• 한국해양학회지
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• 제22권3호
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• pp.130-142
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• 1987

제주남방해역 표층퇴적물에 대해 입도분석, 경광물 및 점토광물, 그리고 미량원소 분석을 실시하였다. 본 연구해역의 퇴적물상은 남동부의 오조립질 분포역 과 남서부 조`세립질 분포지로 구분되며, 남서쪽 끝지역에는 소규모의 현생니질퇴적 물 분포대(mud zone)도 존재한다. 본 역에 분포하는 퇴적물은 분급이 불량하고 negative~positive skewed할뿐 아니라 platykurtic~leptokurtic한 특성을 나타냈으며, 조립질은 도약(saltation)에 의해, 세립질은 도약 및 부유(suspension)에 의해 운반된 것으로 보여 진다. 측정된 13종의 지화학적원소성분중 Co, Ni, Ca, Ag를 제외한 9 종은 남동부지역에서 남서부지역으로 향함에 따라 함량이 증가하는 경향을 보였고, Co와 Ni은 동`서부간에 유사한 함량분포를 나타냈으나 Ca와 Ag은 남동부지역에서 함량치가 높았다. 탄산염함량은 남동부의 조립질 분포역에서가 남서부보다 높게나 타난 반면 총 유기물함량은 이와는 상반된 경향을 보였다. 경광물은 석영, 암편, K- 장석, Na-Ca장석 순의 조성을 보였는데 제주도 주변 해역에서 외해쪽으로 향함에 따라 석영과 K-장석의 함량증가하고 Na-Ca장석과 암편은 감소하는 경향을 나타냈 다. 조사지역 남서쪽 끝 mud 지역의 점토광물로는 illite, chlorite, kaolinite, feldspar, calcite등인데, chlorite가 양적으로 많고 calcite peak가 현저하게 나타날 뿐만 아니라 Ca, Pb, Ni등의 지화학적원소성분의 함량도 황하기원퇴적물의 특성치 와 유사하여 이 지역세립질퇴적물 대부분은 황하기원인 것으로 사료된다.

• 한국농림기상학회지
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• 제7권4호
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• pp.265-273
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• 2005

본 연구에서는 폐탄광 주변 산림의 복원을 위한 기초자료를 제공하고자 경북 문경지역에 위치한 폐탄광 중 4개의 광산을 대상으로 산림토양의 화학적 특성과 중금속 오염현황을 i.자한 결과를 보고한다 폐탄광지 산림토양의 pH는 $5.30\~6.76$의 범위에 있었으며, 대조구 지역의 토양 pH는 5.23이었다. 폐탄광지역의 산림토양 중 유기물과 전질소 함량은 각각 $4.46\~7.19\%,\;0.07\~0.15\%$의 범위에 있는 것으로 조사되었다. 평균 유효인산 함량은 삼창탄광 6.54, 봉명탄광 6.52, 갑정탄광 3.94, 단봉탄광 5.45 그리고 대조구 5.25mg/kg으로 토양 pH와 정의 상관을 가지는 것으로 나타났다. 폐탄광지역의 치환성양이온 평균 함량은 Ca 196.1, Mg 88.7, K 88.2 그리고 Na $10.2cmol^+/kg$로 나타났으며, 그 범위는 Ca $132.1\~242.1,\;Mg 24.2\~138.6,\;K 64.9\~120.8$ 그리고 Na $8\~12.2cmol^+/kg$에 있는 것으로 조사되었다 대조구 지역의 Ca, Mg, K, Na의 평균 함량은 각각 192.8, 95.8, 104 and $21.2 cmol^+/kg$로 조사되었다. 폐탄광지 산림토양의 중금속(Al, As, Cd, Cr, Cu, Fe, Mn, Ni, Pb, Zn) 함량은 대조구 산림토양보다 높은 것으로 분석되었다. 특히, Al, Mn 그리고 Pb의 함량은 대조구에 비해 폐탄광지가 아주 높은 것으로 나타났다. 폐탄광지 산림토양의 Al함량은 $397\~917 ppm$으로 나타나 식물생육에 영향을 미칠 수 있을 것으로 추정된다 그러므로 과거 석탄채굴이 활발하게 이루어졌던 폐탄광지에 대해서는 환경문제를 최소화하기 위하여 산림토양을 대상으로 한 적절한 관리가 필요할 것으로 추정된다.

• 한국해양학회지
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• 제22권1호
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• pp.43-56
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• 1987

한국 동남해역의 일부, 남해해역의 일부 및 대한해협의 대륙붕에 관한 해양지 질학적이며 지구화학적 관점의 기초 해양학적 연구가 실시되었다. 본 연구해서의 대륙붕은 미세지형도인과 표층 퇴적물의 분포패턴등으로 내 대륙붕과 외대륙붕으로 구분되었다. 즉 내 대륙붕과 외 대륙붕의 경계지형은 약 80m수심의 해서이며 내 대륙붕의 해저는 해안선의 방향과 평행하는 발달 추세를 나타내는 반면 외 대륙붕 의 해저는 한국해협 해곡(KSR)등을 크고 작은 기복지형을 나타낸다. 내 대륙붕의 표층 퇴적물은 이토(mud)와 사질 실트로 구성된 세립질 퇴적상이며 외 대륙붕은 조립질 퇴적물(모래와 자갈)로 구성된 잔류퇴적상(relict sediment facies)을 나타낸 다. 내 대륙붕의 퇴적물은 외 대륙붕의 퇴적물보다 높은 $\varepsilon$$_{A1}$ 보이나 Ni, Cr, Cu 등의 오염영향을 거의 보이지 않는다. 그러나 Zn, Pb 등의 원소에 관한한 오염의 영향을 나타내는 것으로 해석된다. 본 연구 지역의 탄성파층서는 음향기 반암과 강한반사면 R에 의한 3층서단위로 구성된다. 이들은 하부로부터 기반암(음향), 하부퇴적층(B) 및 상부퇴적층(A)이며 상부퇴적층은 현세 퇴적층이며 하부퇴적층은 선 현세(pre-Holocene)퇴적층이다.다.

• 한국수산과학회지
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• 제39권2호
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• pp.106-117
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• 2006

We measured the concentrations of organic matter and metallic elements (Al, Fe, Cr, Mn, Ni, Cu, Zn, As, Cd, Pb and Hg) in the surface sediments of Masan Harbor (in the southern sea, Korea) to evaluate the geochemical characters of sediment and the pollutions by organic matter and metallic elements. The mean grain size of the surface sediments in the study area ranged from $5.6{\phi}$ to $7.8{\phi}$, indicating silt sediment. The water content of the surface sediments exceeded 60% except at some stations. The contents of ignition loss (IL), total organic carbon (TOC) and total nitrogen (TN) ranged from 7.2-14.3%, 1.2-3.2%, and 0.10-0.28%, respectively. Based on the C/N ratios, the organic matter in the surface sediments of Masan Harbor may originate from terrigenous sources including fluvial inputs (mainly sewage in urban areas). The chemical oxygen demand (COD) and acid volatile sulfide (AVS) ranged from $11.3-29.9\;mgO_2/g\;dry$ and 0.20-4.47 mgS/g dry, respectively, and low concentrations were observed near a shipping route. In addition, the concentrations of metallic elements showed large spatial variations in Masan Harbor and the distributions of metallic elements were also comparable to those of organic matter. This implies that the distributions of organic matter and metallic elements in the surface sediments of Masan Harbor are mainly controlled by biogenic matter and artificial action (mainly dredging). In addition, we calculated the enrichment facto. (EF) and geoaccumulation index (Igeo) in order to evaluate pollution by metallic elements. The enrichment of metallic elements relative to Al was three to eighteen times higher at the study sites, compared to levels in the Earth's crust except for Fe, Ni and Mn. In addition, the Igeo class indicated that the surface sediments in the study area were moderately to strongly polluted in terms of metallic elements.

• 한국환경과학회지
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• 제22권7호
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• pp.787-799
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• 2013

The aim of this study was to investigate the accumulation of metallic elements and the control effect of marine pollution caused by ocean dumping in the sediments at a waste disposal area in the Yellow Sea. In July 2009, concentrations of organic matter and metallic elements (Al, Fe, As, Cd, Cr, Co, Hg, Ni, Mn, Pb, and Zn) were measured in surface sediments at the site. The ignition loss (IL) in the surface sediments showed a mean value of 15.4%, about 1.5 times higher than the mean value of the sediments in the coastal areas of Korea. The chemical oxygen demand (COD) at some disposal sites exceeded 20 mg $O_2/g{\cdot}dry$, which signifies the initial concentration of marine sediment pollutants in Japan. The disposal sites contain higher concentrations of Cr, Cu and Zn than the sediments of bays and estuaries that might be contaminated. The magnitude of both metal enrichment factors (EF) and adverse biological effects suggest that pollution with Cr and Ni occurred due to the dumping of waste in the study area. In addition, the geoaccumulation index (Igeo) showed that the surface sediments were moderately contaminated. By the mid-2000s, when the amount of waste dumped at this site was the highest, the concentration of metallic elements was higher than ever recorded. On the other hand, in 2008-09, the need for environmental management was relatively low compare with the peak. As a result, the quality of marine sediment has been enhanced, considering the effect of waste reduction and natural dilution in the disposal area.

• 자원환경지질
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• 제30권5호
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• pp.443-450
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• 1997

The main purpose of this study is to investigate mineralogical and chemical changes during natural weathering, and assess the mobility of major and trace elements. Yongwol power plant utilize anthracite coal which is mainly composed of illite, kaolinite, pyrophyllite and quartz in mineralogy. Coal and coal-derived fly ash samples were sampled by the electrostatic precipitator in Yongwol coal-fired power plant in Korea. Short term weathered fly ash were also collected in ash disposal mound, and two profile soil samples were taken from an ash near the power plant. Amorphous materials are the main component of the fly ash, and mullite, quartz, magnetite and heamatite are present in all coal-derived fly ash. In chemistry, Si and Al are the most abundant elements of the total content. The ash samples were fractionated into upper $90{\mu}m$ and under $45{\mu}m$ size. Finer particles show higher concentrations in metal contents including Co, Cr, Cu, Ni, V, Zn and Pb. Concentration of Zn and Pb are nearly 4 times higher concentration in the finer particles. For the profile samples, the concentrations of $SiO_2$, $Na_2O$, MgO and $K_2O$ generally show increasing trends with depth, whereas those of $Fe_2O_3$ and $TiO_2$ appear to decrease with depth. Content of MnO does not show any specific depth trend. For the trace elements, Co, Cu, Ni and V show increasing concentrations with depth.

• 플랜트 저널
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• 제4권2호
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• pp.60-65
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• 2008

As the operating conditions in a supercritical oxidation reactor are set in high temperature with high pressure causing a reactor suffering from the harsh circumstances. It means the reactor adopts itself with Fe-Cr alloy in acidic atmosphere with low pH value and Ni alloy in basic atmosphere with high pH value due to its superior corrosion resistance. The study, whose target waster water is pertinent to the latter part, has selected Ni alloy such as ostenite type stainless steel 304 and 316, superstainless steel AL6XN, Inconel 625, MAT 21, and titanium Gr. 5 in order to measure corrosion resistance against those samples under the same conditions of temperature and pressure applied for a supercritical oxidation reactor. The result shows the identifiable difference in corrosion resistance by observing the surface states through a scanning probe microscope as well as measuring the weight loss through making the samples above deposited in wastewater for two-week and four-week stay. The purpose of this corrosion experiment is to identify the most corrosion-resistant material among sample species pre-selected according to pH concentration of wastewater in pursue of applying for a reactor exposed to the extreme corrosion environment. It is because such a reactor made of a verified material enables to safeguard a stable operation under the supercritical wastewater processing facility.

• 한국염색가공학회지
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• 제21권5호
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• pp.51-57
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• 2009

Since heavy metal pollution is a significant global environmental problem and very dangerous to human health, the improved methods for detecting heavy metals are required recently. Colorimetric chemosensors are now considered as one of the most effective analytical method used in the environment monitoring. New direct dyes having the function of colorimetric chemosensors were synthesized. When metal ions such as $Al^{3+}$, $Ca^{2+}$, $Cd^{2+}$, $Cr^{3+}$, $Cu^{2+}$, $Fe^{2+}$, $Fe^{3+}$, $Hg^{2+}$, $Li^+$, $Mg^{2+}$, $Na^+$, $Ni^{2+}$, $Pb^{2+}$ and $Zn^{2+}$ were added each solution of new direct dyes, the color of solution was changed and can be easily detected with naked eyes without expensive experimental equipment such as atomic absorption spectrometer (AAS) or inductively coupled plasma?mass spectrometer (ICP-MS). The new benzidine analogues were diazotized and reacted with couplers such as H-acid, J-acid, Chromotropic acid, Nevill-winther acid and gamma acid to synthesize new direct dyes. The structures of the new direct dyes were confirmed by high resolution mass spectrometer (FAB ionization) and evaluated with UV-Vis spectroscopy. The UV-VIS spectroscopy was measured for the dye solutions by adding various concentrations of metal ions. It was observed that the absorbance in UV-Vis spectra was changed as the heavy metal ions were added.

• 자원환경지질
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• 제38권4호
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• pp.481-492
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• 2005

이 연구에서는 광주지역 하상퇴적물에 대한 지질집단별 지구화학적 특성에 대해 규명 하고자 한다. 이를 위해 물이 흐르고 있는 1차 수계를 대상으로 하상퇴적물시료 104개를 채취하였고, 실험실에서 자연건조 시켰다. 화학분석을 위한 시료는 알루미나 몰타르를 이용하여 200메쉬 이하로 분쇄하였고, XRF ICP-AES, NAA분석을 실시하였다. 연구지역 하상퇴적물에 대해, 지질집단별 지구화학적 특성 비교와 기존 암석에 대한 연구에서 얻어진 암석화학적인 특성과의 비교를 위해, 선캠브리아기 화강편마암 지역, 쥬라기 화강암 지역, 백악기 화순안산암 지역으로 분리하였다 광주지역 하상퇴적물의 주성분원소 함량은 $SiO_2\;51.89\~70.63\;wt.\%,\;Al_2O-3\;12.91\~21.95\;wt.\%,\;Fe_2O_3\;3.22\~9.89\;wt.\%,\;K_2O\;1.85\~4.49\;wt.\%,\;MgO\;0.68\~2.90\;wt.\%,\;Na_2O\;0.48\~2.34\;wt.\%,\;CaO\;0.42\~6.72\;wt.\%,\;TiO_2\;0.53\~l.32\;wt.\%,\;P_2O_5\;0.06~0.51\;wt.\%\;and\;MnO\;0.05\~0.69\;wt.\%.$이다. 하상퇴적물과 암석에 대한 AMF 삼각도에서, 암석은 칼크-알칼리계열에 도시되는데 비하여, 하상퇴적물은 솔레아이트 계열과 칼크-알칼리계열의 경계부위에 도시된다. 이는 $Fe_2O_3$ 함량이 암석에서보다 하상퇴적물에 더 많이 함유되어 있는 것과 관련이 있는 것으로 보인다. $SiO_2$에 대한 $K_2O+Na_2O$의 비교그림에서, 하상퇴적물은 암석에서와 같이 subalkaline 계열에 점시된다. 하상퇴적물의 미량성분원소 및 희토류 원소 함량은 $Ba 590\~2170ppm$, Be$1\~2.4$ppm, Cu $13\~179ppm$, Nb $20\~34ppm$, Ni$10\~50ppm$, Pb $17\~30$ppm, Sr $70\~1025$ ppm, V$42\~135$ ppm, Zr$45\~171$ ppm, Li$19\~77$ppm, Co$4.3\~19.3$ppm, Cr$28\~131$ppm, Cs$3.1\~17.6$ ppm, Hf $5\~27.6$ ppm, Rb $388\~202$ ppm, Sb$0.2\~l.2$ ppm, Sc$6.4\~17$ ppm, Zn $47\~389$ ppm, Pa $8.8\~68.8$ ppm, Ce$62\~272$ppm, Eu$1\~2.7$ppm and Yb$0.9\~6$ppm의 범위를 보인다.

• 자원환경지질
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• 제32권6호
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• pp.611-631
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• 1999

Enviromental geochemisty and heary metal contamination at the Kongjueil mine creek were underaken on the basis of physicohemical properties and mineralogy for various kinds of water (surface, mine and ground water),soil, precipitate and sediment collected of April and December in 1998. Hydrgeochemical composition of the water samples are characterized by relatively significant enricant of Ca+Na, alkiali ions $NO_3$ and Cl inground and surfore water, wheras the mine waters are relatively eneripheral water of the mining creek have the characteristics of the (Ca+Mg)-$(HCO_3+SO_4)$type. The pH of the mine water is high acidity (3.24)and high EC (613$\mu$S/cm)compared with those of surface and ground water. The range of $\delta$D and $\delta^{18}O$ values (relative to SMOW) in the waters are shpwn in -50.2 to -61.6% and -7.0 to -8.6$\textperthousand$(d value=5.8 to 8.7). Using computer program, saturation index of albite, calcite, dolomite in mine water are nearly saturated. The gibbiste, kaolinite and smectite are superaturated in the surface and ground water, respectively. Calculated water-mineral reaction and stabilities suggest that weathing of silicate minerals may be stable kaolinite owing to the continuous water-rock reaction. Geochemical modeling showed that mostly toxic heavy metals may exist larfely in the from of metal-sulfate $(MSO_4\;^2)$and free metal $(M^{2+})$ in nmine water. These metals in the ground and surface water could be formed of $CO_3$ and OH complex ions. The average enrichment indices of water samples are 2.72 of the groundwater, 2.26 of the surface water and 14.15 of the acid mine water, normalizing by surface water composition at the non-mining creek, repectively. Characteristics of some major, minor and rate earth elements (Al/Na, K/Na, V/Ni, Cr/V, Ni/Co, La/Ce, Th/Yb, $La_N/Yb_N$, Co/Th, La/Sc and Sc/Th) in soil and sediment are revealed a narrow range and homogeneous compositions may be explained by acidic to intermediate igneous rocks. And these suggested that sediment source of host granitic gneiss colud be due to rocks of high grade metamorphism originated by sedimentary rocks. Maximum concentrations of environmentally toxic elements in sediment and soil are Fe=53.80 wt.% As=660, Cd=4, Cr=175, Cu=158, Mn=1010, Pb=2933, Sb=4 and Zn=3740 ppm, and extremely high concentrations are found are found in the subsurface soil near the ore dump and precipitates. Normalizing by composition of host granitic gneiss, the average enerichment indices are 3.72 of the sediments, 3.48 of the soils, 10.40 of the precipitates of acid mine drainage and 6.25 of the soils near the main adit. The level of enerichment was very severe in mining drainage sediments, while it was not so great in the soils. mineral composition of soil and sediment near the mining area were partly variable being composed of quartz, mica, feldspar, chlorite, vermiculite, bethierin and clay minerals. reddish variable being composed of quartz, mica, feldspar, chlorite, vermiculite, bethierin and clay minerals. Reddish brown precipitation mineral in the acid mine drainage identifies by schwertmanite. From the separated mineralgy, soil and sediment are composed of some pyrite, arsenopyite, chalcopyrite, sphalerite, galena, malachite, goethite and various kinds of hydroxied minerals.