, ; 50d, 134 Cs 3, 70d, 134 Cs ; 70d, 134 Cs 1, 115 114 113, 2 3 ; (70d),,3 ;,



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2009,23 (1) :123 127 Journal of Nuclear Agricultural Sciences 123 :100028551 (2009) 0120123205 1,2 2,3 1 4 2 (11, 310024 ;21, 310029 ; 31, 272100 ; 41, 300191) :, Cs 3,,;50d, Cs 3, 70d, Cs ;70d, Cs 1, 115 114 113, 2 3 ; (70d),,3 ;, :; ; ; Cs ; UPTAKE OF RADIOCESIUM BY THREE PLANTS GROWN IN Cs CONTAMINATED SOIL UNDER POT EXPERIMENT CONDITION ZHENGJie2min 1,2 LI Hong2yan 1,3 NIU Tian2xin 1 TANG Shi2rong 1,4 CHEN Zi2yuan 1 (11 Hang Zhou Academy of Agricultural Sciences, Zhejiang, Hangzhou 310024 ; 21 Institute of Nuclear Agricultural Sciences, Zhejiang University, Zhejiang, Hangzhou 310029 ; 31Jining Environmental Protection Agency, Shandong, Jining 272100 ; 41 Centre for Research in Ecotoxicology and Environmental Remediation, Institute of Agro2environmental Protection, Ministry of Agriculture of China, Tianjin 300191) Abstract :Pot experiment was conducted to investigate the accumulation dynamics of Cs in shoots of Rumex acetosa, Rumex hastatus and Helianthus annuus grown in Cs contaminated soil under greenhouse condition. Results showed that shoot biomass of H. annuus was significantly higher than that of R. acetosa and R. hastatus ; among 3 plant species, Cs specific activity in shoots was the highest in H. annuus after treatment for 50 days, however after treatment for 70 days, that in R. acetosa was the highest. Bioaccumulation ratio reached 115, 114 and 113 in R. acetosa, R. hastatus and H. annuus at the end of experiment, respectively, and the former two plants kept with trend of continuously increasing during the experiment period. Three plants were tolerant to Cs contaminated soil and capable to translocate Cs from soil to plants. Among them, H. annuus removed greatest Cs amount in the above ground part, and R. acetosa, R. hastatus showed higher tranclocation factor of Cs than H. annuus. Three plants are promising for phytoremediation of soil contaminated with radiocesium, and also could be used for phytoremediation of radiocesium and heavy metals complex contamination, potentially. :2008206209 :2008209213 :( G1999011800) : (19772),,,, Tel :0571287581397 ; E2mail :jmzh04 @1631com : (19632),,,,,E2mail :tangshir @hotmail. com

124 23 Key words : Rumex acetosa ; Rumex hastatus ; Helianthus annuus Cs ; phytoremediation,, 137 Cs, 30117,,,,, -,,, [1 ],, [2 8 ] Broadley [5 ], ( Rumex acetosa) ( Rumex hastatus),,, [9,10 ] ; ( Helianthus annuus),,cd Cu [11,12 ] Cs ( 21062 ) 137 Cs,,, 3 1 111 Cs,, 3mm, ( 1), [13 ] 18cm,15cm, 110 kg() Ca (NO 3 ) 2 H 2 O CaHPO 4 KH 2 PO 4 H 3 BO 3 kg ( ) 100mg 400mg 126mg 1mg [14 ],,2, kg Cs 1141 10 5 Bq,,, 8 1 Table 1 Physical and chemical properties of the soil used in experiment main physical and chemical properties value clay ( %) 917 silt ( %) 7417 sand ( %) 1516 N total N( %) 0106 P total P ( %) 0124 P available P (mgπkg) 58110 K available K (mgπkg) 22174 ph (H 2 O) 7114 0101molΠL CaCl 2 (0101 molπl CaCl 2 ) 6189 CEC (cmolπ100g ) 7127 C organic matter C ( %) 1150 112 1 %NaClO 10min, 3, ( = 1 1) 1 2,,,, 3, 15 30 40 50 60 70d,3, 113,,,110 30 min,80,110 g (g10mm), Cs 114 Cs Cs, BH21224 - () g700mm NaI,, 625V,0118,: Cs,, (310 410 ) ; Cs (,2000 5 ), 5 % ;

1 125 10min (4 ) + 010471 ( r = 019408, P < 0101) 40d, 2 211 3 Cs 3 1 1,, Cs 3, 3, ( P < 0101),,, Cs,40d,70d, Cs 3, Cs (BqΠg) t ( ) : y = 218964 t - 321222( r = 019365, P < 0101) Cs 50d,,50d, Cs (BqΠ g) t ( ) : y = 212971 t - 161455( r = 01916, P < 0101) 2 Cs Fig. 2 Changes of Cs specific activity in aboveground 1 Fig. 1 Changes of aboveground biomass 212 3 Cs 3 Cs 2, Cs, 70d, Cs 14615 17110 15411 BqΠg, Cs 2 2,,3 Cs 50d, 2, 50d, Cs Cs, Cs (BqΠg) t ( ) : y = 21225 t 213 3 Cs Cs ( Cs ),Cs 3,,3 Cs,70d, Cs 58817 34716 29316 BqΠpot, Cs 2 ( P < 0101), Cs ( P < 0105) Cs 2, 214 3 Cs (BCF = Cs Π Cs ) 3 Cs 4,3 Cs,, 70d, 113 115 114

126 23 3 Cs Fig. 3 Changes of Cs removal amount by aboveground,, 3 4 Cs Fig. 4 Changes of Cs BCF of H. annuus, R. acetosa and R. hastatus,,3, Cs, Cs 2 Cs, Cs 70 d, 17110 15411 BqΠg,(14615 BqΠg),, Cs Cs [15,16 ], Cs [17 ], 185kBq Cs, Cs, 76196 BqΠg ; [18 ],, Cs, Cs, 128124 BqΠg Cs Lasat [7 ] 137 Cs, 137 Cs 0 110 ; Cs 0105 [19 ] Dushenkov [20 ] 013 2103 ; Tang [15 ], Cs 2120 3122, Cs 2141 2179, 3 Cs,1,,, Cs, [21 ] Lasat [7 ] 137 Cs, 137 Cs 110 310 ; Strandberg [22 ], Cs 259 BqΠg2 Cs, Cs,, Cs, 3,, : [ 1 ]. - [J ]., 2002, 13 (2) : 243 246 [ 2 ] Tang S R, Zheng J M, Chen Z Y, Fang Y H. Uptake and accumulation of Cs by six plant varieties from the Amaranthaceae grown in nutrient

Journal of Nuclear Agricultural Sciences 2009,23 (1) :123 127 solution[j ]., 2004, 18 (6) : 474 479 [ 3 ] Negri M C, Hinchman R R. The use of plants for the treatment of radionuclides. In Raskin I and Ensley B ( eds. ) Phytoremediation of toxic metals using plants to clean up the environment [ M]. New York : John Willey & Sons Inc, 2000 : 107 132 [ 4 ] Entry J A, Watrud L S. Potential remediation of 137 Cs and 90 Sr contaminated soil by accumulation in Alamo switchgrass[j ]. Water, Air and Soil Pollution, 1998, 104 (3 4) : 339 352 [ 5 ] Broadley M R, Willey N J. Differences in root uptake of radiocaesium by 30 plant taxa[j ]. Environmental Pollution, 1997, 97 : 11 15 [ 6 ] Willey N J, Martin M H. A comparison of stable cesium uptake by six grass species of contrasting growth strategy[j ]. Environmental Pollution, 1997, 95 (3) : 311 317 [ 7 ] Lasat M M, Wendell A N, Kochian L V. Potential for phytoectration of 137 Cs from a contaminated soil[j ]. 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