본 연구는 낙동강 하류역 강하먼지의 조성 특성을 파악하기 위하여, 광구병형 Dust jar를 사용하여 2002년 6월부터 2003년 5월까지 1년간 낙동강 하류역의 5개 지점에서 시료를 채취하였다. 채취된 강하먼지에 함유된 불용성 성분(Al, Ca, Cd, Cr, Cu, Fe, K, Mg, Mn, Na, Ni, Pb, Si, V, Zn) 및 수용성 성분(Cl-, NO3-, SO42-, NH4+, Ca2+, K+, MG2+)들은 ICP/AES, AAS, IC 및 UV를 이용하여 정량하었다. 성분에 대한 지각농축계수를 지역별로 비교한 결과 인위적인 오염원인 Cd, Cu, Pb, Zn에서 10 이상의 높은 값을 보였다. 특히 Pb는 감전동, 원동, 신라대, 삼랑진 및 물금 지점 순으로 감소하는 것으로 조사되었다. 계절별 토양입자의 기여율은 겨울철에 16.3 %로서 가장 높았으며, 1년간 평균 기여율은 11.2%이었다. 계절별[SO42-/NO3-] 당량비는 겨울철(5.12)이 가장 높았고, 가을철(3.30)이 가장 낮게 나타났다. 지역별로는 신라대, 감전동, 물금, 원동 및 삼랑진 순으로, 특히 도심에 인접한 지점의 경우가 높게 나타났으며, 평균 당량비는 4.28이었다. 총 강하먼지에 대한 수용성 이온성분의 총 침적량의 비율은 봄철(71.6%), 여름(61.2%), 가을(49.2%) 및 겨울철(48.6%)의 순으로 나타났으며, 평균은 57.6%이었다. 해염입자의 지역별 기여율 분포는 신라대(34.5%), 감전동(28.3%), 원동(17.3%), 삼랑진(17.2%) 및 물금(13.8%)의 순으로 나타났으며, 평균 기여율은 22.1%로 나타났다.

Weather elements were observed by the AWS (Automatic Weather System) and dustfall particles were collected by the modified American dust jar (wide inlet bottle type) at 4 sampling sites in Busan area from March, 1999 to February, 2000. Thirteen chemical species (Al, Ca, Cd, Cr, Cu, Fe, K, Mg, Mn, Ni, Pb, Si, and Zn) were analyzed by AAS and ICP. The purposes of this study were to estimate qualitatively various bulk deposition flux of dustfall and insoluble components by applying regional and seasonal wind intensity. Frequency of wind speed were found in order of low(1-3㎧), very low(<1㎧), medium(3-8㎧) and high(>8㎧), and annual mean had higher range at low(1-3㎧) for 56.3%. Strong negative linear correlation were observed between dustfall and wind direction (northeastern and eastern), but strong positive linear correlation were observed between dustfall and wind direction (western and northwestern) at industrial, commercial and coastal zone(p<0.05). While a negative correlation were observed between wind speed frequency of very low(<1㎧) and dustfall, and positive correlation were observed between wind speed frequency of low(1-3㎧) and dustfall in coastal zone(p<0.05). The correlation coefficient was observed 0.556 between wind speed frequency of low(1-3㎧) and Ni by commercial zone(p<0.05). The correlation coefficient show well-defined insoluble trace metals (Al, Ca, Cr, Cu, Fe, Pb, and Zn) and wind speed frequency of low(1-3㎧) at coastal zone, which was found significant difference(p<0.01).

Dustfall particles were collected by the modified American dust jar (wide inlet bottle type) at 6 sampling sites in Pusan area from March, 1999 to February, 2000. Thirteen chemical species (Al, Ca, Cd, Cr, Cu, Fe, K, Mg, Mn, Ni, Pb, Si, and Zn) were analyzed by AAS and ICP. The purposes of this study were to estimate qualitatively various bulk deposition flux of dustfall and insoluble components by applying regional and seasonal distribution. Dustfall amount of regional variations were found in order of coastal zone, industrial zone, commercial zone, agricultural zone and residential zone, and seasonal total dustfall had higher concentrations during spring for 6.741 ton/㎢/season, lower concentrations during summer for 1.989 ton/㎢/season, and annual total concentration was 17.742 ton/㎢/year. The regional distributions of enrichment factor show well-defined anthropogenic metals (Cd, Cu, Pb, and Zn) at industrial and agricultural zone, and contribution rate of soil particles were found in order of summer, fall, winter and spring. Factor loading effects of chemical composition of dustfall were found in order of road traffic emission source and combustion processed source, industrial activity source, soil source and marine source.

In order to investigate the characteristics of dustfall at eight sites in Pusan, the dustfall samples were collected with dust jar method from May to September 1995, and Cr, Mn, Fe, Ni, Cu, Zn, Cd and Pb were analyzed. The main results of this study are summarized as follows; 1) The total mean value of dustfall was 11.30 ton/℃/month. 2) The maximum and minimum values of dustfall were industrial and resident area respectively. 3) The dustfall showed the general trend in order as May>Jun>September>July. 4) The general trend of the heavymetals in dustfall was in order as Fe>Cu>Zn>Pb>Ni>Cd>Cr>Mn and the concentrations of heavymetals had different tendencies according to sources of pollutant meterials. 5) The Concentrations of Fe, Cu, Pb, Ni, Cd and Cr in industrial area and Mn, Pb and Zn in traffic area were high. The concentrations of heavymetals in residence area and unpolluted area were generally low. 6) Cr, Cu and Cd were influenced by the steel industry and the metal products plant and Zn was influenced by the automobils. Mn, Fe and Ni were influenced by the soil as wel as artificial outlet. 7) The correlation between the total amount of dustfall and the concentrations of the heavymetals by month was high and the correlation between the heavymetals of the same origin was high.