• Proceedings of the KSEEG Conference
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• 2000.04a
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• pp.90-91
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• 2000

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2005.04a
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• pp.276-279
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• 2005

마금산온천 지역에 대한 기초적인 지화학 조사를 수행하였다. 연구지역내에는 일반 지하수와 온천수가 함께 산출되며, 온천수의 지화학적 특성은 마금산 온천이 해수의 영향을 받았음을 지시한다. 또한 주변의 일반지하수와의 혼합정도에 따라 지화학적 특성이 변화하고 있으며, 일반지하수 또한 온천수의 영향을 지역적으로 받고 있는 것으로 판단된다. 따라서 마금산온천을 생성시킨 지열수가 연구지역의 지하수체계에 광범위하게 영향을 주고 있다.

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2003.09a
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• pp.597-600
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• 2003

용인시 백암취수장 주변 지역의 지하수에 대해 기초적인 지화학적 조사를 수행하였다. 현장측정자료에서는 취수정의 pH와 EC값이 주변지하수보다 지표수와 유사한 값을 보이며, 취수정의 용존산소(DO) 함량이 천층지하수보다 높은 값을 보인다. 더구나 취수정의 경우 NO$_3$함량이 10.5-12.1 mg/L이며 주변 지하수는 7.2-25.3 mg/L, 지표수는 13.1-14.9 mg/L로서 취수정의 설치심도가 70-180m로서 상대적으로 깊은 암반층에 설치되어 있다 하더라도 주변지하수 및 인접 지표수의 혼입에 의해 영향을 받아 오염이 진행되고 있음을 알 수 있다. 이와 같이 연구 지역은 현재 취수정이 모두 청미천변에 위치하고 있어서, 현재 암반 지하수로 개발하고 있는 취수정 지하수가 주변 천부지하수 및 지표수에 의한 혼입 및 오염가능성이 높기 때문에, 앞으로 장기적인 모니터링 및 지화학적 연구가 지속적으로 이루어 져야 할 것으로 사료된다.

• Proceedings of the KSEEG Conference
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• 1999.04a
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• pp.8-10
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• 1999

• Economic and Environmental Geology
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• v.50 no.6
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• pp.545-554
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• 2017

Birnessite is one of the dominant Mn (oxyhydr)oxide phases commonly found in soil and deep ocean environments. It typically occurs as nano-sized and poorly crystalline aggregates in the natural environment. It is well known that birnessite participates in a wide variety of bio/geochemical reactions as a reactive mineral phase with structural defects, cation vacancies, and mixed valences of structural Mn. These various bio/geochemical reactions control not only the fate and transport of inorganic and organic substances in the environment, but also the formation of diverse Mn (oxyhydr)oxides through birnessite transformation. This review assessed and discussed about the phase transformation of birnessite under a wide range of environmental conditions and about the potential geochemical factors controlling the corresponding reactions in the literature. Birnessite transformation to other types of Mn (oxyhydr)oxides were affected by dissolved Mn(II), dissolved oxygen, solution pH, and co-existing cation (i.e., $Mg^{2+}$). However, there still have been many issues to be unraveled on the complex bio/geochemical processes involved in the phase transformation of birnessite. Future work on the detail mechanisms of birnessite transformation should be further investigated.

• Economic and Environmental Geology
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• v.44 no.3
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• pp.203-215
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• 2011

Geochemical and mineralogical properties of a contamited soil should be taken into account to decide a remediation strategy for a given contaminant because development and optimization of soil remedial technologies are based on geochemical and mineralogical separation techniques. The objective of this study was to investigate the geochemical and mineralogical characteristics of arsenic-contaminated soils. The arsenic-contaminated soil samples were obtained from Chonam gold mine, Gwangyang, Chonnam, Particle size analysis, sequential extraction, and mineralogical analyses were used to characterize geochemical and mineralogical characteristics of the As-contaminated soils. Particle size analyses of the As-contaminated soils showed the soils contained 17-36% sand, 25-54% silt, 9-28% clay and the soil texture were sandy loam, loam, and silt loam. The soil pH ranged from 4.5 to 6.6. The amount of arsenic concentrations from the sequential soil leaching is mainly associated with iron oxides (1 to 75%) and residuals (12 to 91%). Major minerals of sand and silt fractions in the soils were feldspar, kaolinite, mica, and quartz and minor mineral of which is an iron oxide. Major minerals of clay fraction were composed of illite, kaolinite, quartz, and vermiculite. And minor minerals are iron oxide and rutile. The geochemical and mineralogical analyses indicated the arsenic is adsorbed or coprecipitated with iron oxides or phyllosilicate minerals. The results may provide understanding of geochemical and mineralogical characteristics for the site remediation of arsenic-contaminated soils.

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2000.05a
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• pp.158-158
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• 2000

• Proceedings of the KSEEG Conference
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• 2005.04a
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• pp.101-103
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• 2005

• Proceedings of the KSEEG Conference
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• 2002.04a
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• pp.56-58
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• 2002

• Proceedings of the KSEEG Conference
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• 2001.04a
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• pp.400-403
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• 2001