生态环境学报
生態環境學報
생태배경학보
ECOLOGY AND ENVIRONMENT
2009年
5期
1788-1792
,共5页
粒径分布%多环芳烃%累积量%TOC%北京
粒徑分佈%多環芳烴%纍積量%TOC%北京
립경분포%다배방경%루적량%TOC%북경
road dust%size distribution%PAHs%accumulation%Beijing
对北京城市不同道路类型的道路积尘进行了为期16个月的采样,分别分析了道路尘的粒径、多环芳烃及TOC.道路积尘的粒径呈三峰态分布,<75 μm部分的颗粒所占体积最大,>214 μm部分颗粒所占体积最小.>214 μm这部分颗粒中的多环芳烃质量分数最低,<75μm和75~214μm这两部分颗粒中多环芳烃的质量分数没有显著差异,但由于<75μm部分颗粒所占的体积和质量比例最大,这部分颗粒的多环芳烃累积量所占比例最高.不同道路的积尘粒径存在差异,海淀路和成府路机动车道的积尘颗粒相比自行车道和人行道的颗粒更粗.由于粒径分布的差异和多环芳烃质量分数的差异,不同类型道路的多环芳烃累积量的粒径分布呈现差异.多环芳烃质量分数和累积量的粒度分布也呈现季节差异,冬春季<75 μm颗粒中的多环芳烃质量分数最高,多环芳烃的累积量所占比例也较夏秋季高.在三个粒级中,TOC与多环芳烃质量分数均呈现显著的正相关.高比例的细颗粒及细颗粒中的多环芳烃使得道路积尘再悬浮进入大气以及随湿沉降进入地表径流的环境风险加大.
對北京城市不同道路類型的道路積塵進行瞭為期16箇月的採樣,分彆分析瞭道路塵的粒徑、多環芳烴及TOC.道路積塵的粒徑呈三峰態分佈,<75 μm部分的顆粒所佔體積最大,>214 μm部分顆粒所佔體積最小.>214 μm這部分顆粒中的多環芳烴質量分數最低,<75μm和75~214μm這兩部分顆粒中多環芳烴的質量分數沒有顯著差異,但由于<75μm部分顆粒所佔的體積和質量比例最大,這部分顆粒的多環芳烴纍積量所佔比例最高.不同道路的積塵粒徑存在差異,海澱路和成府路機動車道的積塵顆粒相比自行車道和人行道的顆粒更粗.由于粒徑分佈的差異和多環芳烴質量分數的差異,不同類型道路的多環芳烴纍積量的粒徑分佈呈現差異.多環芳烴質量分數和纍積量的粒度分佈也呈現季節差異,鼕春季<75 μm顆粒中的多環芳烴質量分數最高,多環芳烴的纍積量所佔比例也較夏鞦季高.在三箇粒級中,TOC與多環芳烴質量分數均呈現顯著的正相關.高比例的細顆粒及細顆粒中的多環芳烴使得道路積塵再懸浮進入大氣以及隨濕沉降進入地錶徑流的環境風險加大.
대북경성시불동도로류형적도로적진진행료위기16개월적채양,분별분석료도로진적립경、다배방경급TOC.도로적진적립경정삼봉태분포,<75 μm부분적과립소점체적최대,>214 μm부분과립소점체적최소.>214 μm저부분과립중적다배방경질량분수최저,<75μm화75~214μm저량부분과립중다배방경적질량분수몰유현저차이,단유우<75μm부분과립소점적체적화질량비례최대,저부분과립적다배방경루적량소점비례최고.불동도로적적진립경존재차이,해정로화성부로궤동차도적적진과립상비자행차도화인행도적과립경조.유우립경분포적차이화다배방경질량분수적차이,불동류형도로적다배방경루적량적립경분포정현차이.다배방경질량분수화루적량적립도분포야정현계절차이,동춘계<75 μm과립중적다배방경질량분수최고,다배방경적루적량소점비례야교하추계고.재삼개립급중,TOC여다배방경질량분수균정현현저적정상관.고비례적세과립급세과립중적다배방경사득도로적진재현부진입대기이급수습침강진입지표경류적배경풍험가대.
Road dust for different types of traffic roads was collected monthly for 16 months in Beijing. Size distribution of PAHs and TOC of road dust were investigated. The size distribution of road dust showed a trimodal spectrum. The particles of<75 μm and >214 μm constituted the highest and lowest percentage by volume, respectively. No significant difference was found for PAHs be-tween the fractions of<75 μm and 75~214 μm. While PAHs content was lowest in >214 μm fraction, <75 μm fraction contributed the highest percentage of total PAHs. Size distribution of dust was found to be different among different types of roads, and the sizes of dusts in vehicle lane of Haidian Road and Chengfu Road were larger than bicycle lane and sidewalk. As a result of the variations of PAHs content and size distribution of dust, the size distribution of accumulated PAHs varied among different types of roads. The size distributions of PAHs accumulation varied with seasons. For <75 μm fraction, the road dust had a higher PAHs content and con-tributed higher percentage of total PAHs in winter and spring. For all the three size fractions, TOC revealed a significant positive correlation with PAHs content.