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(1)‚“æ~>Æ·~ã²æ. ò‰. Vol. 8, No. 3, pp. 45~55, 2003. ZÁö7ÖæöB öÒÚ 7.³~ šÒ; 5 ÏÂßWö &‚ ’. f>7 Á·Ò~ ÁšÒ' Á*ç^ 1. 2. 3. 1. ;ö&v ¶"& ~ã"" ;ö&v b~㦠BÞã&v ~ã". 1. 2. 3. A Study on Fractions and Leaching PotentialG of Heavy Metals in Abandoned Mine Wastes. Á. Á. Á. Hee Joung Kim1 Jae Yang2 Jai Young Lee3 and Sang Ho Jun1 1. Department of Environmental Science, Kangwon National University Division of Environmental Biological Engineering, Kangwon National University, Chunchon, Korea 3 Department of Environmental Eng., University of Seoul. 2. . Abstract This study investigates the fractional composition and the leaching characteristics of heavy metals in polluted soils due to mining activities. The fractionated composition of heavy metals is classified into five fractions; adsorbed, carbonate, reducible, organic and residual fraction. The status of humic substances in mine wastes of most sites are polyhumic except tailing from Sangdong mine. According to the sequential extraction procedures (SEPs), leaching probabilities of Cd in coal wastes and tailing are relatively low due to high percentage of residual fraction. 46.4% of Ni in tailings from Sangdong mine is probably leached under oxidized environment, and 39.4% of Cu in these tailings is readily extracted under strongly oxidized environment by organic fraction. According to leaching condition of pH 3.0 and pH 5.6, the amount of heavy metals leached out of coal wastes and tailing increases to 1/2 hours. At pH 3.0 and pH 5.6, concentration of Ni in tailing increases up three times of the initial value. Heavy metals released from coal wastes and tailing were not influenced significantly by leaching time. Key wards : sequential extraction procedures (SEPs), polluted soil, heavy metal, tailing, leaching. º £ ^. ’~ Ï'f 7ւÿö ~š BB öÒö ~š J"B Æ·ö ŽB 7.³~ šÒ;f ÏÂßWö &~ jv ªC~º– ® . þö šÏB 7.³ šÒ; ª~º U&æ‚ adsorbed, carbonate, reducible, organic " residual ;‚ ¾*î . Æ·Ú FVb~ Žï ;êº çÿ7ÖöB BB 7& CêöÒ Ôf ©b‚ ¾æÒ . J"B Æ·~ 7.³ Ï þö ~~š CêöC" 7Ú~ šÚ~ ãÖ Ôf ÏÂïj &b–, &¦ªš reduciblel fractionöB ÏÂB ©b‚ &V>î . çÿ7ÖöB BB 7ö ŽB î.f 6VW ç š >š Cï~ £ 46.4%& ÏÂF ©b‚ Òò>–, ’Ò~ ãÖ £ 39.4%& ÏÂF ©b‚ 6B . pH 3.0 " pH 5.6~ Ï–š~öB Cê öC" 7~ ÏÂï~ 6ê'ž Ã&º 30ªnö šÚrb–, 7~ ãÖ î .f pH 3.0" pH 5.6öB Ï 3*ræ ê³ Ã&>º ç¢ & . "BÚ : ³ŽÂ», Æ·J", 7.³, 7, Ï *Corresponding author : [email protected] : 2003. 9. 4 : 2003. 9. 18 : 2003. 12 30. ö7>¢ î~ 5 Æ~. ²Òߞ¢ ræ. 45.

(2) f>7Á·Ò~ÁšÒ'Á*ç^. 46. 1.. B †. 7Ö öVbö ~‚ ~ãJ"öº >î, &V, Æ·ö &‚ J"j > ®æò ‚"ö çš~ ®º ^B 7 ~¾º 7ւÿö ~š BB 7öÒö ~‚ ©b‚ ß ® ê7‚ÿö ~š BB öC" F7·ë ÖÂB 7  öB BB  «~~ J" bîš æ~>, ;, Æ·j Ž‚ ¶ êö F«>šB Fšbî~ · š ¶;ËKj >bšB B>º ~ã^Bš . ¢>' b‚, Æ·b‚ F«>º J"bîf Æ·ö ~š ¶' ;z";j –ö n;z>º–, Æ·š &æº ;zËK ~ "öf bö ~‚ ªš·Ï" Æ·FVbö ~‚ J"bî~ ‡O𢠆 > ® . ¾, 7Ö öÒ ö ŽFB 7.³f Æ· b~ ‚ÿj ÛB~ Æ· š &ê ;zËKj &~ʖ, 7ö ‡OB ;‚ š Ò~º 7.³ f "æöB BB ÖW7ÖV>¾ Ö Wjö ~š "¯b‚ Ÿj ¾J–¾ ®Ïz>Ú ~Âb ‚ F«>º ";öB 2N'ž >îJ"j ¢bʺ öž š B . š‚ 7.³~ šÿb‚ ž‚ Æ·" ~ 5 æ~>J"f 7Ö öÒö ŽFB 7.³ö² ~ ªf. ãæ "ææ~ bÒ, z' æzö "6‚ >wj  šæ‚ š ö² Wª ~ Ï 5 –ÿö &‚ æš ìbš ;{‚ 7"š ®&Ë~ . Ï 5 –ÿö &‚ ’º 7ւÿö ~‚ 7ÖöVb –ÿö 'Ϛ &Ë ~ ß® 7¢ ã 6º 7Ò6ö ~š ÏÒ~&j ãÖ ~Âb‚~ šÿ, æ~>‚~ FÂ, æ Æ·~ J " &ËWj .G~º– 7º‚ ;¢ B† ©b‚ 6 B . š‚ GšöB Öë‚ÿö ~š VÂ>º J" bî~ F«b‚ ž‚ "ææ~ Æ·J"š¾ Æ·ö ~‚ J"bî~ B–V·j šš~V *šB Æ·ö Ž FB 7.³~ ÏÂßWj ’«~º ’& jº† ©b ‚ ÒòB . V¢B  ’öBº Kÿ ç~æ~ ö ê7~ öÒf çÿ7ë²öB ÖÂB 7¢ &çb‚ 7Ö öÒö ŽFB 7.³~ šÒ;ö Vž šÿW" pH~ æzö ~‚ >w*ê 7.³~ Ï ßWj j v~ ¦Æ~& . 1). 2). 2.. Òò 5 O». –Òæ Bº  ’ æ~ æîf –~ &¦ª ²* FÆ2ÒjV ~ WÖÞzÚ‚ rJê 7æWzb‚ >Ú®, 𢠦;b‚ b‚ Æ2‚-JJêjÊV~ –F*[ 2.1.. Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003. –" &«‚ FÆ2ÒjV~ zWzê Ž‚ . 6‚ æ ' ßWj š ;öê 'ú– çÿsj &Û~ vš º Kÿ ç~ö *~‚ b‚ öê7" 7C7ÖöB BB öÒ& ÖÒ>Ú ® . ’æ~ öê7öB B B öC òº Kÿ ç~æ~ «ê öê7öB B B ö҂ "ææö 7º*~² *~~ ®b–, . ³7Ö~ öÒº çÿ7ë²öB F7 ÖÂB 7‚ öW’öB VÂ>º ÖW7ÖV>f ;Öö ~š Kÿ ~‚ F«> ® . ò~ ªCO» Òòž 7ÖöÒº «êê7öB CêFê·ë ê öV B öC" çÿ7ë²öB F7·ë";öB BB 7 ¢ ‚[(0~15 cm)öB j~& . ò~ &‚Wj ¸šV *š 2 m *Ï~ ; OË Ï ¶¢ B 10B~ ¦ªò¢ j~ b‚ *Ú~  ò& 1 kg šç >êƒ ~&b–, ¶ š–Î ê ï¶ ÒBj šÏ~ ªê‚ r 2 mmڂ Úî‚ ê, š. j »ª~ 64 µm š~~ «ãj <º ò¢ zªC Ïb‚ ~& . ;6ïf ³š‚ ò¢ 550 CöB 2* ÿn & ‚ ê &~V *"~ Z²N‚ Ö;~& . FVî² Ž ïf Kjeldahl»ö ~š G;~& . Æ·~ «êªCf 2 mm‚ Úî‚ ò¢ ÒÏ~ sieve and pipet» ö V ¢ ~&b–, Æ·~ –ç ª~º Shepard~ O» j V¶ . ¦zêº î²f ;6ï~ j‚ Ö;~&b –, 20 š~º oligohumic, 20~25º mesohumic, 25 š çf polyhumicb‚ ~& . 7.³~ šÒ;º Tessier ~ O» ö V¢ adsorbed 2.2.. o. 4). 5). 6). 7). metal, carbonate metal, reducible metal, organic metal,.  5&æ ;‚ ºÂ~& . Æ· 7~ 7.³f  &æ ;‚ šÒ~æò ¢> 'b‚ ã¶~ ‚šö ‡OB adsorbed metal, êÖ"~ ;‚ šÒ~º carbonate metal, .³Özb" ŽB reducible metal, FVb" &N>–¾ Fzb ;‚ ª~ >º organic metal, 'b ¶Ú~ ’WWª" &NB residual metal b‚ ª~B . ºÂB ò 7~ 7.³ ³êº 0.45 µm glass fiber filter‚ 6{"‚ ê ç‡j residual metal. ICP(Perkin Elmer XL 3100, USAAAS(Atomic Absorption. ‚ G;~& . J"bî~ šÿ &ËW ï&º 7.³~ šÿ &˂ ¦ªž adsorbed, carbonate, reducible, organic fraction ~ ''~ ï Žïj~ b‚ ï&~& .. Spectrometry : Varian Techtron AA-6). 7).

(3) ZÁö7ÖæöB öÒÚ 7.³~ šÒ; 5 ÏÂßWö &‚ ’. 7.³~ ÏÂßW Æ· 7ö ŽFB 7.³~ ÏÂßWj ¦Æ~V *‚ Ï þf “ÚÏÂþ»~ Ï–š(‡j=10)j  J~ ò 5 gj Ã~> 50 mlf b~ pH, Ï * j æzʚB >¯~& . 2.3.. ö Vž 7.³~ Ï–ÿ Æ· 7ö ŽFB 7.³š ;Öö ~š ÏÂ>º ;ê ¢ rjV *š, Ã~>¢ ÒÏ~ Æ· òö &‚ Ï þj >¯~& .  ’öBº pH 3.0f pH 5.6 öB '' >¯~&b–, pH 3.0f ¾ê7öB VÂB Ö W7ÖV>f ÖWj ö ~‚ 7.³~ Ï–ÿj ï &~V *‚ ©š .. y : concentration (mg/kg) of heavy metal released at time t b : release rate constant a : concentration (mg/kg) of initial heavy metal t : reaction time (hr). 3.. 2.3.1 pH. ÏÂ*ö Vž 7.³ Ï–ÿ Æ· 7ö šÒ~º 7.³~ *ö Vž Ï–ÿj rjV *š 0.5 h, 1 h, 2 h, 4 h, 8 h, 12 h, 24 h, 48 h, 72 h ÿn 9ê‚ ’ª~ >¯~& . 2.3.2. þO» 2.4.1 >w*ö Vž Ï þ ªCÏ ò 1 gj 50 ml â'2¢Ê’ö ‚ ê ºÂ ‡ 10 ml¢ &~& . ºÂ‡~ pHº šN;ê¢ 0.01 M ‚ –.‚ Ã~>¢ ÒÏ~ '' pH 3.0, 5.6b‚ –. ~& . 6‚ >w*ö Vž 7.³ ÏÂïj rjV *~ 0.5, 1, 2, 4, 8, 12, 24, 48, 72* ÿn 25 C 160 rpmöB êûV . êûΠχf 0.45 µm ï  "æ‚ 6{ "Î ê ç‡ö ®º ÏÂB 7.³j Fê֏ 2¢®î(ICP)‚ ªC~& . ªCÖ"¢ Kinetic modelö 'Ï~ >w³êê>¢ êÂ~& . 'ÏB Î žf “Power function”šî . Ξf r" ? . 5 Power function Kinetic model (1) y=aÜ t 2.4.. o. b. ln y = ln a + b ln t. (2). 47. Ö" 5 V. Cê öC 5 7~ šz' ßW f j‚ ò~ šz' ßWj ¾æÞ ©š. . çÿæ öê7~ öÒf çÿ7ë²öB BB 7 ~ pHº ' 3.3" 5.8b‚ ¾æ¾, Cê öÒ& 7. ;‚ ÖWj & . Cê öÒ~ pH& 7 ÖWj ¾æÚº šFº C ê~ W";öB ¾æÂ ßWb‚ æ'æÿb‚ ÖB bÚ *ö 6N vâÚ 'bš ”& Ö²/š 7 B ç~ö ªš·Ïj –~º "; 7ö bö f‚ JÊ Wªb‚ Ú®~ H, N, O ~ &¦ª" CWª ~ ¢¦& zê&Ê(CH ),zÎîj(NH ), >ª b‚ æ ~–, ê³>º æ[~ {K" ö ~~ êz·Ïš ê ¯(Carbonization)";öB bÒz' æzö ~š FVb š ªš>šB ÖWê& Ã& ~&V r^b‚ 6B . –Òæ Cê öÒf 7~ ·šN~~Ïïf 2.3" 6.3 cmol(+) kg ~ º*& . ÆWf Clay loam" Sand clay loamšîb–, &ڂ 7 º Cê~ öÒ& Î ¾º ', Òf 6Æ~ ·f ôf ©b‚ –Ò>î . ß®, Cê~ öÒ~ ãÖ Ò¾ 6Æ~ Žïš z ¸f ©b‚ ¾æÒº–, šº ;Öf :²ö ~š šÿ &Ë Wš z ¸j ©b‚ 6>–, š‚ žš öê7æ~ Æ·š¾ ~š F B öÒö ~š J"F > ®j © b‚ .G† > ®î . Cê öÒf 7~ FVb Žï f 15.0%f 1.7%~ º*& . 3.1.. Table 1. 4. 3. −1. 7.³~ šÒ;(fractionation) öÒ¾ 7 7~ 7.³f šÒ;ö V¢ ֏^V 3.2.. Table 1. Physical and chemical properties of the experimental mine tailing samples pH (1:5). CEC TOC T-N OM OM/N Humic level Sand Silt Clay cmol(+)/kg ---- % -------- % ---C. W. 3.3 2.3 39.7 0.3 15.0 50.0 polyhumic 43.6 26.3 30.2 S. T. 5.8 6.3 2.0 0.2 1.7 8.3 oligohumic 47.7 25.8 26.6 CEC; Cation exchange capacity; TOC; Total organic carbon; T-N ; Total nitrogen; OM; Organic matter. C. W.; Coal waste. S. T.; Sangdong mine tailing.. Soil texture Clay loam Sand clay loam. Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003.

(4) 48. f>7Á·Ò~ÁšÒ'Á*ç^. Fig. 1. Relative distribution of Cd, Cu, Ni, Pb, Zn fractions in the coal wastes and mine tailing.. ¾ ÏÂ;êö Nš& ® . Adsorbed formf ã¶ ‚ šö ‡OB 7.³b‚ 7.³š 6Æ ~ ‚šö z 'b‚ ‡OB ©b‚  ֏Kš £~ «¶~ v¦š ¾ pH æzö ~š £² îO, šÿF > ®º ¦ªš . Carbonate formf êÖ"~ ;‚ šÒ~º 7.³b‚ >[öB pH& Ôjæš £² ÏÂ>º ¦ªš . Reducible formf .³ Özb" ŽB 7.³b‚ 6Æ ‚šö ƚ¾ * Özb" Ž>Ú ®º ¦ªb‚ 6 VW ç‚ F r Ïš ¢ÚÆ &ËWš ’ . Organic formf FVbö ‡OB 7.³ 6º FVb ªšö ~š Fzb‚ šÒ~º 7.³b‚ ^VW çöB FVb~ Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003. ªš Ïš ¢ÚÆ &ËWš ’ . Residual formf 7 b~ Ö; ’– ³ö šÒ~º 7.³b‚ ¶' ~ãö Bº –~ Ïš >æ pb¾ ³z 5 ªš(decomposition) ö ~šB ÏÂF &ËWš ® . Table 2º öÒf 7 7 ' 7.³(Cd, Cu, Ni, Pb, Zn)~ šÒ;ê ³ê¢ ¾æÞ ©š, Fig. 1f ' 7.³~ šÒ;ê jNj ¾æÞ ©š . Cê öC" 7 7 šÚ~ Cïf 22.7~22.9 mg/kg ¢ '' ¾æÚÚ vòöB j݂ ³ê‚ ¾æÒ. (Table 2). ¾, š‚ 8 f Bowen š ‚ 0.35 mg/kg, Paisf Jones, Jr. & ‚ 0.11~3.0 mg/kg, 8). 10). 11).

(5) ZÁö7ÖæöB öÒÚ 7.³~ šÒ; 5 ÏÂßWö &‚ ’. 49. Table 2. Fractions concentration of various heavy metal in coal waste and mine tailing. Sample I. D Cd Cu Ni Pb Zn. C. S. C. S. C. S. C. S. C. S.. W. T. W. T. W. T. W. T. W. T.. Adsorbed. Carbonate. 1.9 2.0 23.0 1.2 11.1 14.5 2.4 2.6 18.7 12.6. 2.9 1.3 35.4 30.3 13.2 13.4 2.6 4.9 68.7 29.4.  š ‚ 0.1~0.5 mg/kg, Bear & ‚ 0.01~0.7 mg/kg~ Æ· 7 šÚ~ ¦šï" jv† r  –Òæf £ 5.5VöB ô²º 200Všç ¸f 8j  šÚö ~š v æ~ ò& J"B ©b ‚ ÒòB . öC" 7ö ŽFB šÚ~ šÒ;º adsorbed fractionš 1.9~2.0 mg/kg, carbonate fractionš 2.9~1.3 mg/kg, reducible fractionš 1.7~2.1 mg/kg, organic fraction š 3.7~2.0 mg/kg, residual fractionš 12.5~15.5 mg/kg b‚ ¾æ¾, *Ò~ ¶~ãöB šÿ &˂ šÚ~ šÒ;º Cê öC~ ãÖ adsorbed fraction" carbonate fractionb‚ Cï~ £ 21.2%‚ 4.8 mg/kg~ šښ šÿF > ®j ©b‚ .G>–, Cï 7 residual fractionš Næ~º jNf £ 55.1%& . 7~ ãÖ šÿ &˂ šÒ;º ¦zê& oligohumic ç‚ F7 ·ë ÒÏB VBf ¦FB ž fatty acids ¾ R.žÖ" ?f FVb~ ªš& ê³F © b‚ .ç>Ú adsorbed fraction" carbonate fraction, organic fractionb‚ Cï~ £ 23.2%‚ 5.3 mg/kg~ š ښ 7‚ ¦V "æ~ ~ãb‚ šÿ† ©b‚ .ç >–, Cï 7 residual fractionš Næ~º jNf £ 67.6%‚ ¾æÒ . V¢B Cê öCš¾ 7 7 šÿš Ϛ‚ šÒ& ï ŽF>Ú ®Ú öê7æš¾ 7Ò 6öB B>º FÂ>ö ~šBê ï~ šښ ~  ê¾ "æ ~ãj J"Ò > ®V r^ö ö 'ž &kš jº~ . öC" 7ö ŽFB ’Ò~ šÒ;º adsorbed fractionš 23.0~1.2 mg/kg, carbonate fractionš 35.4~ 30.3 mg/kg, reducible fractionš 205.4~63.8 mg/kg, organic fractionš 540.1~434.1 mg/kg, residual fractionš 1317.2~ Rose. 12). 13). Reducible ------------------- mg/kg 1.7 2.1 205.4 63.8 44.8 43.8 40.2 57.3 191.3 241.8. Organic ------------------3.7 2.0 540.1 434.1 104.1 170.4 37.6 131.6 545.3 484.6. Residual. Total. 12.5 15.5 1317.2 654.7 375.5 185.3 489.2 364.0 1457.2 1466.2. 22.7 22.9 2121.0 1184.1 548.8 427.4 572.0 560.4 2281.2 2234.7. b‚ ¾æ¾, *Ò~ ¶~ãöB šÿ &Ë ‚ ’Ò~ šÒ;º Cê öC~ ãÖ adsorbed fraction " carbonate fractionb‚ Cï~ £ 2.8%‚ 58.4 mg/kg ~ šÿF > ®j ©b‚ .G>–, Cï 7 residual fractionš Næ~º jNf £ 62.1%‚ ¾æÒ (Table 2). *ö ¾æÂ Ö"¢ Æ&‚ Bowen š ‚ 30.0 (2.0~250) mg/kg, Paisf Jones, Jr. & ‚ 2.0~100.0 mg/kg, Rose  š ‚ 15.0 mg/kg, Bear &  ‚ 2.0~100.0 mg/kg~ Æ· 7 ’Ò~ ¦šï" j v† r v æš ’Òö ~š '~² J"B ©b‚ Òò>î . 6‚ ¶ê‚ šÿ&ËWš ®j ©b‚ . ç>º ³êê ''~ òöB ¦šïj ç²~º 8b‚ ¾æÒb– ß® 7~ ãÖ ô²º 250V ;ê ¸f 8b‚ ¾æ¾ 7& ¶~ãö žÂ>îj ãÖ šÿWš Ö š ©b‚ ÒòB . öC" 7ö ŽFB î.~ šÒ;º adsorbed fractionš 11.1~14.5 mg/kg, carbonate fractionš 13.2~ 13.4 mg/kg, reducible fractionš 44.8~43.8 mg/kg, organic fractionš 104.1~170.4 mg/kg, residual fractionš 375.5~ 185.3 mg/kgb‚ ¾æ¾, *Ò~ ¶~ãöB šÿ &Ë ‚ ’Ò~ šÒ;º Cê öC~ ãÖ adsorbed fraction " carbonate fractionb‚ Cï~ £ 4.4%‚ 24.3 mg/kg ~ šÿF > ®j ©b‚ .G>–, Cï 7 residual fractionš Næ~º jNf £ 68.4%‚ ¾æÒ (Table 2). 7~ ãÖ šÿ &˂ šÒ;º adsorbed fraction " carbonate fraction, organic fractionb‚ Cï~ £ 46.4%‚ 198.3 mg/kg~ î.š 7‚ ¦V "æ~ ~ ãb‚ šÿ† ©b‚ .ç>–, Cï 7 residual fractionš Næ~º jNf £ 43.4%‚ ¾æÒ . *ö ¾æÂ Ö"¢ Kloke & ‚ 100.0 mg/kg~ 654.7 mg/kg. 10). 11). 12). 13). 14). Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003.

(6) f>7Á·Ò~ÁšÒ'Á*ç^. 50. Æ· 7 î.~ J"V&>~ ï" jv† r v æš î.ö ~š '~² J"B ©b‚ Òò>î . ¾ ¶ê‚ šÿ&ËWš ®j ©b‚ .ç>º ³êê C ê öÒ º 7öB J"V&~¢ ç²~º 8b‚ ¾æ¾ 7& ¶~ãö žÂ>îj ãÖ šÿWš. Ö š ©b‚ ÒòB . öC" 7ö ŽFB Ï~ šÒ;º adsorbed fractionš 2.4~2.6 mg/kg, carbonate fractionš 2.6~4.9 mg/kg, reducible fractionš 40.2~57.3 mg/kg, organic fractionš 37.6~131.6 mg/kg, residual fractionš 489.2~ 364.0 mg/kgb‚ ¾æ¾, *Ò~ ¶~ãöB šÿ &Ë ‚ Ï~ šÒ;º Cê öC~ ãÖ adsorbed fraction " carbonate fractionb‚ Cï~ £ 0.8%‚ 5.0 mg/kg ~ šÿF > ®j ©b‚ .G>–, Cï 7 residual fractionš Næ~º jNf £ 85.5%‚ ¾æÒ (Table 2). 7~ ãÖ šÿ &˂ šÒ;º adsorbed fraction " carbonate fraction, organic fractionb‚ Cï~ £ 24.9%‚ 139.1 mg/kg~ Ϛ 7‚ ¦V "æ~ ~ãb ‚ šÿ† ©b‚ .ç>–, Cï 7 residual fractionš Næ~º jNf £ 65.0%‚ ¾æÒ . *ö ¾æÂ Ö" ¢ Æ·~ã*» ö BB &kV&(& æ)ž 300 mg/kg" Paisf Jones, Jr. & ‚ 3~189 mg/kg, Rose  š ‚ 17 mg/kg, Bear f Levinson š ‚ 2~200 mg/kg~ Æ· 7 Ï~ ¦šï" jv † r v æöB Cïf V&~ šç~ 8j ¾æÚ Cê öÒf 7& ÖҚ ®º æš J"B ©b‚ Òò>îb–, ¶ê‚ šÿ&ËWš ®j ©b‚ .ç >º ³êê ''~ òöB ¦šï  Ôf 8j ¾æ¾ ¶~ãö žÂ>îj ãÖ šÿWš Ôj "æ ~ãö ~º '˚ ž 7.³ º 'j ©b‚ Ò ò>–, Ï~ Cï 7 residual fractionš Næ~º jN f &¦ª~ òöB 70% šçb‚ –Ò>Ú ¶ç öB Ï~ šÿWf ·j ©b‚ 6>¾ ÆÒ'ž J" öb‚ Òò>V r^ö F š¾ ³zö &‚ &kš j º~ . öC" 7ö ŽFB j~ šÒ;º adsorbed fractionš 18.7~12.6 mg/kg, carbonate fractionš 68.7~ 29.4 mg/kg, reducible fractionš 191.3~241.8 mg/kg, organic fractionš 545.3~484.6 mg/kg, residual fraction š 1457.2~1466.2 mg/kgb‚ ¾æ¾, *Ò~ ¶~ãö B šÿ &˂ j~ šÒ;º Cê öC~ ãÖ adsorbed fraction" carbonate fractionb‚ Cï~ £ 3.8%‚ 87.4 mg/kg~ šÿF > ®j ©b‚ .G>–, 9). 11). 12). 13). Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003. 15). Cï 7 residual fractionš Næ~º jNf £ 63.9% ‚ ¾æÒ (Table 2). 7~ ãÖ šÿ &˂ šÒ;º adsorbed fraction " carbonate fraction, organic fractionb‚ Cï~ £ 23.6%‚ 526.6mg/kg~ jš "æ~ ~ãb‚ šÿ† ©b‚ .ç>–, Cï 7 residual fractionš Næ~º j Nf £ 65.6%‚ ¾æÒ . *ö ¾æÂ Ö"¢ Kloke & B‚ Æ·J"V& ž 300 mg/kg" Rose  š  ‚ 36 mg/kg, Bear f Levinson š ‚ 50 mg/kg " 20 mg/kg~ Æ· 7 j~ ¦šï" jv† r v æöB Cïf V&~ šç~ 8j ¾æÚ Cê ö Òf 7& ÖҚ ®º æš J"B ©b‚ Òò>î b–, ¶ê‚ šÿ&ËWš ®j ©b‚ .ç>º ³ê ê Cê öÒ º 7öB J"V&~¢ ç²~º 8 b‚ ¾æ¾ 7& ¶~ãö žÂ>îj ãÖ šÿW š Ö š ©b‚ ÒòB . CêöÒf 7¢ jv~ š &¦ª~ 7öB šÿWš ¸j ©b‚ .ç>º adsorbed fraction𠏲 ¾æÒ . carbonatef organic fraction~ ãÖ 7. º Cê öÒöB ¸f 8b‚ ¾æÒb–, residual fractionf &¦ª~ 7.³š CêöÒöB ¸f 8j  & .. 14). 9). 12). 13). 15). >w*ö Vž Ï ßW Table 3~6f CêöÒf çÿ 7¢ Power function Ξ‚ ’‚ j " ® . ²æO;(y = a + bx) öB VÞV(b)º >w³êç> 8j ¾æÚ, >w³ê ç>(b)º 7.³~ Ï ßWj ï&~º– 7º‚ æ> š . ²æO;öB VÞV(b)º >w³êç>‚B b8 š š>ƒ ϳê& †ªj ~‚ . CêöÒf 7º H SO f HClj šÏ~ pH& ' ' 3.0 5.6ž ºÂχöB 30ª* >wÎ ê öò~ pH‚ ï;j šî . š©f ºÂχ~ šN;ê& Ô j pH~ jÏËj ç ‚ ©b‚ 'B .  Ö" 7 .³~ ³êº pH~ 'Ëj Aæ pf ©b‚ ¾æÒ . Fig. 2~3f Cê öC" 7öB H SO ¢ pH 3.0b ‚ –.B χj šÏ~ ÏÂ>º 7.³ö &š Power function modelö 'ς ¾*š . ¾*öB æ>‚  8j ~Ö~ >w*ö Vž 7.³ ÏÂïj ÚÚ š öC~ ãÖ Cd ³êº 0.1~0.2 mg/kg, Cu ³êº 0.6~0.9 mg/kg, Pb ³êº 71.4~72.0 mg/kg, Ni ³êº 6.7~6.9 mg/kg, Zn ³êº 2.7~23.6 mg/kg~ º*‚ ¾æ Òb–, 7~ ãÖ Cd ³êº 1.1~1.2 mg/kg, Cu ³ê 3.3. pH,. 2. 4. 2. 4.

(7) ZÁö7ÖæöB öÒÚ 7.³~ šÒ; 5 ÏÂßWö &‚ ’. 51. Table 3. The rate constant (b), coefficients of determination (r2) and regression equation for release of heavy metals in Coal wastes & Tailing (pH 3.0, H2SO4) Element. b. Coal wastes Tailing Cd 0.0020 0.0009 Cu 0.0735 0.0014 Pb 0.0010 0.0036 Ni 0.0047 0.0553 Zn 0.3849 0.0251 b : rate constant of metal release. r2 : coefficient of determination. * : significant at P<0.05. ** : significant at P<0.01.. Regression equation Coal wastes Tailing y = −0.002x − 1.9274 y = 0.0009x + 0.1321 y = −0.0735x − 0.2173 y = −0.0014x + 1.0941 y = −0.001x + 4.2752 y = 0.0036x + 2.2532 y = −0.0047x + 1.9300 y = 0.0553x + 1.2972 y = −0.3849x + 2.6848 y = 0.0251x + 0.1051. r2 Coal wastes 0.0185 0.7233* 0.4167* 0.6939* 0.8951**. Tailing 0.0681 0.1545 0.0318 0.2527 0.083. Table 4. The rate constant (b), coefficients of determination (r2) and regression equation for release of heavy metals in Coal wastes & Tailing (pH 5.6, H2SO4). Element Cd Cu Pb Ni Zn. b Regression equation r2 Coal wastes Tailing Coal wastes Tailing Coal wastes 0.0078 0.0157 y = −0.0078x + 4.2799 y = −0.0157x − 0.0083 0.6112* 0.0153 0.0052 y = 0.0153x + 0.1604 y = −0.0052x + 1.0522 0.6339* 0.0816 0.0007 y = -0.0816x − 1.8713 y = 0.0007x + 1.9178 0.5065 0.0079 0.0012 y = 0.0079x + 1.8354 y = 0.0012x + 1.324 0.4304 0.1011 0.0422 y = 0.1011x + 0.6073 y = 0.0422x + 0.0027 0.3583 b : rate constant of metal release. r2 : coefficient of determination. * : significant at P<0.05. Tailing 0.5324 0.5969 0.007 0.0429 0.5706*. Table 5. The rate constant (b), coefficients of determination (r2) and regression equation for release of heavy metals in Coal wastes & Tailing (pH 3.0, HCl) Element. b. Coal wastes Cd 0.0410 Cu 0.0202 Pb 0.0005 Ni 0.0046 Zn 0.0946 b : rate constant of metal release. r2 : coefficient of determination. * : significant at P<0.05.. Tailing 0.0132 0.0309 0.0020 0.1011 0.0079. Regression equation Coal wastes Tailing y = 0.041x − 2.2633 y = −0.0132x + 0.0275 y = −0.0202x + 0.0565 y = −0.0309x + 1.0376 y = −0.0005x + 4.2481 y = −0.002x + 1.7692 y = 0.0046x + 1.9056 y = 0.1011x + 0.6073 y = −0.0946x + 1.5252 y = 0.0079x + 1.8354. r2 Coal wastes 0.014* 0.4342* 0.0025 0.2793 0.161. Tailing 0.0842 0.4957* 0.0322 0.3563 0.4304. Table 6. The rate constant (b), coefficients of determination (r2) and regression equation for release of heavy metals in Coal wastes & Tailing (pH 5.6, HCl) Element. b. Coal wastes Tailing Cd 0.1127 0.0136 Cu 0.0015 0.0200 Pb 0.0002 0.0041 Ni 0.1000 0.5348 Zn 0.0426 0.0481 b : rate constant of metal release. r2 : coefficient of determination. * : significant at P<0.05.. Regression equation Coal wastes Tailing y = −0.1127x − 2.2669 y = −0.0136x − 0.2219 y = 0.0015x − 0.0229 y = -0.02x + 0.8913 y = 0.0002x + 4.2333 y = 0.0041x + 1.7016 y = 0.1x − 1.1492 y = 0.5348x − 1.5141 y = 0.0426x + 0.521 y = 0.0481x − 0.2048. r2 Coal wastes 0.6002* 0.0159 0.0004 0.1439 0.1605. Tailing 0.3167 0.396 0.0671 0.5757 0.5749. Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003.

(8) f>7Á·Ò~ÁšÒ'Á*ç^. 52. Fig. 2. Rate curves for the released Cd, Cu, Ni, Pb and Zn in coal wastes (pH 3.0, H2SO4).. Fig. 3. Rate curves for the released Cd, Cu, Ni, Pb and Zn in tailing (pH 3.0, H2SO4).. º 2.9~3.0 mg/kg, Pb ³êº 9.0~10.0 mg/kg, Ni ³êº ³êº 0.9~2.0 mg/kg~ º*‚ ¾æ Ò . .V >wž 30ªræ ÏÂïf /³® Ã&~–,  šê >w*ö Vž ÏÂïf Znj Bž‚ * 7. ³öB .V³êf j݂ 8b‚ ¾æ¾ * V* ÿn ï;j šî . Pbf Niº .Vö ¸f ÏÂ³ê¢  &b–, 7 º öCöB Pb, Zn, Ni~ ÏÂïš ¸ ² ¾æÒ . Fig. 1~2öB FêB ²æO;" >w³êç>(b) Ò  Ö;ê>(r )¢ Table 3ö ¾æÚî . ' 7.³~ > w³êº öCöB 0.0010~0.3849, 7öBº 0.0009~ 0.0251~ º*‚ ¾æÒb–, ' 7.³ *öº – Nš & ®î . 7.³~ >w³êº öCöBº Zn>Cu>Ni >Cd>Pb, 7öBº Ni>Zn>Pb>Cu>Cd~ Bb‚ Ï š ŽÒ ¢Ú¾º ©b‚ ¾æÒ . öC~ ãÖ ²æO ;öB VÞV(b)& (−) 8f *(t)ö Vž ÏÂïš 6²~º ©j ~‚ . Fig. 4f 5º Cê öC" 7öB H SO ¢ pH 5.6 b‚ –.B χj šÏ~ ÏÂ>º 7.³ö &š. Power function modelö 'ς ¾*š . ¾*öB æ>‚ 8j ~Ö~ >w*ö Vž 7.³ ÏÂï j ÚÚš öC~" 7öB pH 3.0" F҂ .V >wž 30ªræ ÏÂïš /³® Ã&~–,  šê > w*ö Vž ÏÂïf * 7.³öB .V³êf jÝ ‚ 8b‚ ¾æ¾ * V* ÿn ï;j šî . Fig. 3" 4öB FêB ²æO;" >w³êç>(b) Ò Ö;ê>(r )¢ Table 4ö ¾æÚî . ' 7.³~ >w³êº öCöB 0.0078~0.1011, 7öBº 0.0007 ~0.0422~ º*‚ ¾æÒb–, ' 7.³*ö – Nš& ®î . 7.³~ >w³êº öCöBº Zn>Pb>Cu>Ni >Cd, 7öBº Zn>Cd>Cu>Ni>Pb~ Bb‚ Ïš ŽÒ ¢Ú¾º ©b‚ ¾æÒ . Fig. 6~7f Cê öC" 7öB HClj pH 3.0" 5.6b‚ –.B χj šÏ~ ÏÂ>º 7.³ö &š Power function modelö 'ς ¾*š . ¾*öB æ>‚ 8j ~Ö~ >w*ö Vž 7.³ ÏÂï j ÚÚš pH 3.0" 5.6öB öC~ ãÖ Cd ³êº ' 0.1 mg/kg, Cu ³êº ' 0.9~1.1 mg/kg" 1.0 mg/kg,. 3.7~3.9 mg/kg, Zn. 2. 2. 4. Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003. 2.

(9) ZÁö7ÖæöB öÒÚ 7.³~ šÒ; 5 ÏÂßWö &‚ ’. 53. Fig. 4. Rate curves for the released Cd, Cu, Ni, Pb and Zn in coal wastes (pH 5.6, H2SO4).. Fig. 6. Rate curves for the released Cd, Cu, Ni, Pb and Zn in coal wastes (pH 3.0, HCl).. Fig. 5. Rate curves for the released Cd, Cu, Ni, Pb and Zn in tailing (pH 5.6, H2SO4).. Fig. 7. Rate curves for the released Cd, Cu, Ni, Pb and Zn in tailing(pH 3.0, HCl). Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003.

(10) f>7Á·Ò~ÁšÒ'Á*ç^. 54. Fig. 8. Rate curves for the released Cd, Cu, Ni, Pb and Zn in coal wastes(pH 5.6, HCl).. Pb ³êº ' 68.2~72.1 mg/kg" 67.6~70.6 mg/kg, Ni ³êº ' 6.7~7.0 mg/kg" 6.8~7.0 mg/kg, Zn ³êº ' 2.4~7.7 mg/kg" 1.6~3.7 mg/kg~ º*‚ ¾æÒb–, 7 ~ ãÖ Cd ³êº ' 0.9~1.1 mg/kg" 0.8~0.9 mg/kg, Cu ³êº ' 2.3~2.9 mg/kg" 2.1~2.6 mg/kg, Pb ³ê º ' 5.7~6.1 mg/kg" 5.2~5.7 mg/kg, Ni ³êº ' 0.2~0.8 mg/kg" 0.1~1.7 mg/kg, Zn ³êº 1.5~2.5 mg/kg " 0.8~1.1 mg/kg~ º*‚ ¾æÒ . .V >wž 30ª ræ ÏÂïf /³® Ã&~–,  šê >w*ö V ž ÏÂïf H SO ¢ šÏ‚ χ"º Ò * 7. ³öB .V~ Ï ³ê& ¸² ¾æÂ >š 7Vf ö VöBº ϳê& 6²~º ãËj & . Fig. 6, 7, 8, 9öB FêB ²æO;" >w³êç> (b) Ò Ö;ê>(r )¢ Table 5f 6ö ¾æÚî . ' 7.³~ >w³êº pH 3.0~ çöB öCöB 0.0005~0.0946, 7öB 0.0020~0.1011~ º*‚ ¾æÒ b–, pH 5.6öBº öCš 0.0002~0.1127, 7º 0.0041~0.5348b‚ ¾æ¾ 7.³ö V¢ – Nš& ®î. . 7.³~ >w³êº pH 3.0¢ r öCöB Zn>Cd 2. 4. 2. Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003. Fig. 9. Rate curves for the released Cd, Cu, Ni, Pb and Zn in tailing (pH 5.6, HCl).. 7öBº Ni>Cu>Cd>Zn>Pb~ Bb‚ Ïš ŽÒ ¢Ú¾º ©b‚ ¾æÒ, pH 5.6¢ r ö CöB Cd>Ni>Zn>Cu>Pb, 7öB Ni>Zn>Cu>Cd> Pb~ Bb‚ Ïš ŽÒ ¢Ú¾º ©b‚ ¾æÒ . >Cu>Ni>Pb,. 4.. Ö †.  ’º 7ÖöVbö &‚ šz' ßW 5 7.³ ~ šÒ;¢ –Ò~, ö Vž 7.³~ šÿ &Ë Wj «~&b–, 7öÒö &‚ pHf >w*ö Vž Ï þj ۚ 7.³~ ÏÂßWj 2k~V *š > ¯>î . 1. ’ò~ šz' ßWöBº 7 º Cêö Ò& ;‚ ÖWj ¾æî . 2. Cê öC 5 7~ 7.³ Žïf *æöB Æ · 5 æ'~ ïŽFïj ."~ 7.³b‚ J"> Ú ®b–, ß® Cu& v òöB &Ë ¸f ³ê¢  & ..

(11) ZÁö7ÖæöB öÒÚ 7.³~ šÒ; 5 ÏÂßWö &‚ ’ 3. –Òæ Ú ò~ šÒ;º Ï~ ãÖ ®ÏW ;& "¢ šîb¾, šښ¾ ’Òº šÿWš – adsorbed fraction" carbonate fraction~ jNš 10% Ú ž‚ ;Ö¾ :²ö ~šB £² ~š¾ "æ Æ·b‚ šÿF > ®j ©b‚ 6>î . 4. Cê öCö šÒ~º 7.³~ šÒ;¢ ÚÚ Ö" ¶çöB Ïš Ϛ‚ šÒ;º adsorbed, carbonate fractionb‚ ¾æÒ, 7~ ãÖ FVb~ ¦ ;ê& oligohumicž çž 6b‚ Ú adsorbed, carbonate 5 organic fractionš šÿ &ËWš ®º ¦ ªb‚ 66 V¢B CêöC º 7öB šÿš &˂ ¦ªjN𠏲 ¾æ¾ 7ö ~‚ Æ· 5 ~ ÂJ"š š ©b‚ ÒòB . 5. Cê öC" 7öB H SO ¢ pH 3.0b‚ –.B χöB 7.³~ >w³êº öCöB Zn>Cu>Ni>Cd >Pb, 7º Ni>Zn>Pb>Cu>Cd~ Bb‚ Ïš ŽÒ ¢Ú¾º ©b‚ ¾æÒb–, pH 5.6öB 7.³~ >w ³êº öCöBº Zn>Pb>Cu>Ni>Cd, 7öBº Zn >Cd>Cu>Ni>Pb~ Bb‚ Ïš ŽÒ ¢Ú¾º ©b‚ ¾æÒ . 6. HClj pH 3.0" 5.6b‚ –.B χöB~ 7.³ ~ >w³êº pH 3.0¢ r öCöB Zn>Cd>Cu>Ni> Pb, 7öBº Ni>Cu>Cd>Zn>Pb~ Bb‚ Ïš Ž Ò ¢Ú¾º ©b‚ ¾æÒ, pH 5.6¢ r öCöB Cd >Ni>Zn>Cu>Pb, 7öB Ni>Zn>Cu>Cd>Pb~ Bb ‚ Ïš ŽÒ ¢Ú¾º ©b‚ ¾æÒ . 7. pHf >w*ö Vž Ï þÖ" pHº 7.³ ~ ³êöº 'Ëj ~æ pº ©b‚ ¾æÒ . šº χ~ šN;êö ~‚ 'Ëb‚ ÒòB . 8. ' 7.³~ >w³êç>¢ jv‚ Ö" CêöC š ² ¸f Ö"¢ ¾æîb–, ' 7.³ö V¢ Ï ³êöB – N𢠾æî . V¢B 7ÖöVbö šÒ ~º 7.³ f öVb «~, 7.³~ «~ 5 þO» ö V¢ Ï ßWš 'V š² ¾æÆ ©b‚ 6> –, ¶ ~㖚ö V¢Bê Ï ;ê& ¢ ©b‚ ÒòB . 2. 4. 55. ^^ò 1. Forstner, U. and Salomon, W. Mobilization of metals from sediments, Metals and Their compound in environment (ed. by E, Merian), pp. 379-398 (1991). 2. Park, Y.A. “Designing and applicability of soil pollution indices for estimating quality of soil polluted with heavy metals and arsenic”, J. of KOSES 1(1): 47-54 (1996). 3. Kim, O. J. Geological map of Korea (1:50,000), Geological survey of Korea, (1974). 4. Park, Y.A. “Distribution and transportation of fine-grained sediments on the intercontinental shelf off the Kuem river estuary”, Korea, J. of Geo. Soc. of Korea 20(2), 154-168 (1984). 5. Shepard, F. P. “Nomenclature Based on sand-silt-clay ratios”, J. Sed. Pet. 24, 151-158 (1954). 6. Hakanson, L. and Jansson, M. Principles of lake sedimentology. Springer -Verlag, Berlin, 316, (1983). 7. Tessier, A., Campbell, P.G.C. and Bisson, M. Sequential extraction procedure for the speciation of particulate trace metals. Analytical chemistry, 51(7), 844-851 (1979). 8. Salomons, E.L. Mobilization of metals from sediments, Metals and Their compound in environment (ed. by E, Marin), 357, (1994). 9. Ministry of environment. Korea environmental information, (1999). 10. Bowen, H.J.M. Environmental chemistry of the elements, Academic press, London, (1979). 11. Istvan, P. and Jones Jr. Trace elements, CRC., Lucie Press, (1997). 12. Rose, A.W., Hawkes, H.E. and Webb, J.S. Geochemistry in Mineral Exploration : Academic Press, pp. 549-581 (1979). 13. Bear, F.E. Chemistry of the soil, (2nd ed); Reinhold Publishing Corp., New York, p. 246 (1964). 14. Kloke, A. Content of arsenic, cadmium, chromium, fluorine, lead, mercury, nickel in plants grown on contaminated soil: UN-ECE Symp, (1979). 15. Levinsion, A.A. Introduction to exploration geochemistry: Applied Publishing Ltd., May Wood, p. 614 (1974).. Journal of KoSSGE Vol. 8, No. 3, pp. 45~55, 2003.

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