공다배방경(PAHs)진행료정량분석.결과표명,보산공업구、오경화공구화금산화공구파리표면PAHs평균함량분별위10.66,16.48,31.94μg/m2,공업구부근대조점PAHs평균함량분별위2.7,8.86,4.18μg/m2.각채양점파리표면불동배수PAHs분포특정상사,이3배화4배PAHs위주,평균함량분별점∑16PAHs적25%화47%;기차위5배화6배PAHs,분별점∑16PAHs적14%화9%,최저위2배PAHs,부점5%.단체PAH이Phe、Fluo、Py화Chry위주.원해석표명,파리표면PAHs주요래원우매화초탄연소,부분래원우석유연소.질량표준화독성당량농도범위재0.07~3.23μg/g지간,대독성당량공헌최대적단체PAH분별시BaP,BbF,BkF,DahA.
Sixteen priority control polycyclic aromatic hydrocarbons (PAHs) on glass surface from major industrial areas in Shanghai were quantitatively analyzed by GC-MS. High levels of PAHs were observed. Average concentrations of PAHs from the Baoshan Industrial Zone, Wu Jing Chemical Industry Zone and Jinshan Chemical Industry Park were 10.66, 16.48, 31.94μg/m2, while those of control sites were 2.70, 8.86, 4.18μg/m2, respectively. The PAHs compositions were dominated by 3 and 4 rings PAHs, which accounted for 25% and 47% of Σ16PAHs, while 5 and 6 rings PAHs accounted for 14%and 9%ofΣ16PAHs, respectively, and 2 rings PAHs only accounted for 5%. The most abundant PAHs were phenanthrene, fluorene, pyrene and chrysene. The source apportionment showed that the PAHs mainly came from the combustion of coal and coke, and partly derived from petroleum sources. The concentration of BaPeq (benzo [a] pyrene equivalent) varied from 0.07 to 3.23 μg/g, and the major carcinogenic contributor of 16PAHs were benzo (a) pyrene, benzo (b) fluoranthene, benzo (k) fluoranthene, bibenzo (a,h) anthracene.