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Possible Phytoremediation of Cadmium Pollution Soil with Kenaf ( ࠤ࠽ࡈߦࠃࠆࠞ࠼ࡒ࠙ࡓ㒰ᨴߩน⢻ᕈ ) ㊀㊄ዻᳪᨴ࿯ფ߆ࠄᳪᨴ‛⾰ࠍ࿁෼ߔࠆ㜞ᯏ⢻ⅣႺୃᓳᬀ‛ߩត⚝

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(1)

Science Journal of Kanagawa University17 : 39-42 (2006)

©Research Institute for Integrated Science, Kanagawa University

عේ ⪺ع 2004-2005

ᐕᐲ␹ᄹᎹᄢቇ౒ห⎇ⓥᅑബഥᚑ⺰ᢥ

㊀㊄ዻᳪᨴ࿯ფ߆ࠄᳪᨴ‛⾰ࠍ࿁෼ߔࠆ㜞ᯏ⢻ⅣႺୃᓳᬀ‛ߩត⚝

(ࠤ࠽ࡈߦࠃࠆࠞ࠼ࡒ࠙ࡓ㒰ᨴߩน⢻ᕈ)

Ỉ਄⥶৻㇢

1

Ⓑ૑ാ᳇

2

ᄢ⍹ਇੑᄦ

2

੗਄๺ੳ

1

⷏ᧄฝሶ

2

㋈ᧁ␽ᒄ

1,3

Possible Phytoremediation of Cadmium Pollution Soil with Kenaf

Koichiro Sawakami

1

, Yuki Inazumi

2

, Fujio Ohishi

2

, Kazuhito Inoue

1

, Yuko Nishimoto

2

and Yoshihiro Suzuki

1,3

1 Department of Biological Sciences, and

2 Department of Chemistry, Faculty of Science, Kanagawa University, Hiratsuka-City, Kanagawa 259-1293, Japan

3 To whom correspondence should be addressed. E-mail: syoshi@bio.kanagawa-u.ac.jp

Abstract: Kenaf (Hibiscus cannabinus L.), which can grow rapidly and maintain high primary production, was examined for its ability to decontaminate cadmium ions (Cd) from polluted soil. Although its germination and growth were not affected at first, its photosynthesis dependent growth was disturbed by Cd in the soil. No growth after expanding the true leaves was observed at above 111 ppm Cd. At 74.1 ppm Cd, kenaf could acclimate and began to grow after a few weeks lag. The biomass increased by 2.4 times from 4 to 6 weeks after sawing. Higher accumulation rates were observed in the plant body at below 74.1 ppm Cd. The rate increased to 6.4 times in the plant body at 1.48 ppm Cd. Assuming the same productions of kenaf as on the soil without Cd, it could decontaminate 1.48 ppm Cd from the polluted soil for ca. 16 years and could more efficiently from the soil containing lower concentrations of Cd. These results suggested the possible phytoremediation with kenaf applied to the polluted soil with lower concentrations of Cd.

Keywords: acclimation, cadmium, decontamination, kenaf, phytoremediation

ᐨ⺰

Ꮏ႐〔࿾߿↥ᬺᑄ᫈‛ಣℂ႐ߥߤߩ๟ㄝߩ࿯࿾ࠍౣ

೑↪ߔࠆ㓙ޔၮḰ୯ࠍ⿥߃ࠆ㊀㊄ዻ߿ើ⊒ᕈ᦭ᯏൻ ว‛ߦࠃࠆᳪᨴ߇⷗ߟ߆ࠆߎߣߪዋߥߊߥ޿ޕߎ߁ ߒߚ࿯࿾ࠍ㒰ᨴߒޔౣ߮೑↪น⢻ߦߔࠆߚ߼ߦߪޔ ᄙᄢߥࠦࠬ࠻߇ᔅⷐߢ޽ࠅޔᣣᧄ࿖ౝߛߌߢ߽ޔኻ

╷⾌↪ߪ13ళ౞ߦ㆐ߔࠆߣ⹜▚ߐࠇߡ޿ࠆ1)ޕ߹ߚޔ Ꮏᬺൻߩㅴࠎߛ⊒ዷㅜ਄࿖ߢ߽࿯ფᳪᨴߪᷓೞߥ໧

㗴ߢ޽ࠅޔ㒰ᨴ⾌↪ࠍᜬߚߥ޿ߎࠇࠄㅜ਄࿖ߦߣߞ ߡޔૐࠦࠬ࠻ߩ㒰ᨴᛛⴚ߇ਇนᰳߥ߽ߩߣߥߞߡ޿

ࠆޕ

ㄭᐕޔૐࠦࠬ࠻ߩ㒰ᨴᛛⴚߣߒߡޔᓸ↢‛ࠍ↪޿

ࠆ㒰ᨴᣇᴺ㧔ࡃࠗࠝ࡟ࡔ࠺ࠖࠛ࡯࡚ࠪࡦ㧕߇ᵈ⋡ߐ ࠇߡ޿ࠆޕࡃࠗࠝ࡟ࡔ࠺ࠖࠛ࡯࡚ࠪࡦᴺߪޔᓸ↢‛

ࠍ↪޿ߡើ⊒ᕈ᦭ᯏൻว‛ࠍಽ⸃ߔࠆ㒰ᨴᴺߢޔ࠲

ࡦࠞ࡯߆ࠄߩᵹ಴ේᴤߩ㒰ᨴߥߤߦᵴ↪ߐࠇߡ޿ࠆޕ ߎߩᣇᴺߢ߽ޔ㊀㊄ዻൻว‛ࠍนṁൻ޽ࠆ޿ߪήᲥ

ൻߔࠆߎߣ߇น⢻ߢ޽ࠆ߇ޔర⚛⥄૕߇Ქᕈࠍᜬߟ

㊀㊄ዻࠍ࿁෼࡮㒰෰ߔࠆߎߣߪߢ߈ߥ޿ 2)ޕߎࠇߦ ኻߒޔ⛽▤᧤ᬀ‛ࠍ↪޿ޔర⚛⥄りࠍ࿁෼࡮㒰෰ߒޔ ᳪᨴ࿯ფߩ㒰ᨴࠍⴕ߁ᣇᴺ߇޽ࠆޕ⛽▤᧤ᬀ‛ߩ⫳

ᢔߦ઻߁᳓ߩᵹࠇࠍ೑↪ߒߡޔᳪᨴ‛⾰ࠍᬀ‛૕ౝ

ߦ࿁෼ߒޔᬀ‛૕ߣߣ߽ߦ㒰෰ߔࠆߎߣߢ㒰ᨴࠍⴕ ߁ߎߩᣇᴺߪޔࡈࠔࠗ࠻࡟ࡔ࠺ࠖࠛ࡯࡚ࠪࡦߣ๭߫

ࠇߡ޿ࠆޕ

ߎࠇ߹ߢߩࡈࠔࠗ࠻࡟ࡔ࠺ࠖࠛ࡯࡚ࠪࡦߢߪޔ㋶

ጊ࿾ၞߦ․⇣⊛ߦಽᏓߒޔᳪᨴ࿯ფߢ߽ᩱၭߢ߈ࠆ ߎߣ߇੍߼ಽ߆ߞߡ޿ࠆ㊀㊄ዻ⠴ᕈᬀ‛߇↪޿ࠄࠇ ߡ߈ߚޕߒ߆ߒޔߎ߁ߒߚ㊀㊄ዻ⠴ᕈᬀ‛ߩᄙߊߪޔ

↢㐳߇ㆃߊޔࡃࠗࠝࡑࠬ߇ዊߐ޿ߚ߼ޔᄢ㊂ߩᳪᨴ

‛⾰ࠍല₸ࠃߊ࿁෼ߔࠆߎߣߪ㔍ߒ߆ߞߚޕߘߩᓟޔ ߐ߹ߑ߹ߥᬀ‛ߢᳪᨴ࿯ფߦኻߔࠆ⠴ᕈ߇⹜㛎ߐࠇޔ

㊀㊄ዻ⠴ᕈᬀ‛એᄖߢ߽ޔ৻ቯߩỚᐲߩᳪᨴߦኻߒ

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40 Science Journal of Kanagawa University Vol. 17, 2006

⠴ᕈ߇޽ࠅޔߒ߆߽↢㐳߇ㅦߊࡃࠗࠝࡑࠬ߇ᄢ߈޿

ߚ߼ޔ㊀㊄ዻࠍ᦭ലߦ࿁෼ߔࠆᬀ‛ߎߣ߇ಽ߆ࠅ3)ޔ ല₸ߩࠃ޿㒰ᨴ߇น⢻ߣߥࠅߟߟ޽ࠆޕᧄ⎇ⓥߢߪޔ

↢㐳߇ㅦߊࡃࠗࠝࡑࠬ߇ᄢ߈޿߫߆ࠅߢߥߊޔ⫳ᢔ ㅦᐲ߇㜞ߊޔ⫳ᢔߦ઻߁᳓߿࿯ფ߆ࠄߩ‛⾰⒖േ㊂ ߇ᄢ߈޿ߎߣ߇⍮ࠄࠇߡ޿ࠆࠤ࠽ࡈ㧔Hibuscus cannabinus L.㧕ߦ⌕⋡ߒޔࡈࠔࠗ࠻࡟ࡔ࠺ࠖࠛ࡯

࡚ࠪࡦ߳ߩ೑↪ࠍᬌ⸛ߒߚޕࠤ࠽ࡈߢߪޔㄘᬺၮḰ ୯㧔1 ppm㧕Ớᐲߩࠞ࠼ࡒ࠙ࡓ㧔Cd㧕㒰ᨴߦ৻ቯߩ ലᨐ߇ᦼᓙߐࠇߡ޿ࠆ 4)ޕᧄ⎇ⓥߢߪޔ᭽ޘߥỚᐲ ߩCd ᳪᨴ࿯ფߢࠤ࠽ࡈࠍᩱၭߒޔᳪᨴ࿯ფߦኻߔ ࠆᔕ╵ࠍ᣿ࠄ߆ߦߒޔߐࠄߦޔߤߩࠃ߁ߥỚᐲߩCd ᳪᨴ࿯ფߢല₸ࠃߊ㒰ᨴߔࠆߎߣ߇น⢻߆ࠍቯ㊂⊛

ߦᬌ⸛ߒߚޕ

᧚ᢱߣᣇᴺ

㤥࿯㧔㤥࿯, ࠕࠗ࡝ࠬࠝ࡯ࡗࡑ㧕ޔ⿒₹࿯㧔਄⾰⿒₹

࿯࡮ዊ☸, ࠕࠗ࡝ࠬࠝ࡯ࡗࡑ㧕ࠍ 1:1 ߩᲧ₸ߢᷙว ߒߚ࿯ფࠍ↪޿ߚޕࡊ࡜ࠬ࠴࠶ࠢኈེ㧔ౝᓘ380˜ 260˜240 mm㧕ߦ20 l ߩᷙว࿯ფࠍḩߚߒޔ㧝ޔ 10ޔ100ޔ150ޔ300 mg࡮l-1 ߩCdỚᐲߦߥࠆࠃ߁

⎫㉄ࠞ࠼ࡒ࠙ࡓ᳓ṁᶧࠍട߃ޔዪᚲ⊛ߥỚᐲߩᄌൻ ࠍߢ߈ࠆ㒢ࠅዋߥߊߔࠆࠃ߁චಽߦᠣᜈߒߚᓟޔᳪ ᨴ࿯ფߣߒߡ↪޿ߚޕᳪᨴ࿯ფߣCd ࠍᷙวߒߥ޿

ኻᾖ࿯ფ㧔0 ppm㧕ߩฦ20 l ߦޔൻᚑ⢈ᢱ㧔㘺ᢱ૞

‛㈩ว246ภ, ో࿖ㄘᬺදห⚵วㅪวળ㧕ࠍ25 g ᷙ วߒޔᣉ⢈ߒߚޕฦኈེߦࠤ࠽ࡈ㧔H. cannabinus cv.

Evergrades41㧕ߩ⒳ሶࠍ30☸㧔10☸ߠߟ3೉㧕᠞

⒳ߒޔ᳇᷷ 30͠ޔḨᐲ65㧑ࠍ଻ߜޔ㓁శ࡜ࡦࡊߦ ࠃࠅ16ᤨ㑆᣿ᦼ/8 ᤨ㑆ᥧᦼ㧔500Ǵmol photons㨯 m-2㨯s-1㧕ߩశ᧦ઙߦ೙ᓮߒߚੱᎿ᳇⽎ቶ㧔ዊ♻Ꮏᬺ

ᩣᑼળ␠㧕ౝߢᩱၭࠍⴕߞߚޕᩱၭᦼ㑆ਛߪలಽߥ ẑ᳓ࠍⴕ޿ޔ࿯ფ߇ੇ῎ߒߥ޿ࠃ߁⇐ᗧߒߚޕ ᠞⒳ 31 ᣣᓟޔฦ♽೉ߢᩱၭߐࠇߚ୘૕ߩ⊒⧘₸

ࠍ⺞ߴޔฦ୘૕ߩ⪲ߩᨎᢙࠍ᷹ቯߒߚᓟޔᬀ‛૕ࠍ

࿁෼ߒޔశวᚑེቭ㧔⪲㧕ޔᡰᜬེቭ㧔⪲ᨩ࡮⨍࡮ᩮ㧕ޔ ಽⵚེቭ㧔⨍㗂࡮⣠⧘㧕ߦಽߌߚޕฦེቭࠍ⚕ⴼߦ

౉ࠇޔ60͠ߦ⸳ቯߒߚੇ῎ᯏ㧔DRYING OVEN, SANYO㧕ౝߢ2ㅳ㑆ੇ῎ߒޔੇ῎㊀㊂ࠍ᷹ቯߒߚޕ

ᬀ‛૕ਛߩ Cd Ớᐲࠍ᷹ቯߒޔ↢㐳ߦ઻߁࿯ფ Cd ᚑಽߩᬀ‛૕߳ߩๆ෼࡮⫾Ⓧࠍ⺞ߴߚޕੇ῎ߐߖߚ ࠤ࠽ࡈ⹜ᢱߪޔߘࠇߙࠇߩེቭߏߣߦ㔚േࡒ࡞ 㧔IFM - 100, IWATANI㧕ߦ߆ߌ⎕⎈ߒߚޕဋ৻ߥ

☳ᧃߣߥߞߚᬀ‛૕߆ࠄฦ1.0 gࠍᱜ⏕ߦ⒊㊂ߒߡ

࡞࠷ࡏߦ⒖ߒޔ㔚᳇Ἱ㧔1Cဳޔᨋ㔚Ꮏ㧕ਛޔ500͠ ߢἯൻߒߚޕἯൻߒߚ⹜ᢱߪޔ0.1 M⎣㉄ṁᶧ100 ml ਛߢ 30 ಽ㑆ᠣᜈߒޔ㊀㊄ዻࠍṁ಴ߐߖߚޕṁᶧࠍ ቯ㊂ỹ⚕㧔No.5BߣNo.5C, ADVANTEC㧕ߣࠪ࡝ࡦ

ࠫࡈࠖ࡞࠲࡯㧔No.190, ሹᓘ0.45 mm, NALGENE㧕 ߢỹㆊߒޔICP̄MSߣࡈ࡟࡯ࡓේሶๆశࠍ↪޿ߡಽ ᨆࠍⴕߞߚޕ

275 ml ߩࡐ࠶࠻ࠍ↪޿ߡᳪᨴ࿯ფਛߢࠤ࠽ࡈࠍ

ᩱၭߒޔห᭽ߩታ㛎ࠍⴕߞߚޕCdỚᐲ0ޔ50ޔ75ޔ 100 mg࡮l-1ߩᷙว࿯ფࠍߘࠇߙࠇ200 ml౉ࠇޔࠤ

࠽ࡈ⒳ሶࠍฦ3☸᠞⒳ߒߚޕᶧ૕⢈ᢱ㧔ࡂࠗࡐࡀ࠶

ࠢࠬᶧ6-10-5, Hyponex␠㧕ߩ500୚Ꮧ㉼ᶧࠍਈ߃ ߡᩱၭߒޔሶ⪲ዷ㐿ᓟޔ↢⢒ߩ⦟޿1ᩣࠍᱷߒޔᱷ ࠅ2ᩣࠍ㑆ᒁ޿ߚޕ2ㅳ㑆Ფߦ࿾਄㜞ߣ࿾⴫ߩ⨍⋥

ᓘࠍ᷹ቯߒޔ⨍ߩᒻ⁁ࠍ౞㍙ߦㄭૃߒߡޔ⨍૕Ⓧࠍ

᳞߼ޔ↢‛㊂ࠍផቯߒߚޕ

⚿ᨐߣ⸛⺰

࿯ფߩኒᐲࠃࠅޔฦᳪᨴ࿯ფߩ 1ޔ10ޔ100ޔ150ޔ 300mg࡮l-1ߩCdỚᐲߪߘࠇߙࠇޔ1.48ޔ14.8ޔ148ޔ

222ޔ444 ppmߦ឵▚ߐࠇߚޕࠤ࠽ࡈ⒳ሶߪޔోߡ

ߩỚᐲߩᳪᨴ࿯ფߢޔ᠞⒳ᓟ2߆ࠄ3ᣣߢ⊒⧘ߒߚޕ

᠞⒳ᓟ 31 ᣣ⋡ߩฦᳪᨴ࿯ფߢ↢⢒ߒߡ޿ߚᬀ‛૕

ߣ᠞⒳ߒߚ⒳ሶᢙࠍᲧセߒ⊒⧘₸ࠍ᳞߼ߚ⚿ᨐޔో

ߡߩ࿯ფߢ80㧑એ਄ߣߥࠅޔCdߦࠃࠆࠤ࠽ࡈ⒳ሶ ߩ⊒⧘㒖ኂߪ⹺߼ࠄࠇߥ߆ߞߚ㧔⴫1㧕ޕ߹ߚޔ⊒⧘

ᓟޔሶ⪲߇ዷ㐿ߔࠆ߹ߢߪฦ࿯ფߢࠤ࠽ࡈߩ↢㐳ߦ 㗼⪺ߥ㆑޿ߪ⹺߼ࠄࠇߥ߆ߞߚ߇ޔߘߩᓟߩ↢㐳ߪޔ

࿯ფߩ Cd Ớᐲߦࠃࠅ⇣ߥߞߡ޿ߚޕૐỚᐲߩ Cd ࠍ฽߻࿯ფߢ߽↢㐳߇㒖ኂߐࠇޔߘߩ⒟ᐲߪCdỚ ᐲ߇㜞޿߶ߤ⪺ߒ߆ߞߚ㧔࿑1㧕ޕ148 ppm ࠍ⿧߃ ࠆᳪᨴỚᐲߢߪޔᧄ⪲ߩዷ㐿߇ㆃࠇޔߘߩᓟޔ↢㐳 ߇⪺ߒߊ㒖ኂߐࠇߚޕߎߩߚ߼ޔ᠞⒳ 31 ᣣ⋡ߩᤨ

ὐߢዷ㐿ߒߚ⪲ᨎᢙ߽Cd Ớᐲߩ਄᣹ߣߣ߽ߦૐਅ ߒߚ㧔⴫㧝㧕ޕ߹ߚޔኈེ޽ߚࠅߩోੇ῎㊀㊂߽ޔ 148 ppmએ਄ߩᳪᨴỚᐲߢߪޔCdࠍ฽߹ߥ޿ኻᾖ

࿯ფߩ 10㧑ᧂḩߣߥߞߚ㧔࿑ 1㧕ޕౝ⬿ߔࠆ⾗Ḯࠍ

↪޿ߡ↢㐳ߔࠆሶ⪲ߩዷ㐿߹ߢߪᳪᨴߦࠃࠆᓇ㗀߇

⹺߼ࠄࠇߕޔߘߩᓟߩ↢㐳ߢᏅ߇↢ߓߡ޿ࠆߎߣߪޔ Cd ߇ࠤ࠽ࡈߩశวᚑ࡮৻ᰴ↢↥ࠍ૗ࠄ߆ߩᒻߢ㒖 ኂߒߡ޿ࠆߎߣࠍ␜ߒߡ޿ࠆޕ

ฦᳪᨴ࿯ფߢᩱၭߒߚࠤ࠽ࡈߩੇ῎㊀㊂߆ࠄ࿾਄

ㇱߣ࿾ਅㇱᲧࠍ᳞߼ࠆߣޔCdỚᐲ߇0㨪14.8 ppm ߩᬀ‛૕ߢߪޔ6.0r0.33 ߢ߶߷৻ቯߢ޽ߞߚߩߦ ኻߒޔ148 ppmࠍ⿥߃ࠆߣᓢޘߦૐਅߒޔ444 ppm ߩᬀ‛૕ߢߪ1.9߹ߢૐਅߒߚ㧔⴫1㧕ޕCd ߪᩮߦ

⫾Ⓧߒ߿ߔ޿㊀㊄ዻߢ޽ࠆߎߣ߇⍮ࠄࠇߡ޿ࠆ 5)ޕ Cd ߦࠃࠅ࿾਄ㇱߦᲧߴ࿾ਅㇱߩഀว߇Ⴧടߒߚߎ ߣߪޔCd ߩᓇ㗀ࠍᒝߊฃߌޔ᭽ޘߥᵴᕈߩૐਅߔ ࠆ࿾ਅㇱߩ↢‛㊂ࠍჇ߿ߒޔᓇ㗀ߩᲧセ⊛ዊߐ޿࿾

਄ㇱߩᵴᕈߣࡃ࡜ࡦࠬࠍߣࠆ㗅ൻ߇ⴕࠊࠇߚน⢻ᕈ ࠍ␜ໂߒߡ޿ࠆޕ৻ᣇޔ⪲ߣ⨍ߩᲧߪޔCdỚᐲߦ

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Ỉ਄㧘Ⓑ૑ ઁ: 㜞ᯏ⢻ⅣႺୃᓳᬀ‛ߦࠃࠆ࿯ფ߆ࠄߩࠞ࠼ࡒ࠙ࡓߩ㒰ᨴ 41

㑐ࠊࠄߕ৻ቯ㧔1.2r0.06㧕ߢ޽ߞߚ㧔⴫ 1㧕ޕᬀ‛

ߢߒ߫ߒ߫⹺߼ࠄࠇࠆᳪᨴ‛⾰ឃ಴ߦޔ⪲ߦ㓸Ⓧߒ ߚᳪᨴ‛⾰ࠍ⪲ߣߣ߽ߦᨗᱫ࡮⣕⪭ߐߖࠆᣇᴺ߇޽ࠆ

5)ޕࠤ࠽ࡈߩ⪲ߣ⨍ߩᲧ߇Cdߦࠃࠅᄌൻߒߥ޿ߎߣ ߪޔ⪲ߩ⣕⪭ߦࠃࠆCd ߩឃ಴߇ࠤ࠽ࡈߢߪ㗼⪺ߢ ߥ޿ߎߣࠍ␜ߒߡ޿ࠆޕ

275 ml ߩࡐ࠶࠻ࠍ↪޿ߡฦ㧝୘૕ߩࠤ࠽ࡈࠍᩱ

ၭߒߚޕߘࠇߙࠇߩࠤ࠽ࡈߩ࿾਄㜞ߣ࿾⴫ߩ⨍⋥ᓘ ࠍ᷹ቯߒޔ౞㍙ߦㄭૃߒߡ᳞߼ߚ⨍૕Ⓧࠍ᳞߼ޔ㕖

⎕უ⊛ߦޔ⛮⛯ߒߡฦ୘૕ߩ↢‛㊂ࠍផቯߒߚޕߎ ߩ⚿ᨐࠍ߽ߣߦ↢㐳⸃ᨆࠍⴕߥߞߚޕCd ࠍ฽߹ߥ

޿ኻᾖ࿯ფߢߪޔᧄ⪲ߩዷ㐿߇ᆎ߹ࠆ᠞⒳2ㅳ㑆ᓟ ࠃࠅޔࠤ࠽ࡈߩ⨍૕Ⓧ߇ኻᢙ㑐ᢙ⊛ߦჇടߒߚ㧔࿑

2㧕ޕߎࠇߦኻߒߡޔCd ࠍ฽߻࿯ფߢߪޔᧄ⪲ߩዷ 㐿߇ㆃᑧߒޔዷ㐿ᓟ߽⨍૕ⓍߩჇടߪ4ㅳ㑆⋡߹ߢ

⹺߼ࠄࠇߥ߆ߞߚޕߘߩᓟޔ148 ppm Cd࿯ფߢߪ

૕Ⓧߩૐਅ߇ᆎ߹ࠅޔᦨ⚳⊛ߦᨗᱫߒߚޕߘࠇࠃࠅ CdỚᐲߩૐ޿111 ppmߢ߽ޔታ㛎ᦼ㑆ਛߩ૕Ⓧߩ Ⴧടߪ⹺߼ࠄࠇߥ߆ߞߚޕߒ߆ߒޔߐࠄߦCd Ớᐲ ߩૐ޿74.1 ppm Cd࿯ფߢߪޔ4ㅳ㑆⋡߆ࠄ↢㐳ࠍ

ౣ㐿ߒޔ6ㅳ㑆⋡ߦߪ4ㅳ㑆⋡ߩ૕Ⓧߩ2.4୚ߣߥߞ ߚޕߎࠇࠄߩ⚿ᨐߪޔࠤ࠽ࡈߩCd ⠴ᕈߩ㒢⇇߇ޔ 74.1㨪148 ppm ߩ㑆ߩᭂ߼ߡ㜞޿CdỚᐲߦ޽ࠆߎ ߣࠍ␜ߒߡ޿ࠆޕ߹ߚޔ74.1 ppm Cd࿯ფߢ⹺߼ࠄ ࠇߚ↢㐳ߩ৻ᤨ⊛ߥ஗ᱛߪޔ㜞Ớᐲ㋦ᳪᨴ࿯ფߢߩ ࠤ࠽ࡈߩ↢㐳ߦ߽⹺߼ࠄࠇߚ⃻⽎ߢ޽ࠆ 6)ޕ㜞Ớᐲ ߩ㊀㊄ዻߦᳪᨴߐࠇߚ࿯ფߢᩱၭߐࠇߚࠤ࠽ࡈߦ⹺

߼ࠄࠇࠆޔߎߩࠃ߁ߥ↢㐳ߩ৻ᤨ⊛ߥ஗ᱛߣౣ㐿ᓟ ߩ↢㐳߆ࠄߪޔࠤ࠽ࡈ߇㊀㊄ዻᳪᨴ࿯ფߢ↢㐳ߔࠆ ߚ߼ߩ⠴ᕈࠍ₪ᓧߔࠆߚ߼ߦޔ৻ቯߩᤨ㑆ࠍᔅⷐߣ ߔࠆߎߣ߇ࠊ߆ࠆޕߎߩ㑆ޔ⠴ᕈߩ₪ᓧߦ㑐ਈߔࠆ ㆮવሶߩ⊒⃻ߥߤޔ૗ࠄ߆ߩ㗅ൻᔕ╵ࠍⴕߥߞߡ޿

ࠆߎߣ߇ᒝߊ␜ໂߐࠇߚޕ

᭽ޘߥCdỚᐲߩᳪᨴ࿯ფߢᩱၭߒߚࠤ࠽ࡈߩ࿾

਄ㇱੇ῎㊀㊂޽ߚࠅߩCd Ớᐲߪޔ࿯ფߩCd Ớᐲ ߣߣ߽ߦ਄᣹ߒޔ222 ppm Cdᳪᨴ࿯ფߩᬀ‛૕ߢ

ߪ440 ppmߦ㆐ߒߚޕߒ߆ߒޔᩱၭታ㛎ߢᦨ⚳⊛ߦ

ᨗᱫߒߚ 444 ppm Cd ᳪᨴ࿯ფߩᬀ‛૕ߢߪ 290 ppmߩCdߒ߆ᬌ಴ߐࠇߥ߆ߞߚ㧔࿑3㧕ޕ444 ppm ᳪᨴ࿯ფߩᬀ‛૕એᄖߢߪޔ࿯ფਛߩCd Ớᐲࠃࠅ

߽ᬀ‛૕ਛߩ CdỚᐲߩᣇ߇㜞޿୯ࠍ␜ߒޔࠤ࠽ࡈ ߦࠃࠅ Cd߇Ớ❗ߐࠇߚࠆߎߣ߇␜ߐࠇߚޕᬀ‛૕

ߩ CdỚᐲߣ࿯ფਛߩCd Ớᐲ߆ࠄỚ❗₸ࠍ᳞߼ࠆ ߣޔᬀ‛૕ਛߦᦨ߽㜞Ớᐲߩ Cd߇⹺߼ࠄࠇߚ 222

ppm Cdᳪᨴ࿯ფߢᩱၭߐࠇߚᬀ‛૕ߢ2୚ߣߥߞ

ߚޕ148 ppm Cdᳪᨴ࿯ფߢᩱၭߐࠇߚᬀ‛૕ߢ߽

Ớ❗₸ߪ2୚ߣߥߞߚ߇ޔ14.8 ppm Cdᳪᨴ࿯ფߢ

ᩱၭߐࠇߚᬀ‛૕ߢ 3 ୚ࠍ⿥߃ࠆỚ❗₸ࠍ␜ߒޔ 1.48 ppm Cdᳪᨴ࿯ფߢᩱၭߐࠇߚᬀ‛૕ߢߪޔ6

୚ࠍ⿥߃ࠆ㜞޿Ớ❗₸ࠍ␜ߒߚ㧔࿑3㧕ޕߎࠇࠄߩ⚿

ᨐߪޔ࿯ფਛߩCd Ớᐲ߇ૐ޿࿯ფߢᩱၭߒߚᬀ‛

૕ਛߢߪ CdỚᐲߪૐ޿߇ޔ࿯ფ߆ࠄߩỚ❗₸ߪ㜞 ߊߥࠆߎߣࠍ␜ߒߡ޿ߚޕᧄታ㛎ߢߪᩱၭᓟޔ⚂1ࡩ

᦬ߢಿࠅขࠅࠍⴕߞߚߚ߼ޔᬀ‛૕ߩ↢‛㊂ߪ㕖Ᏹ ߦዊߐߊޔታ㓙ߦ࿯ფ߆ࠄ㒰෰ߐࠇߚ Cd ㊂ߪዋߥ ߆ߞߚޕߒ߆ߒߥ߇ࠄޔ᧲੩ㄭ㇠ߦ߅޿ߡᄐቄߦ࿛

႐ߢࠤ࠽ࡈࠍᩱၭߔࠆ႐วߦߪޔࠤ࠽ࡈ߇㜞޿৻ᰴ

↢↥ࠍ␜ߒޔඨᐕ㑆ߢޔ⚂2 kg࡮m-2㆐ߔࠆߎߣ߇

⍮ࠄࠇߡ޿ࠆ 7)ޕߎߩࠃ߁ߥࠤ࠽ࡈߩ㜞޿৻ᰴ↢↥

㊂ࠍ⠨ᘦߔࠆߣޔᧄ⎇ⓥߢ␜ߐࠇߚࠤ࠽ࡈߦࠃࠆ࿯

ფਛߩCdߩỚ❗⢻ജߦࠃࠅޔ1.48 ppmߩCdᳪᨴ

࿯ფߢ18.8 mg㨯m-2ޔ14.8 ppmߩCdᳪᨴ࿯ფߢ98 mg㨯m-2ߩCd߇1࿁ߩᩱၭߢ࿁෼ߢ߈ࠆߎߣ߇ផቯ ߢ߈ࠆޕ1.48 ppmߩCdᳪᨴ࿯ფߩᲧ㊀ࠍ0.7ߣߔ ࠆߣޔ࿾⴫߆ࠄ30 cmߩ࿯ფߦߪ⚂310 mgߩCd ࠍ฽߻ޕߎߩ⚿ᨐߪޔࠤ࠽ࡈࠍ↪޿ߡ࿯ფ߆ࠄ Cd 㒰෰ߔࠆߚ߼ߦޔ16ᐕએ਄ߩᤨ㑆ࠍᔅⷐߣߔࠆߎߣ

߽␜ߒߡ޿ߚޕ

⴫1. ᭽ޘߥỚᐲߩCdࠍ฽߻࿯ფߢ31ᣣ㑆ᩱၭߒߚࠤ

࠽ࡈߩ⊒⧘₸ޔ⪲ᢙޔోੇ῎㊀㊂ߣੇ῎㊀㊂ߩᲧ CdỚᐲ㧔ppm㧕 0 1.48 14.8 148 222 444

⊒⧘₸(%) 90.0 93.3 80.0 80.0 80.0 80.0

⪲ᨎᢙ 9.89 9.13 5.96 4.29 2.54 㧙

ోੇ῎㊀㊂(g) 31.1 28.4 24.4 2.51 1.27 0.93

࿾਄ㇱ/࿾ਅㇱ 6.03 5.69 6.36 4.46 2.53 1.91

/ 1.25 1.16 1.15 1.25 1.23 1.13

㪇 㪈㪅㪋㪏 㪈㪋㪅㪏 㪈㪋㪏 㪉㪉㪉 㪋㪋㪋 㪌

㪇 㪌 㪈㪇 㪈㪌 㪉㪇 㪉㪌 㪊㪇

࿯ფ㪚㪻Ớᐲ䇭㩿㫇㫇㫄㪀

ੇ῎㊀㊂䇭㩿㪾㪀

࿾਄ㇱ

࿾ਅㇱ

࿑1. ᭽ޘߥỚᐲߩCdࠍ฽߻ᳪᨴ࿯ფߢᩱၭߒߚࠤ

࠽ࡈฦེቭߩੇ῎㊀㊂. ᠞⒳ᓟ31 ᣣ⋡ߩᬀ‛૕ࠍታ 㛎඙ಽᲤߦోߡ㓸߼, ಽⵚེቭ(᷆Ἧ),శวᚑེቭ (⊕), ᡰᜬེቭ(࿾਄ㇱ:ỚἯ, ࿾ਅㇱ:㤥)ߦಽߌ, ⚕ⴼ ਛ, 60͠ߢ2ㅳ㑆ੇ῎ߐߖ᷹ቯߒߚ.

(4)

42 Science Journal of Kanagawa University Vol. 17, 2006

ᬀ‛ࠍ㜞Ớᐲ㧔30 ppm㧕ߩCdᳪᨴ࿯ფߢᩱၭߒ ߚ႐วޔỚ❗₸ߪ100㧑೨ᓟ߆ߘࠇએਅߣߥࠆߎߣ ߆ࠄޔߎࠇ߹ߢߩ⎇ⓥߢߪޔࡈࠔࠗ࠻࡟ࡔ࠺ࠖࠛ࡯

࡚ࠪࡦࠍCdߩ㒰ᨴߦ↪޿ࠆߎߣߪ㔍ߒ޿ߣ⠨߃ࠄ ࠇߡ޿ߚ8)ޕߒ߆ߒޔᧄ⎇ⓥߢߪޔࠤ࠽ࡈ߇ᭂ߼ߡ 㜞޿ᳪᨴ⁁ᘒߦ޽ࠆ 74.1㨪148 ppm ߩ㑆ߦ↢㐳ߩ

⠴ᕈ㒢⇇ࠍᜬߜޔ222 ppmߩCdᳪᨴ࿯ფߢ߽Cd ࠍỚ❗ߢ߈ࠆߎߣ߿ޔ14.8 ppmߩCdᳪᨴ࿯ფߢߪޔ 㜞޿৻ᰴ↢↥ߔࠄ⛽ᜬߢ߈ࠆߎߣߥߤޔCd 㒰ᨴߦ ߣߞߡߎࠇ߹ߢߦ⺞ߴࠄࠇߚᬀ‛ߦߥ޿ᅢㆡߥ․ᕈ ࠍᜬߟߎߣ߇␜ߐࠇߚޕߒ߆ߒޔᧄ⎇ⓥߩ⚿ᨐ߆ࠄ ߪޔ㜞޿Ớ❗₸ࠍ␜ߒޔ৻ᰴ↢↥߇⛽ᜬߐࠇࠆ1.48 ppmޔ14.8 ppmߩCdᳪᨴ࿯ფߢ߽ޔࠤ࠽ࡈߦࠃࠆ Cdߩ㒰ᨴߦߪ16ᐕએ਄ߩᤨ㑆߇⷗Ⓧ߽ࠄࠇߚޕ࿯

ფ߆ࠄߩᳪᨴ‛⾰ߩ࿁෼ߪޔ࿁෼ߔࠆᬀ‛૕ߩ↢‛

㊂ߣߣ߽ߦޔ↢‛૕߳ߩᳪᨴ‛⾰ߩỚ❗߇߈ࠊ߼ߡ

㊀ⷐߢ޽ࠆޕࠤ࠽ࡈએ਄ߩ৻ᰴ↢↥ࠍⴕ޿ޔᬀ‛૕

ߩ↢‛㊂߇ᄢ߈ߊߥࠆᬀ‛߇ዋߥ޿ޕߎߩߚ߼ޔࡈࠔ

ࠗ࠻࡟ࡔ࠺ࠖࠛ࡯࡚ࠪࡦࠍࠃࠅല₸⊛ߦⴕ߁ߦߪޔ

ᬀ‛૕ߦ㜞޿Ớ❗₸ߢCd ࠍ࿁෼ߔࠆߎߣ߇ਇนᰳ

ߢ޽ࠆߣ⠨߃ࠄࠇࠆޕૐỚᐲ߶ߤ㜞޿Ớ❗₸ߢ Cd ࠍ࿁෼ߔࠆߎߣࠍ␜ߒߚᧄ⎇ⓥߩ⚿ᨐ㧔࿑ 3㧕ߪޔ

1.48 ppm એਅߩૐ޿Ớᐲߢᳪᨴߐࠇߚ࿯ფߢޔࠤ

࠽ࡈ߇㜞Ớ❗₸ߢCdࠍ࿁෼ߔࠆน⢻ᕈࠍ␜ໂߒߡ

޿ࠆޕ

ૐỚᐲᳪᨴ࿯ფߢߩࠤ࠽ࡈߩCdỚ❗₸ޔߐࠄߦޔ ᧄታ㛎ߢⴕߥࠊࠇߥ߆ߞߚࠤ࠽ࡈ࿾ਅㇱߩ Cd Ớ

❗࡮࿁෼․ᕈޔઁຠ⒳ߩ․ᕈߩᬌ⸽ߥߤޔ੹ᓟ᣿ࠄ ߆ߦߔߴ߈ὐߪᄙ޿ޕߒ߆ߒޔᧄ⎇ⓥߪޔࠤ࠽ࡈࠍ

↪޿ߚࡈࠔࠗ࠻࡟ࡔ࠺ࠖࠛ࡯࡚ࠪࡦ߇ޔૐỚᐲᳪᨴ

࿯ფ߆ࠄߩቢోߥCd㒰෰ߦ᦭ലߢ޽ࠆߎߣࠍቯ㊂

⊛ߦ޽߈ࠄ߆ߦߔࠆ߽ߩߢ޽ࠆޕ

⻢ㄉ

ᧄ⎇ⓥߪޔ2005ᐕᐲ ␹ᄹᎹᄢቇ౒ห⎇ⓥᅑബ㊄ߦ ࠃࠆᡰេࠍฃߌߡታᣉߐࠇߚޕ

ᧄ⎇ⓥࠍㅴ߼ࠆߦ޽ߚࠅޔᄙᄢߥࠆߏදജࠍ⾦ߞߚ

ࠬࡒࠦࡦ࠮࡞࠹࠶ࠢᩣᑼળ␠ߩੑ⷗㆐਽᳁ޔ㊍㊁ᓼ

᣿␹ᄹᎹᄢቇฬ⹷ᢎ᝼ߦᷓߊᗵ⻢↳ߒ਄ߍࠆޕ

ᢥ₂

1) ࿯ფⅣႺ࠮ࡦ࠲࡯✬ (2000) ᚒ߇࿖ߦ߅ߌࠆ࿯ფᳪ ᨴኻ╷⾌↪ߩផቯ̆࿯ფᳪᨴኻ╷⾌↪ߩផቯ̆̆࿯

ფᳪᨴᵺൻ⾌↪ߩផቯ̆. (␠) ࿯ფⅣႺ࠮ࡦ࠲࡯. 2) ᄢ᫪ବ㓶 (2000) ㊀㊄ዻᳪᨴߩᓸ↢‛㒰෰, ╙8 ┨.

ⅣႺᓸ↢‛ቇ ⅣႺࡃࠗࠝ࠹ࠢࡁࡠࠫ࡯. (ᩣ)ᤘᤩၴ. pp. 106-116.

3) Scheper T (2003) Phytoremediation of heavy met- als from soils. In: Phytoremediation, Advance S in Biochemical Engineering Biotechnology. Springer- Verlag, Berlin. pp. 98-123.

4) Kurihara H, Watanabe M and Hayakawa T. (2005) Phytoremediation with Kenaf (Hibiscus cannabinus) for Cadmium-Contaminated Paddy Field in Southwest Area of Japan. Jpn. J. Soil. Sci. Plant Nutr. 76: 27-34.

5) Fitter AH and Hay RKM (1987) Ionic toxicity. In:

Environmental Physiology of Plants, 2nd ed.

Academic Press Inc, San Diego. pp.225-259 6) Sawakami K, Ohishi F, Kurosawa S and Suzuki Y

(2005) Acclimations of Kenaf (Hibiscus cannabinus L.) to Pb in a Polluted Soil. Sci. J. Kanagawa Univ.

16: 63-66.

7) ㋈ ᧁ ␽ ᒄ, ㊍ ㊁ ᓼ ᣿, ㋈ ᧁ ␭ ਽ (2001) ࠤ ࠽ ࡈ (Hibiscus cannabinus L.) 12ຠ⒳ߩ৻ᰴ↢↥ㅦᐲߩ ቄ▵ᄌൻߣᐕ㑆৻ᰴ↢↥ߩ㆑޿. ␹ᄹᎹᄢቇℂቇㇱ

✚วℂቇ⎇ⓥᚲᐕႎ2000.12: 67-89.

8) ⥪Ꮉᵗ (1975) ᬀ‛ࠍ೑↪ߒߚ࿯ფਛߩࠞ࠼ࡒ࠙ࡓ

ߩ㒰ᨴᣇᴺ. ㄘᬺ࿯ᧁቇળ⹹.43: 674-681.

࿑ 2. ⨍૕Ⓧ߆ࠄ᳞߼ߚࠤ࠽ࡈߩ↢㐳ߦኻߔࠆ࿯ფ Cdߩᓇ㗀. CdỚᐲ0 ppm (٨), 74.1 ppm (ع), 111 ppm (ً) 148 ppm (ٕ) ߩ࿯ფߢࠤ࠽ࡈࠍᩱၭߒ, 2ㅳ 㑆Ფߦ࿾਄㜞ߣၮㇱ⨍⋥ᓘࠍ᷹ቯߒ, ౞㍙ߦㄭૃߒߡ

⨍૕Ⓧࠍ᳞߼ߚ.

㪇 㪈 㪉 㪊 㪋 㪌 㪍 㪎

㪇 㪇㪅㪈 㪇㪅㪉 㪇㪅㪊 㪇㪅㪋 㪇㪅㪌 㪇㪅㪍

ᩱၭᤨ㑆㩷㩿ㅳ㑆㪀

⨍૕Ⓧ㩷㩿㪺

㪇㩷㫇㫇㫄

㪎㪋㪅㪈㩷㫇㫇㫄

㪈㪈㪈㩷㫇㫇㫄 㪈㪋㪏㩷㫇㫇㫄

࿑3. ᭽ޘߥỚᐲߩCdᳪᨴ࿯ფߢᩱၭߒߚࠤ࠽ࡈਛ ߩCd ỚᐲߣỚ❗₸. Ἧ᫔ߪᬀ‛૕ਛߩ Cd Ớᐲࠍ, 㤥ਣߪỚ❗₸ࠍ␜ߔ.

㪇 㪈㪅㪋㪏 㪈㪋㪅㪏 㪈㪋㪏 㪉㪉㪉 㪋㪋㪋 㪇

㪈㪇㪇 㪉㪇㪇 㪊㪇㪇 㪋㪇㪇 㪌㪇㪇

࿯ფ㪚㪻Ớᐲ㩷㩿㫇㫇㫄㪀

‛૕ਛ㪚㪻㩷㩿㫇㫇㫄

㪇 㪈㪇㪇 㪉㪇㪇 㪊㪇㪇 㪋㪇㪇 㪌㪇㪇 㪍㪇㪇 㪎㪇㪇

Ớ❗₸㩷㩿䋦

参照

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Standard domino tableaux have already been considered by many authors [33], [6], [34], [8], [1], but, to the best of our knowledge, the expression of the