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Comparative Study on the Characteristics of Two Sequential Extraction Methods for Arsenic Fractionations in the Soil

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ഠઑٛणীଭ୼୍෴೾ค଴ଡ଍෉ܪۚծ࣢౟ౢ࣑ଭ൉নण֗઴֜

෉෱୺



 ׌ச૳



 ଲࣦ೾



 ׌լ૽



 ׌ଗ৤



 ଲ஼৤



Comparative Study on the Characteristics of Two Sequential Extraction Methods for Arsenic Fractionations in the Soil

Hyeop-Jo Han, Ju-Yong Kim, Byung-Tae Lee, Kyoung-Woong Kim , Yoon-Soo Kim and Jin-Soo Lee

Abstract :Arsenic fractionations in 21 soil samples collected from abandoned mine areas were determined by two sequential extraction methods, Tessier’s methods and Ahn’s methods. Compared to the total As by aqua regia digestion, sum of As fractionated by sequential extractions showed the 70-130% of recoveries in most soils.

More than 90% of As were considered as residuals by Tessier’s methods in all samples, while Ahn's methods showed that 50-80% of arsenic were fractionated at 1-3 steps of extractions. Phytoaccessible As fractions determined by Mehlich 3 leaching procedure were significantly correlated with the sum of step 1 and 2 by both two sequential extraction methods (p<0.01). The correlation coefficients (R=0.920) of Ahn’s methods was much higher than Tessier’s (R=0.667). Though Tessier's method has widely used for metal fractionation in soils, it is not proper for As which exist oxyanionic forms such as arsenite and arsenate. Our results implied that Ahn’s methods were more suitable for As fractionation than Tessier’s methods.

Key words : Soil, Arsenic, Sequential extraction, Phytoavailability

څ أ ĶǴदŚ՚ġԓܳѺȬąݓۆҼՙ١ّࢹت21Òε޽ࠄॠيTessier ߸߻ѪфAhn ߸߻Ѫˣ

2Àݓۆɳćѻ߸߻Ѫںۺڌॠٕɰ. ɳćѻ߸߻Ѫقۆ३ڌ߻ʽҼՙۆߪ॥͟ںٶսқ३Ѫںࣀ३ঝۍॢ

Ҽՙۆۻ॥͟ęҼİॠٕڷ϶, ŔĀę42Òܼ34ÒÀ±30% ѩڦǴ١޲ε҃يɳćѻ߸߻ۆধսڱ(%)ۋ

ʂߕۺڷͿ100%قŖۿ॥ںঝۍॠٕɰ. ࢹتǴҼՙۆܕۦ঍ࢗəTessier ߸߻ѪںۋڌॢąڍۛΪН

঍ࢗ(4ɳć)ÀϿ˜֨ΒقԴ90% ۋԜۆҼڱں޲ݓॢъϸAhn ߸߻ѪقԴəԜʂۺڷͿۋʴՁۋȭڹ

1~3ɳćۆҼڱۋ50~80%ۆҼڱں޲ݓॠيʂߕۺڷͿČδқपεٕ҃ɰ. ࢹتǴҼՙۆ॥ܼ֩͟Нۻ ۋÀɠՁۋەə঍ࢗε߸߻ॠəMehlich 3 ڌ߻Ѫęɳćѻ߸߻2ɳćūݓۆɀۺ॥͟ÂۆԜěқԵںսॱ

ॢĀęTessier ߸߻Ѫ(R=0.667)قҼॠيAhn ߸߻Ѫ(R=0.920)ۋښˣ০ȭڹԜěՁںٕ҃ɰ. ٍ҆ĵۆ

Āęεܛ०ॠϸ, Ǭ, ĵν, ؉ٍˣۆܼŚ՚ںʂԜڷͿČ؋ʽTessier ߸߻ѪڹۻՃćۺڷͿÀۤȇν

ۋڌʼəɳćѻ߸߻Ѫۋݓχ, ٍۙԜقԴԓজڼۋ٣঍ࢗۆজॡۺäʴں҃ۋəҼՙۆܕۦ঍ࢗथÀقə

ۺ०ॠݓ؍ںսەڼںঝۍॠٕɰ. ̚ॢࢹتǴҼՙۆ֩Нড়սʪقʂॢě۾ڷͿ҇˺, ʂߕۺڷͿ

Tessier ߸߻ѪقҼ३Ahn ߸߻ѪۋҼՙۆܕۦ঍ࢗथÀقۺ०ॢتԜںǣࢍǸںঝۍॠٕɰ.

ܳڅر  ࢹت, Ҽՙ, ɳćѻ߸߻, ֩НۋڌÀɠՁ

2012ț12ښ14ێۿս, 2012ț12ښ31ێ֮ԐٰΒ 2013ț2ښ14ێóۦঝ܁

1) ġܳęॡşցڙঞąėॡҙ

2) ॢĶġ३ěνėɳġ३şցٍĵՙ

*Corresponding Author(ťąږ) E-mail; [email protected]

Address; Department of Environmental Science and Engineering, Gwangju Institute of Science and Technology (GIST)

ISSN 2287-4321(Online) Vol. 50, No. 1 O2013PGpp. 35-43

Դ΁

ġԓф܃ʹটʴقۆ३ьԦʽҼՙ, ࠢ˚в, ĵν, Ǭ, ؉ٍˣۆʫՁڙՙ˞ڹН, ʂş, ࢹتˣۆۋʴϔ ߕεࣀ३ԦНń, ࢹتń, սń, ʂşńںप॥ॠəɰ تॢݓĵ֨֟ࢰঞąڷͿۋʴ, қԓʼ϶ۍÂںҼ΅

ॢڮşԦϼߕق࠘ϼۺۍक़३εйࠚɰ(Thornton, 1983;

Jung, 1995). ߯Ŗقəۋ͠ॢġԓটʴقۆॢঞą١

ّۆ֮ÁՁۋҙÁʼϸԴ܁ҙəĶǴ্·दġԓقʂ

ٍĵȦЛ

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ॢÒডф܁нܓԐεսॱॢцەڷ϶, ইۦəॢĶġ ३ěνėɳˣںࣀॠيࢹت, սݗ١ّ, ݓъࠞॠ, ԓρ

ী՜ˣɰتॢġ३ইԜقʂॢߪ०ۺěνεսॱॠ Čەɰ(Ko et al., 2009). ĶǴġԓܳѺȬąݓࢹتق

ʂॢ١ّʪܓԐĀę, 255ÒदŚ՚ġԓܳѺۆܼŚ

՚١ّࢹتܼ52% ۋԜۋҼՙͿ١ّʼرەəìڷ ͿǣࢍǣҼՙقۆॢĶǴȬąݓࢹت١ّۋ֮Áॢ

ìڷͿ ǣࢍǮɰ(KIGAM, 2006).

2006țԺςʽॢĶġ३ěνėɳڹܼŚ՚фҼՙͿ

١ّʽࢹتۆߌνşѪܼԵধ, ڮşНݗ, ߏ/ϐÂԓ জНęÏڹজॡۺĀ०܃εۋڌॠي؋܁জεڮʪॠ əҝڌজ(immobilization) şցںۋڌॠيĶǴ Ȭą ݓࢹتۆ܁জεսॱॠČەɰ. ؋܁জ܃ٮܼŚ՚ф

Ҽՙۆড়޳(adsorption), ėࠞ(co-precipitation) ইԜˣ ۆşۚںۋڌॠəۋѓѪڹ١ّНݗۆۋʴՁںÇ ՙ֨ࡈ֩Нۻۋ܁ʪε۹Çॠə١ّࢹت܁জşѪۋ

϶(Ahn, 2000; Kumpience et al., 2008), ࣢০١ّ܁জ

঳Нνۺ࣢ՁѺজεڮьॠݓ؍ڷдͿȬąݓۦԐ ڌࠑϸقԴϔڍমęۺۍѓѪۋɰ(Ko et al., 2010).

؋܁জėѪڹŚ՚ۆۋʴʪεÇՙ֨ࡈ֩НͿۻۋ ʼəŚ՚ۆتںÇՙ֨ࢅ϶, মڱۺۍ؋܁জėѪۆ

ۺڌфěνεڦ३Դəࢹت-֩НقʂॢԜ঒ěćε

őϼॣज़څÀەɰ. ֩НۋࢹتڷͿҙࢢŚ՚ںড়ս ॠəϭࠢɦݏںۋ३ॠşڦ३Դə֩НۆŚ՚ড়սق

ٖॳںܳəۍۙ˞, ݌ࢹتۍۙ(ࢹتۆŚ՚॥͟, pH, ڮşН॥͟, تۋ٣İঞɠͳфࢹتۆܓݔˣ)ٮ֩Н ۍۙ(֩НۆܛΪҙқ, ٍͺˣ) ŔνČş٣, Ìս͟ę

Ïڹş঳ۍۙ˞قʂॢ܁ঝॢۋ३Àज़څॠɰ(Jung, 1994). ێъۺڷͿ֩НǴۆŚ՚॥͟ںĀ܁ॠəÀۤ

ܼڅॢڅՙəࢹتǴۆŚ՚॥͟ۋݓχ(Alloway et al., 1990), ࢹتǴŚ՚ۆۻ॥͟ۋٽقʪࢹتۓۙशϸ ۆ࣢Ձ, Ā०Ìʪ, ࢹتսۆ࣢ՁˣŚ՚ۆۋʴʪق

ٖॳںй࠘əŚ՚-ࢹتÂۆԜ঒ěć, ݌ࢹتǴŚ՚

ۆܕۦ঍ࢗÀ ϔڍܼڅॢ څۍۋɰ(Filgueiras et al., 2002; Ure et al., 1995; Ure and Davidson, 2001).

ࢹتфࣅۺНǴقܕۦॠəܼŚ՚ڹজॡܛق˰

͆ʫՁۋࡾóɵ͆ݓəʚۋ͠ॢܼŚ՚ۆজॡۺܕ ۦ঍ࢗε؎؉҃şڦॠيɰتॢٍĵѓѪۋ܃֨ʼؽ ɰ(Tessier et al., 1979; Calmano, 1983; Kerstern and Forstner, 1986; Domingues et al., 1990; Lee et al., 2004;

Vaisanen and Kiljunen, 2005). ۋܼ߯ŖūݓʪÀۤ

ȇνۋڌʼČەəɳćѻ߸߻ѪڹTessier ˣ(1979)ۋ

܃؋ॢѓѪڷͿ, ࢹتǴܼŚ՚ںİঞՁۋ٣঍ࢗ, ࢏ ԓّ঍ࢗ, ߏ-ϐÂԓজН঍ࢗ, ڮşН-ডজН঍ࢗ, ۛΪ

঍ࢗۆ 5Àݓ ɳćͿ ĵқॠي ߸߻ॠə ѓѪۋɰ. ۋ

ѓѪڹࢹتڷͿҙࢢ֩Нۋড়սÀɠॢܼŚ՚ۆ॥͟

ںٚࠑॠäǣܼŚ՚ۋࢹتقԴ֩НͿۋʴʼəąͿ ε߸ۺॠəʚ ۋڌÀɠॠɰ(Tessier et al., 1979).

Ś·ڹġԓقԴۆ ܳʽ Ҽՙ ١ّڙڹ ġНީƃş Ǵ

ڮҼߏԵۋ϶, ԓজʼݓ؍ڹڮҼߏԵǴҼՙəܳͿ

-1À঍ࢗ(As-1 85%, As0 15%), Нۋǣėşٮۿߤॠي

ԓজʾąڍŔशϸقԴ+3, +5, ф+1À঍ࢗÀ-1À

঍ࢗٮʴˣॢتڷͿǣࢍǦɰ(Nesbitt et al., 1995). Ҽ ՙۆԓজԜࢗəսڌؚۆpHٮEh ܓæقۆ३Ā܁ʼ

϶, ێъۺڷͿ+2À঍ࢗۍܼŚ՚ęəɵνҼՙəܳ

Ϳ ԓজঞąقԴ Ҽԓۋ٣(H2AsO4-, HAsO42-

)ڷͿ, ঞ ڙঞąقԴ؉Ҽԓۋ٣(H3AsO30

, H2AsO3-

)ڷͿܕۦॢ

ɰ(Cullen and Reimer, 1989; Masscheleyn et al., 1991;

Jones et al., 2000). ҼՙəŔԓজԜࢗٮڮş·Иş঍

ࢗق˰͆ʫՁۋɵ͆ݓ϶, ێъۺڷͿԓজঞąقԴۆ

Ҽԓۋ٣قҼ३ঞڙঞąقԴۆ؉Ҽԓۋ٣ۋڌ३ʪ

фۋʴʪÀȭڷ϶ʫՁʪ20~60ѕۋԜȭڹìڷͿ

؎Ͳ܋ەɰ(Bhumbla and Keefer, 1994; Ahn et al., 2003).

Ҽՙəۻ঍ۺۍݓॠսۆpH фԓজঞڙۻڦঞą قԴɰδܼŚ՚ۋǣܵŚ՚ęəԜۋॢۋʴ࣢Ձں

ǣࢍǶɰ. ݌սڌؚԜࢗقԴتۋ٣ڷͿܕۦॠəʂ ҙқۆʫՁܼŚ՚ڙՙ˞ڹpHÀÇՙ॥ق˰͆ڌ३ ʪÀ ݒÀॠČ, ܼՁ ф ؎ࠥνՁۆ pHقԴə ԓজН, սԓজНф࢏ԓّ̚əۍԓّġН˞ęėࠞۻʼäǣ

̚əսজʽŚ՚ԓজН, ۾ࢹ, ڮşНݗقÌॠóড়޳

ʿڷͿۍ३ڌ३ʪÀ۹ॠʽɰ(Alloway et al., 1990).

ъϸ, Ҽՙε प॥ॢ ʂҙқۆ ԓজڼۋ٣ں ঍Ձॠə

ڙՙ˞ڹpHÀݒÀ॥ق˰͆ড়޳ͳۋ̆ر܋սćǴ ۆ॥͟ۋݒÀॠə࣢Ձں҃ۍɰ. ̚ॢێъۺڷͿԓ জڼۋ٣˞ۋঞڙԜࢗقԴۋʴʪÀǰ؉ݓəъϸق

ҼՙəԓজԜࢗقԴܳѺۆߏԓজНˣق֖óড়޳

ॠəˣԜʂۺڷͿǰڹۋʴʪε҃ۍɰ(Gulens and Champ, 1979; Lee and Park, 2005; Alloway et al., 1990). ݌, ҼՙəܼŚ՚Ӽχ؉ɦ͆ɰδԓজڼۋ٣ ęʪݓĵজॡۺ࣢Ձۋĵѻʼ϶, ۋ͠ॢۋڮͿێъ ۺۍܼŚ՚ۆܕۦ঍ࢗεঝۍॠəɳćѻ߸߻Ѫۆۺ ڌ ÀɠՁں ঝۍॣज़څÀ ەɰ.

֩НͿۆŚ՚ۻۋεथÀॠşڦ३Č؋ʽMehlich 3ڌ߻Ѫڹĵν, ؉ٍˣۆܼŚ՚ۋٽقʪߏ, ϐÂ,

ࠥ֜, υŔȐ֜, ǣ࣡ήˣࢹتǴܕۦॠəɰتॢڙ ՙۆ ߸߻ق ۋڌʼر ٵڷ϶(Hanlon and Johnson, 1984; Michaelson et al., 1987; Tran and Giroux, 1989;

Mehlich, 1984; Makarim and Cox 1983; Mascagni and Cox, 1985), ҼՙٮࢹتǴقԴۆজॡۺäʴۋҼ֦

ॢۍۆ߸߻قʪۋڌʼرٵɰ(Hanlon and Johnson,

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Table 1. Procedure of two sequential extraction methods (Tessier et al., 1979; Ahn et al., 2005) Extraction

steps

Tessier’s methods Ahn’s methods

Phases Leaching conditions Phases Leaching conditions

Step 1 Exchangeable 0.5M MgCl2, 1hour,

room temp Ionically bound 1M MgCl2, 2hour, room temp Step 2 Bound to carbonate or

adsorbed

1M CH3COONa, 2 hour,

room temp Strongly adsorbed 0.1M NaOH, 12 hour, room temp

Step 3 Bound to organic and sulfides

0.04M NH2OH·HCl in HOAc 25%

3 hour, 96 oC

Co-precipitated with amorphous Fe oxyhydroxides

0.2M ammonium oxalate/

oxalic acid, 2 hour, room temp Step 4 Residual Aqua regia, 1 hour, 70oC Residual Aqua regia, 1 hour, 70oC 1984; Tran and Giroux, 1985; Tran and Giroux, 1989;

Michaelson et al., 1987). ࣢০, Tranę Giroux(1985, 1989)ۆٍĵق˰βϸ֩НͿۻۋʽۍ(P)ۆ֬܃ت ęMehlich 3 ڌ߻Ѫقۆ३߸߻ʽۍ(P)ۆتۋԴͿ

ϔڍȭڹԜěěćεٕ҃ڷ϶, ۋ͠ॢٍĵĀęə˃

Àݓɳćѻ߸߻Ѫق˰δҼՙۆܕۦ঍ࢗεঝۍॠČ, Ҽİॠəʚ ەر ϔڍ ۺ०ॠó ۋڌʾ ս ەɰ.

˰͆Դٍ҆ĵقԴəҼՙ-ࢹتÂۆԜ঒ěćεэ০ əʚşߣۙΒε܃ėॠČۙĶǴġԓܳѺȬąݓࢹ تںʂԜڷͿTessier ˣ(1979)ۋ܃؋ॢ ѓѪę Ahn ˣ(2005)ۋ܃؋ॢѓѪںʴێࢹتقۺڌॠٕɰ. ̚

ॢٍĵĀęεц࢖ڷͿۻ॥͟قʂॢ˃Àݓɳćѻ

߸߻ѪۆধսڱêࢹфMehlich 3 ڌ߻ѪęۆԜěқ Եˣںսॱॠي߯ܛۺڷͿÁÁۆɳćѻ߸߻Ѫق˰

δ ࢹتǴ Ҽՙ ڌ߻ تԜں Ҽİॠٕɰ.

֬ॹѓѪ

ࢹت֨Β޽ࠄфНνজॡۺ࣢Ձࣷ؊

ٍ҆ĵقԴսॱʽɳćѻ߸߻фMehlich 3 ɳێڌ

߻ѪڹࢹتǴܕۦॠəܼŚ՚ۆ֩НۻۋÀɠՁں

ঝۍॠə߸߻Ѫۋ϶, ۋ͠ॢЀۺęҙ०ॠəࢹت֨Β εঝ҃ॠČۙĶǴġԓۍŖۆȬąݓقԴࢹتں޽

ࠄॠيٍĵεݕॱॠٕɰ. ̚ॢɰتॢ࣢Ձںݓɨࢹ ت֨Βεঝ҃ॠşڦॠيۻĶۆ9ÒݓًقқपॠČ

ەəदġԓںʂԜڷͿ21Òۆ֨Βε޽ࠄॠٕɰ. ঝ

҃ʽ ࢹتڹ ࢹت١ّė܁֨ॹѓѪق ˰͆ æܓ ঳ 2 mm(-10 mesh) ۋॠͿߕèڼॠٕČ, ۋܼ<2 mm ۓ ʪۆ ࢹتں ʂԜڷͿ ࢹت pH, تۋ٣İঞɠͳ(CEC:

cation exchange capacity) ˣںࠑ܁ॠٕɰ. ̚ॢࢹت

ǴܕۦॠəҼՙۆߪ॥͟ںঝۍॠČۙٶսқ३ε

սॱॠٕɰ.

ɳćѻ߸߻Ҽİٍĵ

Tessie ˣ(1979)ęAhn ˣ(2005)ۋ܃؋ॢ߸߻Ѫں

ʴێࢹتقÁÁۺڌॠي˃Àݓɳćѻ߸߻Ѫق˰

δࢹتǴҼՙۆܕۦ঍ࢗεঝۍॠČۙॠٕɰ. ێъ ۺڷͿɳćѻ߸߻ѪڹࢹتǴܕۦॠəߪܼŚ՚॥

ܼ͟ۋʴՁۋȭڹܼŚ՚ۆԜʂۺҼڱںঝۍॠə

߸߻ѓѪۋݓχ, ٍ҆ĵقԴəٶսқ३εࣀ३߸߻ʽ

ߪ॥͟ęɳćѻ߸߻قۆ३߸߻ʽߪ॥͟ÂۆҼİ εࣀ३߸Àۺۍۼʂۺ॥͟ҼİεսॱॠČۙॠٕ

ɰ. ˰͆Դɳćѻ߸߻Ѫقۋڌʼəڌ߻܃(reagent)ٮ

ࢹتǴҼՙۻ॥͟ঝۍقۋڌʼəڌ߻܃ۆ޲ۋ۾

قۆ३ьԦॠə١޲εܶۋČۙۛΪН঍ࢗۆڌ߻

قəۻ॥͟қԵęʴێॠóٶսεۋڌॠٕɰ. ̚ॢ

ٍ҆ĵÀࢹتǴܕۦॠəҼՙܼۋʴՁۋȭڹ঍

ࢗ, ɰ֨ϊ३֩НۋڌÀɠՁۋȭڹ঍ࢗۆҼՙ॥͟

ںঝۍॠČۋεц࢖ڷͿ˃Àݓɳćѻ߸߻ѪۆҼ İٍĵεսॱॢɰə۾قԴÁɳćѻ߸߻Ѫۆ4ɳć əٍ҆ĵεݕॱॠəʚەرࡾóज़څ࠘؍ɰ. ˰͆Դ

қԵۆठۆՁںڦ३Áɳćѻ߸߻Ѫۆ4ɳćə܃ٽ

ॢ ঳ ֬ॹں ݕॱॠٕɰ(Table 1).

ɳćѻ߸߻ڹߪ4 ܛΪۆ߸߻ڌؚںۋڌॠي2 mm ۋॠۆæܓࢹتںɳćۺڷͿ߸߻ॠٕڷ϶, ڌ߻ۋܛ Βʽۋ঳قəٶսқ३εࣀॢࢹتǴҼՙۆۻ॥͟

ęɳćѻ߸߻قۆ३ڌ߻ʽҼՙۆۻߕ॥͟ںɰڼۆ

֩ں ۋڌॠي Ҽİॠٕɰ.

ধսڱ(%) =ٍ՚߸߻Ѫقۆ३߸߻ʽ4ɳćūݓۆɀۺ॥͟(mg/kg) ٶս߸߻Ѫق ۆ३ ߸߻ʽ ߪ ॥͟(mg/kg) ×100

ɳێڌ߻Ѫ(Mehlich 3 ڌ߻Ѫ)ęۆԜěқԵ

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Table 3. Physical and chemical properties of the soils

Soil pH

CEC (cmol/kg)

As concentration (mg/kg) Total

Tessier's methods Ahn's methods

Step 1

Step 2

Step 3

Step

4 Sum Recovery (%)

Step 1

Step 2

Step 3

Step

4 Sum Recovery (%) 1 5.82 28.0 19.2 1.9 N.D. N.D. 12.5 14.4 74.7 0.7 0.8 N.D. 21.6 23.1 120.3 2 4.80 19.5 44.9 2.0 N.D. N.D. 30.0 32.0 71.3 0.7 1.5 0.3 53.1 55.7 123.9 3 7.22 21.8 83.4 1.9 N.D. N.D. 34.0 35.9 43.0 0.7 2.5 1.2 107.1 111.5 133.6 4 6.52 25.5 81.4 1.4 N.D. N.D. 33.0 34.5 42.3 0.8 0.9 1.6 82.2 85.5 104.9 5 5.69 17.9 164.5 2.1 N.D. N.D. 81.1 83.2 50.6 0.7 10.0 2.2 204.5 217.4 132.2 6 6.73 21.0 21.4 0.1 0.6 N.D. 31.8 32.6 152.1 0.6 7.9 4.8 14.4 27.7 129.3 7 8.08 23.1 53.5 0.3 1.3 N.D. 58.7 60.3 113.0 0.7 13.8 14.0 31.5 60.1 112.7 8 8.81 26.7 30.3 0.3 1.0 N.D. 60.5 61.9 203.9 0.7 12.5 5.8 17.3 36.3 119.5 9 4.73 23.6 19.7 0.1 0.2 N.D. 16.2 16.5 83.8 0.7 6.0 3.7 6.5 16.9 85.8 10 6.13 22.7 35.6 0.3 0.3 N.D. 33.4 34.0 95.3 0.6 13.0 7.6 14.3 35.5 99.5 11 7.88 31.3 190.4 0.3 3.3 16.2 190.4 210.3 110.4 0.8 94.9 40.5 39.9 176.1 92.5 12 7.03 21.9 119.9 0.2 1.7 2.8 112.4 117.1 97.7 0.6 62.9 23.7 32.8 119.9 100.0 13 8.28 22.0 70.4 0.3 1.7 N.D. 64.0 66.0 93.6 0.7 26.4 12.1 39.3 78.4 111.3 14 6.79 23.0 17.8 0.2 0.1 N.D. 17.8 18.1 101.4 0.6 8.1 4.8 5.3 18.8 105.0 15 6.95 23.6 24.4 0.2 0.3 N.D. 22.9 23.4 95.9 0.5 9.5 7.2 6.0 23.2 95.0 16 7.16 19.8 40.7 0.1 0.3 N.D. 41.0 41.5 101.7 0.5 15.4 4.2 12.6 32.7 80.3 17 8.00 31.3 46.5 0.1 N.D. N.D. 77.6 77.7 167.0 0.6 11.6 14.2 31.8 58.2 125.1 18 6.83 14.5 20.1 0.2 N.D. N.D. 18.4 18.6 92.3 0.5 12.7 3.7 4.6 21.5 106.8 19 7.58 26.7 47.8 0.2 N.D. N.D. 52.7 52.9 110.7 0.6 12.3 14.4 19.0 46.3 96.8 20 6.31 22.7 13.9 0.2 N.D. N.D. 16.5 16.8 119.9 0.5 4.6 1.3 8.6 15.0 107.4 21 7.01 17.9 63.0 0.2 N.D. N.D. 70.0 70.2 111.5 0.5 25.2 18.8 15.9 60.4 95.9 Minimum. 4.73 14.53 13.98 0.1 N.D. N.D. 12.5 14.4 80.3 0.5 0.8 N.D. 4.6 15.0 42.3 Maximum. 8.81 31.33 190.43 2.1 3.3 16.2 190.4 210.3 133.6 0.8 94.9 40.5 204.5 217.4 203.9 Median 7.0 22.7 44.9 0.2 0.1 N.D. 34.0 35.9 108.5 0.6 16.8 8.9 36.6 62.9 101.5 Average 6.87 23.06 57.60 0.6 0.5 0.9 51.2 53.2 106.8 0.6 11.6 4.8 19.0 46.3 97.7 N.D. : Not determined Table 2. Procedure of Mehlich-3 method (Mehlich, 1984)

Reactants

· Stock solution M-3: 1.5M NH4F + 0.1M EDTA

· Leaching solution

: 200.1 g (NH4NO3) + 100 mL(Stock solution M-3) + 115 mL (CH3COOH) + 82 mL (10% HNO3) in 10 L DIW

Leaching condition Soil : Leaching solution = 1 : 10, 5 min, 120 rpm, room temp

şܕۆٍĵقԴ֩НͿۻۋʽۍ(P)ۆ֬܃تęȭ ڹԜěՁں҃ۋČ, ŔٽقʪɰتॢŚ՚ۆ֩Нۻۋ ÀɠՁںঝۍॠəʚۋڌʼر٣Mehlich 3 ڌ߻Ѫںۺ ڌॠيҼՙۆ֩НۻۋÀɠՁںêࢹॠٕڷ϶, ߸Àۺڷ Ϳ˃Àݓɳćѻ߸߻ѪęۆԜěқԵںսॱॠٕɰ.

ێъۺڷͿ֩Нۆąڍɳćѻ߸߻Ѫܼ1~2ɳć঍

ࢗۆܼŚ՚ۋԦНॡۺڷͿۋڌÀɠॢ঍ࢗͿ҃Čʼ رٵڷ϶(Li et al., 2007; Hong et al., 2009), ˰͆Դ

ٍ҆ĵقԴəMehlich 3 ڌ߻ѪęۆԜěқԵսॱ֨

ɳćѻ߸߻2ɳćūݓۆɀۺ॥͟ںۋڌॠٕɰ. Mehlich 3ڌ߻ѪۆۙՃॢқԵѓѪڹTable 2قǣࢍǴؽɰ.

Āęф३Ե

ࢹت֨Β޽ࠄфНνজॡۺ࣢Ձࣷ؊

޽ࠄॢࢹتۆНνজॡۺ࣢ՁںTable 3قश֨ॠٕ

ɰ. ࢹتpHə4.73 ~ 8.81, تۋ٣İঞɠͳڹ14.5~31.3 cmolc/kg, ࢹت ǴҼՙۆۻ॥͟ڹ 13.9~190.4 mg/kg

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(a) Tessier’s method

(b) Ahn’s method

Fig. 1. Mode of (a) Tessier’s method and (b) Ahn’s method through sequential extraction.

ڷͿɰتॠóǣࢍǮɰ. pHق˰δࢹتқΪĀę, ԓ Ձࢹ(pH<5) - 2Ò, أԓՁࢹ(pH 5~6.5) - 4Ò, ܼՁࢹ (pH 6.5~7.5) - 9Ò, أّşՁࢹ(pH 7.5~9.0) - 6ÒͿɰ تॢpH ѩڦۆࢹت֨ΒÀٍĵقۋڌʼؽڼںঝۍ ॠٕɰ(Choi et al., 1996). Kim ˣ(2006)ق˰βϸتۋ ٣İঞɠͳق˰͆ࢹتںԐࢹ(1~5 cmolc/kg), йՃԐت ࢹ(5~10 cmolc/kg), تࢹфйԐݗتࢹ(5~15 cmolc/kg), ֩ تࢹ(15~30 cmolc/kg), ֩ࢹ(30 cmolc/kg ۋԜ)ˣڷͿ

ĵқॣսەڷ϶, ۋεٍ҆ĵۆĀęقۺڌॠϸȬą ݓࢹتۆ࣢ݜۍйςݗۆ֩تࢹ(clay loam)À18ÒͿ

ǣࢍǮɰ. Ȭʪق˰δқΪۆąڍইۦĶǴࢹت١ّ

ڍͲşܵ(25 mg/kg) фʂ޾şܵ(75 mg/kg)ںц࢖ڷͿ

ڍͲşܵۆ50% Ȭʪ~ ڍͲşܵйχ(7Ò), ڍͲşܵ

ߣę~ ʂ޾şܵйχ(9Ò), ʂ޾şܵߣę~ ʂ޾şܵ

ۆ2ѕ(3Ò), ʂ޾şܵ2ѕߣę(2Ò)Ϳĵқॠٕɰ. ޽ ࠄॢ ࢹت ֨Βۆ Нνজॡۺ ࣢Ձ ࣷ؊ Āę, ɰتॢ

pH ѩڦф١ّȬʪε҃ۋə Ȭąݓ ࢹتۋ ٍĵق

ۋڌʼؽڼں ঝۍॣ ս ەؽɰ.

ɳćѻ߸߻Ҽİٍĵ

ɳćѻ߸߻ѪڹࢹتǴɰتॢۍۙͿۍॢ߸߻Ѫۺ ڌۆॢć, ֨ΒߌνЛ܃, ՙڅ֨Â, ܼ҄߸߻, ߸߻ڌϔ

ۆۺ०Ձˣۆॢć۾ںÀݓČەڷ϶(Rapin et al., 1986;

Belzile et al., 1989; Kim and Fergusson, 1991; Jung, 1994), ۋͿۍ३ࢹتǴܼŚ՚ۆԜʂۺۋʴՁںঝۍ ॠəʚܳͿۋڌۋʽɰ. Ŕ͠ǣٍ҆ĵقԴə˃Àݓ

߸߻Ѫں ݔۿۺڷͿҼİॠČۙɳćѻ߸߻ںࣀ३ধ սʽتęٶսқ३قۆ३߸߻ʽߪ॥͟Âۆ޲ۋε

ঝۍ॰ڷ϶, ٍĵ ĀęεTable 3قǣࢍǴؽɰ.

ٍĵĀę, 42Ò֨Βܼ34Ò֨ΒقԴ±30%ۆ١޲

ѩڦε҃يɳćѻ߸߻қԵۆĀęٮۻ॥͟Āęٮۆ

ێěՁںঝۍॣսەؽڷǣ, Tessier ߸߻Ѫںۋڌॢ

ێҙ֨Β(3 - 57%, 4 - 58%, 6 - 52%, 8 - 103%, 17 - 67%)ۆąڍϔڍࢀ١޲ε҃ۋşʪ॰ɰ. ۋ͠ॢ

ێҙ֨ΒۆĀęəɳćѻ߸߻ѪۋÍəॢć۾قۆॢ

ٖॳʪەڷǣ, қԵę܁ܼьԦॢ١ΪÀɰՙٖॳں

йࠚìڷͿࣺɳʽɰ. ̚ॢধսڱ100%εşܵڷͿߣ ęॢÉęйɵʽÉۆथŒںÁÁĵॢĀę, Ahn ߸߻

Ѫڹ116%ٮ92%, Tessier ߸߻Ѫڹ129%ٮ76%ۆĀ ęε҃يAhn ߸߻ѪۋTessier ߸߻ѪقҼॠيʂߕ ۺڷͿ ধսڱۋ 100%قÀūڏìڷͿ ঝۍʼؽɰ.

21ÒʂԜࢹتقʂ३˃Àݓɳćѻ߸߻Ѫںۺڌ

ॢĀęəFig. 1قǣࢍǴؽɰ. Tessier ߸߻Ѫںۋڌ

ॢąڍ, Ͽ˜֨ΒقԴۛΪН঍ࢗۍ4ɳćۆҼڱۋ

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Fig. 2. Correlation between Sequential extraction and Mehlich 3 leaching method.

90% ۋԜڷͿȭڹҼڱں޲ݓ॰ڷ϶, ԜʂۺڷͿۋ ʴՁۋȭڹ1ɳć~3ɳćۆҼڱڹŕ০ййॠٕɰ. ъ ϸقAhn ߸߻ѪںۋڌॢąڍقəTessier ߸߻Ѫę əԜۋॢĀęεٕ҃ɰ. ێҙ֨Β(1~5)ۆąڍTessier

߸߻ѪęʴێॠóۛΪН঍ࢗۆҼڱۋ90%εߣę ॠəتԜں҃ۋşʪ॰ڷ϶, ۋ͠ॢۋڮͿ֨Β1ۆ

ąڍ3ɳćÀҝࠑ܁ڷͿǣࢍǣşʪॠٕɰ. Ŕ͠ǣۋ

˞ێҙ֨Βε܃ٽॢǣϢݓ16Ò֨ΒۆąڍԜʂۺ ڷͿۋʴՁۋȭڹ1~3ɳćۆҼڱۋ50~80%قۋε

܁ʪͿȭڹҼڱں޲ݓॠيʂߕۺڷͿ1~4ɳćÀČ βóқपॠəتԜںٕ҃ɰ. ۋ͠ॢٍĵĀęəAhn

߸߻ѪۋࢹتǴҼՙۆܕۦ঍ࢗεՃқজॣսەڷ

϶, Tessier ߸߻ѪقҼॠيԜʂۺڷͿঞąݓĵজॡۺ ڷͿڮڌॢ܁҃ε ܃ėॣս ەڼںǣࢍǶɰ.

ɳێڌ߻Ѫę(Mehlich 3 ڌ߻Ѫ)ۆԜěҼİ

ؘԸ˃Àݓɳćѻ߸߻ѪۆۺڌĀę, ࢹتǴܕۦ ॠəҼՙۆܕۦ঍ࢗقەرԴͿԜۋॠóɰδتԜ ں҃ےںঝۍॠٕɰ. Ŕ͠ǣۋ͠ॢٍĵĀęə˃ɳ ćѻ߸߻ѪÂۆ Ԝʂۺۍ ޲ۋε ǣࢍǷ Ӽۋ϶, ࢹت

ǴܕۦॠəҼՙۆۋʴʪεݔۿۺڷͿǣࢍǴəìڹ

؉ɦɰ. ݌, Tessier ߸߻ѪںۋڌॢąڍϿ˜֨Βق ԴۛΪН঍ࢗÀʂҙқۋؽČAhn ߸߻ѪڹԜʂۺ ڷͿ1~4ɳćÀČδқपεٕ҃ݓχ, ۋ͠ॢٍĵĀ ęχڷͿࢹتǴҼՙۆܕۦ঍ࢗεঝۍॠəʚەر

ʌڎۺ०ॢѓѪںԸѻॠəìڹҝÀॠɰ. ˰͆Դࢹ تڷͿҙࢢ֩НͿۆۻۋÀÀɠॢҼՙۆتںঝۍॠ şڦ३ԸѻʽMehlich 3 ڌ߻Ѫںۺڌॠٕڷ϶, ۋε

ц࢖ڷͿɳćѻ߸߻2ɳćūݓۆɀۺ॥͟ęԜěՁں

ঝۍॠٕɰ(Fig. 2). Tessier ߸߻ѪęMehlich 3 ڌ߻Ѫ ęۆԜěқԵĀę, şڐşə1.243ڷͿMehlich 3 ڌ

߻Ѫقۆॢڌ߻͟ęTessier ߸߻Ѫقۆॢڌ߻͟ۋ

Ҽ֦ॢ ѩڦε ҃ےں ঝۍॠٕɰ. ъϸ Ahn ߸߻Ѫۆ

şڐşə0.072ͿǣࢍǮڷ϶, ۋս࠘əAhn ߸߻Ѫۋ

Mehlich 3 ڌ߻Ѫقۆ३ڌ߻ʽتۆ10ѕۋԜں߸߻

॥ںÂۿۺڷͿǣࢍǶɰČ҇սەɰ. Ŕ͠ǣ˃ɳć ѻ߸߻Ѫę Mehlich 3 ڌ߻ѪÂۆԜěՁқԵĀęə

Ahn ߸߻ѪۋȭڹتۆԜěěć(positive correlation) ε ҃ۍъϸԜʂۺڷͿTessier ߸߻ѪڹǰڹԜěě ćεٕ҃ɰ. ࣢০˃ѺսÂۆԜěěćε܁͟ۺڷͿ

ǣࢍǴəR2 ÉقԴAhn ߸߻Ѫڹ0.847, Tessier ߸߻

Ѫڹ0.445ε҃ي˃߸߻ѪÂۆŕϼॢ޲ۋε҃يܳ

ؽɰ. Richard(1990)ق˰βϸ, |R|0.35 ۋϸأॢԸ

঍ěć, 0.36|R|G 0.67 ۋϸ ۺۼॢ Ը঍ěć, 0.68

|R|G1.00 ۋϸÌॢԸ঍ěćεÍəɰČशইॠ϶,

࣢০0.90|R|ڹϔڍÌॢԸ঍ěćεǣࢍǶɰČॣ

սەɰ. Ahn ߸߻ѪۆR2Éۍ0.847ںR ÉڷͿঞԓ ॠϸ0.920ۋ϶, ˰͆ԴMehlich 3 ڌ߻ѪęAhn ߸߻

ѪÂقəϔڍÌॢԸ঍ěćεǣࢍǶɰČॣսەɰ.

Ā΁

Ahn߸߻Ѫقۆॢܕۦ঍ࢗঝۍ֨1~4ɳćÀČβ óқपॠČەؽʏъϸ, Tessier ߸߻Ѫڹʂҙқۆ

֨ΒقԴ 4ɳć(residual fraction)À 90% ۋԜۆ ȭڹ

Ҽڱں޲ݓ॰ɰ. Mehlich 3 ڌ߻ѪęԜěқԵںսॱ

ॢĀę̚ॢTessier ߸߻Ѫ(R=0.667)قҼॠيAhn ߸

߻Ѫ(R=0.920)ۋښˣ০ȭڹتۆԜěěćεٕ҃ɰ.

Tessier ˣ(1997)ۋ܃؋ॢѓѪڹսڌؚԜࢗقԴت ۋ٣ڷͿܕۦॠəܼŚ՚ڙՙ˞ںʂԜڷͿČ؋ʼؽ ڷдͿ, սڌؚԜࢗقԴԓজڼۋ٣ڷͿܕۦॠəҼՙ əۋ͠ॢѓѪۋۺ०ॠݓ؍ںսەڷ϶(Keon et al., 2001; Han et al., 2011), ۋ͠ॢۋڮͿ߯ŖܼŚ՚ۋ

؉ɨҼՙقۺ०ॢɳćѻ߸߻ѓѪںČ؋ॠəٍĵÀ

টь০ݕॱܼۋɰ(Tokunaga et al., 1991; Keon et al., 2001; Wensel et al., 2001; Mihaljevic et al., 2003; Ahn et al., 2005). ۋٍĵقԴə߯ŖقČ؋ʽAhn ߸߻Ѫ ęTessier ߸߻ѪںݔۿҼİ॰ڷ϶, ٍĵĀęTessier

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ۆѓѪۋAhn ߸߻ѪقҼॠيࢹتǴҼՙۆܕۦ঍

ࢗεঝۍॠəʚەرԜʂۺڷͿҙۺ०ॠɰəĀęε

صؽɰ. ˰͆ԴTessier ߸߻ѪۋҼ΀ۻՃćۺڷͿÀ

ۤ ȇν ۋڌʼə ɳćѻ߸߻Ѫۋݓχ, ܼŚ՚ۋ ؉ɨ

ࢹتǴҼՙۆܕۦ঍ࢗεঝۍॠČۙɳćѻ߸߻Ѫں

ۺڌॣąڍقəۋ͠ॢǴڌۋČͲʼرآॢɰ. Ŕ͠

ǣܼŚ՚١ّࢹتۆąڍҼՙٮ҄०ۺڷͿ١ّʽ

ࢹتۋψڷдͿ, ИܓæۺڷͿʴێॢࢹتق˃Àݓ

ɳćѻ߸߻ѪںۺڌॠəìڹϔڍҼমڱۺۍێۋʾ

սەɰ. ˰͆Դॳ঳ҼՙٮܼŚ՚ۆܕۦ঍ࢗεʴ֨

قঝۍÀɠॢɳێɳćѻ߸߻ѪۆČ؋ۋज़څॠ϶ۋ ق ˰δݓ՚ۺۍ ٍĵÀ ݕॱʼرآ ॣ ìۋɰ.

ԐԐ

ۋٍĵəॢĶġ३ěνėɳۆݓڙقۆ३սॱʼؽ ڷ϶ ۋق ÇԐ˚ςɦɰ.

޷ČЛॶ

Ahn, J.S., 2000, “Environmental contamination of arsenic and heavy metals by past Au-Ag mining activities and design of containment system for mine wastes,” Ph.D thesis, Seoul University.

Ahn, J.S., Kim, J.Y., Chon, C.M. and Moon, H.S., 2003,

“Mineralogical and chemical characterization of arsenic solid phases in weathered mine tailings and their leaching potential,” Econ, Environ. Geol., Vol. 36, pp. 27-38.

Ahn, J.S., Park, Y.S., Kim, J.Y. and Kim, K.Y., 2005,

“Mineralogical and geochemical characterization of arsenic in an abandoned mine tailings of Korea,”

Environmental Geochemistry and Health, Vol. 27, pp.

147-157.

Alloway, B.J., 1990, Heavy Metals in Soils, 2nd ED, Blackie and Professional, UK, pp. 105-224.

Alloway, B.J., Jackson, A.P. and Morgan, H., 1990, “The accumulation of cadmium by vegetables grown on soils contaminated from a variety of sources,” Sci. Tot.

Environ., Vol. 91, pp. 223-236.

Belzile, N., Lecomte, P. and Tessier, A., 1989, “Testing readsorption of trace elements during partial chemical extraction of bottom sediments,” Environmental Science and Technology, Vol. 23, pp. 1015-1020.

Bhumbla, K.K. and Keefer, R.F., 1994, Arsenic Mobilization and Bioavailability in Soils, In Mriagu, J.O. (ed.) Arsenic in the Environment, Wiley, New york, pp. 51-82.

Calmano, W., 1983, “Chemical extraction of heavy metals

in polluted river sediments in central europe,” Science of the Total Environment, Vol. 28, pp. 77-90.

Choi, S.W. and Kim, U.S., 1996, Medical environmental geochemistry, ChunKwang, pp. 401-442.

Cullen, W.R. and Reimer, K.J., 1989, “Arsenic speciation in the environment,” Chem. Rev, Vol. 89, pp. 713-764.

Domingues, H., Silva, J.M. and Vieira, E., 1990, “Copper and znic in sandy, granitic and schist soils,” Environ- mental Technology, Vol. 11, pp. 463-468.

Filgueiras, A.V., Lavilla, I. and Bendicho, C., 2002,

“Chemical sequential extraction for metal partitioning in environmental solid samples,” Journal of Environmental Monitoring, Vol. 4, pp. 823-857.

Gulens, J. and Champ, D.R., 1979, Influence of Redox Environments on the Mobility of Arsenic in Groundwater, In Jenne E.A. (ed). Chemical Modeling in Aqueous Systems, ACS Press, Washington, DC., pp. 81-95.

Han, H.J., Lee, J.U. and Chon, H.T., 2011, “Comparison of bioleaching of heavy metals and arsenic from contaminated soil in the vincinity of a refinery using sulfur-oxidizing and iron-oxidizing bacteria,” J. Kor. Soc.

Geosystem Eng., Vol. 48-6, pp. 713-722.

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׌ச૳

1991țԴڐʂॡİėęʂॡۙڙėॡ ę ėॡԐ

1993țԴڐʂॡİʂॡڙۙڙėॡę

ėॡԵԐ

1998țԴڐʂॡİʂॡڙۙڙėॡę

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ইۦ ġܳęॡşցڙ ঞąėॡҙ ٍĵİս (E-mail; [email protected])

׌լ૽

1987țԴڐʂॡİۙڙėॡęėॡԐ 1989țԴڐʂॡİۙڙėॡęėॡԵԐ 1993țٖĶ͢ʏʂॡİےगνضʂॡ

ėॡчԐ

ইۦ ġܳęॡşցڙ ঞąėॡę İս (E-mail; [email protected])

ଲ஼৤

1990țۋজيۙʂॡİęॡİگęۋ ॡԐ

1992țۋজيۙʂॡİęॡİگęİ گॡԵԐ

1997țԴڐʂॡİۙڙėॡęėॡчԐ

ইۦ ॢĶġ३ěνėɳ ġ३şցٍĵՙ ࣷ࣡ۤ

(E-mail; [email protected])

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ইۦ ġܳęॡşցڙ ঞąėॡҙ чԐę܁

(欧G 彳櫾躇G 缧48嘳G 缧6埲G 垾畢)

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1998țġڏʂॡİėęʂॡঞąėॡ ę ėॡԐ

2000țġܳęॡşցڙঞąėॡҙė ॡԵԐ

2008țġܳęॡşցڙঞąėॡҙė ॡчԐ

ইۦ ġܳęॡşցڙ ঞąėॡҙ ٍĵİս (E-mail; [email protected])

׌ଗ৤

ইۦ ॢĶġ३ěνėɳ ۦݔ (欧G 彳櫾躇G 缧48嘳G 缧3埲G 垾畢)

Amsterdam, pp. 505-523.

Ure, A.M. and Davidson, C.M., 2001, Chemical Speciation in the Environment, Blackie, Glasgow, pp. 265-321.

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수치

Table 1. Procedure of two sequential extraction methods (Tessier et al., 1979; Ahn et al., 2005) Extraction
Table 3. Physical and chemical properties of the soils Soil pH CEC (cmol/kg) As concentration (mg/kg) Total
Fig. 1. Mode of (a) Tessier’s method and (b) Ahn’s method through sequential extraction.
Fig. 2.  Correlation between Sequential extraction and  Mehlich 3 leaching method.

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