For the remediation of the contaminated soil with heavy metals, Cd, Cr, Cu, and Pb, the reaction parameters were optimized. Tartaric acid (TA) and oxalic acid(OA) as a washing agent were evaluated as a function of concentration, reaction time, mixing ratio of washing agent and recovery of metals. The optimum washing conditions of TA and OA were in the ratio of 1 : 20 between soil and acid solution during 2 hr reaction under unbuffered pH solutions. At the optimized reaction conditions, the removal efficiencies were compared with that of 0.1 M HC1 and ethylenediamine tetraacetic acid(EDTA). TA showed higher efficiency on the removal of Pb than that of EDTA, which established for the remediation of contaminated soil with Pb and Cd metals. The recovery of metal ions from washing solution was achieved by adding calcium hydroxide and sodium sulfide by forming the precipitation of metal hydroxide and metal sulfide. Optimum amounts of sodium sulfide and calcium hydroxide were Cd = 25g/ℓ, Cu = 5∼10g/ℓ and Pb = 5∼10g/ℓ for the washing solution of OA and 2∼5g/ℓ for the washing solution of TA, respectively. The amounts of Na2S and Ca(OH)2 for the tartaric acid was less than that of oxalic acid.

The toxicity values of various heavy metals were evaluated by acute immobilization and chronic reproduction impairment tests, using Daphnia magna. Acute tests were evaluated by the inhibition of their mobilization after 24hrs without food addition. The tests of reproductive impairment were investigated for 21 days by food addition and exchange of water. The effect of each concentration was assessed by Probit analysis and t-test. The results obtained from this study were as follows : 1) The change of pH and DO was not significant in the acute tests, while, in the reproductive tests, pH was increased by 0.3∼1.4 and DO also increased. 2) The EiG50 values of immobilization to Daphnia magna in artificial fresh water were 0.030㎎/ℓ(Cu), 0.054㎎/ℓ(Cd), 0.12㎎/ℓ(Cr), 0.74㎎/ℓ(Pb), 3.4㎎/ℓ(As) and the NOEiC values were 0.010㎎/ℓ(Cu), 0.018㎎/ℓ(Cd), 0.010㎎/ℓ(Cr), 0.10㎎/ℓ(Pb), and 1.8㎎/ℓ(As). 3) The EiC50 values of reproductive impairment to Daphnia magna were 13.8㎍/ℓ(Cu), 2.9㎍/ℓ(Cd), 15.5㎍/ℓ(Cr), 61.7㎍/ℓ(Pb), 759㎍/ℓ(As), and NOErC values were 0.95㎍/ℓ(Cu), 0.54㎍/ℓ(Cd), 1.2㎍/ℓ(Cd), 7.4㎍/ℓ(Pb), 110㎍/ℓ(As). The results of tests using OECD artificial culture water were more sensitive than natural water for culturing. The presented data show that an artificial culture water is suitable in the experiment of bioassay for assessing the toxicity of materials.

The biosorption abilities of different parts of waste brown seaweeds and their derivatives to remove heavy metals(Cd, Zn, Pb, Cu, Fe, Ni, Mn) from waste water were evaluated. The two parts of waste brown seaweeds (Undaria pinnatifida) were stems and sporophyls, and the brown seaweed derivatives were alginic fibers, active carbon added alginate(AC-alginate) and dealginate. The abilities of the sporophyls to adsorb the heavy metal ions were higher than those of stems, and those of alginates were slightly higher than those of dealginate in single ion solution. With decreasing the size of biosorbents, the velocity and the amount of adsorption increased. The abilities of alginate to remove the heavy metal ions increased in multi-ion solutions by adding active carbon to alginate. The selectivity of these biosorbents(alginate, AC-alginate) to lead ion was highest and to manganese ion was lowest.

방해석 결정 성장시 나타나는 미량금속 양이온의 분배현상을 표면침전 및 연속 결정 성장과정을 통하여 관찰하였다. A, B, C 유형의 순수한 방해석이 각각 3가지 다른 초기 농도 즉 0.02, 0.2, 0.4M의 CaCl2.2H2O로부터 형성되었으며 이들의 표면 형태는 합성용액의 조성과 성장 속도에 의해 조절됨을 알 수 있었다. B 유형이 표면형태가 좀더 복잡하지만 A, B 유형은 대체로 단순한1014면을 가진 방해석과 유사한 표면형태를 보여준다. 이에 반해 C 유형에서는 0112면이 주로관찰되었다. 순수한 방해석 위에 (Ca, Me)CO3층의 대해 1014면 3 방향에 대한 전자현미분석 결과 금속이온의 특징적인 분배현상을 알수 있었다. Mn2+ /과 Co2+ 는 0112 에 수직으로 반면 Sr2+ /는 1014에 수직 또는 평행한 방향으로 선택적으로 분배되는 현상이 관찰되었다. 합성 방해석 표면 형태에 따른 금속 이온들의 분배 친화도를 Mn2+ 이 C 유형〉B 유형 〉A 유형 그리고 Co2+ 은 B 유형 〉A 유형 〉C 유형이다. 이들중 Sr2+는 특히 1014면이 잘발달된 A유형에 더 많은 친화도를 갖는 것으로 나타났다.

In order to study the long-term change of heavy metal concentrations in the Kumho river water, water analysis was conducted at l3sites surrounding the Kumho river system for l8times from September 1993 to August 1999. Analytical items for the study of water quality are Cu, Zn, Cd, Cr, Fe, Mn and Pb. The six year term studied in this work was divided into Part Ⅰ and Part Ⅱ, which covers the period from September 1993 to August 1996 and the period from September 1996 to August 1999, respectively. The mean concentrations of Cu, Zn, Cd, Cr, Fe, Mn and Pb in the unit of ppm for the PartⅠ period showed 0.032, 0.025, 0.006, 0.006, 0.050, 0.053 and 0.019, respectively. The mean concentrations of Cu, Zn, Cd, Cr, Fe, Mn and Pb in the unit of ppm for the Part Ⅱ period showed 0.001, 0.001, 0.001, 0.004, 0.020, 0.002 and 0.002, respectively. The heavy metal concentrations in the Kumho river water for the second period were found to be decreased by 1/32, 1/25, 1/6, 1/1.5, 1/2.5, 1/26.5 and 1/9.5 for Cu, Zn, Cd, Cr, Fe, Mn and Pb, respectively. The present results clearly indicate that the water quality in the Kumho river is improving in terms of heavy metal contaminations.

The purpose of this study was to evaluate the effects of Ca(OH)2 and CO2 additions on the corrosion of metal coupons (ductile iron, galvanized steel, copper and stainless steel). Corrosion rate and released metal ion concentration of ductile iron and galvanized steel was decreased by adjusting alkalinity, calcium hardness and pH with Ca(OH)2 & CO2 additions named CCPP (Calcium Carbonate Precipitation Potential) index control process. But the effects of Ca(OH)2 & CO2 additions on copper and stainless steel were less than those on ductile iron and galvanized steel. When ductile iron coupon was exposed to water treated with Ca(OH)2 & CO2 additions, the main components of corrosion product formed on its surface were CaCO3 and Fe2O3 or Fe3O4, which often reduce the corrosion rate by prohibiting oxygen transport to the metal surface.