• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2003년도 추계학술발표회
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• pp.379-381
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• 2003

Metal sorption onto the ICS (Iron oxide coated sand) was studied in batch experiments. Heavy metal cations such as Cd, Pb, and Cu, and a metal anion, As, which sporadically exist in mine sites, were tested for the sorptive removal by ICS. In low pH conditions As showed the highest removal efficiency compared to the other metal cations. And the sorption removal of As was apparently pH-independent reaction. However, removal of metal cations increased with pH and above pH 7 most metal cations showed very low soluble concentrations after treatment. Such a high removal ratio of metal cations above the neutral pH appeared predominantly due to precipitation.

• 한국토양비료학회지
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• 제28권2호
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• pp.114-122
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• 1995

토양유기물(土壤有機物)에 의한 중금속(重金屬)의 흡착(吸着)현상을 구명(究明)하기 위하여 이탄토(泥炭土)에서 humic acid를 분리정제(分離精製)하여, humid acid-metal complex 생성반응(生成反應)에 대한 mechanism을 조사(調査)하였다. 1. Humic acid-metal complex의 흡광도(吸光度)는 장파장영역(長波長領域)에서 단파장영역(短波長領域)으로 갈수록 Zn-HA > Cd-HA > Cu-HA의 순(順)으로 증가(增加)하였다. 2. Humic acid의 carboxyl group과 phenolic OH group들이 중금속(重金屬) ion들과 반응(反應)하여 complex를 생성(生成)하였으며 그 생성량(生成量)은 Cu > Zn ≧ Cd의 순(順)이었다. 3. Humic acid-medal complex의 안정도(安定度) 상수(常數)는 pH가 증가(增加)함에 따라 增加하였으며 1차(次) 안정도(安定度) 상수(常數)는 Zn>Cd>Cu 순(順)이었고, 2차(次) 안정도(安定度) 상수(常數)는 Cu>Zn>Cd의 순(順)이었으며, 總安定도 常數는 Cu>Zn>Cd의 순(順)이었다. 4. Humlc acid와 중금속(重金屬)ion들 상호(相互) 간(間)의 평균결합수(平均結合數)는 pH가 증가(增加)함에 따라 Cu>Zn>Cd의 順으고 增加하였다. 5. Humic acid에 의한 중금속(重金屬) ion들의 complex생성과정(生成課程)에서 barboxyl group만이 관여(關與)하는 것과 car-boxyl gruup 및 phenolic OH group이 동시(同時)에 관여(關與)하는 두가지 흡착(吸着)mechanlsm을 제안할 수 있었다.

• 자원환경지질
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• 제28권3호
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• pp.231-241
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• 1995

It is well known that hydroxyapatite [$Ca_{10}(PO_4)_6(OH)_2$] have an exchangeability for various heavy metal ions in aqueous solution. To evalute the feasibility of employing the synthetic hydroxyapatites as an eliminatable exchanger for environmentally noxious caions in waste water, the adsorption properties, the removal capacities and the selectivity of the apatites for various cations were investigated in more detailed. The heavy metal cations have been exchanged in calcium part of hydroxyapatite. The order of the degree of amount exchanged of the investigated cations is $Pb^{2+}>Cd^{2+}>Zn^{2+}>Ba^{2+}$. The molar ratios between released $Cd^{2+}$ ions and remeved divalent metal cations in the reacted solution with hydroxyapatite are roughly close to an integer 1.0, suggesting that an ion-exchange reaction could have played a major role in the removal of heavy metals rather then an adsorption effect. The exchangeability of the hydroxyapatite powder of Ca/P molar ratio 1.67, which have specipic surface area of $104.5m^2g^{-1}$, appeared to be better then $237.6{\mu}g$ per g for $Pb^{2+}$ ions. The removal capacity of the heavy metal ions varies directly as particle size of hydroxyapatites. All evidences obtained indicate that the synthesized hydroxyapatite powders by precipitation reaction method can be employed as an effective cation exchanger for eliminating noxious ions in waste water even in some improvemental.

• Applied Biological Chemistry
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• 제41권8호
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• pp.587-594
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• 1998

The objective of this research was to characterize effects of Cu or Cd additions on chemistry of soil quality indices, such as pH, EC, cation distribution and buffering capacity. Metals were added at rates ranging from 0 to 400 mg $kg^{-1}$ of soil. Soil solution was sequentially extracted from saturated pastes using vacuum. Concentrations of Cu or Cd remaining in soil solutions were very low as compared to those added to the soils, warranting that most of the added metals were recovered as nonavailable fractions. Adsorption of the added metals released cations into soil solution causing increases of ionic strength of soil solution. At metal additions of $200{\sim}400\;mg\;kg^{-1}$, EC of soil solution increased to as much as $2{\sim}4\;m^{-1}$; salinity levels considered high enough to cause detrimental effects on plant production. More divalent cations than monovalent cations were exchanged by Cu or Cd adsorption. The nutrient buffering capacity of soils was decreased due to the metal adsorption and release of cations. pH of soil solution decreased linearly with increasing metal loading rates, with a decrement of up to 1.3 units at 400 mg Cu $kg^{-1}$ addition. Influences of Cu on each of these soil quality parameters were consistently greater than those of Cd. These effects were of a detrimental nature and large enough in most cases to significantly impact soil productivity. It is clear that new protocols are needed for evaluating potential effects of heavy metal loading of soils.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 1997년도 총회 및 춘계 학술발표회 논문집
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• pp.8-11
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• 1997

Current methods of evaluating soil contamination by heavy metals rely on analyzing samples for total contents of metals or quantities recovered in various chemical extracting solutions. Results from these approaches provide only an index for evaluation because these methodologies yield values not directly related to bioavailability of soil-borne metals. In addition, even though concentrations of metals may be less than those required to cause toxic effects to biota, they may cause substantial effects on soil chemical parameters that determine soil quality and sustainable productivity. The objective of this research was to characterize effects of Cu or Cd additions on soil solution chemistry of soil quality indices, such as pH, EC, nutrient cation distribution and quantity/intensity relations (buffer capacity). Metals were added at rates ranging from 0 to 400 mg/kg of soil. Soil solution was sequentially extracted from saturated pastes using vacuum. Concentrations of Cu or Cd remaining in soil solutions were very low as compared to those added to the soils, warranting that most of the added metals were recovered as nonavailable (strongly adsorbed) fractions. Adsorption of the added metals released cations into soil solution causing increases of soluble cation contents and thus ionic strength of soil solution. At metal additions of 200~400 mg/kg, EC of soil solution increased to as much as 2~4 dS/m; salinity levels considered high enough to cause detrimental effects on plant production. More divalent cations (Ca+Mg) than monovalent cations (K+Na) were exchanged by Cu or Cd adsorption. The loss of exchangeable nutrient cations decreased long-term nutrient supplying capacity or each soil. At 100 mg/kg or metal loading, the buffering capacity was decreased by 60%. pH of soil solution decreased linearly with increasing metal loading rates, with a decrement of up to 1.3 units at 400 mg Cu/kg addition. Influences of Cu on each of these soil quality parameters were consistently greater than those of Cd. These effects were of a detrimental nature and large enough in most cases to significantly impact soil productivity. It is clear that new protocols are needed for evaluating potential effects of heavy metal loading of soils.

• 한국토양비료학회지
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• 제28권2호
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• pp.105-113
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• 1995

토양(土壤)의 구성성분(構成成分) 중 많은 부분(部分)을 차지하고 있는 철(鐵) 및 알루미늄의 수산화물(水酸化物)에 의한 중금속(重金屬)ion들의 흡착(吸着) mechanism을 구명(究明)하기 위하여, 무정형(無晶型) Fe 및 Al 수산화물(水酸化物), Goethite 및 Gibbsite에 의한 중금속(重金屬)ion들의 흡착(吸着) mechanism을 조사(調査)하였다. 1. 철(鐵) 및 알루미늄의 수산화물(水酸化物)에 의한 중금속(重金屬)ion들의 흡착등온선(吸着等溫線)은 Langmuir식(式)에 잘 부합되었으며, 이들의 최대흡착량(最大吸着量) 및 흡착(吸着)에너지는 무정형(無晶型) 수산화물(水酸化物)이 결정형(結晶型) 수산화물(水酸化物)보다 또 알루미늄 수산화물(水酸化物)이 철수산화물(鐵水酸化物)보다 많았다. 2. 중금속(重金屬)ion별(別) 최대흡착량(最大吸着量) 및 흡착(吸着)에너지는 Cu>Zn>Cd의 순(順)으로 CEC, 비표면적(比表面積) 및 하전밀도(荷電密度)와 정(正)의 상관(相關)이 인정(認定)되었다. 3. Goethite 및 Gibbsite에 의한 중금속(重金屬)ion들의 첫번째 흡착(吸着) mechanism은 $Cl^-$를 수반하는 nonspecific adsorption으로 1 Mole의 중금속(重金屬)ion이 흡착(吸着)되는데 대하여 표면(表面) aquo group이나 hydroxo group으로 부터 1 Mole의 H가 탈착(脫着)되었으며, 회응비율(灰應比率)은 pH가 증가(增加)할수록 감소(減少)되고 흡착(吸着)된 중금속(重金屬)ion들은 치환성양(置煥性陽)ion에 의하여 재치환(再置換)될 수 있었다. 4. Goethite 및 Gibbsite에 의한 중금속(重金屬)ion들의 두번째 흡착(吸着) mechanism은 $Cl^-$을 수반하지 않는 specific adsorption으로 1 Mole의 중금속(重金屬)ion이 흡착(吸着)되는데 대하여 표면(表面) aquo group이나 hydroxo group으로부터 2 Mole의 $H^+$가 탈착(脫着)되었으며. 흡착반응(吸着反應)의 비율(比率)은 pH가 증가(增加)할수록 증가(增加)되었으며 흡착(吸着)된 중금속(重金屬)들은 置換性 陽ion에 의하여 再置煥되지 않았다.

• 한국항해항만학회:학술대회논문집
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• 한국항해항만학회 2016년도 춘계학술대회
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• pp.130-131
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• 2016

Although many metals contaminated sediment from coastal area contain both anionic and cationic heavy metals, the current remediation technologies are not effective for stabilize heavy metals of both anionic and cationic elements from contaminated coastal region. the present work investigated the efficiency and mechanism of immobilization of Fe, Zn, Cr, Cu, Pb and Cd metal solutions in modified zeolite based biostimulant ball. Biostimulant ball containing acetate, nitrate and sulphate which are enhance the activity of marine microorganisms and it can act as electron donors and electron acceptors. Modified zeolite and chelating agent is greatly enhance the metal stabilization due to increased immobility of the analysed metals. The XRD, FT-IR and SEM of modified zeolite which cheating agents containing heavy metals were investigated. The results indicated that heavy metals could be effectively immobilized in modified zeolite and chelating agents in BSB added sediment. The immobilization of heavy metals in modified zeolite and chelating agents along with BSB could be due to stabilize of heavy metal cations. Immobilization of heavy metals using BSB with modified zeolite and chelating agent has lower cost effect and enhance the sediment quality.

• 한국물환경학회지
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• 제25권1호
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• pp.151-158
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• 2009

The objective of this study was to determine on optimum ratio of oxidant and catalyst and to evaluate affecting factors such as anions and cations on persulfate oxidation of organic pollutant. Fe(II) activated the persulfate anion to produce a sulfate free radicals and thus effectively used to degrade the target organic pollutant in aqueous system. The chloride ions reacted with sulfate radical produced the $Cl^{\cdot}$ atom and had positive effects on the oxidation of organic pollutant at the initial stage. However, it was observed that chloride ions had the scavenging effects on the rate of oxidation of organic pollutant. Cations and some heavy metals were partly able to activate the persulfate anion to generate a sulfate free radical. However, high levels of cations inhibited the oxidation of organic pollutant.

• 한국환경농학회지
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• 제7권2호
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• pp.96-101
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• 1988

Ionic strength 및 공존(共存) 음(陰)Ion($Cl^-$, $SO^{2-}\;_4$, $ClO^-\;_4$)이 Zeolite에 의(依)한 중금속(重金屬)의 흡착(吸着)에 미치는 영향(影響)을 조사(調査)한 결과(結果)는 다음과 같다. Ionic strength별(別) Zeolite에 의(依)한 Cd, Cu 및 Zn의 흡착등온선(吸着等溫線)은 Freundlich 식(式)에 잘 부합(符合)되었다. Ionic strength가 증가(增加)할수록 중금속(重金屬)의 흡착량(吸着量)은 3종(種)의 서로 다른 음(陰)Ion이 공존(共存)하여도 모두 감소(減少)하는 경향(傾向)이었다. Background salt의 음(陰)Ion 종류별(種類別) 중금속(重金屬) 흡착량(吸着量)은 $ClO^-\;_4>SO^{2-}\;_4>Cl^-$의 순(順)이었으며 흡착평형용액내(吸着平衡溶液內)에서 음(陰)Ion은 Ligand로 작용(作用)하여 중금속(重金屬) Ion들과 Complex를 형성(形成)하는 능력(能力)에 차이(差異)가 있음이 인정(認定)되었다.

• 대한화학회지
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• 제48권2호
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• pp.129-136
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• 2004

타이테늄과 [타이테늄 + 나트륨 (칼륨)]으로 치환된 11${\AA}$의 토버모라이트 고체가 180 $^{\circ}C$의 수열반응 조건하에서 합성되었고, 이 화합물은 Fe$^{2+},\;Zn^{2+},\;Cd^{2+},\;Pb^{2+}$과 같은 중금속 양이온에 대해서 양이온 교환 성질을 보였다. 이 고체에 흡착된 중금속 양이온은 Fe$^{2+}>Zn^{2+}>Cd^{2+}>Pb^{2+}$의 순서로 그 양이 감소하였고, 10% [타이테늄 + 칼륨]으로 치환된 토버모라이트가 최대값을 보였다. 총 양이온 교환능은 10% [타이테늄 + 칼륨]으로 치환된 토버모라이트와 타이테늄으로만 치환된 토버모라이트에 대해서 각각 71에서 89 meq/100 g와 50에서 56 meq/100 g로 측정되었다. 이 결과는 10% [타이테늄 + 칼륨]치환이 비치환 토버모라이이트 보다 2.4배 이상의 양이온 교환능이 있음을 보여준다. 이는 교환체의 활성자리 수의 증가에 의한 것이다. 합성된 토버모라이트의 격자구조로의 타이테늄과 [타이테늄 + 나트륨 (칼륨)]의 포함은 각각 Ti$^{4+}\;{\Leftrightarrow}\;2Ca^{2+}$와 Ti$^{4+}+2Na^+(K^+)\;{\Leftrightarrow}\;3Ca^{2+}$의 치환에 의한 것이다. 합성과정 중 고체의 결정 격자로의 타이테늄과 [타이테늄 + 나트륨 (칼륨)]의 포함에 관한 메커니즘과 이들 고체에 의한 중금속 양이온 흡수가 연구되었다.