• 한국농림기상학회지
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• 제6권4호
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• pp.250-255
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• 2004

수원과 태안 지역에서 영농기간 중 강우의 화학적 특성을 알아보기 위하여 2002년 및 2003년 2년간 각각 69점 및 71점의 빗물을 채수하여 화학적 성분조성과 강우량을 고려한 가중평균(volume-weighted mean) 이온농도 변화를 조사한 결과는 다음과 같다. 조사 기간 중 pH별 강우 분포는 수원은 pH 5.0-5.6 범위가 가장 많았으며, 태안은 pH 4.5∼5.0 범위가 많았다. 연차별로는 수원지역은 2002년도에 비해 2003년도에 pH 5.6 이상의 강우 분포가 크게 줄어든 반면, pH 4.0∼5.0 범위의 강우가 증가하는 경향을 보였고, 태안지역은 pH 5.0 이상의 강우가 증가하고 pH 4.0∼5.0 범위의 강우 분포가 줄어드는 경향을 나타내었다. 강우의 산성도 중화는 강우량이 많은 시기가 다른 기간에 비해 낮게 나타났다 빗물의 EC 농도는 강우량이 많았던 7월 이후 낮은 농도를 보이다 강우량이 적었던 10월 이후 다시 증가하는 경향을 나타내었으며, 평균 농도는 지역별로 큰 차이를 보이지 않았다. 빗물중 양이온은 수원지역이 N $H_4$$^{+}$ > $H^{+}$ > $Ca^{2+}$ > $Mg^{2+}$ > $K^{+}$의 순이었으며, 태안지역은 $Ca^{2+}$ > N $H_4$$^{+}$ > $H^{+}$ > $K^{+}$ $Mg^{2+}$의 순으로 나타났다. 음이온은 수원지역이 S $O_4$$^{2-}$ > N $O_3$$^{-}$ > C $l^{-}$, 태안지역은 S $O_4$$^{2-}$ > C $l^{-}$ > N $O_3$$^{-}$ 순이었다. 빗물 중에 용존하는 sulfate의 평균 함량은 수원과 태안지역이 각각 130과 117 $\mu$eq $L^{-1}$이었으며, 총 sulfate 함량 중 nss-S $I_4$$^{2-}$ 함량은 수원과 태안 지역이 각각 89% 및 88%로 나타나 대부분이 인위적인 발생원에서 기인된 것으로 판단되었다.

• 한국토양비료학회지
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• 제42권5호
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• pp.336-340
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• 2009

최근 급속한 산업화가 진행되고 있는 중국의 편서풍 영향 하에 위치한 우리나라의 경우에는 장거리 이동에 따른 강우의 산성도 변화 및 예상되는 피해에 대한 대책 마련을 위하여 강우의 화학성에 대한 지속적인 모니터링이 필요하다. 태안지역 강우의 화학적 특성을 알아보기 위하여 2007년 4월부터 10월까지 19점의 빗물을 채수하여 pH 및 화학적 성분조성을 조사하였다. 강우량을 고려한 가중평균(volume-weighted mean) 이온농도 변화와 알카리성 물질들에 의한 빗물의 산성도 중화를 평가한 결과는 다음과 같다. 조사기간 중 평균 pH값은 4.9를 보였다. 빗물의 EC는 조사기간 평균 $32.9{\mu}S\;cm^{-1}$을 나타냈으며, 월별로는 9월에 $9.7{\mu}S\;cm^{-1}$로 조사기간 중 가장 낮은 값을 보였으며, 강우량이 가장 적었던 4월에 $91.4{\mu}S\;cm^{-1}$의 높은 수치를 나타내어 강우량 분포에 따른 EC의 계절적 특성을 보였다. 빗물의 조성에서 양이온 구성은 $Na^+$> $NH_4{^+}$ > $Ca^{2+}$ > $H^+$ > $Mg^{2+}$ > $K^+$의 순이었으며, $Na^+$와 $NH_4{^+}$가 전체 양이온 함량의 70% 이상을 차지하였다. 음이온은 $SO_4{^{2-}}$ > $NO_3{^-}$ > $Cl^{-}$ 순으로 $SO_4{^{2-}}$가 약 56%를 차지하였다. Sulfate의 조사기간 중 평균 함량은 $152.1{\mu}eq\;L^{-1}$ 이었다. 총 sulfate 함량 중 비해염 sulfate $(nss-SO_4)^-$ 함량은 평균 90%로 빗물 중에 함유된 sulfate의 대부분이 인위적인 발생원에서 기인되었다. 또한, 강우 산성도의 중화 정도를 알아보기 위하여 평가한 fractional acidity (pAi) 및 theoretical acidity ($pH_{the}$.) pH를 비교한 결과 1:1 직선의 오른쪽으로 분포되어 있음에 따라 본 조사기간 강우의 산성도가 빗물에 포함된 각종 알카리 물질들에 의해 중화되었음을 보였다.

• 한국환경농학회지
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• 제18권3호
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• pp.204-208
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• 1999

태안지역 빗물의 화학적 특성을 알아보기 위하여 '98년 영농기(5월${\sim}$10월) 동안 태안지역에 내린 빗물의 화학적 성분조성과 분석결과의 신뢰성을 조사한 결과는 다음과 같다.각 분석시료에 대한 이온균형과 전기전도도 수지를 조사한 결과, 고농도 시료를 제외하고는 분석의 신뢰성이 인정되었다. 빗물의 pH별 분포는 pH $4.5{\sim}5.0$ 및 $5.0{\sim}5.6$ 범위에서 각각 43%와 38%이었으며, 강우량별 빗물의 이온함량과 pH 변화는 초기강우(1mm 이하)가 그 이후의 강우에 비해 높았다. 빗물의 조성은 $SO_4\;^{2-}$와 $NO_3\;^-$가 음이온의 80% 이상 그리고 양이온은 $NH_4\;^+$와 $Ca^{2+}$가 60% 이상을 차지하고 있었다. 월별 빗물의 pH는 강우량이 많았던 8월에 4.3으로 가장 낮았고 조사지역 강우중 비해염 sulfate는 총 sulfate 함량의 약 97%이었다. 빗물의 $nss-SO_4\;^{2-}/NO_3\;^-$비는 평균 2.4로 비해염 $SO_4^{2-}$의 강우 산성도에 대한 기여율이 $NO_3\;^-$보다 2.4배 높았다.

• 한국대기환경학회지
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• 제22권1호
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• pp.15-24
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• 2006

Precipitation samples were collected at Anmyeon (1997 - 2004), Uljin, and Gosan (1998 ~ 2004), the background area of the Korean Peninsula. These samples were analyzed for the concentration of 9 major ionic components ($F^{-}$,$Cl^{-}$, $NO_{3}^{-}$, $SO_{4}^{2-}$, $Na^{+}$, $NH_{4}^{+}$, $K^{+}$, $Mg^{2+}$, $Ca^{2+}$) with including a pH and an electric conductivity. Data quality for these samples was verified by ion balance and conductivity balance which are based on GAW manual for precipitation chemistry and the number of valid data at Anmyeon, Uljin, and Gosan is 249, 173, and 188, respectively. During the study period, the precipitation-weighted average pH at Anmyeon, Uljin, and Gosan was found to be 4.81, 4.87 and 4.89, respectively and each annual average pH was showed below pH 5.6 for every site. From the frequency survey on the precipitation acidity, the occurrence rate of acid rain below pH 5.6 is greater than $80\%$ for every site. Particularly, the highest occurrence rate for strong acid rain below pH 4.5 was found at Anmyeon, $32.1\%$, compared with other sites ($10.4\%$ at Uljin, $15.4\%$ at Gosan). That's because acidifying species (nss-$SO_{4}^{2-}$, $NO_{3}^{-}$) are remarkably high concentration at Anmyeon.

• Bulletin of the Korean Chemical Society
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• 제24권3호
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• pp.363-368
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• 2003

The major ionic components of precipitation collected at the 1100 Site of Mt. Halla and Jeju city have been determined. The reliability of the analytical data was verified by the comparison of ion balances, electric conductivities and acid fractions; all of their correlation coefficients were above 0.94. Ionic strengths lower than $10^{-4}$ M were found in 53% of the 1100 Site samples and 28% of the Jeju city samples. Compared with other inland areas, the wet deposition of $Na^+,\;Cl^-\;and\;Mg^{2+}$ was relatively larger, but that of $NH_4^+,\;nss-SO_4^{2-}$(non-sea salt sulfate) and $NO_3^-$ was lower. Especially the wet deposition increase of $Ca^{2+}$ in the spring season supports the possibility of the Asian Dust effect. The acidification of precipitation was caused mostly by $SO_4^{2-}\;and\;NO_3^-$ in the Jeju area, and the organic acids have contributed only about 7% to the acidity. The neutralization factors by NH₃were 0.47 and 0.48, and that of CaCO₃was 0.31 and 0.25 at the 1100 Site and Jeju city, respectively. Investigation into major influencing sources on precipitation components by factor analysis showed that the precipitation at the 1100 Site had been influenced mostly by an anthropogenic source, followed by soil and seawater sources. The precipitation at Jeju city was mainly influenced by oceanic sources, followed by anthropogenic and soil sources.

• 한국환경보건학회지
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• 제34권4호
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• pp.300-310
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• 2008

In order to further determine the mass concentration and ion composition of size-segregated particulate matter (PM) during the non-Asian dust storm of spring, $PM_{2.5}$ (fine particle), $PM_{10-2.5}$ (coarse particle), and $PM_{over-10}$ (PM with an aerodynamic diameter larger than $10{\mu}m$) were collected using a MCI (multi-nozzle cascade impactor) sampler of a three-stage filter pack in the spring season of 2007 in the Iksan area. During the sampling period from 5 April to 21 April, a total of 34 samples for size-segregated PM were collected, and then measured for PM mass concentrations by gravimetric measurements and for water-soluble inorganic ion species by using ion chromatography. Average mass concentrations of $PM_{2.5}$, $PM_{10-2.5}$, $PM_{over-10}$ were $35.4{\pm}11.5{\mu}g/m^3$, $13.3{\pm}5.5{\mu}g/m^3$ and $9.5{\pm}4.7{\mu}g/m^3$, respectively. On average, $PM_{2.5}$ accounted for 74% of $PM_{10}$. Compared with the literature from other areas in Korea, the measured concentration of $PM_{2.5}$ were relatively high. Water-soluble inorganic ion fractions in $PM_{2.5}$, $PM_{10-2.5}$, and $PM_{over-10}$ were found to be 47.8%, 28.5%, and 14.7%, respectively. Among the water-soluble inorganic ion species, $SO_4^{2-}$, $NO_3^-$ and $NH_4^+$ were the main components in $PM_{2.5}$, while $NO_3^-$ dominantly existed in both $PM_{10-2.5}$ and $PM_{over-10}$. Non-seasalt $SO_4^{2-}$ (nss-$SO_4^{2-}$ and $NO_3^-$ were found to mainly exist as the neutralized chemical components of $(NH_4)_2SO_4$ and $NH_4NO_3$ in fine particles.

• 한국토양비료학회지
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• 제46권5호
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• pp.386-390
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• 2013

Recently, special attention has been given to acid rain and its problem to environment such as acid precipitation and air pollution in East Asia. In the present study, rainwater samples were collected from Apr to Nov in 2012. The samples were chemically characterized for the assessment of emission sources. Suwon and Yeoju regions, typical agricultural areas in South Korea, were chosen for study sites. Ion composition and cation-affected neutralization were determined to evaluate the contribution of cations to the acidity of rainwater. Ion and electrical conductivity between the measured and the estimated showed high correlation. The cations observed in Suwon and Yeoju were $Na^+$ > $NH_4{^+}$ > $K^+$ > $Ca^{2+}$ > $Mg^{2+}$ > $H^+$ and $Na^+$ > $K^+$ > $NH_4{^+}$ > $Ca^{2+}$ > $Mg^{2+}=H^+$, respectively. The anions of all sites were $SO{_4}^{2-}$ > $NO_3{^-}$ > $Cl^-$. While the amounts of sulfate, one of the major dissolved components of rainwater, were 77.6 and 75.6 ueq $L^{-1}$ in Suwon and Yeoju, the ones of NSS-$SO{_4}^{2-}$ (Non-Sea Salt sulfate) were 83 and 82% in Suwon and Yeoju, respectively. The comparison of observed pH values ($pH_{obs}$) with the theoretical pH values ($pH_{the}$) showed that the neutralization of rain water considerably went along during the study periods. The highest amounts of rainfall throughout the year in Suwon and Yeoju were 572.3 and 484.6 mm in July, and its corresponding nitrogen loadings in Suwon and Yeoju were 5.28 and 3.50 kg $ha^{-1}$, respectively. The major ion contents for crop growth with $SO{_4}^{2-}$, $Ca^{2+}$, $K^+$ and $Mg^{2+}$ were 51.7, 5.2, 11.8 and 1.8 kg $ha^{-1}$ in Suwon and 34.2, 4.0, 4.2 and 1.1 kg $ha^{-1}$ in Yeoju.

• 한국대기환경학회지
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• 제27권5호
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• pp.603-613
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• 2011

The collection of $PM_{10}$ and $PM_{2.5}$ samples was made at Gosan site of Jeju Island. Their ionic compositions of both inorganic and organic phases were then analyzed to examine their acidification and neutralization characteristics in atmospheric aerosols. The mass concentrations of $PM_{10}$ and $PM_{2.5}$ at Gosan site were $37.6{\pm}20.1$ and $22.9{\pm}14.3{\mu}g/m^3$, respectively, showing the content ratio of $PM_{2.5}$ to $PM_{10}$ as 61.0%. In the evaluation of ionic balance, the correlation coefficients (r) between the sums of cationic and anionic equivalent concentrations were excellent with 0.982 ($PM_{10}$) and 0.991 ($PM_{2.5}$). The concentration ratios of $PM_{2.5}/PM_{10}$ derived for nss-$SO_4^{2-}$, $NO_3^-$, and $NH_4^+$ were 0.94, 0.56, and 1.02, respectively, indicating the relative dominance of fine fractions. The acidifying capacity of inorganic anions ($SO_4^{2-}$ and $NO_3^-$) in $PM_{10}$ and $PM_{2.5}$ were 96.5% and 97.3%, while those of organic anions ($HCOO^-$ and $CH_3COO^-$) in each fraction were 2.9% and 2.0%, respectively. On the other hand, the neutralizing capacity of $PM_{10}$ and $PM_{2.5}$ by $NH_3$ were 72.8% and 82.3%, while their $CaCO_3$ counter parts were 22.5% and 13.3%, respectively.

• 한국대기환경학회지
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• 제15권2호
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• pp.89-100
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• 1999

The rain water samples were collected at Chunchon and Seoul by using wet only automatic sampler from January 1996 through 1997. The daily base rain water samples collected over than 95% rainy events components, $SO_4^{-2}$, $NO_3^-$, $CI^-$, NH_4^+$, $Ca^{2+}$, $Mg^{2+}$, $Na^+$, and $K^+$, by ion chromatography. In 1996, about 77% of sampled rain water showed below pH 5.6 and the 60% of rain water was lower than pH 5.0. The volume weighted average pH was 4.7 at all sites. In 1997, the volume weighted average pH was 4.6 and 4.9 at Seoul and Chunchon, respectively. Among the rain water samples,, 87% and 55% fo samples showed below than pH 5.6 and 5.0, respectively. The pH value of Chunchon was significantly (p＜0.05) lower than Seoul at the rain samples for less than 20mm rainfall. However conductivity of the rain samples were 20.9$\mu$S/cm for 1996 and 27.7$\mu$S/cm for 1997 at Seoul, and 19.1$\mu$S/cm for 1996 and 14.1$\mu$S/cm for 1997 at Chunchon. $H_2SO_4$ and $HNO_3$ contributed 65.9% and 29.6% of free acidity at Seoul, respectively. The ratio of [$NO_3^-$]/[nss-$SO_4^{-2}$] were 0.43 at Seoul and 0.51 at Chunchon for rain samples for less than 20mm rainfall. The annual wet deposition of $CI^-$, $NO_3^-$, $SO_4^{-2}$, $H^+$M, $Na^+$, NH_4^+$, $K^+$, $Mg^{2+}$, and $Ca^{2+}$, respectively, 568.8kg/$ extrm{km}^2$, 1489.3kg/$\textrm{km}^2$, 3184.8kg/$\textrm{km}^2$, 20.9kg/$\textrm{km}^2$, 249.4kg/$\textrm{km}^2$, 1091.2kg/$\textrm{km}^2$, 189.8kg/ $\textrm{km}^2$, 90.2kg/$\textrm{km}^2$ and 702.4kg/$\textrm{km}^2$ at Seoul for 1996; 656.4kg/$\textrm{km}^2$, 2029.7kg/$\textrm{km}^2$, 3280.7kg/$\textrm{km}^2$, 27.2kg /$\textrm{km}^2$, 229.4kg/$\textrm{km}^2$, 1063.9kg/$\textrm{km}^2$, 106.9kg/$\textrm{km}^2$, 78.2kg/$\textrm{km}^2$, 645.3kg/$\textrm{km}^2$ at Seoul for 1997; 116.9kg/ $\textrm{km}^2$, 983.3kg/$\textrm{km}^2$, 1797.0kg/$\textrm{km}^2$, 21.4kg/$\textrm{km}^2$, 83.2kg/$\textrm{km}^2$, 648.1kg/$\textrm{km}^2$, 78.0kg/$\textrm{km}^2$, 22.2kg/$\textrm{km}^2$, 368.8kg/$\textrm{km}^2$ at chunchon for 1996; 100.2kg/$\textrm{km}^2$, 1077.6kg/$\textrm{km}^2$, 1754.0kg/$\textrm{km}^2$, 13.4kg/$\textrm{km}^2$, 146.0kg/$\textrm{km}^2$, 602.3kg/$\textrm{km}^2$, 88.8kg/$\textrm{km}^2$, 16.2kg/$\textrm{km}^2$ and 206.8kg/$\textrm{km}^2$ at chunchon for 1997.