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(1)‚“æ~>Æ·~ã²æ. ò‰. Vol. 8, No. 4, pp. 53~63, 2003. ö7Öæ ã·æ Æ·~ 7.³ šÒ;f Æ·J"ï&. f>7 Á·Ò~ ÁšÒ' Á‚ç¢ Á*ç^ 1. 2. 3. 4. 1. ;ö&v ¶"& ~ã"", ;ö&v b~㦠BÞã&v ~ã¦, 7Ú&v ~ã" 2. 1. 4. 3. Fraction and Soil Pollution Assesment Index of heavy metals in cultivated land soils near the abandoned mine. Á. Á. Á. Á. Hee Joung Kim1 Jae E Yang2 Jai-Young Lee3 Sang-1l Choi1 Sang Ho Jun1 1. Department of Environmental Science, Kangwon National University. 2. . Division of Environmental Biological Engineering, Kangwon National University, Chunchon, Korea 3 Department of Environmental Eng., University of Seoul 4 Department of Environmental Eng., Kwangwoon University. ABSTRACT Objectives of this research were to fractionate heavy metals in soil samples in the upper Okdong River basin and to assess the potential pollution index of each metal fraction. Soil samples were collected from the cultivated land soils and analyzed for physical and chemical properties. pH of cultivated soils ranged from 5.2 to 7.6. Contents of total kelhaldal nitrogen and loss on ignition were in the ranges of 0.6~2.5%, and 1.9~12.9%, respectively. Heavy metals in the cultivated land soils were higher in the abandoned closed coal mine near field soils than those in the paddy soils. Total concentrations of metals in the cultivated land soils were in the orders of Zn > Pb > Ni > Cu > Cd, exceed the corrective action level of the Soil Environment Conservation Law and higher than the naturals were abundance levels reported from uncontaminated cultivated land soils. Mobile fractions of metals were relatively small compared to the total concentrations. Soil Pollution Assesment Index (SPAI) values of each fraction of metals were leveled from Non polluted to Moderately polluted based on total concentrations. SPAI values of mobil fractions were lower than those of immobile fractions. Results on metal fractions and SPAI values of the cultivated land soils indicate that field soils samples were contaminated with heavy metals and had potential to cause a detrimental effects on plants. A prompt countermeasure to prevent field soils in the abandoned closed coal mine near fields are urgently needed. Key words : Cultivated land soil, Paddy soil, Field soil, Metal fraction, Soil Pollution Assesment Index.. º £ ^. ’~ Ï'f Kÿ F Æ·~ 7.³~ šÒ;f šÒ;ö Vž 7.³~ J"æ>¢ Ö;~º– ® . Æ ·jº ã·æ Æ·j &çb‚ ~& Æ·f bÒ' ßW" šz' ßWj ªC~& .  Ö" ã·æ Æ· ~ pHº 5.2öB 7.6j, Cî² Žï" loss on ignitionf '' 0.6~2.5%, 1.9~12.9%¢ ¾æî . ã·æ Æ·~ 7 .³ ³êº ö7B ê7æ~ ¢Æ·öB ¸² ¾æÒb–, C 7.³~ ³êº Zn > Pb > Ni > Cu > Cd Bb‚ ¾ æÒ . š‚ Ö"º Æ·~ãV&~f jJ" ã·æ Æ·~ 7.³ ³ê  ¸² ¾æ¾º ãËj &b–, C 7.³ 7 ¢ ¦ªš šÿ &ËWš ®º ¦ªb‚ ¾æÒ . Æ·J" ï&æ>(SPAI)º –Òæ Æ·öB Non pollutedf Moderately polluted¢ ¾æîb–, š‚ Ö"º j šÿW ; º šÿW ;~ 8š Ò² ¾æÒ. . ã·æ Æ·öB 7.³ šÒ;f SPAI 8f 7.³ö ~‚ J"" bÚö ~º ÆÒ'ž Fš‚ Ö"¢ áj> ® . V¢B Ö"öB ê öê7æ~ Æ·j ö~V *šB ³‚ &kš jº~ . "BÚ : ã·æ Æ·, ¢Æ·, SÆ·, 7.³ šÒ;, Æ·J"ï&æ> *Corresponding author : [email protected] : 2003. 10. 29 : 2003. 11. 03 : 2004. 3. 30. ö7>¢ î~ 5 Æ~. ²Òߞ¢ ræ. 53.

(2) f>7Á·Ò~ÁšÒ'Á‚ç¢Á*ç^. 54. 1.. B †. j& ê>¦V /³® ~V ·‚ 7ëf *Ò ;öê ÿΦæö ôf ö ê7" ZÁö7B .³7 Öj ÖÂ~& . š‚ ZÁö7Öf "æ ~ãö ~ º 'ËKš ’V r^ö *Ò ;¦öBê 7Ö öVbö ~‚ Æ· 5 ~ J"~ 'Ë ï&¢ ~ ® .  ¾ ¢>'b‚ ¾Ò>æ pf 7¾ 7Ò, 'b, ŽÂ >, FÂ> ~ 7ւÿö ~‚ öVbö ŽFB Fš 7 .³~ ³êº ÖÒ¾¢~ Æ·~ãš»š¾ >î~ã š»~ V& ¸f ©b‚ > ®b– , 7ÖöV bö ~‚ ³ãæ~ J" &ËWf 7ÖöVbö ŽFB 7.³ ~ ªf "æ ~ãö Vž 7.³~ Ï 5 – ÿö &‚ æš ìbš '.‚ 7"š ®&Ë~ . ‚"ö çš~ ®º ^B 7~ ~¾º 7ւÿö ~ š BB 7öÒ ö ~‚ ©b‚ 7Öö>, 7ÖöVb   «~~ J" bîš æ~>, ;, Æ·j Ž‚ ¶ êö F«>šB Fšbî~ ·š ¶;ËKj º*¢ >bšB B>º ~ã^Bš . š-² "ææ ~ ~ãö 'Ëj ~º J"~ "öžf 7Ö ‚ÿö ~š B>º Fš 7.³" ?f J"bî" ZÁö7 š B ê 7 öÒË, öWê, öC öB B>º Ž Â>f ÏÂ>º Fš 7.³ š–, š‚ Fš 7. ³f Æ· 5 >ê‚ šÿ~ ~Â, Æ· 5 ³ãæ¢ J"Ê ® . 7.³~ šÒ;f Ï ßW~ ’«ö &‚ ’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‚ 6B. . ÖÒ¾¢~ ÿÎ öB §B Ú OËb‚ ª~  ®º .³7֚¾ Cê7Öæ~ Ö7b 7 ŽF >Ú ®º '« Fš 7.³š "ææ~ ³ãæ j J"Ò > ®º ÆÒ'ž J"öš F > ® . V¢B ö ê7" ZÁö .³7Ö 5 7Ò6ö &‚ Æ·J" &ËWö &‚ ÖF B* Ö;š jº~– šö V¢ J "æö &‚ ~ã öÖFB*¢ Ö;† > ® . š‚ öÖF B*¢ Ö;~V *šBº ZÁö. ³7Ö 5 ê7, öÒ¾ÒË ž"æö 7.³š FÂ> Ú ~ãö šÒ~º 7.³š žÚ 5 ~ãö Ú¶ ;ê ~ Fš‚ 'Ëj ~º&¢ 6† > ®Ú¢ ‚ . š ‚ J"ï&¢ ~V *‚ V&š 7.³ö ~‚ J"6 š V&𢠆 > ® . ZÁö7B 7Öæ~ J" 80. 1). 2,3). öj B–† > ®º VF'ž 7"O»š šÚæV * ~ ZÁö7B 7Öæj &çb‚ 7.³ö ~‚ J "6V&š J;>Ú¢ ~, ZÁö7B 7Öæ~ öÖFB*¢ Ö;~¢ ‚ . 7.³ö ~‚ J"6V&~ J;f ZÁö.³7Ö 5 ê7, öÒ¾ÒËöB VÂ>º 7.³š ž" Æ· 5 ~Âb‚ FÂ>æ‚ 7Öæ~ J"*~ 6f Æ· (³ãæ 5 j³ãæ), ž"~ 5 WÚ >f ŽÂ>,  bÚöB~ 7.³ö ~‚ J";ê¢ V&b‚ J;>Ú ¢ ‚ . ¾, ÖÒ¾¢f ž“öB~ 7ÖæöB VÂ>º 7.³ö ~‚ J"6V&~ J;š «{~² BB : ì .  ’º Kÿ æj &çb‚ öê7 5 ZÁö 7B .³7ÖöB BB 7öÒf ÖW7ÖV>ö ~‚ "ææ ³ãæ Æ·ö ŽFB 7.³(Pb, Cd, Zn, Cu, Ni)~ šÒ;~ ßWj ’«~ šÿ &ËW" 7.³ šÒ;ö Vž J"6V& J;~ Òê&Ò&kš ¾ ö&kj *‚ V.' ¶ò¢ B~J ‚ . 1). 4). 5). 6). Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003. 2.. Òò 5 O». –Òæ6 5 òj  ’ö ÒÏB òº ;öê 'ú– çÿsj &Û ~ všº Kÿ "ææ~ ³ãæ Æ·j j‚ © š . –Òæ~ ³ãæ Æ· òº Kÿ ç~æ~ öê7š ÖҚ ®º æ" çÿ7ë² "ææ 5 7 Ò6æ~ ³ãæ, 7~~ ’7Ò6" 7Ò6 æ~ ³ãæ 5 ~~~ ÖW7ÖV>~ 'Ëj A~j ©b‚ .ç>º Kÿ öê7 æ~ ³ãæ¢ &çb‚ ~ ‚ [, 0~15 cm~ æ6öB ò¢ j~& . j‚ òº &‚Wj Fæ~V *~ 7Ò6~ ‚[ šj 1~2 m *Ï~ 9B æb‚ ªÒ~ ''~ ÆöB ò¢ j‚ ê b~ ÒÏ~& . Table 1" Fig. 1f j ò«" jæ6 j ¾æÞ ©š . 2.1. –Òæ~ æî' ßW ;öê 'ú–ö çÿs ’¾Ò¦V &~Òö ššº KÿÂf WÖ ~ 'Ëb‚ êš jv' p  >ê& ö^B KÿÂj ;W‚ . š æf CêV z C, &C²z, æWz 5 z;z~‚ ’W>Ú ®b–, & ¦ªš S ã·æ‚ ;WB ç~æf Cê7 ö> 5. C7b š ~Âb‚ F«Nb‚Ž ³ã >ö æ&‚ 'Ëj ~ ® 6‚ çÿ7Ö" –ê7ÖöB ¾J 2.2.

(3) ö7Öæ ã·æ Æ·~ 7.³ šÒ;f Æ·J"ï& Table 1. Sample ID of cultivated land and sampling locations Sample I.D. soil sampling locations site characteristics F-1 Myungjin abandoned mine Field soil F-2 Sejin abandoned mine Field soil F-3 Sangdong mine Field soil F-4 Sangdong Field soil F-5 New tailing dam Field soil F-6 New tailing dam Field soil F-7 Old tailing dam Field soil F-8 Old tailing dam Field soil F-9 Kasan Field soil F-10 Kasan Paddy rice soil F-11 Nokjun Field soil F-12 Nokjun Paddy rice soil F-13 Yarouo Field soil F-14 Yarouo Paddy rice soil F-15 Limestone mine Field soil F-16 Okdong abandoned mine Field soil F-17 Okdong abandoned mine Paddy rice soil. 55. ~ ‚[ Æ·~ ãÖ ÎÞ" *ö B>º :²ö ~š ^‚ ªêš "æ ³ãæ ‚Æö 9šVê ~ J"& ËWj zš" ® . ò~ ªC 5 ï& O» 7~ 7.³ ª³z¢ >¯~V *š ò¢ 40 Cö B š–B .~ ’V 63 µmž j.³ Ú(nylon bolting cloth sieve)‚ Úî ~ ªCö ÒÏ~& . « ê ªCf Ú ªC(sieving)" Ž; ªC(pipette method) j ÷¯~ ~& . 64 µm šç~ «ãj <º « ¶º ڂ ž ÚÚ Ú ªCj ~  š~º Ž; ª Cj ~& . Æ·~ ÆW(texture)f “ ³Z¦»ö V¢ ª~~&, «ê ªCf Shepard , ï «êº Folk ~ ª~ O»j V¶ . 2 mm Ú¢ Û"‚ 7 Æ ·~ FVb Žïf ;6ï»j ÒÏ~ G;~&b–, C FV ê² Žïf Gaudette  ~ O»ö V¢ ªC ~& . Æ· FVb~ ¦zêº Kjeldahl»b‚ G;‚ Cî²f ;6ï»b‚ G;‚ FVb~ j¢ šÏ~ Ö;~&b–, Cî²f FVb~ j& 20š~¢ ãÖº Oligohumic, 20~25¢ ãÖº Mesohumic, 25 šç¢ r º Polyhumicb‚ ’ª~& . Æ· Ú 7.³~ šÒ ;º Tessier  ~ O»ö V¢ adsorbed form, carbonate form, reducible form, organic form, residual form‚ ª ~~ ºÂ~&b–, 7.³~ ³êº ICP (Perkin Elmer XL 3100, USA)¢ šÏ~ G;~& . –Ò æ ~ 7.³ šÒ;ö Vž J"6V&f ~~ J"6V&j Æ&‚ ~ Non polluted, Weakly polluted, Moderately polluted, Heavily polluted‚ ª~ ~ ï&~& (Table 2). Æ·J"ï&æ>º 7.³~ šÒ;ê ªCB ¶ò ¢ ' êî ªC~¢ Interdepartmental Committee 2.3. o. 7). 8). 9). 10). 11). 6). Fig. 1. Location of the cultivated land sampling sites in the study area.. º 7ÖV>ê KÿÂb‚ F«>–, 7~ö F~‚ 7 Ò6" ’7Ò6~ ŽÂ>f 7Ò6ö 9jz 7 5 ~ ~~ CêöC '~Ë f s>V r ;Öö ~š ~Âb ‚ F«>Ú >îJ"j &7Ê ®b–, ß® 76 Table 2. The pollution division level of various heavy metals (unit: mg/kg dry soil) Pollution division Non Weakly Moderately Heavily polluted polluted polluted polluted Cd 1 3 10 50 Cu 100 200 500 2500 Pb 200 500 1000 5000 Ni 20 50 200 1000 Zn 250 500 1000 5000 Interdepartmental Committee on the Redevelopment of Committee. Land (ICRCL) (1987).. on the Redevelopment of Committee Land(ICRCL). 1987;. f Hobson ~ ¢^öB ¾æÞ J"6V&~ >~‚ ¾. ê ªCB ö²ž Cd, Cu, Pb, Ni, Zn~ j ö²~ >‚ ¾. 8j Æ·J"ï&æ>(Soil Pollution Assesment Index)‚ Ö;~& . J"êæ> ï& Ö; êÖf r" ? . Kelly12). 13).  Heavy metal fraction concentration in soil  ∑  ∑ ------------------------------------------------------------------------------------------------------------------Pollution Division Tolerable level S.P.A.I.= -------------------------------------------------------------------------------------------------------------------------Number heavy metal. S. P. A. I. : Soil Pollution Assesment Index Heavy metal fraction concentration :. šÒ;ê Žï. ªCB ö²~. Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003.

(4) f>7Á·Ò~ÁšÒ'Á‚ç¢Á*ç^. 56. ' ö²~ J" ª~ö Vž Æ· Ú tolerance level Number of heavy metal : ªCB ö²~ > * ö ~š êÖB Æ·J"6V& Ö;f ' 7 .³~ J"6V&ö š~º îÏ ‚ê~ö &‚ j ¢ ï‚ ©šæ‚ –Òæ~ ³ê& V&~ ’ š Æ·š 7.³ö ~š J"š B ©b‚ ï&† > ® . Pollution Division Tolerable level:. 3.. Ö" 5 V. ³ãæ~ šz' ßW Table 3f j‚ 7 ò~ šz' ßWj ¾æÞ ©š . ³ãæ~ pHº 5.2~7.6b‚ Ÿ*v æ~ S Æ ·öB 5.2‚ ÖÒ¾¢~ "º Æ·ž nÏÛ, nÛ, W ’Û, >ÂÛ, n{Û, N“Û, ÂÛ, šöÛ, ËöÛ  ~ 4.8~5.4f j݂ º*¢ š &æ ®º £ ÖWj ¾æÚî, çÿs æ~ S Æ·öB 7.6b‚ £ rš ÒWö š>º 8j ¾æî . ·šN~~Ïïf 7.4~12.4 cmol(+)/kgb‚ ¾æÒb–, C î²~ Žïf 0.6~2.5%‚ öê7 æ~ S Æ·ž ;6 F-1öB 2.5%‚ &Ë ¸f 8j ¾æîb– çÿ7 ë² æ~ S Æ·ž ;6 F-3öB &Ë Ôf 8j ¾ æî . 3.1. ·šN ~~Ïïš Ôf ¢¦æ~ ã·æÆ·f ÖÒ ¾¢ Æ·~ ·šN ~~Ïï ê 'Ú jò¢ Ú¶ ; ê ôš Ï ~ê "j*çš 'j ©b‚ ÒòB . 6‚ š Æ·~ ãÖ Æ·ö jò¢ Ï ~š Æ·~ "V ~~Ïï ò¢ Æ·«¶ö ‡O> ¾^æº Æ· χö Ÿj ® & ·bö :‚ ‡> šÏ>–¾ _f b" Žþ Ïî>Ú F >² >Ú 2N J"j B~V ’Þ ©b‚ ÒòB . š‚ ãÖ 7Ò6öB BB 7 .³ Žïš ¸f ^ªêš ã·æ Æ·b‚ šÿ>š jÏËKš 'Ú Fšê& ¸f 7.³f Æ·öB ‡O ö ~‚ Fšbî jÏÎ"¢ Î"'b‚ ¾æâ > ìÚ, ;Ö¾ "æ~ãæz¢ ۚ J"B Æ·‚šb‚¦V Ï Â>º 7.³š >‚¾ æ>j ۚ FÂ>Ú > ê ö 'Ëj * &ËWš š ©b‚ ÒòB . Ignition loss~ Žïf 1.9~12.9%‚ &Öv æ~ S Æ·ž ;6 F-9öB &Ë ¸f 8j ¾æîb–, Kÿ 7Ö æ~ S Æ·ž ;6 F-16öB &Ë Ôf ŽFï b‚ ¾æÒb–, C î²~ Žïf 0.6~2.5%‚ öê7 æ~ S Æ·ž ;6 F-1öB 2.5%‚ &Ë ¸f 8j ¾æîb– çÿ7ë² æ~ S Æ·ž ;6 F-3öB &Ë Ôf 8b‚ ¾æÒ . ¦zêº 1.2~14.4‚ ¾æÚÚ ã·æ Æ·š &æ ®º ßWž jò¾ j~ Ú‚ šš Vº ³¦‚ î. Table 3. Physical and chemical properties of the experimental cultivated land soils pH (1:5). CEC. cmol(+)/kg F-1 6.6 7.6 F-2 6.2 10.0 F-3 5.8 11.2 F-4 7.6 10.8 F-5 5.5 12.4 F-6 5.7 9.4 F-7 6.1 7.6 F-8 5.7 9.1 F-9 6.0 9.8 F-10 5.6 11.6 F-11 5.2 10.7 F-12 5.4 8.4 F-13 5.5 7.4 F-14 5.3 11.2 F-15 6.4 10.3 F-16 6.1 9.1 F-17 5.4 11.5 CEC; Cation exchange capacity. TOC; Total organic carbon. TKN; Total Kjeldahl nitrogen.. TKN. 2.5 1.0 0.6 1.4 2.4 2.1 1.4 1.4 1.4 1.4 1.5 1.4 2.1 1.4 1.6 1.6 2.4. Loss on Ignition ---- % ----5.9 4.0 8.7 6.9 9.3 3.2 2.8 4.0 12.9 3.8 4.6 5.3 5.9 5.8 2.6 1.9 12.4. Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003. I.G./N. Humic level. Sand. Silt. Clay. Soil texture. 2.4 4.2 14.4 4.8 3.8 1.5 2.0 2.8 9.2 2.7 3.0 3.6 2.8 4.0 1.6 1.2 5.2. oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic oligohumic. 40.1 37.1 29.3 17.0 5.6 53.9 63.9 48.5 90.9 51.2 67.5 65.2 58.4 54.6 46.7 82.5 8.0. ---- % ---22.3 43.9 44.6 71.8 91.1 23.8 26.2 33.1 4.8 37.3 19.1 19.2 24.4 23.6 46.3 8.2 53.1. 37.7 19.1 26.1 11.1 3.3 22.3 9.9 18.5 4.3 11.5 13.4 15.6 17.2 21.8 7.1 9.3 39.0. Clay lom Loam Loam Silty loam Silt Sandy loam Sandy loam Loam Sand Loam Sandy loam Sandy loam Sandy loam Sandy clay loam Loam Loamy sand Silty clay loam.

(5) ö7Öæ ã·æ Æ·~ 7.³ šÒ;f Æ·J"ï&. ² Žïö ~š B>º *çb‚ ÒòB . Oligohumic çž ã·æ Æ·f 7.³š FVb" ֏B ¦ª~ šÒ;j& ¸ š FVbš ªš>šB ž ;¾ 6º bš šÏWš ±f šN ;‚ šÿ &ËWš š ©b‚ .ç>Ú bÚö 'Ëj * ©b‚ ÒòB . * æ~ «êº &¦ªš Sandf silt~ Žïš ¸f loam sandy loamb‚ ξ, Ò, 6Æ~ Žïš '' 8.0~90.9%, 4.8~91.1%, 3.3~39.0%‚ ¾æÒ . 3.2. ³ãæ 7.³~ šÒ;(fractionation) 5 šÿW. (mobilization). *Ò ¯> ®º ã·æ Æ·~ ªC O»f 7.³ ~ C Žïòj G;~² >Ú ® . š‚ ªCO»f ã·æ Æ·ö ª~ ®º 7.³~ šÿ ;¾ Ï &ËWö &‚ .Gš ÚJÚ ;š . V¢B ã·æ Æ ·Ú~ 7.³~ šÒ;¢ ªC~ áÚê ¶ò& z × Fς Æ·J"~ ;¢ áj > ®  ~ ® . 7.³š "6‚ ~ãæzöB bioavailabilityf Æ·7 šÿWö &Ë 'Ëj † > ®º ;º adsorbed fractionš . ¾ ã·æ Æ· ÚöB 㷖šæzö ~š Æ·š 6VW ;¾ _f FVb ªšö ~‚ > ²šN ³ê Ã&ö ~‚ pH 6²f ?f ·‚ ~ãæ z& ¾æÆ > ® , V¢B ã·æ Æ·~ 7.³~ š Ò; 7 carbonate¾ reducible fractionš >Ͼ ~ ~‚ æzF &ËWš ¸ . 14,15). 6). 57. ’æž ã·æ Æ·~ Cd Cïf &Öv æ~ ¢ Æ·ž ;6 F-10öB 22.3 mg/kgb‚ &Ë ¸f ³ ê¢ ¾æîb–, Ÿ*v æ S Æ·ž ;6 F-11öB 10.2 mg/kgb‚ &Ë Ôf 8b‚ ¾æÒ . Cu Cïf 154.7 mg/kg~455.8 mg/kg‚, Pb Cïf 143.8 mg/kg~573.1 mg/kg, Ni Cïf 168.3 mg/kg~ 501.3 mg/kg, Zn Cïf 149.8 mg/kg~1334.6 mg/kg~ ª¢ ¾æÚ &¦ªš Kÿ öê7 ~~ö *~‚ S Æ·öB &Ë ¸f ³ê¢ ¾æîb–, Kÿ 7~‚ jv' J "ööB ö–Òö *~‚ Ÿ*v æ S Æ·öB &Ë Ôf 8b‚ ¾æÒ . ' 7.³~ šÒ;ê ³êê çÿ7ë² æb‚ 7ւÿö ~š BB J"bî~ 'Ëj Aj ©b‚ .ç>º "ææ~ S Æ·öB &Ë ¸f 8j ¾æÚ î, jv' J"ööB fÒ *~‚ ¢ Æ·öB &Ë Ôf 8j ¾æî . *ö ¾æÂ Ö"¢ ï Æ· 7 Cd, Cu, Pb, Ni, Zn Žïž 0.35 mg/kg , 30.0 mg/kg , 3.0~189.0 mg/kg , 15). 15). 3.0~189.0 mg/kg16), 50.0 mg/kg(Bowen, 1979)15),. 16). 400.0 mg/. º* 60.0~2000.0 mg/kg) " jv~š &¦ª~ 7. ³öB adsorbed, carbonatef reducible fraction𠢦 æj Bž‚ * æöB 20VöB ô²º 50Vræ. Ö ¸f Žïj ¾æîb–, Kloke & B‚ Æ·öB ~ Tolerance levelš adsorbed 5 carbonate, reducible fraction𠢦æ" residual fractionf *æ~ ³ãæ Æ·öB £ 1V~6V;ê ç²~º 8j ¾æî, šÒ kg(. 15). 17). Fig. 2. Fractional composition of cadmium (Cd) in the cultivated land soils. Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003.

(6) f>7Á·Ò~ÁšÒ'Á‚ç¢Á*ç^. 58. Fig. 3. Fractional composition of copper (Cu) in the cultivated land soils.. ;~ ßWç. j Bž‚ šÒ; 7 organic fractionš &Ë ¸f ³ê¢ ¾æîb¾, ¢ ãæ Æ·öBº reducible fractionš &Ë ¸f ¦ªjNj N æ~& . ³ãæ Æ·ö ŽFB šÚf "æ~㚾 ê‚ šÿF > ®º labile‚ ¦ªš 12.2%~43.0%‚ &Öv æ ¢ Æ·ž ;6 F-9öB šÿWš &Ë ¸f ©b‚ ¾æÒb–, Kÿ ç~æö *~‚ çÿsÚ~ S Æ ·ž ;6 F-4öB &Ë šÿWš Ô² ¾æÒ (Fig. 2). *ö ¾æÂ Ö"º ¢>'ž Æ·öBº Æ· Ú~ Ö²& Æ·b~ ‚ÿö ~š 6V' ç¢ šVº ÚJÚ 6j Ú Æ·Ú Ö²º «¶f «¶*~ ö ŽB Ö²ö ~š ^VW ç¢ Fæ† ©b‚ .ç> ¾ ã·æ Æ·~ ãÖ jò~ R«" ¢ ãæ~ ãÖ ã ·~ ßWç Æ·‚šš bö ~š &V[" ¾*Úæ– 6V' çj ò ² >Ú ~ö ç¢ Fæ~² >Ú. B ƚ¾ *~ Özb" ֏B ;~ 7.³š ~ö ç‚ >šB ֏B šښ ÏÂ>Ú labile‚ ¦ªö ŽV . 6‚ FVb" ֏B šÚ~ ãÖ ¦z ;êö V¢ šÿ &ËWš ®j ©b‚ Òò>Ú ã·æ Æ·~ ãÖ &¦ª~ FVbf ªšF ©b‚ Ú F Vb" ֏B šښ Gç ê¾ bڂ ‡>& F ©b‚ .ç>Ú šÿ &ËW ¦ªöB ŽV . ³ãæ Æ·ö ŽFB ’Ò 7 "æ~㚾 ê‚ šÿF > ®º labile‚ ¦ªf 19.3%~49.3%‚ ¾æÒ. (Fig. 3). residual fraction. Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003. Kÿ 7~~ Ÿ*v æf ê7 5 .³7ւÿ æ öB fÒ ÎÚ^ ®b¾ ~Â>¢ šÏ~ 㷂ÿ j ~&j ©b‚ .ç>º ¢ Æ·ž ;6 F-12öB š ÿWš &Ë ¸j ©b‚ ¾æÒ . V¢B š æöB  Ö>º ³·bê ’Ò~ ³ê& ¸j ©b‚ Òò>–, £ 84.9 mg/kg ;ê~ ’Ò& "æ ê‚ šÿF ©b‚ ÒòB . Ï~ ãÖ šÒ;~ ßWç residual fractionj Bž‚ šÒ; 7 organic fraction š &Ë ¸f ³ê‚ ¾æÒ b¾ Kÿ ç~~ öê7~ 7ÖV>& F«>º æ~f çÿ7ë²~ 7ÖV>& F«>º æ 5 C²7ë²~ VÂ>& F«>º æ~ S Æ· 5 jv' J"š ‚B ©b‚ .ç>º Ÿ*v æ~ ¢ Æ·öB ÆÖzb 5 * Özb" ֏B Ï~ ³ê& ¸² ¾æ¾ S Æ·~ ãÖº ÖW7ÖV>& F«>º ~Â>& ³ëÏ>‚ Ò Ï>Ú ¾æÂ Ö"‚ Òò>–, ¢ Æ·~ ãÖ S Æ· "º ž ·¦ÚêöB ¾æÂ Ö"‚ ÒòB . Ï~ šÿWf ³ãæ *æš Humic levelš oligohumic ç‚ ¾æ¾, Æ·Ú FVb~ ªš‚ ž~  >²šN ³ê çß" FVb" ֏B Ϛ FVb ªš  ê³'ž Ïš BF ©b‚ Òò>Ú šö 'Ëj Aj ©b‚ .ç>º adsorbed fraction, carbonate fraction, reducible fraction 5 organic fractionš ¦ª' b‚ ÏÂF ©b‚ .çB . ß® š ¦ªf Cï~ 3.7%~36.5%¢ Næ~ 17.4 mg/kg~87.8 mg/kg~ Ϛ ã·æ Æ·öB erosionš¾ 㷂ÿö ~šB "æ .

(7) ö7Öæ ã·æ Æ·~ 7.³ šÒ;f Æ·J"ï&. 59. Fig. 4. Fractional composition of lead (Pb) in the cultivated land soils.. Fig. 5. Fractional composition of nickel (Ni) in the cultivated land soils.. ê‚ šÿ &ËW ®j ©b‚ ÒòB (Fig. 4). î.f ž 7.³"º Ò C²7ë²~ VÂ>& F «>º æ~ S Æ·öB carbonate fraction" residual fractionš ¸f 8b‚ ¾æÒ . š‚ *çf C²7Ö ~ ßûž ¸f C²Wª~ 'Ëb‚ ÒòB . î.~ šÿWf ³ãæ *æš Humic levelš oligohumic ç‚ ¾æ¾, Æ·Ú FVb~ ªš‚ ž~  >²šN ³ê çß" FVb" ֏B î.š FV b ªš  ê³'ž Ïš BF ©b‚ Òò>Ú š. ö 'Ëj Aj ©b‚ .ç>º adsorbed fraction, carbonate fraction, reducible fraction 5 organic fraction š ¦ª'b‚ ÏÂF ©b‚ .çB . ß® š ¦ªf Cï~ 34.7%~50.6%¢ Næ~ 37.7 mg/kg~231.2 mg/kg ~ î.š ã·æ Æ·öB erosionš¾ 㷂ÿö ~š B "æ ê‚ šÿ &ËW ®j ©b‚ ÒòB. (Fig. 5).. jf šÒ;~ ßWç residual fractionj Bž~ organic fraction š &Ë ¸f ³ê‚ ¾æÒb–, ¢¦æ Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003.

(8) 60. f>7Á·Ò~ÁšÒ'Á‚ç¢Á*ç^. Fig. 6. Fractional composition of zinc (Zn) in the cultivated land soils.. ~ ¢ Æ·öBº organic fraction  º redcible fractionš ¸f 8j & . ß® öê7~ ÖW7ÖV> & F«>º æ~ S Æ·öBº ž æ"º Ò organic fraction" reducible fraction jNš ç® Ôf 8j ¾æÚ ã· ‚ÿ  "æ ~Âj šÏ~ ³ã> ‚ ÒÏ>îj ©b‚ .çB . j~ šÿWf ³ãæ *æš Humic levelš oligohumic ç‚ ¾æ¾, Æ·Ú FVb~ ªš‚ ž~  >²šN ³ê çß" FVb" ֏B î.š FVb ªš  ê³'ž Ïš BF ©b‚ Òò>Ú šö 'Ëj Aj ©b‚ .ç>º adsorbed fraction, carbonate fraction, reducible fraction 5 organic fractionš ¦ª' b‚ Ï F ©b‚ ÒòB . ß® š ¦ªf Cï~ 7.0%~51.7%¢ Næ~ 22.8 mg/kg~610.5 mg/kg~ j š ã·æ Æ·öB erosionš¾ 㷂ÿö ~šB "æ ê‚ šÿ &ËW ®j ©b‚ ÒòB (Fig. 6). j~ šÿ &ËWš B¢ ¸² ¾æÂ æf Kÿ öê7~ ÖW7ÖV>& F«>º æ~ S Æ·öB &Ë ¸² ¾æÒb–, Kÿ 7Á~~ö *~‚ fv æ~ ¢ Æ·öB &Ë Ô² ¾æ¾ jö ~‚ ÒV ·bš¾ "æ êö ~º 'Ëf ÖW7ÖV>¢ ³ëÏ>‚ šÏ~º Kÿê7 æ~ S Æ·š B¢ š ©b‚ ÒòB . (2) 7.³ šÒ;ö Vž J"6V& J;. ’æ öê7" ZÁö.³7Ö 5 7Ò6ö &‚ Æ Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003. ·J"ö &š ZÁö.³7Ö 5 ê7, öÒ¾ÒË(7Ò 6)ö &‚ J" &ËWö &‚ ÖF B* Ö;š jº~ – šö V¢ ¶ê ’ÖFB*¢ Ö;† > ® . š‚ ’ÖF B*¢ Ö;~V *šBº ZÁö. ³7Ö 5 ê7, öÒ¾ÒË ž"æö 7.³š FÂ> Ú ~ãö šÒ~º 7.³š žÚ 5 ~ãö Ú¶ ;ê ~ Fš‚ 'Ëj ~º&¢ 6† > ®Ú¢ ‚ . š ‚ J"ï&¢ ~V *‚ V&š 7.³ö ~‚ J"6 š V&𢠆 > ® . ZÁö7B 7Öæ~ J"öj B–† > ®º VF 'ž 7"O»š šÚæV *~ ZÁö7B 7Öæ j &çb‚ 7.³ö ~‚ J"6V&š J;>Ú¢ ~ , ZÁö7B 7Öæ~ ’ÖFB*¢ Ö;~¢ ‚ . 7.³ö ~‚ J"6V&~ J;f ZÁö.³7Ö 5 ê7, öÒ¾ÒËöB VÂ>º 7.³š ž" Æ· 5 ~Âb‚ FÂ>æ‚ 7Öæ~ J"*~ 6f Æ· (³ãæ 5 j³ãæ), ž"~ 5 WÚ>f ŽÂ>,  bÚöB~ 7.³ö ~‚ J";ê¢ V&b‚ J;>Ú ¢ ‚ . ¾, ÖÒ¾¢f ž“öB~ 7ÖæöB VÂ>º 7.³ö ~‚ J"6V&~ J;š «{~² BB : ì . V¢B  ’öBº '“~ ~~ J"6V&j Æ&‚ ~ Non polluted, Weakly polluted, Moderately polluted, Heavily polluted‚ ª~~ ï&~& . Æ·J"ï&æ>º 7.³~ šÒ;ê ªCB ¶ò 1).

(9) ö7Öæ ã·æ Æ·~ 7.³ šÒ;f Æ·J"ï&. ¢ ' stepî ªC~¢ Interdepartmental Committee on the Redevelopment of Committee Land(ICRCL) öB ¾æÞ J"6V&~ >~‚ ¾. ê ªCB ö²ž Cd, Cu, Pb, Ni, Zn~ j ö²~ >‚ ¾. 8j Æ· J"ï&æ>(Soil Pollution Assesment Index)‚ Ö;~& b–, Æ·J" ª~º Non polluted, Weakly polluted, Moderately polluted, Heavily polluted‚ ¾*î . Non pollutedº ž*' Öë‚ÿö ~š J">æ pf Æ·b‚ ¶ ŽFï º*ö ŽB ³ê ‚ ž*~ š ;öº 'Ëj ~æ pº 7.³~ ³ê¢ ö‚ . Weakly pollutedº J"B Æ·b‚ ž;>¾ J"~ ;êº £‚ ç‚ '“~ ~~ J"Æ·ª~V& 1 ö š>º º*¢ ¾æÞ . Moderately pollutedº Æ·š Ö뚾 ã· " ? f ž*' ‚ÿö ~š ç® J">Ú ®º ç¢ ~ ~– ~~ J"Æ·ª~V& 2ö š>º º*š –, Heavily pollutedº Öë‚ÿ" ?f ž*~ ‚ÿö ~š Æ·š j;ç'b‚ ~² J"B ç‚ ‚k~ Æ·J"ç‚ J"Æ·ª~V& 3~4ö š>º º* š . š-² ª~B Æ·J"6V&j ã· O»š¾ Æ· "æ ~ãö V¢ šÒ;ö ~š ªCB 7.³~ ³ê ¢ J"Æ·ª~V&ö ~š V&j J;~& . šÒ;ö Vž Cïö &‚ 7.³ Æ·J"6V& f *æöB non pollutedf weakly polluted º*¢ *¦ ."~&b–, moderately pollutedº çÿ7ë² æ " 7Ò6 æ~ ³ãæž ;6 F-5, F-7" C²7Ö æ~ S Æ·ž ;6 F-15f Kÿ ¾ê7 æb‚  æöB BB öÒf ÖW7ÖV>~ 'Ëj A~j ©b‚ .ç>º S Æ·" ¢ Æ·ž ;6 F-15, F-16, F-17öB ."~º 8b‚ ¾æÒ . Heavily polluted¢ ç²~–¾ V&ö š~º æf * ;6öB ¾æ¾æ p~ . ã·æ Æ·š ³z";" ³·b~ ÒV¾ ãJö ~‚ ~ã 'Ëj B¢ ôš Aj ©b‚ .G>º adsorbed fraction" carbonate fraction~ ž labile‚ ç Æ· J"6V&f ’7Ò6 æ~ S Æ·ž ;6 F-7" F-8öB non polluted º*¢ ."®b¾ weakly polluted f moderately polluted, heavily pollutedº * æöB Æ·J"6V&j ç²~–¾ V& 6ö š~º >~ º ¾æ¾æ p~ . ã·æ Æ·š 㷂ÿ 5 ~ã æzö ~š 6V' –š~ ;¢ Fæ~² F r .ç>º labile‚ ;~ 12,13). 18). 12,13). 12,13). 61. Æ·J"6V&f Kÿ ç~ö *~‚ öê7æ~ S Æ·ž ;6 F-1" Kÿ 7Á~~æb‚ jv' ê7š¾ .³7Ö~ '˚ 'j ©b‚ .ç>º &Ö v æ~ S Æ·ž ;6 F-9f Ÿ*v æ~ S" ¢ Æ·ž ;6 F-11 5 F-12, fv æ~ S Æ·ž ; 6 F-13j Bž‚ *æöB non polluted º*¢ ." ~&b–, weakly polluted 5 moderately polluted, heavily pollutedº Kÿ "ææ~ ³ãæöB Æ·J "6V&j ç²~–¾ V& 6ö š>º æš * ;6öB ¾æ¾æ p~ . Æ·~ FVb~ ªš‚ ž~ šÿWš &7F ©b ‚ .ç>º labile‚ ;~ Æ·J"6V&f Kÿ ç~ö *~‚ ö ê7æ~ S Æ·ž ;6 F-1j Bž ‚ *æöB non polluted º*¢ ."~&b–, weakly pollutedº C²7֚ BW 7ž æ~ S Æ· ž ;6 F-15f Kÿ öê7 æb‚  æöB B B öÒf ÖW7ÖV>~ 'Ëj A~j ©b‚ .ç> º S Æ·" ¢ Æ·ž ;6 F-15, F-16öB ."~º 8b‚ ¾æÒ . ¾ moderately pollutedf heavily pollutedº Æ·J"6V& š~‚ ¾æÒ . *f ?f Ö"º šÒ;öB ªCB Cïö &‚ 7.³~ Æ· J"6V&š ³ãæ ~ã~ 'Ëj Aj ©b‚ .ç >º šÒ;~ ' ¦ª~ V&>~ ç&'b‚ Ï Â >–¾ ž ê‚~ šÿb‚ ž‚ êö J"bî ~ »' _f ~«' Fš¢ "² F ©b‚ Òò>º ³ê ¸² ï&> ® . š‚ ï& šç~ >~ º J"B æj z' O»ö ~š ö O»ž Æ· ~ ®Ïzž Æ·~ ~öz /ê(Eh~ &~)š¾ Æ·~ pH çß(precipitation) 6º žÖ" ~ W/ê " ‡Ozö šÏ~º 6Æ7bÒò~ šÏ _f Æ·BïÒ ò~ šÏ" Æ·Ú ŽB 7.³~ Ïî O»ž Æ·^ ;ö ~‚ B–(washing)f b' O»ž 7.³j F 'b‚ ‡>~º b~ šÏ(Phytoremediation) " ³ ëÆÏ'O»ž >*ã, CÆ, VÆ, VÆCÆ " ? f O»ö '.® ö Onj B~V Ú[–¾ 澂 ¸f Æ·J"6V& B‚ ž~ B>º ãB' ^B¾ ~ã ^B& jºšçb‚ ¾æ¾² F ©b‚ Ò òB . V¢B ã·æ~ Æ·~ ßWš¾ ã·O»ö V ¢ Æ·J"6V& Ö; O»ö Nš¢ vÚ¢ † ©b ‚ ÒòB . Æ·ö ŽB 7.³(Cd, Cu, Ni, Pb, Zn) šÒ;ê ³êö ~š Ö;B šÿ&ËWš ®º adsorbed fraction, carbonate fraction" reducible fraction, organic fraction~ 19). Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003.

(10) f>7Á·Ò~ÁšÒ'Á‚ç¢Á*ç^. 62. Table 4. Pollution division level of metal fraction in cultivated land soils. Total. A+C. A+C+R. Pollution division level 1 2 3 4 1 2 3 4 1 2 F-1 9.4 3.7 0.9 0.2 0.2 0.1 0.0 0.1 0.4 0.1 F-2 8.6 3.4 0.9 0.2 0.7 0.3 0.1 0.0 1.1 0.4 F-3 9.8 3.9 1.0 0.2 0.8 0.3 0.1 0.0 1.5 0.5 F-4 9.3 3.6 0.9 0.2 0.5 0.2 0.1 0.0 1.0 0.4 F-5 9.7 3.8 1.0 0.2 0.5 0.2 0.1 0.0 1.4 0.5 F-6 9.0 3.5 0.9 0.2 0.7 0.3 0.1 0.0 1.3 0.5 F-7 9.6 3.7 1.0 0.2 1.1 0.4 0.1 0.0 1.4 0.5 F-8 9.1 3.5 0.9 0.2 1.1 0.4 0.1 0.0 1.3 0.5 F-9 6.9 2.7 0.7 0.1 0.6 0.2 0.1 0.0 0.6 0.2 F-10 9.3 3.5 0.9 0.2 0.4 0.1 0.0 0.0 1.5 0.5 F-11 6.5 2.5 0.6 0.1 0.4 0.2 0.0 0.0 0.9 0.3 F-12 8.5 3.2 0.8 0.2 0.7 0.2 0.1 0.0 0.8 0.3 F-13 6.5 2.5 0.6 0.1 0.6 0.2 0.1 0.0 0.9 0.3 F-14 5.5 2.2 0.6 0.1 0.5 0.2 0.1 0.0 1.0 0.4 F-15 10.5 4.2 1.1 0.2 0.5 0.2 0.1 0.0 1.3 0.5 F-16 10.2 4.1 1.0 0.2 0.7 0.3 0.1 0.0 1.1 0.4 F-17 10.5 4.1 1.1 0.2 0.5 0.2 0.1 0.0 2.3 0.8 A+C; Sum of adsorbed + carbonate. A+C+R; Sum of adsorbed + carbonate + reducible. A+C+R+O; Sum of adsorbed + carbonate + reducible + organic. 1; Non polluted, 2; Weakly polluted, 3; Moderately polluted, 4; Heavily polluted.. A+C+R+O. Site. ‚ ³êö &‚ J"ï& æ>º Table 4ö vî . 4.. Ö †.  ’öBº Kÿ F ã·æ¢ &çb‚ "æ ZÁö.³7ÖöB BB öÒö ~š 7.³ö &‚ J"ê¢ ï&~V *š ³ºÂ»j ۂ ã·æ Æ· 7 7.³~ šÒ; ªCj >¯~&, š Ö"¢ š Ï~ Æ·J"ï&æ>(SPAI)¢ ÖÂ~& .  Ö"º. r" ? . 1. ã·æ Æ·~ pHº &¦ªš £ÖWb‚ ¾æÒb ¾ .³7Öæ~ S Æ·öBº æ Æ·Û"º Ò ršÒWb‚ ¾æÒ . 2. ’Ò¢ Bž‚ 7.³ &¦ªš ZÁö .³7Öæ ~ ã·æ º ÖW7ÖV>~ F «ïš ôf öê 7æöB ¸f ³ê¢ &b–, šÒ;ª~ö ~‚ šÿ &ËWê ¸² ¾æ¾ š æ~ ·bÚ Ú~ 7. ³ ŽFïš ¸j ©b‚ 6>î . 3. –Òæ Ú ã·æ~ šÒ;ê J"ï&V&f * ;6öBnon polluted º*¢ ." ~&b–, Kÿ öê7 5 BW 7ž C²7Ö æöB moderately pollutedj ç²~– ¾ V& 6ö š>º 8j ¾æÚÚ š æ š ÖF'b‚ ã·æ ö Onš šÚ ^¢ † ©b Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003. 3 0.0 0.1 0.2 0.1 0.2 0.1 0.2 0.1 0.1 0.2 0.1 0.1 0.1 0.1 0.2 0.1 0.2. 4 0.2 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.0 0.1 0.0 0.1. 1 0.8 1.9 2.4 2.0 2.6 2.1 2.1 2.4 1.8 2.2 1.8 1.5 1.8 1.6 3.4 3.5 3.8. 2 0.3 0.6 0.8 0.6 0.9 0.7 0.8 0.9 0.6 0.7 0.6 0.5 0.6 0.6 1.2 1.3 1.4. 3 0.1 0.2 0.3 0.2 0.3 0.3 0.3 0.3 0.2 0.2 0.2 0.2 0.2 0.2 0.5 0.5 0.5. 4 0.4 0.0 0.1 0.0 0.1 0.1 0.1 0.1 0.0 0.0 0.0 0.0 0.0 0.0 0.2 0.2 0.1. ‚ 6B . 4. Cïö &‚ Æ·J"6V&š ³ãæ ~ã~ ' Ëj Aj ©b‚ .ç>º šÒ; ~ ' ¦ª~ V& >~ ¸² ï&> ® . V¢B ã·æ~ Æ·~ ß Wš¾ ã· O»ö V¢ Æ·J"6V& Ö; O»ö Nš¢ vÚ¢ † ©b‚ 6B .. ^^ò 1. 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). 2. Forstner, U. and Salomon, W., Mobilization of metals from sediments, Metals and Their compound in environment, Ed. by E, Merian, pp. 379-398 (1991). 3. Jung, M.C., Heavy metal contamination of soil, plants, waters and sediments in the vicinity of metalliferous mine in Korea, Ph.D thesis, University of London, p. 455 (1995). 4. Sengupta, M. “Environmental impacts of mine drainage on streams of United States”. Env. Geol. Water Sci., 11, pp. 141-152 (1993). 5. Davis, J.A. and Leckie, J.O. “Surface ionization and complexation at the oxide/water interface”, Journal of Colloid and Interface Science, 67, pp. 90-107 (1978). 6. Tessier, A., P.G.C. Campbell, and M. Bisson. Sequential extraction procedure for the speciation of particulate trace.

(11) ö7Öæ ã·æ Æ·~ 7.³ šÒ;f Æ·J"ï& metals. Analytical Chemistry, 51(7), pp. 844-851 (1979). 7. Park, Y.A. “Distribution and transportation of fine-grained sediments on the innercontinental shelf off the Kuem river estuary”, Korea, J. of Geo. Soc. of Korea, 20(2), pp. 154168 (1984). 8. Shepard, F.P. “Nomenclature Based on sand-silt-clay ratios”, J. Sed. Pet., 24, pp. 151-158 (1954). 9. Folk, R. L. “A Review of grain-size Parameters”, Sedimentology, 6, pp. 73-93 (1966) 10. Gaudette, H.E. and Flight, W.R. “Inexpensive titration of organic carbon in recent sediment”, J. Sed. Petro., 44, pp. 24-253 (1974). 11. Hakanson, L. and M. Jansson, Principles of lake sedimentology. Springer -Verlag, Berlin, 316p (1983). 12. Kelly, R. T., Site investigation and material problems, in Reclamation of Contaminated Land. B2/1-B2/12. Society of Chemical Industry (1980). 13. Hobson, M., Rational site investigation. In: Contaminated Land problems and solutions. Ed. T. Cairney. Blackie Aca-. 63. demic & Professional, Chapman & Hall Press (1993). 14. Alloway, B. J., Soil processes and the behavior of metals, In “Heavy metals in soils (Alloway, B. J. (ed))” : Blackie and Son, pp. 7-28 (1990). 15. Bowen, H.J.M. Environmental chemistry of the elements, Academic press, London (1979). 16. Istvan, P. and Jones Jr. Trace elements, CRC., Lucie Press (1997). 17. Kloke, A. Content of arsenic, cadmium, chromium, fluorine, lead, mercury, nikel in plants grown on contaminated soil: UN-ECE Symp (1979). 18. Australian and New Zealand Environment and Conservation Council, Australian and New Zealand Guidelines for the Assessment and management of contaminated sites, National Health and Medical Research Council. (1992). 19. Kim, S.H. and H.T. Jun, Contamination of heavy metals in soils and stream sediments in the vicinity of the sambo PbZn-Barite mine, Econ. Environ. Geol., 26, 271-226 (1993).. Journal of KoSSGE Vol. 8, No. 4, pp. 53~63, 2003.

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