• 한국지하수토양환경학회지:지하수토양환경
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• 제18권3호
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• pp.93-108
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• 2013

This study is aimed to prepare the effective detail survey methods(Phase II) of abandoned metal mines through the contamination assessment for mine types and facilities in the abandoned metal mine areas. The study sites of 12 abandoned mines are located in Gyeonggi-do and Gangwon-do and those were chosen among 310 sites that the Phase II survey was conducted from 2007 to 2009 after considering the results of Phase I for abandoned mines scattered all over the country. 12 study sites were classified into four types; Type I sites only have pit mouth. Type II sites have pit mouth and mine-waste field. Type III sites have pit mouth and tailing sorting field. Type IV sites have pit mouth, tailing sorting field and concentrator(s). In forest land, paddy soil and farm land of Type I, As and Cd were showed average concentration, and Cu and Pb were high on the pit mouth area in one mines where the pit mouth was developed within 500 m. In the mines of Type II, Cu and Pb were showed average concentration too, but As and Cd were slightly high in pit mouth and mine-waste field. The mines of Type III which had grinding particle process through physical separation milling or hitting showed similar tendency with Type II. However, mines of Type IV pit mouth, mine-waste field and showed various results depending on defining the contamination sources. For example, if contamination source was pit mouth, the mixed results of Type I, II, II were showed. In tailing sorting field which was regarded as the most important source and having high mobility, however, if there were no facilities or it was difficult to access directly, field sampling was missed occasionally during phase I and phase II survey. For that reason, the assessment for tailing sorting field is missed and it leads to completely different results. In the areas of Type I mines, the concentration of heavy metals exceeded precautionary standards of soil contamination or not within 1,000 meters of pit mouth. Nickel(Ni) was the largest factor of the heavy metal contamination in this type. The heavy metals except Arsenic(As) were shown high levels of concentration in Type II areas, where pit mouth and mine-waste field were operated for making powder in upriver region; therefore, to the areas in the vicinity of midstream and downstream, the high content of heavy metals were shown. The tendency of high level of heavy metals and toxic materials contained in flotation agent used during sorting process were found in soil around sorting and tailing field. In the abandoned-pit-mouth area, drygrinding area and tailing sorting field area, the content of Cupper(Cu) and Zinc(Zn) were higher than other areas. Also, the contaminated area were larger than mine reclamation area(2,000 m) and the location of tailing sorting field was one of the important factors to estimate contaminated area.

• 대한화학회지
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• 제54권5호
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• pp.541-550
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• 2010

새로운 일곱 자리 질소-산소($N_4O_3$)계 리간드 N,N'-Bis(2-hydroxybenzyl)-1,3-bis[(2-aminoethyl)amino]-2-propanol(H-BAP 4HCl)를 합성하였다. H-BAP 4HCl의 페놀 수산기의 para위치에 브롬, 염소, 메톡 시기 및 메틸기를 가진 Br-BAP 4HCl, Cl-BAP 4HCl, $CH_3O$-BAP 4HCl 및 $CH_3$-BAP 4HCl 염산염을 합성 하였다. 각 리간드의 화학구조는 C, H, N 원소분석법, $^1H$-NMR 및 $^{13}C$-NMR 분광법, 적외선 분광법 및 질량분석법을 통하여 확인하였다. 합성된 $N_4O_3$계 리간드의 전위차 적정 법을 이용하여 계산된 양성자 단계 해리상수는 여섯 단계의 해리상수(${\logK_n}^H$)값을 나타내었고, 각 리간드의 양성자 총괄 해리상수($log{\beta}_p$) 값은 Br-BAP < Cl-BAP < H-BAP < $CH_3O$-BAP < $CH_3$-BAP의 순서로 para Hammett 치환기상수($\sigma_p$) 값의 순서와 역순으로 잘 일치하였다. 각 리간드들과 전이금속(II) 이온들의 착물 안정도상수($logK_{ML}$) 값의 크기순서는 Co(II) < Ni(II) < Cu(II) > Zn(II) > Cd(II) > Pb(II)로 나타났다. 이때 각 리간드들과 전이금속(II) 이온들의 착물 안정도상수 값은 리간드의 총괄 해리상수 값의 크기순서와 같은 경향을 나타내었다.

• 한국산업융합학회 논문집
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• 제7권1호
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• pp.107-113
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• 2004

Several transition metal complexes, [$M(L)X_2$](M=Pd(II), Ni(II); X=CI, Br) are prepared with aminophosphine ligands such as 1,2-bis{(diphenylphosphino)amino}ethane{$Ph_2PNHCH_2CH_2NHPPh_2$}($L_1$), 1,2-bis{(diphenylphosphino)amino}propane{$Ph_2PNHCH(CH_3)CH_2NHPPh_2$}($L_2$), trans-1,2-bis{(diphenylphosphino)amino}cyclohexane{$Ph_2PNHC_6H_{10}NHPPh_2$}($L_3$) and 1,2-bis{(diphenylphosphino)amino}benzene{$Ph_2PNHC_6H_4NHPPh_2$}($L_4$). The properties of these complexes are characterized by optical spectroscopic methods including UV/vis spectroscopy, CD, IR, $^1H$- and $^{31}P-NMR$ together with conductometer and elemental analysis. All complexes are stable under atmospheric environment. Catalytic reactivity for C-C coupling between [$M(L)X_2$] and Grignard reagents(RMgX; R=phenyl, propyl, buthyl) by thermolysis were investigated utilizing GC/mass, $^1H$- and $^{13}C-NMR$. When mol scale is 1:20 at [$Pd(L)Cl_2$] and Grignard reagents, the high catalytic activity for C-C coupling is apparent. The [$M(L)X_2$](X=Cl, Br) complexes which have strong bond at M-P exhibit high yields for C-C coupling reactions. When the central metal ion is Pd(II), the high catalytic activity for C-C coupling is apparent. The complex coordinated with Br shows higher catalytic activity for C-C coupling reactions compared to Cl.

• 약학회지
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• 제45권5호
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• pp.448-454
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• 2001

The contents of heavy metals in boiled Sibjeonaebotang with those in its herbal ingredients are compared. The herbal medicines of Sibjeonaebotang were bought at 10 defferent markets. The contents of 14 heavy metals (Ag, As, Ba, Cd, Cr Cu, Fe, Hg, Mn, Ni, Pb, Sb, Sn, Zn) were analysed using ICP It was found out that 5 heavy metals (Pb, As, Ba, Fe, Sb) were detected in only one boiled Sibjeonaebotang But they were detectable in all Sibjeonaebotang and its herbal before boiling. For example the content of Hg in one pack of Sibjeonaebotang before boiling was 0.064$\pm$0.016 me and Hg in boiled one was 0.002$\pm$0.005mg. These results suggest that boiled Sibjeonaebotang which we take is less harmful than herbal medicine itself by heavy metals.

• 대한화학회지
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• 제35권6호
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• pp.645-652
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• 1991

몇 가지 전이금속이온(Co(Ⅱ), Ni(Ⅱ), Cu(Ⅱ), Zn(Ⅱ)) 및 후전이금속이온(Cd(Ⅱ), Hg(Ⅱ), Pb(Ⅱ))과 $N_2O_3$계 거대고리 리간드인 1,15-diaza-3,4 : 12,13-dibenzo-5,8,11-trioxacyclooctadecane 사이에 형성되는 착물의 안정도 상수를 수용액에서 전위차 적정법으로 결정하였다. 각 착물의 안정도 상수$(logK_f)$는 $25^{\circ}$C에서 Co(Ⅱ): 3.83, Ni(Ⅱ) : 4.56, Cu(Ⅱ) : 7.74, Zn(Ⅱ) : 4.98, Cd(Ⅱ) : 3.91, Hg(II) : 14.87, Pb(Ⅱ) : 6.65이었다. 전이금속착물의 안정도 순위는 Williams-Irving 서열인 Co(Ⅱ) < Ni(Ⅱ) < Cu(Ⅱ) < Zn(Ⅱ)와 일치하였고, 후전이금속착물의 안정도는 Cd(Ⅱ) < Pb(Ⅱ) < Hg(Ⅱ)이 순위이었다. 한편 메탄올 용액에서 자외-가시선이온과 리간드가 1:1인 조성을 가졌으나, Ni(Ⅱ), 착물은 1:1과 1:2 두 가지 조성을 가질 수 있음을 알았으며, 또 디메틸술폭시드 용액에서 $^1H-$와 $^{13}C-$핵자기공명스펙트럼을 분석하여 후전이금속이온 착물은 주로 리간드의 질소원자가 결합에 기여함을 알았다. Cu(Ⅱ)와 Zn(Ⅱ)이 고체착물은 원소분석, 전기전도도, 자화율 측정, 자외-가시선 및 적외선 스펙트럼분석 등으로 Cu(Ⅱ) 착물은 일그러진 팔면체, 그리고 Zn(Ⅱ) 착물은 사면체 구조를 이루고 있는 것으로 예측되었다.

• 분석과학
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• 제17권3호
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• pp.199-210
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• 2004

Amberite XAD-16 다공성 수지에 4,5-dihydroxynaphthalene-2,7-disulfonic acid (chromotropic acid, CTA)를 화학적으로 결합시켜 XAD-16-CTA형 새로운 킬레이트 수지를 합성하고, 적외선분광법과 원소분석법으로 확인하였다. 이 킬레이트 수지에 대한 금속마감 산업과 관련 있는 9개 금속이온을 포함하는 Cr(III) 및 Cr(VI) 이온들의 흡착 및 탈착 특성을 뱃치법과 용리법으로 조사하였다. XAD-16-CTA 킬레이트수지는 1~5 M의 HCl, $HNO_3$ 및 NaOH 등의 산과 염기 용액에서 매우 안정하였다. pH 2에서 Cr(VI) 이온과 Cr(III) 이온이 공존하는 혼합용액으로부터 Cr(VI) 이온만을 선택적으로 분리할 수 있음을 확인하였으며, Cr(VI)의 최대 흡착용량은 1.2 mmol/g 이었다. 또한 Cr(VI) 이온의 흡착에 미치는 공존 음이온의 영향을 검토한 결과 음이온인 $F^-$, $SO{_4}^{2-}$, $CN^-$, $CH_3COO^-$, $NO{_3}^-$ 이온은 흡착율을 감소시켰으며, $PO{_4}^{3-}$와 $Cl^-$는 흡착에 큰 영향을 미치지 않았다. pH 2에서 킬레이트 수지에 의한 돌파점용량과 총괄용량으로부터 얻은 금속이온의 용리순서는 Cr(VI)>Sn(II)>Fe(III)>Cu(II)>Cd(II)${\simeq}Pb(II){\simeq}Cr(III){\simeq}Mn(II){\simeq}Ni(II){\simeq}Al(III)$이었다. 한편 $HNO_3$, HCl 및 $H_2SO_4$ 등의 탈착제에 의한 Cr(VI) 이온의 탈착특성을 조사한 결과 3 M HCl에서 높은 탈착효율을 나타내었다. 결과적으로, XAD-16-CTA 킬레이트 수지는 여러 가지 금속이온이 혼합된 금속마감산업 인공폐액 중 Cr(VI) 이온의 선택적 분리, 농축 및 회수에 매우 유용함을 알 수 있었다.

• 대한예방한의학회지
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• 제3권2호
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• pp.151-170
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• 1999

This study was to investigate the metal accumulation from SipJeonDaeBo-Decoction to rat blood of Sprague Dawley. 1. There were no significance in body weight, water dose feed ingestion quantity, liver, kidney, brain, bone weights between the control and the experimental groups. Under the experiment with drinking waters was no metal ${\sim}\;0.65mg/L$ detected. Metal level within feed found 0.0001-376.983mg/kg. 2. In the pack of SipJeonDaeBo-decoction, there detected no metal ${\sim}2.086mg/L$ 3. After P.O(per os) SipJeonDaeBo-decoction, As is detected $2.390{\pm}0.812mg/kg$ in blood; Cd $0.001{\pm}0.001mg/kg$, Co $0.003{\pm}0.001mg/kg$, Cr $0.432{\pm}0.234mg/kg$, Cu $1.013{\pm}0.373mg/kg$, Fe $426.293{\pm}114.842mg/kg$, no Hg, Mn $0.109{\pm}0.082mg/kg$, Ni $0.122{\pm}0.068mg/kg$, Zn $3.584{\pm}1.270mg/kg$. 4. The concentration of Hazardous heavy metal (As, Cd, Co, Cr, Hg, Ni, Pb) within blood control group is searched $0.488{\pm}0.138\;mg/l$; experiment I group $0.432{\pm}0.080mg/l$, experiment II group $0.588{\pm}0.213mg/l$. In the concentration of non hazardous heavy metal(Cu, Fe, Mn, Zn) control group $101.409{\pm}6.832mg/l$; experiment I group $96.062{\pm}5.732\;mg/l$, experiment II group $125.139{\pm}044.820mg/l$. 5. Correlation among every metal in blood Zn and Cr was 0.87956 ; Cd and As -0.02316, Pb and As -0.08738, Ni and As 0.07824, Mn and As 0.07824, Mn and Cd 0.04999. Briefly under the injection of SipJeonDaeBo-decoction, this study was defined within safety in blood level by P.O. during 10 days.

• 대한한의학회지
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• 제23권1호
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• pp.67-82
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• 2002

Objectives: In recent years, extensive focus has been laid on adulteration of herbal medicine with heavy metals. This may be mainly due to soil contamination by environmental pollution. The objective of this study is to identify the contents of various heavy metals in the blood from Ohjeok-san (Wuji-san) Decoction (OD) treated-rats. Methods: For this study, 13 kinds of metals including essential and heavy metals, i.e. A1, As, Cd, Co, Cr, Cu, Fe, Hg, Mn, Ni, Pb, Se and Zn were analyzed by a slight modification of EP A methods and the following results are obtained. Results: 1. There was no significant difference between the OD-treated groups and control group in liver, kidney, bone, brain and weight, especially no significant difference at the 5th and 10th days in weight and the amount of food intake. 2. The amount of each metal analyzed in the blood were as follows; A1: 2.3~3.07 mg/l, As: 2.90~3.66 mg/l, Cd: 0~0.001 mg/l, Co: 0~0.01 mg/l, Cr: 0.40~043 mg/l, Cu: 0.93~1.88 mg/l, Fe: 414.35~464.46 mg/l, Hg: 0.01 mg/l, Mn: 0.10~0.17 mg/l, Ni: 0.01 mg/l, Pb: 0.03~012 mg/l, Se: 0.73 mg/l, Zn: 3.41~4.13 mg/l by groups, respectively. In control and experimental group, Experimental I and other experimental II, III, IV, and V groups, there were no significant differences. 3. The amount of non-toxic metals (A1, Co, Cu, Fe, Mn, Se, Zn) were $64.1{\pm}7.71{\;}mg/l$ in the control group and 60.70~67.58 mg/l in the experimental groups I, II, III, IV and V. The amount of Toxic metals (As, Cd, Cr, Ag, Pb) were $0.68{\pm}0.21{\;}mg/l$ in the control group and 0.57 ~ 0.66mg/l in the experimental groups. The total amount of metals were 32.35 mg/l in the control group and 30.48~34.12 mg/l in the test groups I, II, III, IV and V, respectively. Conclusions: There was no significant difference of metal concentration in the blood from the OD-treated-rats compared to those of the control group even if higher dosage (1~8 times the dosage for a person) of OD was administered. This may be mainly due to a decoction treatment which contains only supernatants filtered from the herb-mass after boiling. This indicates the legal limitation for metal concentration in herbal medicine must be applied according to different treatment methods of herbal medicine.

• 생태와환경
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• 제52권3호
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• pp.179-191
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• 2019

시화호 중금속 오염원을 추적하기 위하여 산업단지 5개 하천에서 하천수와 퇴적물을 채취하여 중금속 분포 특성과 오염도를 평가하였다. 용존 및 입자성 Ni과 Cu는 군자천에서, Zn과 Pb은 정왕천에서, Cd은 시흥천에서 상대적으로 높은 농도를 보이고 있어, 하천에 따라 유출되는 금속 오염원이 다른 것을 알 수 있었다. 하천 퇴적물 내 중금속의 평균농도는 Cu가 $2,549mg\;kg^{-1}$로 가장 높았으며 Cu>Zn>Pb>Cr>Ni>As>Cd>Hg의 농도순이었다. 시흥천에서 As를 제외한 금속원소의 평균농도가 다른 하천에 비해 매우 금속오염도가 큰 것으로 나타났다. 전체 하천 퇴적물 조사 정점 중 Cr (57%), Ni (62%), Cu (84%), Zn (60%), Cd (68%), Pb (81%)이 저서생물에 독성이 나타날 가능성이 있는 II 등급이상의 높은 농도였다. 농집지수를 통한 오염도 평가 결과, 하천 퇴적물 내 Cu와 Cd은 extremely polluted, Zn과 Pb은 heavily polluted의 오염상태로 구분되었다. 전체 퇴적물의 59%가 독성이 나타날 가능성이 높아 오염규모 확인이 필요한 "나쁨"의 등급이었으며, 35%의 조사 정점은 중장기적으로 배출시설 관리가 필요한 "매우 나쁨"에 해당되는 오염단계를 보이고 있었다. 하천수와 퇴적물 내 높은 금속 농도와 공간분포 특성을 고려하였을 때 금속오염은 금속의 제조와 사용과 관련된 산업폐수 즉 하천에 직접 유출되는 하수구를 통한 오염임을 알 수 있었다. 시화호의 주요한 금속 오염원은 산업활동에 기인한 높은 농도의 중금속을 포함한 폐수이며, 이 폐수가 지속적으로 하천을 통해 공급되고 있는 것으로 판단된다.

• 대한예방한의학회지
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• 제6권2호
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• pp.66-85
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• 2002

Traditional herbal medicine is used extensively among the Korean populations, and other Asian countries employ similar therapies as well In recent years, extensive focus was laid on adulteration of the herbal medicine with heavy metals. This may be mainly due to a soil contamination by an environmental pollution. The objective of this study is to identify the contents of various heavy metals in the blood from OhJeokSan-Decoction (OD) treated-rats. For this study, 13 kinds of metals including essential and heavy metals, i.e. Al, As, Cd, Co, Cr, Cu, Fe, Hg, Mn, Ni, Pb, Se and Zn were analyzed by a slight modification of EPA methods and the following results are obtained. ; 1. There is no significant difference between the OD-treated groups and control group in liver, kidney, bone, brain, weight, food intake. 2. The amount of each metal analyzed in the liver are as follows; Al ; $0.235{\sim}4.215mg／kg$, As ; $0.103{\sim}0.461mg／kg$, Cd ; $0.005{\sim}0.010mg／kg$, Co ; $0.017{\sim}0.046mg／kg$, Cr ; $0.137{\sim}0.403mg／kg$, Cu ; $1.736{\sim}4.827mg／kg$, Fe ; $54.472{\sim}381.447mg／kg$, Hg ; not detected, Mn ; $1.159{\sim}2.803mg／kg$, Ni ; $0.007{\sim}0.095mg／kg$, Pb ; not detected, Se ; $0.682{\sim}1.887mg／kg$, Zn ; $10.213{\sim}26.119mg／kg$, by groups, respectively. In control and other experimental group, several metal (Co, Cu, Mn, Zn, As, Cr) has a significant difference, but in experimental I and other experimental II, III, IV, V groups, there are no significant difference. 3. The amount of each metal analyzed in the kidney are as follows; Al ; $1.712{\sim}31.230mg／kg$, As ; $0.062{\sim}0.439mg／kg$, Cd ; $0.010{\sim}0.062mg／kg$, Co ; $0.000{\sim}0.101mg／kg$, Cr ; $0.125{\sim}0.636mg／kg$, Cu ; $3.385{\sim}12.502mg／kg$, Fe ; $41.148{\sim}99.709mg／kg$, Hg ; $0.000{\sim}0.270mg／kg$, Mn ; $0.433{\sim}2.301mg／kg$, Ni ; $0.000{\sim}0.221mg／kg$, Pb ; $0.000{\sim}0.584mg／kg$, Se ; $0.540{\sim}1.600mg／kg$, Zn ; $8.775{\sim}17.060mg／kg$, by groups, respectively. The concentration of Cu, Se, Cr, and Hg are variated significantly in control and other experimental group, and Cu, Se, Cd, Cr are variated significantly in experimental I and other experimental II, III, IV, V groups. 4. The amount of each metal analyzed in the bone(tibia and fibula) are as follows; Al ; $9.557{\sim}119.464mg／kg$, As ; $0.139{\sim}12.250mg／kg$, Cd ; $0.000{\sim}0.295mg／kg$, Co ; $0.022{\sim}0.243mg／kg$, Cr ; $0.239{\sim}1.999mg／kg$, Cu ; $0.000{\sim}2.291mg／kg$, Fe ; $240.249{\sim}841.956mg／kg$, Hg ; $0.000{\sim}0.983mg／kg$, Mn ; $0.214{\sim}7.353mg／kg$, Ni ; $5.473{\sim}11.453mg／kg$, Pb ; $0.000{\sim}8.502mg／kg$, Se ; $0.000{\sim}3.005mg／kg$, Zn ; $61.158{\sim}195.038mg／kg$, by groups, respectively. The concentration of Se, Cd are variated significantly in control and other experimental groups, and Se is variated significantly in experimental I and other experimental II, III, IV, V groups. 5. Exceptionally several metal concentration is increased or decreased. but there is no significant harmful difference of metal concentration in the liver, kidney and bone, from the OD-treated-rats compared to those of the control group even if higher dosage($1{\sim}8$ times dosage of person) of OD was administered. Thus, it is expected that the herbal decoction in the traditional herbal medicine would not lay any burden on the body and the heavy metal toxins would not affect our physiological system. However, other kinds of herbal treatment, such as i.v. and i.p. should be considered in terms of metal toxicity in the body since the level of certain metal.