• Title/Summary/Keyword: 함안지역

Search Result 70, Processing Time 0.03 seconds

Microbial Community Structures Related to Arsenic Concentrations in Groundwater Occurring in Haman Area, South Korea (함안지역 지하수의 비소(As) 함량과 미생물 군집 특성과의 연관성 검토)

  • Kim, Dong-Hun;Moon, Sang-Ho;Ko, Kyung-Seok;Kim, Sunghyun
    • Economic and Environmental Geology
    • /
    • v.53 no.6
    • /
    • pp.655-666
    • /
    • 2020
  • This study evaluated the characteristics of arsenic production in groundwater through microbial community analysis of groundwater contaminated with high arsenic in Haman area. Groundwater in Haman area is contaminated with arsenic in the range of 0-757.2 ㎍/L, which represents the highest arsenic contamination concentration reported in Korea as natural groundwater pollution source. Of the total 200 samples, 29 samples (14.5%) showed higher arsenic concentration than that of 10 ㎍/L, which is the standard for drinking water quality, and 8 samples (4%) found in wells with 80-100 m depth were above 50 ㎍/L. In addition, seven wells with arsenic concentration more than 100 ㎍/L located in the northern part of Haman. As a result of microbial community analysis for high arsenic-contaminated groundwater, the microbial community compositions were significantly different between each sample, and Proteobacteria was the most dominant phyla with an average of 61.5%. At the genus level, the Gallinonella genus was predominant with about 12.8% proportion, followed by the Acinetobacter and Methermicoccus genus with about 7.8 and 7.3%, respectively. It is expected that high arsenic groundwater in the study area was caused by a complex reaction of geochemical characteristics and biogeochemical processes. Therefore, it is expected that the constructed information on geochemical characteristics and microbial communities through this study could be used to identify the origin of high arsenic groundwater and the development of its controlling technology.

낙동강 함안군 칠서 강변여과 개발 예정지역의 수리지구화학적 특성조사

  • 김주환;백건하;김형수;김진삼;윤성택
    • Proceedings of the Korean Society of Soil and Groundwater Environment Conference
    • /
    • 2003.09a
    • /
    • pp.561-564
    • /
    • 2003
  • 강변여과수 개발 예정지역인 함안군 칠서지역의 수질특성을 알아보기 위해 2003년 4월과 2003년 8월 2회에 걸쳐 강변여과수 양수정, 관측정, 주변지역 지하수 및 낙동강 원수 등 총 38개의 물시료를 채수하여 분석하였다. 용존 이온 분석 결과 연구 지역 지하수의 경우는 Ca-HCO$_3$ 유형 또는 Ca-Cl 유형에 속하며, 조사 지점에 따라 충적층 및 암반 지하수의 특징이 확연히 구분되었다. 조사된 지하수의 경우, 질산성질소와 철, 망간의 농도가 다른 성분에 비해 상대적으로 높은 것으로 나타났으며, 그 외의 중금속의 오염은 미미한 것으로 나타난다. 낙동강 원수의 경우 질산성 질소, 철, 망간은 지하수에 비해 낮은 것으로 나타났으나, 조류의 영향으로 매우 높은 pH 값을 보여주었다. 채수된 전체 시료의 분석 결과, 질산성질소(39.1%), 철(13%), 망간(39.1%)이 주로 먹는 물 수질기준을 초과하는 항목으로 나타났다.

  • PDF

Quality of Surface Water for lrrigation around Controlled Horticultural Area in Gyeongnam (경남지방 시설원예지 농업용 지표수의 수질 현황)

  • Heo, Jong-Soo;Ha, Yeong-Rae;Seo, Jeoung-Yoon;Cho, Ju-Sik;Lee, Sung-Tae;Lee, Hong-Jae
    • Korean Journal of Environmental Agriculture
    • /
    • v.16 no.4
    • /
    • pp.356-364
    • /
    • 1997
  • To investigate the water quality status of agricultural water source for greenhouse area in Gyeongnam, the surface water quality was examined six times from October in 1995 to March in 1996 at five areas in Gyeongnam. The pH values of surface water were in the range of 6.6${\sim}$9.1 pH in Kimhae and Changnyong areas were out of range in 6.0${\sim}$8.5 which was water quality standard for agriculture. The DO values of surface water were relatively high with average 10.0mg/l in Kimhae, Changnyong, Sacheon and Chinju areas except for Haman area. The BOD values of surface water exceeded water quality standard for agriculture(8.0mg/l) in three sites and one site in Haman and Sacheon, respectively. The COD values of surface water exceeded water quality standard for agriculture(8.0mg/l) in Kimhae, Changnyong and Haman. The ${NH_4}^+-N$ values in surface water of Changnyong and Haman areas were 1.21mg/l and 2.75mg/l, respectively. The average values of $NO_3\;^--N$ in surface water was appropriate for agriculture. The values of $K^+,\;Na^+,\;Mg^{2+},\;Ca^{2+},\;{PO_4}^{3-}$ and $SO_4^{2-}$ in Haman were the highest of those of the others. And Pb was below 0.1mg/l which was water quality standard for agriculture. The average values of Cu, Cd and Zn were below water quality standard for agriculture. Between COD and SS in surface water was positively correlated with r$=0.799^{{\ast}{\ast}}$. BOD in surface water was positively correlated with $NH_4\;^+-N,\;PO_4\;^{3-},\;SS,\;K^+,\;Na^+$ and $Cl^-$. Surface water pollution status of agricultural water source of greenhouse areas in Gyeongnam was in order of Chinju< Sacheon< Kimhae< Changnyong< Haman area.

  • PDF

A geochemical study on the metal contamination of groundwater in Taegu City (대구시 지하수의 금속 오염에 대한 지화학적 연구)

  • 이재영;김영기;이진국;서정율
    • The Journal of Engineering Geology
    • /
    • v.2 no.2
    • /
    • pp.173-200
    • /
    • 1992
  • The quality of groundwater in the central part of Taegu City is influenced by upstreams of Sin-stream and Beomeo-stream because the stream waters are main source of the groundwater, and chemical composition of the upstream waters has close relationship with andesite and monzonite in the igneous rock terrain. The pH of upstreams are weak acid ~ neutral in the igneous rock area and weak alkaline in the sedimentary rock area. Contents of $Ca^{2+}$ and $Mg^{2+}$ in the streams are apparently high, and $Na^{+}$ content is only slightly high in the sedimentary rock area. But $K^{+}$ content is lower in the Panyaweol formation area than in the monzonite area. The contents of heavy metals and $N0_3^{-}$ are also higher in the sedimentary rock area of residential sections and industrial complexes than those in the igneous rock area. The groundwater is contaminated in comparison to the upstream water of the igneous rock areas, and there are some differences in pollution level between the Panyaweol formation area of residential sections and the Haman formation area of industrial complexes. K, Na, Ca, Mg, Cl, $SO_4$ and $NO_3$ contents in the Haman formation area are relatively higher than those in the Panyaweol formation area. But pH is nearly equal in the two areas. The content of heavy metal ions is still lower than the drinking water standard of Korea and only slightly differs in the two sedimentary rock areas. But the groundwater in the Haman formation area is considerably contaminated by Kongdanstream and Dalseo-stream.

  • PDF

Musical Characteristics and Locality of Naeseo-deulsori (내서들일소리의 음악적 특징과 지역성)

  • Seo, Jeong-mae
    • (The) Research of the performance art and culture
    • /
    • no.43
    • /
    • pp.325-356
    • /
    • 2021
  • This study is to analyze the current status of transmission and musical characteristics of Naeseo-deulilsori in Changwon, and the purpose of this study is to illuminate the value of deulilsori in Naeseo region, so that it can be continuously inherited. Naeseo-deulsori consists of the Mosimgi-sori, Nonmaegi-sori, and Chingchingi-sori. Mosimgi-sori, which is called when planting a seedling, is divided into 6 types according to the order and situation of work. ① rice planting sound, ② rice planting sound called in the morning, ③ rice planting sound called at lunch time, ④ rice planting sound called after lunch, ⑤ rice planting sound called when it is raining or cloudy, ⑥ rice planting sound called at sunset. Mosimgi-sori, which is called when planting a seedling, is based on Menali-tori, but partly influenced by Yugjabaegi-tori. However, it was typical Menali-tori in the slow The sound of rice planting in the nearby Haman region, but as the speed increased in the fast The sound of rice planting, the characteristics of Menali-tori faded and la↘mi perfect fourth descending frequently appeared. In the sound of rice planting in Goseong, both slow and fast sounds were strongly influenced by Yugjabaegi-tori. In the end, the sound of rice planting in the Naeseo region is less Yugjabaegi-tori than in the Goseong region and stronger than in Haman region. This combination of tori is a musical bargaining phenomenon that appears in the border region, and it can be said to be a geographical and regional characteristic of the Naeseo region. Nonmaegi-sori has the same sound as 'Sangsadeio' throughout the nearby Goseong and Haman regions. However, in Nonmaegi-sori in the Naeseo region, a strong Gyeong-tori tendency is found in the sound received. Looking at the flow of the melody of Nonmaegi-sori, it seems that the pitch has been changed by the intestines in recent years, and this modified melodic form has continued as it is. In order to guarantee locality, this part seems to need to be corrected in the future.

Geochemical Environments of Copper-bearing Ore Mineralization in the Haman Mineralized Area (함안지역 함 동 광화작용의 지화학적 환경)

  • Choi, Sang-Hoon
    • Economic and Environmental Geology
    • /
    • v.42 no.1
    • /
    • pp.1-8
    • /
    • 2009
  • The Haman mineralized area is located within the Cretaceous Gyeongsang Basin along the southeastern part of the Korean peninsula. Almost all occurrences in the Haman area are representative of copper-bearing polymetallic hydrothermal vein-type mineralization. Within the area are a number of fissure-filling hydrothermal veins which contain tourmaline, quartz and carbonates with Fe-oxide, base-metal sulfide and sulfosalt minerals. The Gunbuk, Jeilgunbuk and Haman mines are each located on such veins. The ore and gangue mineral paragenesis can be divided into three distinct stages: Stage I, tourmaline + quartz + Fe-Cu ore mineralization; Stage II, quartz + sulfides + sulfosalts + carbonates; Stage III, barren calcite. Equilibrium thermodynamic data combined with mineral paragenesis indicate that copper minerals precipitated mainly within a temperature range of $350^{\circ}C$ to $250^{\circ}C$. During early mineralization at $350^{\circ}C$, significant amounts of copper ($10^3$ to $10^2\;ppm$) could be dissolved in weakly acid NaCl solutions. For late mineralization at $250^{\circ}C$, about $10^0$ to $10^{-1}\;ppm$ copper could be dissolved. Equilibrium thermodynamic interpretation indicates that the copper in the Haman-Gunbuk systems could have been transported as a chloride complex and the copper precipitation occurred as a result of cooling accompanied by changes in the geochemical environments ($fs_2$, $fo_2$, pH, etc.) resulting in decrease of solubility of copper chloride complexes.