Ge,2004Overexpression of OsRAA1

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2004年发表的文章

2004年发表的文章

2004年发表的文章2004年发表的文章一、国外刊物上发表的文章1.Carbon monoxide oxidation over Cu/CeO2 catalystsXiaolan Tang, Baocai Zhang, Y ong Li, Y ide Xu, Qin Xin, Wenjie ShenCatalysis Today, 93(2004)191-1982.Methane dehydroaromatization over Mo/HZSM-5 catalysts in theabsence of oxygen: effects of silanation in HZSM-5 zeolite Hongmei Liu, Y ong Li, Wenjie Shen, Xinhe Bao, Yide XuCatalysis Today, 93(2004)65-733.Pd/CeO2–TiO2 catalyst for CO oxidation at low temperature: A TPRstudy with H2 and CO as reducing agentsHuaqing Zhu, Zhangfeng Qin, Wenjuan Shan, Wenjie Shen and Jianguo Wang Journal of Catalysis, 225(2004)267-2774.Oxidative steam reforming of methanol on Ce0.9Cu0.1O Y catalystsprepared by deposition-precipitation,co-precipitation andcomplexation-combustion methodsWenjuan Shan, Zhaochi Feng, Zhonglai Li, Jing Zhang, Wenjie Shen, Can Li Journal of Catalysis, 228(2004)206-2175.In-situ magnetic resonance investigation on the mechanism of styreneoxidation over TS-1 zeolitesJianqin Zhuang, Gang Y ang, Ding Ma, Xijie Lan, Xiumei Liu, Xiuwen Han, Xinhe Bao, Ulrich MuellerAngew. Chem.-Int. Edit., 116(2004)6377-63816.In situ assembly of zeolitic building blocks into high-order structuresGang Hu, Ding Ma, Lin Liu, Mojie Cheng, Xinhe BaoAngew. Chem.-Int. Edit., 43(2004)3452-34567.A mechanism for enhanced photocatalytic activity of silver-loadedtitanium dioxideS.X. Liu, Zhenping Qu, Xiuwen Han, C.L. SunCatal. Today, 93-95(2004)877-8848.Asymmetric hydrogenation of quinolines catalyzed by iridium with chiralferrocenyloxazoline derived N,P ligandsShengmei Lu, Xiuwen Han, Y onggui ZhouAdvanced synthesis & catalysis, 346(2004)909-9129.Kinetic study on the photo-catalytic degradation of pyridine in TiO2 suspensionsystemsHong Zhao, Suohong Xu, Junbo Zhong, Xinhe BaoCatal. Today, 93-95(2004)857-86110.CO selective oxidation in H2-rich gas over Ag nanoparticles-effect of oxygentreatment temperature on the activity of silver particles mechanicallymixed with SiO2Zhenping Qu, Mojie Cheng, Xinglong Dong and Xinhe Bao Catal. Today, 93-95(2004)247-25511.Solid state MAS NMR studies on the hydrothermal stability of the zeolitecatalysts for residual oil selective catalytic crackingJianqin Zhuang, Ding Ma, Gang Y ang, Zhinmin Y an, XiumeiLiu,Xianchun Liu, Xiuwen Han, Xinhe Bao, Peng Xie, Zhongmin LiuJ. Catal., 228(2004)234-24212.Effect of Ag+ cations on nonoxidative activation of methane toC2-hydrocarbonShaojun Miao, Y an Wang, Ding Ma, Qingjun Zhu, Shutian Zhou,Lingling Su, Dali Tan, and Xinhe BaoJ. Phys. Chem. B, 108(2004)17866-1787113.Density functional theory study of chemical composition on the acidityof H-MCM-22 zeoliteY an Wang , Gang yang , Danhong Zhou , Xianchun Liu , Xinhe BaoJ. Phys. Chem. B, 108(2004)18228-1823314.On the propagation rate of the chemical waves observed during thecourse of CO oxidation on a Ag/Pt(110) composite surface Weixin Huang, and Xinhe BaoJ. Phys. Chem. B, 108(2004)8390-839615.Unusual mesoporous SBA-15 with parallel channels runningalong the short axisHe Zhang, Junming Sun, Ding Ma, Xinhe Bao, Achim Klein-Hoffmann, Giesela Weinberg, Dangsheng Su and Robert Schlogl J. Am. Chem. Soc., 126(2004)7440-744116.Study on the external surface acidity of MCM-22 zeolite: Theoreticalcalculation and 31P MAS NMRY an Wang, Jianqin Zhuang, Gang Yang, Danhong Zhou, Ding Ma,Xiuwen Han, and Xinhe BaoJ. Phys. Chem. B, 108(2004)1386-139117.Solid-state MAS NMR detection of the oxidation center in TS-1 zeoliteby in-situ probe reactionJianqin Zhuang, Ding Ma, Xiumei Liu, Xiuwen Han, Xinhe Bao, Xuewu Liu, Xinwen Guo, Xiangsheng WangJ. Catal., 221(2004)670-67318.Investigation on the catalytic roles of silver species in the selectivecatalytic reduction of NOx with methaneChuan Shi, Mojie Cheng, Zhenping Qu, Xinhe BaoAppl. Catal. B-Environ., 51(2004)171-18119.Chiral synthesis on catalysts immobilized in microporousand mesoporous materialsCan LiCatal. Rev., 46(2004)419-49220.On the surface sites of MoP/SiO2 catalyst under sulfiding conditions:IR spectroscopy and catalytic reactivity studiesZili Wu, Fuxia Sun, Zhaochi Feng, Weicheng Wu, Changhai Liang, Can Li J. Catal., 222(2004)41-5221.Ultra-deep desulfurization of diesel: Oxidation with a recoverablecatalyst assembled in emulsionCan Li, Zongxuan Jiang, Jinbo Gao, Yongxing Yang, Shaojun Wang,Fuping Tian, Fuxia Sun, Xiuping Sun, Pinliang Ying, Chongren HanA European Journal - Chemistry, 10(2004)2277-228022.Direct synthesis of Al-SBA-15 mesoporous materials viahydrolysis-controlled approachYing Li, Wenhua Zhang, Lei Zhang, Qihua Y ang, Zhaobin Wei, Zhaochi Feng, Can LiJ. Phys. Chem. B, 108(2004) 9739-974423.Water reduction and oxidation on Pt-Ru/Y2Ta2O5N2 catalyst under visiblelight irradiationMeiying Liu, Wansheng Y ou, Zhibin Lei, Guohua Zhou, Jianjun Y ang,Guopeng Wu, Guijun Ma, Guoyou Luan, Tuyoshi Takata, Michikazu Hara, Kazunari Domen, Can LiChem. Commun., (2004)2192-219324.Enhancement of alpha-oxygen formation and N2O decomposition onFe/ZSM-5 catalysts by extraframework AlKeqiang Sun, Haidong Zhang, Haian Xia, Can LiChem. Commun., (2004)2480-248125.ZnO clusters encapsulated inside micropores of zeolites studied by UVRaman and laser-induced luminescence spectroscopiesJun Chen, Zhaochi Feng, Pinliang Ying, Can LiJ. Phys. Chem. B, 108(2004)12669-1267626.Dibenzothiophene hydrodesulfurization activity and surface sites ofsilica-supported MoP, Ni2P and Ni-Mo-P catalystsFuxia Sun, Weicheng Wu, Zili Wu, Jun Guo, Zhaobin Wei, Yongxing Y ang, Zongxuan Jiang, Fuping Tian, and Can Li J. Catal., 228(2004)298–31027.Synthesis of nanostructured ceria, zirconia and ceria-zirconia solidsolutions using an ultrahigh surface area carbon material as a templateChanghai Liang, Jieshan Qiu, Zhonglai Li, Can LiNanotechnology, 15(2004) 843-84728.Hydrothermal stability and catalytic activity of aluminum-containingmesoporous ethane-silicasQihua Y ang, Ying Li, Lei Zhang, Jie Y ang, Jian Liu, Can LiJ. Phys. Chem. B, 108 (2004)7934-793729.The reaction route and active site of catalytic decomposition of hydrazineover molybdenum nitride catalystXiaowei Chen, Tao Zhang, Zili Wu, Weicheng Wu, Can LiJ. Catal., 224(2004)473-47830.n-Heptane isomerization over mesoporous MoO x and Ni–MoO x catalystsXinping Wang, Can Li, Yingjun Wang and Tian-Xi CaiCatalysis Today, 93-95(2004)135-14031.Catalytic performance of MCM-22 zeolite for alkylation of toluenewith methanolZhirong Zhu, Qingling Chen, Wei Zhu, Dejin Kong and Can Li Catalysis Today, 93-95(2004)321-32532.Effect of (n)SiO2/(n)B2O3 in the precursor on chemical–physicsproperties of Ti-ZSM-5 synthesized by gas–solid methodMin Liu, Xinwen Guo, Xiangsheng Wang, Chang-hai Liang and Can LiCatalysis Today, 93-95(2004)659-66433.Novel cobalt-free oxygen permeable membraneXuefeng Zhu, Haihui Wang and Weishen YangChemical Communications, (2004) 1130-113134.Molecular sieving MFI-type zeolite membranes for pervaporationseparationof xylene isomersWenhui Y uan, Y. S. Lin and Weishen Y angJournal of the American chemical society35.Formation of a novel type of reverse microemulsion system and itsapplication in synthesis of the nanostructured La0.95Ba0.05MnAl11O19 catalyst Fei Teng, Jinguang Xu, Zhijian Tian, Junwei Wang, Yunpeng Xu,Zhusheng Xu, Guoxing Xiong, Liwu LinChemical Communications, (2004)1858-185936.Cataltic partial oxidation of gasoline to syngas in a dense membrane reactorWenliang Zhu, Guoxing Xiong, Wei Han, Weishen Y angCatalysis Today, 93-95(2004)257-26137.Preparation of CdS-SiO2 core-shell particles and hollow SiO2 sphereranging from nanometers to microns in the nonionic reverse microemulsions Fei Teng, Zhijian Tian, Guoxing Xiong, Zhusheng XuCatalysis Today, 93-95(2004)651-65738.Effects of reaction conditions on the selective oxidation of propane toacrylic acid on Mo-V-Te-Nb oxidesBaichun Zhu, Hongbo Li, Weishen Yang, Liwu LinCatalysis Today, 93-95(2004)229-23439.An improved palladium-based DMFCs cathode catalystHuanqiao Li, Qin Xin, Wenzhen Li, Zhenhua Zhou, Luhua Jiang,Shaohua Y ang, Gongquan SunChemical Communications, (2004)2776-277740.The effect of methanol and ethanol crossover on the performance ofPtRu based anode DAFCsShuqin Song, Weijiang Zhou, Zhenxing Liang, Rui Cai, Gongquan Sun,Qin Xin, V aios Stergiopoulos, Panagiotis TsiakarasApplied Catalysis B: Environmental, 55(2004)65-7241.Homogeneous and controllable Pt particles deposited on mutil-wall carbonnanotubes as cathode catalyst for direct methanol fuel cells Wenzhen Li, Changhai Liang, Weijiang Zhou, Jieshan Qiu,Huanqiao Li, Gongquan Sun, Qin XinCarbon, 42(2004) 436-43942.Preparation and characterization of PtSn/C anode electrocatalysts fordirect ethanol fuel cellLuhua Jiang, Gongquan Sun, Zhenhua Zhou, Weijiang Zhou, Qin XinCatalyst Today, 93-95(2004)665-67043.Preparation of highly active 40 wt.% Pt/C cathode electrocatalysts forDMFC via different routesZhenhua Zhou, Weijiang Zhou, Suli Wang, Guoxiong Wang, Luhua Jiang, Huanqiao Li, Gongquan Sun, Qin XinCatalysis Today, 93-95(2004) 523-52844.Oxidation of p-cresol to p-hydroxybenzaldehyde with molecular oxygenin the presence of CuMn/oxide heterogeneous catalystFeng Wang, Guang Y ang, Wei Zhang, Wenhai Wu, Jie XuAdvanced Synthesis & Catalysis, 346(2004)633-63845.Metathesis of ethylene and butylene-2 to popylene with Mo onHβ-Al2O3 catalystsShenglin Liu, Shengjun Huang, Wenjie Xin, Jie bai, Sujuan Xie, Longya Xu Catalysis Today, 93-95(2004)471-47646.The PPh3 ligand modified Rh/SiO2 catalyst for hydroformylation of olefinsH.J. Zhu, Y.J. Ding, L. Y an, J.M. Xiong, Y. Lu, L.W. LinCatalysis Today, 93-95(2004)389-39347.NO reduction by CH4 in the presence of excesss O2 over Mn/sulfatedzirconia catalystsNing Li, Aiqin Wang, Xiaodong Wang, Mingyuan Zheng,Ruihua Cheng, Tao ZhangApplied Catalysis B, 48(2004)259-26548.NO reduction by CH4 in the presence of excess O2 over Pd/sulfatedalumina catalystsNing Li, Aiqin Wang, Lin Li, Xiaodong Wang, Lili Ren, Tao ZhangApplied Catalysis B, 50(2004)1-749.Probing into the catalytic nature of Co/sulfated zirconiafor selectivereduction of NO with methaneNing Li, Aiqin Wang, Mingyuan Zheng, Xiaodong Wang,Ruihua Cheng, Tao ZhangJ. Catal., 225(2004)307-315/doc/cd15189216.html,bined single-pass conversion of methane via oxidative couplingand dehydro-aromatization: A combination of La2O3/BaO andMo/HZSM-5 catalyst systemY onggang Li, Hongmei Liu, Wenjie Shen,Yide Xu, Xinhe Bao Studies in surface science and catalysis, 147 (2004)583-58851.Methane dehydto-aromatization process on alkali-treated MCM-22supported Mo catalyst: the effect of pore structureLingling Su, Y onggang Li, Wenjie Shen, Yide Xu, Xinhe Bao Studies in surface science and catalysis, 147(2004)595-60052.Coking kinetics on the catalyst during alkylation of fcc off-gaswith benzene to ethylbenzeneLongya Xu, Jinxiang Liu, Qingxia Wang, Shenglin Liu, Wenjie Xin, Yide Xu Applied Catalysis A: General, 258(2004)47–5353.Structural features and catalytic properties of Pt/CeO2 catalystsprepared by modified reduction- deposition techniquesXiaolan Tang, Baocai Zhang, Y ong Li, Y ide Xu, Qin Xin, Wenjie ShenCatalysis Letters, 97/3-4(2004)163-16954.Kinetics of selective oxidation of dimethyl ether to formaldehyde overAl2O3 -supported VO x and MoO x catalystsXiumin Huang, Y onggang Li, Yide Xu, Wenjie ShenCatalysis letters, 97/3-4(2004)185-19055.Facile synthesis of ginsenoside RoWenjie Peng, Jiansong Sun, Feng Lin, Xiuwen Han, Biao Y u Synlett, (2004)(2)259-26256.A facile preparation of uronates via selective oxidation withTEMPO/KBr/Ca(OCl)(2) under aqueous conditionsFeng Lin, Wenjie Peng, Wen Xu, Xiuwen Han, Biao Y uCarbohydr. Res., 339(2004)1219-122357.Synthesis of a typical glucuronide-containing saponin, 28-O-beta-D-glucopyranosyl oleanate 3-O-beta-D-galactopyranosyl-(1 ->2)-[beta-D-glucopyranosyl-(1 -> 3)]-beta-D-glucuronopyranosideWenjie Peng, Xiuwen Han, Biao Y uSynthesis, (2004)(10)1641-164758.Thermodynamic studies of monuronLiguo Kong, Zhicheng Tan, Jianting Mei, Lixian Sun, Xinhe BaoThermochimica Acta, 414(2004)131-13559.Evidence for perimeter sites over SmOx-modified Rh(100) surface by COchemisorptionZhiquan Jiang, Weiping Zhou, Dali Tan, Runsheng Zhai, Xinhe BaoSurf. Sci., 565(2004)269-27860.Direct synthesis, characterization and catalytic activity of titanium-substitutedSBA-15 mesoporous molecular sievesY angying Chen, Y anlei Huang, Jinghai Xiu, Xiuwen Han, Xinhe BaoAppl. Catal. A-Gen., 273(2004)185-19161.A DFT study on isomorphously substituted MCM-22 zeoliteY an Wang, Danhong Zhou, Gang Y ang, Shaojun Miao,Xianchun Liu, Ding Ma, Xinhe BaoJ. Phys. Chem. A, 108(2004)6730-673462.On the reactivity of Mo species for methane partial oxidation onMo/HMCM-22 catalystsShaojun Miao, Lin Liu, Y uxiang Lian, Xiangxue Zhu, Shutian Zhou,Y an Wang, and Xinhe BaoCatal. Lett., 97(2004)209-21563.Syntheses and structures of sodium aluminodiphosphonates with differentmorphologies (diphosphonate=1-hydroxyethylidenediphosphonate)Zongbin Wu , Zhongmin Liu , Peng Tian , Y ue Y ang , Lei Xu , Haibin Song , Xinhe Bao , Xiumei Liu and Xianchun Liu J. Cryst. Growth, 264(2004)400-40864.Density functional theory study of proto hopping in MCM-22 zeoliteY an Wang, Danhong Zhou, Gang Y ang, Xianchun Liu, Ding Ma,DongBa Liang, Xinhe BaoChem. Phy. Lett., 388(2004)363-36665.On the nature of reaction-controlled phase transferepoxidation of olefin: a 31P NMR investigationY angying Chen, Jianqin Zhuang, Xiumei Liu, Jinbo Gao, Xiuwen Han,Xinhe Bao*, Ning Zhou, Shuang Gao, Zuwei XiCatal. Lett., 93(2004)41-4666.Effect of acidity in TS-1 zeolites on product distribution of the styreneoxidation reactionJianqin Zhuang, Ding Ma, Zhimin Y an, Xiumei Liu, Xiuwen Han,Xinhe Bao, Yihua Zhang, Xinwen Guo, Xiangsheng WangAppl. Catal. A-Gen., 258(2004)1-667.Adsorption and decomposition of Mo(CO)6 on thin Al2O3 films: fabricationof metallic molybdenum model catalystZhiquan Jiang, Weixin Huang, Jian Jiao, Hong Zhao, Dali Tan, Runsheng Zhai, Xinhe BaoAppl. Surf. Sci., 229(2004)43-5068.An IR study on the surface passivation of Mo2C/Al2O3 catalyst with O2,H2O and CO2Weicheng Wu, Zili Wu, Changhai Liang, Pinliang Ying, Zhaochi Feng, Can Li Phys. Chem. Chem. Phys., (2004)5603-560869.Adsorption and reaction of thiophene and H2S on Mo2C/Al2O3 catalyststudied by in situ FT-IR spectroscopyWeicheng Wu, Zili Wu, Zhaochi Feng, Pinliang Ying, Can Li Phys. Chem. Chem. Phys., (2004)5596-560270.Ammonia synthesis on graphitic-nanofilament supportedZhonglai Li, Changhai Liang, Dezheng Wang, Can LiJ. Mol. Catal. A: Chem., 211 (2004)103-10971.The visible luminescent characteristics of ZnO supported on SiO2 powderJun Chen, Zhaochi Feng, Pinliang Ying, Meijun Li, Bo Han,Jianying Shi, Can LiPhys. Chem. Chem. Phys., (2004)4473-447972.SbOx/SiO2 catalysts for the selective oxidation of methane to formaldehydeusing molecular oxygen as oxidantHaidong Zhang, Pinliang Ying, Jing Zhang, Changhai Liang, Zhaochi Feng, Can LiStud. Surf. Sci. & Catal., (147): 547-552 200473.Catalytic decomposition of hydrazine over α-Mo2C/γ-Al2O3 catalystsXiaowei Chen, Tao Zhang, Zili Wu, Weicheng Wu, Can LiInd. Eng. Chem. Res., 43(2004)6040-604774. A spectroscopic study on the reaction-controlled phase transfer catalystfor the epoxidation of cyclohexeneJinbo Gao, Yangying Chen, Bo Han, Zhaochi Feng, Ning Zhou, Shuang Gao, Zuwei Xi, Can LiJ. Mol. Catal. A: Chem., 210 (2004)197-20475.CO-FTIR Characterization of PVP-Protected Pt Nanoclusters on Zeolite BetaJinghong Ma, Shuhua Reng, Ruifeng Li, Weicheng Wu, Can Li, Kecheng XieInternational Journal of Nanoscience, 3(2004)247-25476.Ammonia-treated activated carbon as support of a Ru-Bacatalystfor ammonia synthesisChanghai Liang, Zhaobin Wei, Qin Xin, Can LiReact. Kinet. Catal. Lett., 83 (2004)39-4577.Characterization of the formation of NaA zeolite membrane undermicrowave radiationXiaobo Chen, Weishen Yang, Jie Liu, Liwu LinJournal of Materials Science, 39 (2004) 671– 67378.Low-temperature partial oxidation of n-heptane to CO+H2 overRh-based/γ-Al2O3 catalystsRan Ran, Guoxing Xiong, Shishan Sheng, Weishen YangReaction Kinetics and Catalysis Letters, 81(2004) 27-3279.Synthesis of NaA zeolite membrane on a ceramic hollow fiberXiaochun Xu,Weishen Y ang, Jie Liu, Liwu Lin, Norbert Stroh, Herwig Brunner Journal of membrane science, 229(2004) 81-8580.Oxidative activation of light alkanes on dense ionic oxygenconducting membranesM.Rebeilleau,A.C.V an V een,D.Farrusseng,C.Mirodatos,Z.Shao,G.XiongStudies in surface science and catalysis,147(2004) 655-660 /doc/cd15189216.html,bustion synthesis, annealing, and oxygen permeation propertiesof SrFeCo0.5O y membranesZ.Q. Deng, W. Liu, D.K. Peng, C.S. Chen, Weishen Y angMaterials Research Bulletin, 39(2004)963–96982.Germanium and iron co-substituted SrCoO2.5+δ asoxygen permeable membraneZ.Q. Deng, W. Liu, C.S. Chen, H. Lu, Weishen Y angSolid State Ionics 170 (2004)187–19083.Test of the hydrogen separation from gas mixture using a thin Pd/ceramichollow fiber membrane moduleW.P. Wang, Xiulian Pan, X.L. Zhang, Guoxing Xiong, Weishen Y angInorganic Membranes (Proceedings of Eighth International Conferenceon Inorganic Membranes), (2004)301-304 (ISBN1-929612-67-2)84.Ba0.5Sr0.5Co0.8Fe0.2O3 membrane reactors for catalytic partial oxidationof hydrocarbon to syngasWenliang Zhu, Guoxing Xiong, Wei Han, Weishen Y angInorganic Membranes (Proceedings of Eighth International Conferenceon Inorganic Membranes), (2004) 355-358 (ISBN1-929612-67-2)85.Novel cobalt-free oxygen permeable membraneXuefeng Zhu, Haihui Wang, Y ou Cong, Weishen YangInorganic Membranes (Proceedings of Eighth International Conferenceon Inorganic Membranes), (2004)22-25 (ISBN1-929612-67-2)86.Dehydration of mixed-alcohols produced by fischer-tropsch process byzeolite-A membranesY anshuo Li, Hongliang Chen, Aisheng Huang, Jie Liu,Y uesheng Lin and Weishen Y angInorganic Membranes (Proceedings of Eighth International Conferenceon Inorganic Membranes), (2004)613-617(ISBN1-929612-67-2)87.Preparation of A-type zeolite membranes by using electrophoretic techniqueAisheng Huang, Jie Liu, Y anshuo Li, Y. S. Lin, Weishen Y ang Inorganic Membranes (Proceedings of Eighth International Conferenceon Inorganic Membranes)( 2004)224-228 (ISBN1-929612-67-2)88.Thermal evolution of the structure of a Mg-Al-CO3 layered double hydroxide:Sorption reversibility aspectsYongman Kim, Weishen Yang, Paul K.T.Liu, Muhammad Sahimi,Theodore T.TsotsisIndustrial & Engineering Chemistry Research, 43(2004)4559-457089.Microwave-assisted hydrothermal synthesis of hydroxy-sodalitezeolite membraneXiaochun Xu, Yun Bao, Chunshan Song, Weishen Yang, Jie Liu, Liwu LinMicroporous and Mesoporous Materials, 75(2004)173–18190.Synthesis and properties of A-type zeolite membranes by secondarygrowth method with vacuum seedingAisheng Huang, Y.S. Lin, Weishen YangJournal of Membrane Science, 245(2004)41–5191.Experimental and modeling studies on Ba0.5Sr0.5Co0.8Fe0.2O3-δ (BSCF)tubular membranes for air separationHaihui Wang, Rong Wang, David Tee Liang, Weishen YangJournal of Membrane Science,243(2004)405-41592.Performance comparison of low-temperature direct alcohol fuelcells with different anode catalystsWeijiang Zhou, Bing Zhou, Wenzhen Li, Zhenhua Zhou, Shuqin Song, Gongqun Sun, Qin Xin, S. Douvartzides,M. Goula,P. TsiakarasJournal of Power Sources, 126(2004)16-2293.FT-IR study of the microstructure of nafion? membraneZhenxing Liang, Weimin Chen, Jianguo Liu, Suli Wang, Zhenhua Zhou, Wenzhen Li, Gongqun Sun, Qin XinJournal of Membrane Science, 233(2004) 39-4494.Nano-structured Pt-Fe/C as cathode catalyst in direct methnol fuel cellWenzhen Li, Weijiang Zhou, Huanqiao Li, Zhenhua Zhou, Bing Zhou,Gongquan Sun, Qin XinElectrochimica Acta, 49(2004)1045-105595.The mechanism studies of ethanol oxidation on PdO catalysts byTPSR techniquesRui Lin, Mengfei Luo, Qin Xin, Gongquan SunCatalysis letters, 93(3-4)(2004) 139-14496.Effects of treatment in different atmosphere on Pt3Sn/C electrocatalystsfor ethanol electro-oxidationLuhua Jiang, Zhenhua Zhou, Wenzhen Li, Weijiang Zhou, Shuqin Song,Gonguan Sun, Qin XinEnergy & Fuels, 18(2004) 866-87197.Multi-walled carbon nanotubes supported Pt-Fe cathodic catalyst for direct methanolfuel cellWenzhen Li, Changhai Liang, Weijiang Zhou, Jieshan Qiu, Huanqiao Li,Gongquan Sun, Qin XinReaction Kinetics and Catalysis Letters, 82(2004) 235-24098.Liquid-phase hydrodechlorination of chlorinated benzenes over activecarbon supported nickel catalysts under mild conditionsWenhai Wu, Jie XuCatalysis Comm., 5(2004)591-59599.Pd/C-catalyzed hydrodehalogenation of aromatic halides in aqueoussolutions at room temperature under normal pressureChuanghai Xia, Jie Xu, Wenzhong Wu, Xinmiao LiangCatalysis Comm., 5(2004)383-386100.Multi-scale phenomena in heterogeneous catalytic processes─impact of chemical phenomena under the micro-scale level oncatalyst development and designZhijian Tian, Y unpeng Xu, Liwu LinChemical Engineering Science, 59(2004)1745-1753101.Effect of drying methods on the structure and catalytic combustionactivity of mn-substituted hexaaluminate catalystsJinguang Xu, Zhijian Tian, Junwei Wang, Y unpeng Xu,Zhusheng Xu, Liwu LinReact. Kinet. Catal. Lett., 82(2004)19-25102.The role of acid strength of zeolites in liquid-phase alkylation ofbenzene with ethyleneXinde Sun, Qingxia Wang, Longya Xu, Shenglin LiuCatalysis Letters, 94(2004)75-79/doc/cd15189216.html,parison of 6Mo/MCM-22 and 6Mo/ZSM-5 in the MDA process Jie Bai, Shenglin Liu, Sujuan Xie, Longya Xu, Liwu LinReact. Kinet. Catal. Lett., 82(2004)279-286104.The effect of acidity on olefin aromatization over potassiummodified ZSM-5 catalystsY ueqin Song, Xiangxue Zhu, Sujuan Xie, Qiangxia Wang, Longya XuCatalysis Letters, 97(2004)31-36105.The role of coke in the deactivation of Mo/MCM-22 catalyst for methane dehydroaromatization with CO2 Jie Bai, Shenglin Liu, Sujuan Xie, Longya Xu, Liwu LinStudies in surface science and catalysis, 147(2004)715-720 106.Catalytic alcohols synthesis from CO and H2O on TiO2 catalysts calcined at various temperaturesDeehun Ji, Shenglin Liu, Qingxia Wang, Longya XuStudies in surface science and catalysis, 147(2004)433-438 107.Metathesis of ethylene and 2-butlene to popylene on W/Al2O3-HY catalysts with different HY contentsShengjun Huang, Shenglin Liu, Wenjie Xin, Jie Bai, Sujuan Xie,Qingxia Wang, Longya XuJournal of Molecular Catalysis A: Chemical, 226(2004)61-68 108.Fischer-tropsch synthesis over activated-carbon-supported cobalt catalysts: effect of Co loading and promoters on catalyst performanceWenping Ma, Tunjie Ding, Liwu LinInd. Eng. Chem. Res., 42(2004)2391-2398109.The remarkable effect of In2O3 on the catalytic activity of In/HZSM-5 for the reduction of NO with CH4Lili Ren, Tao Zhang, Changhai Xu, Liwu LinTopics in Catalysis, 30-31(2004)55-57110.Pd/sulfated alumina - a new effective catalyst for the selective catalyticreduction of NO with CH4Ning Li, Aiqin Wang, Lili Ren, Mingyuan Zheng, Xiaodong Wang, Tao Zhang T opics in Catalysis, 30-31(2004)103-105二、在国内刊物上发表的英文文章(仅刊摘要)111.Effect of dimethyl ether Co-feed on catalytic performance of methane dehydroaromatization over Mo/HZSM-5 catalystHuiying Chen, Y onggang Li, Wenjie Shen, Yide Xu, Xinhe Bao Journal of Natural Gas Chemistry, 13/3(2004),1-7112.Catalytic performance of zeolite NU-87 with 10- and 12-member ring for methane dehydroaromatizationHuiying Chen, Liu Lin, Longya Xu, Wenjie Shen, Yide Xu, Xinhe BaoChin. J. Catal., 25(2004)845-846113.A new way to obtain Mo/HZSM-5 catalyst with high activity and selectivity for methane dehydro-aromatization Hongmei Liu, Y ong Li, Wenjie Shen, Xinhe Bao, Yide XuChin. J. 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Chemical methods and phytoremediation of soil contaminated with heavy metals

Chemical methods and phytoremediation of soil contaminated with heavy metals

Chemical methods and phytoremediation of soil contaminatedwith heavy metalsH.M.Chen*,C.R.Zheng,C.Tu,Z.G.ShenInstitute of Soil Science,Chinese Academy of Science,P.O.Box821,Nanjing210008,People's Republic of China AbstractThe e ects of chemical amendments(calcium carbonate(CC),steel sludge(SS)and furnace slag(FS))on the growth and uptake of cadmium(Cd)by wetland rice,Chinese cabbage and wheat grown in a red soil contaminated with Cd were investigated using a pot experiment.The phytoremediation of heavy metal contaminated soil with vetiver grass was also studied in a®eld plot experiment.Results showed that treatments with CC,SS and FS decreased Cd uptake by wetland rice,Chinese cabbage and wheat by23±95%compared with the unamended control.Among the three amendments,FS was the most e cient at suppresing Cd uptake by the plants,probably due to its higher content of available silicon(Si).The concentrations of zinc(Zn),lead(Pb)and Cd in the shoots of vetiver grass were42±67%,500±1200%and120±260%higher in contaminated plots than in control,respectively.Cadmium accumulation by vetiver shoots was218g Cd/ha at a soil Cd concentration of0.33mg Cd/kg.It is suggested that heavy metal-contaminated soil could be remediated with a combination of chemical treatments and plants.Ó2000Elsevier Science Ltd.All rights reserved.1.IntroductionHeavy metal pollution of soils is increasingly be-coming a global problem with the development of in-dustry,mining activity,irrigation of waste water and the application of sewage sludge,even if it is relatively lo-calized at present.The soil±plant system is the funda-mental constructive unit of the geosphere and biosphere. Therefore,heavy metal pollution of soil has an impor-tant in¯uence not only on the yield and quality of crops, but also on the quality of atmospheric and aquatic en-vironment,and even on the health of human beings via food chains,as in the classic example of`itai±itai'disease in Japan,which was traced to the consumption mostly of rice and soybean grown in an environment heavily polluted with Cd from a nearby mine and smelter (Yamagata and Shigematsu,1970,Kobayashi,1970).In the Zhangshi irrigation area of China,large amounts of Cd have accumulated in irrigated soils since irrigation sewage contains large amounts of Cd(Wu et al.,1986). The cadmium content in rice grain,in turn,is also rel-atively high.It was shown that the Cd content in viscera of pigs in the sewage irrigation area is signi®cantly higher than that of the control owing to higher Cd in rice bran and husk used as pig feed.It was recorded that in the irrigation area,Cd in the placenta was2.4Â,and the liver and kidney of fetus2.2Âthan that of the control,which indicates that Cd pollution might also be transferred to the next generation via maternity(Wu et al.,1986).Soil pollution by heavy metals has aroused worldwide attention.Studies of heavy metal pollution in soil have included the sources and behaviour of heavy metals,impacts on public health and the environment, site investigation and analysis,management of remedial action and risk assessment,and the techniques for remediation and so on(Lepp,1981a,b;Assink and van den Brink,1986;Wise and Trantolo,1994;Salomons and Stigliani,1995;Salomons et al.,1995;Brooks,1998;*Corresponding author.0045-6535/00/$-see front matterÓ2000Elsevier Science Ltd.All rights reserved.PII:S0045-6535(99)00415-4Chen,1996).E ective methods for reducing soil heavy metal pollution involve severe control of pollution sources or strict implementation of environmental regulation in terms of waste discharge.Since the1980s, much e ort has been made to control pollution sources and to set up environmental quality standards in China. Some countermeasures for remediation of soil contam-inated with heavy metals have been investigated in-cluding soil moisture management,amendment application,addition of organic manure,selection of crop varieties with a low uptake of heavy metals,and agro-ecological engineering techniques(Chen and Wang,1992;Chen et al.,1999).The present paper re-ports the e ects of application of calcium carbonate (CC),steel sludge(SS)and furnace slag(FS)for red soil contaminated with Cd on the uptake of Cd by wetland rice,Chinese cabbage and wheat,as well as the results of phytoremediation with vetiver,a perennial grass with high biomass,for red soil contaminated with Cd,Cu, Pb,and Zn.2.Materials and methods2.1.Pot experimentRed soil(an Oxisol)was collected from Jinghua, Zhijang Province,with a pH5.2and11.4g/Kg of or-ganic matter.The soil was air-dried,crushed,mixed thoroughly and passed through a1cm sieve.1.5kg portions of the soil were transferred to2l porcelain pots and treated with necessary amounts of fertilizer at a rate of0.5g superphosphate,1.0g urea,and0.2g potassium chloride,and then mixed well.Cadmium was added at a rate of7.0mg Cd/kg as an aqueous solution of CdCl2ÁH2O,and mixed again.Three days later,the chemical remediation treatments(three replicates)were carried out using the di erent chemical amendments shown in Table1.Wetland rice(Oryza sativa L.),Chi-nese cabbage(Brassica sinica),and wheat(Triticum aestivum L.)were grown in rotation with rice initially. The test period was3crop cycles about1year.The experiment design in details was showed elsewhere (Zang et al.,1987).2.2.Field experimentA®eld plot experiment was conducted at the Eco-logical Experimental Station of Red Soil,Chinese Academy of Science,Yingtan,Jangxi Province.Each plot of4m2was separated by a cement¯at.The total soil concentrations of Cd,Cu,Pb,and Zn determined are shown in Table4,which are the typical and repre-sentative for soils contaminated with heavy metals in the area of red soils.Fertilizers were applied at a rate of 37.5g/m2urea,75g/m2superphosphate,and18.75g/m2 potassium chloride.Vetiver grass(Vetiveria zizanioides) was transplanted on9April1997.The vetiver shoots above20cm from the ground were cut for analysis of relative biomass and the concentrations of Cd on day 110after transplanting.Their residual parts were grown continuously.2.3.Analytical methodsSoil sample were taken from pot and®eld plot.The samples were air-dried and ground prior to analysis.Soil available Si was extracted by H2C2O4± NH4 2C2O4(pH 3.2)and determined colorimetrically(Institute of Soil Science,Chinese Academy of Science,1978).Total metal contents were determined with atomic absorption spec-troscopy(AAS)using¯ame or¯ameless mode following HF±HNO3±HClO4digestion procedures(Wei,1992).Plant materials for heavy metal analysis were har-vested after mature(for wetland rice and wheat),or at a certain growth period(for Chinese cabbage and vetiver). The harvested plants were®rst rinsed with tap water and then with distilled water,dried at70°C for48h,and then ground with an electric mill.Plant materials were analyzed for the concentrations of Cd,Cu,Pb,and ZnTable1Treatments and basic characteristics of di erent amendments used in the experimentNo.Amendment a Treatment amount(w/w)%Basic characteristics of amendment1CC0.2Chemical reagent20.43SS0.217.4%(Fe+FeO+Fe2O3),53.1%CaO40.48.7%SiO2,2.6%MgO;`0.21mm50.68%SiO2extracted with0.5mol/l HCl6FS0.252%CaO,32%SiO270.4`0.25mm;23%extracted SiO280.6with0.5mol/l HCla CC:calcium carbonate;SS:steel sludge,from Lingyu steel plant,Hunan Province;FS:furnace slag,from no.2steel and iron plant, Nanjing.230H.M.Chen et al./Chemosphere41(2000)229±234using AAS following HNO3±HClO4digestion(Envi-ronmental Protection Agency of China,1999).3.Results and discussion3.1.E ect of chemical amendments on the growth of plantsThe e ect of chemical amendment on the yields of wetland rice,Chinese cabbage and wheat are shown in Table2.The results showed that the growth of wetland rice was most a ected by the addition of chemical amendments.The e ects,however,were very di erent amongst treatments.Addition of calcium carbonate re-duced yields of straw and grain of rice by37±41%and 48±56%,respectively.The ratio of straw to grain in-creased from1.38in the control to1.69for adding0.2%, and1.87for adding0.4%calcium carbonate treatments due to a delay of crop maturity.Addition of0.2%steel sludge increased yield of rice grain,but0.4%and0.6% steel sludge decreased yield.The addition of furnace slag had no signi®cant e ect on straw and grain yields of rice (Table2).Table2shows that addition of chemical amendments increased the yield of Chinese cabbage because they signi®cantly increased soil pH and improved the growth conditions.The lower yield of the control may be related to the low soil pH and a low tolerance of Chinese cab-bage to acid conditions as well as to the toxicity of Cd in the control with high Cd concentration(Table3).Ad-dition of chemical amendments had bene®cial e ects on the growth of plants because all treatments with amendments had a higher yield than the control.In summary,the addition of chemical amendments can alleviate Cd toxicity and increase yields of Chinese cabbage and wheat,except in the®rst cropping season, where rice yield was decreased by the addition of calci-um carbonate and steel sludge.As mentioned above,the treatments of furnace slag had no signi®cant e ect on the relative yield.It is certain however,that furnace slag is the best chemical amendment for the remediation of soil contaminated with Cd from the point of view of plant yields and Cd concentration in plants(Table3) under the experimental conditions employed.3.2.E ect of amendments on the uptake of Cd by plantsThe chemical amendments employed were very e -cient at reducing Cd uptake.For brown rice,the Cd concentration ranged from4.13mg/kg for the control to 0.32±0.35mg/kg for the treatments with furnace slag (Table3).The concentrations were also markedly af-fected by added calcium carbonate and steel sludge.The Cd concentration in brown rice was signi®cantly reduced by33.0±96.3%by the addition of chemical amendments. This may have resulted from the increase of pH and available Si and Cd®xation in soils(Chen,1988). Stepwise multiple regression analysis revealed the fol-lowing relationship among Cd concentrations in brown rice,pH and available Si in the soil:Y1 18X54À0X6352 Si À2X1531 pH0X0812 SiÂpH 1with R21as0.630 P`0X001 and where Y1is Cd con-centration in brown rice(mg/kg),(Si)and(SiÂpH)are available Si in soil(SiO2,mg/100g soil)and the inter-action of pH and available Si,respectively.Eq.(1)Table2E ect of amendments on yield of plants(expressed as%yield of control)aTreatment Rice straw Rice grain Chinese cabbage Wheat straw Wheat grain CK100a100ab100e100b100bCC0.2%62.9c51.7c673a117a125a0.4%59.0c43.6c543b111ab116abSS0.2%82.9b105ab391d100b108b0.4%77.6b84.6b614ab100b114ab0.6%72.7bc81.9b662a121a127aFS0.2%94.1ab120a479c105b127a0.4%110a102ab539b113ab114ab0.6%103a99.3ab651aa Means followed by the same letter within columns are not signi®cantly di erent at the5%probability level by least signi®cant range (Tukey method).H.M.Chen et al./Chemosphere41(2000)229±234231showed that the Cd concentration in brown rice was markedly a ected by available Si in soil,soil pH,and interaction of available Si and pH.Cadmium concentration of Chinese cabbage ranged from20.0mg/kg at0.6%steel sludge to148mg/kg for the control.The aftere ects of chemical amendments added to the soil on the concentration of Cd in Chinese cabbage were also very marked.FS,SS and CC treat-ments decreased the concentration of Cd by81.3%, 74.3%and73.4%,respectively(Table3).A simple cor-relation analysis indicated signi®cant e ects of pH on Cd concentration in Chinese cabbage r 0X943Y n 25 .Stepwise multiple regression analysis revealed the following relationship among Cd concentrations in Chinese cabbage,pH and available Si in soilY2 950X8À25X76 Si À127X1 pH 3X553 SiÂpH2 with R22as0.960 P`0X001 .Eq.(2)suggests the same tendency as for Cd in wetland rice.Research into interactions in environmental science is very important(Chen and Zheng,1996).E ects of in-teraction of available Si and pH on the concentration of Cd in brown rice and Chinese cabbage suggested that the function of remediation of soil contaminated with heavy metals by chemical amendments could be erro-neous if the interaction between these factors is ne-glected.For example,stepwise multiple regression analysis showed the following relationship between Cd concentration in brown rice and available Si and soil pH neglecting the interactionY3 9X58À0X0601 Si À0X8837 pH 3 with R23as0.586 P`0X001 and where Y3is Cd con-centration in brown rice(mg/kg),and for chinese cabbageY4 559X06À0X6076 Si À71X60 pH 4with R24as0.879 P`0X001 and where Y4is Cd con-centration in Chinese cabbage(mg/kg).If we set up available Si in soil as25mg SiO2/100g soil pH as7.0, then comparing Eqs.(1)and(3),as well as Eqs.(2)and (4),the results indicate that the e ectiveness of remedi-ation with chemical amendments would be underesti-mated by5%for wetland rice and10%for chinese cabbage without the consideration of the interaction aspect in the equation.For wheat,the next crop of Chinese cabbage,Cd concentration ranged from3.76mg/kg at0.6%addition of steel sludge to8.99mg/kg for control(Table3).The concentrations were also signi®cantly a ected by added chemical amendments.A simple correlation analysis indicated signi®cant e ects of pH r À0X84Y n 25 and available Si in soil r À0X52Y n 25 .Stepwise multiple regression analysis,however,revealed the fol-lowing relationship among Cd concentration in wheat grain and pH and available Si in the soilTable3E ect of chemical amendments on Cd concentration in plants aTreatment Brown rice(mg/kg)Relativeconcentration(%)Cabbage(mg/kg)Relativeconcentration(%)Wheat(mg/kg)Relativeconcentration(%)pH AvailableSi bCK4.13a100148a1008.99a1005.5012.5CC0.2% 3.18b77.050.9b34.57.07b78.6 6.8323.00.4% 2.54bc61.527.4c18.6 4.17cd46.47.3224.0SS0.2% 2.91b70.563.7b43.27.92ab88.1 6.7520.00.4% 1.77c42.929.7c20.2 5.31c59.17.1123.00.6%0.42d10.220.0c13.6 3.76d41.27.4823.8FS0.2%0.32d7.735.3c24.0 6.69b74.4 6.5829.10.4%0.34d8.226.0c17.6 5.09c56.67.0050.20.6%0.35d8.521.6c14.6 4.56cd50.77.2255.0a Means followed by the same letter within columns are not signi®cantly di erent at the5%probability level by least signi®cant range (Tukey method).b Unit:mg SiO2/100g soil.Table4Total heavy metal concentration in soil used in the®eld plotexperiment(mg/kg dry soil)Item Cd Cu Pb ZnCK0.00620.432.560.8Plot10.3358.8158112Plot20.95118367173232H.M.Chen et al./Chemosphere41(2000)229±234Y5 24X57À2X71 pH 5 with R25as0.698 P`0X001 and Y5is the concentration of Cd in wheat grain(mg/kg).The results indicate that the e ect of available Si and interaction of pH and available Si did not signi®cantly a ect the concentration of Cd in wheat grain compared to pH.Table3also shows that the residual e ect of chemical amendments on concentration of Cd in wheat grain reduced with time,and there was no di erence between di erent treatments.However,by reducing the Cd concentration in these plants by amendments even the residual actions were much less than in wetland rice and Chinese cab-bage(cf.Table3).3.3.E ectiveness of phytoremediation with vetiverIt is likely that Vetiver Grass Technology(VGT)will become one of the leading biological systems of soil and water conservation,land rehabilitation,and enbank-ment stabilization in the21st century(Grimshaw,1997; Xu,1997).In China,there have been increasing con-cerns about the VGT,and vetiver has been grown in most of the southern and coastal provinces of China. Moreover,vetiver is also able to tolerate a variety of pollutants in soil and water(Truong and Baker,1998; Truong and Baker,1997;Pinthong et al.,1998;Zheng et al.,1998).The present results showed that vetiver can grow well in soil contaminated with Cd,Cu,Pb and Zn (Table4),although high concentrations of Cd,Cu,Pb and Zn in the shoots of vetiver were found(Table5). The Cd accumulation factors,de®ned as the ratio of shoot Cd concentration to the total Cd concentration in soil,were0.67and0.16in plot1and plot2,respectively. These values were close to those of hyperaccumulator Thlaspi caerulescens(Baker et al.,1994).The average dry matter yield of vetiver is99t/ha/year in southeast of China(Zhang,1998).Cadmium accumulation by veti-ver,with a total above-ground uptake of218g/ha at a soil Cd concentration of0.33mg/kg in plot1,was greater than that by hyperaccumulator T.caerulescens, with an uptake of143g/ha at a soil Cd concentration of 13.6mg/kg(Baker et al.,1994).If it is assumed that subsequent crops would remove Cd at the same rate as the®rst crop,about four croppings with this vetiver would be required to extract the excess loading of Cd (729g/ha)in the experimental soil to bring the total soil Cd concentration down to background value,from0.33 to0.006mg/kg.VGT is an e ective low-cost and envi-ronmentally friendly technology to clean Cd contami-nated soil before it is replaced by a hyperaccumulator. Plants that can hyperaccumulate heavy metals are a very attractive phytoremediation option(Brooks,1998),if the low biomass can be improved.A suggestion derived from this study:is there any possibility to transfer the genes of hyperaccumulator to vetiver that with very high biomass?If so,the new plant variety with a gene com-bination to hyperaccumulate heavy metals and with high biomass will bring a revolutionary progress in phyto-remediation technology.4.ConclusionsBased upon the present studies it can be concluded that:1.The chemical amendments,calcium carbonate,steelsludge,and furnace slag,may reduce the concentra-tion of Cd in brown rice,Chinese cabbage and wheat grain.The most e ective is furnace slag from a com-bined evaluation of the e ect on plant yields and Cd concentration in plants.2.The interaction of factors in¯uencing the e ectivenessof remediation should be considered.3.Preliminary results suggest that vetiver grass has arelatively greater ability to remove Cd,Pb and Zn from soil,and further study is needed on how to treat the harvested materials.4.A combination of chemical treatment and phyto-remediation could solve the problem of soil polluted with heavy metals.AcknowledgementsThese studies were jointly supported by the Na-tional Science Foundation of China(49771048; 49631010);State Ministry of Science and Technology, China(96-920-13-03);Ecological Experiment Station of Red Soil and Laboratory of Material Cycling in Ped-osphere,Chinese Academy of Science;and the China Vetiver Network.The authors also want to extend great thanks to the anonymous referee for the invalu-able comments.Table5Concentrations of heavy metals in vetiver shoots(mg/kg dry matter)and accumulation factors(AF)Item Cd AF Cu AF Pb AF Zn AFCK0.03 5.0 3.210.160.270.017.170.12Plot10.220.67 3.800.06 6.840.0420.10.18Plot20.150.16 4.200.04 3.480.0126.30.15H.M.Chen et al./Chemosphere41(2000)229±234233ReferencesAssink,J.W.,van den Brink,W.J.(Ed.),1986.Contaminated Soil.Martinus Nijho Publishers,Dordrecht,The Nether-lands,p.923.Baker,A.J.M.,McGrath,S.P.,Sidoli,C.M.D.,Reeves,R.D., 1994.The possibility if in situ heavy metal decontamination of polluted soils using crops of metal-accumulating plants.Resources Conservation and Recycling11,41±49. 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Truong,P.,Baker,D.,1997.The role of vetiver grass in the rehabilitation of toxic and contaminated lands in australia.International Vetiver Workshop,Fuzhou,China,pp.21±26. Truong,P.,Baker,D.,1998.Vetiver grass system for environ-mental protection.Paci®c Rim Vetiver Network:Technical Bulletin no.1,1998/1,Bangkok,Thailand.Wei,F.S.,1992.Modern Analytical Methods of Soil Elements.Chinese Environ.Sci.Press,Beijing,p.64.Wise,D.L.,Trantolo,D.J.,1994.Remediation of Hazardous Waste Contaminated Soils.Marcel Dekker,New York, p.929.Wu,Y.Y.,Chen,T.,Zheng,X.X.,1986.Study on Cd-pollution ecology in Zhangshi irrigated area of Shenyang.In:Gao, Z.M.(Ed.),Studies on Pollution Ecology of Soil±Plant System.China Science and Technology Press,Beijing, pp.295±301.Xu,L.,1997.Recent development of vetiver technology in China Vetiver Network(CVN).Vetiver Newsletter1,8±12. Yamagata,N.,Shigematsu,I.,1970.Cadmium pollution in perspective.Bulletin of the Institute of Public Health19, 1±27.Zhang,J.,1998.Bene®t and application future of sandy soils on windy Pingtan island.In:Vetiver Rsearch and Development.Agriculture Sci.and Tech.Press,China, pp.179±191.Zang,H.L.,Zheng, C.R.,Chen,H.M.,1987.Study on controlling cadmium absorption by crops in cadmium contamination soil(I).Agro-Environmental Protection 6(3),27±29.Zheng,C.R.,Tu,C.,Chen,H.M.,1998.Preliminary experiment on puri®cation of eutrophic water with vetiver.In:Vetiver Research and Development.Agriculture Sci.and Tech.Press,China,pp.81±84.234H.M.Chen et al./Chemosphere41(2000)229±234。

2004-ELASTO-PLASTIC SIMULATION OF A DIRECT SHEAR TEST

2004-ELASTO-PLASTIC SIMULATION OF A DIRECT SHEAR TEST

A non-associated flow rule is used to avoid the over-estimation of dilation given by the associated flow rule. Lü & Brown made an attempt to develop the elasto-plastic model for estimating the response of rough joints to the external loads. To determine the direction of plastic flow at a stress point on the yield surface, the plastic potential function should be defined. It is assumed that the plastic potential function has the form.
Maksimovic [1], Chung-In Lee & Sang-Don Lee[2] are good examples. These criteria, however, can only be used for the purpose of estimating the peak shear strength and thus failed to find their applications in describing the hardening and softening phenomena in the pre- and post-peak ranges of the shear displacement – shear stress curve. Goodman attempted to make use of the complete normal and shear deformation curve individually in his numerical study of rock joints, but he failed to couple two curves. Plesha[3] proposed a more advanced constitutive model which considers the wear of joint roughness. Lü. M & E.T. Brown[4] developed a joint element finite element using the concepts of mobilized joint roughness coefficient (JRCm). T.S. Nguyen & A.P.S. Selvadurai[ 5] suggested a constitutive law for rock joints which combined Plesha’s model and Barton-Banidis empirical coefficients; the Joint Roughness (JRC) and the Joint Compressive Strength (JCS). However, JRC is known to have some problems such as possibility to involve subjective judgement of the researcher in determining the values.

2004年美国热门处方药·1

2004年美国热门处方药·1

36 508 251 9
NORVASC 抗高血压药 口服片剂 氨氯地平 a m l o d i p i n e
34 729 004 10
TOPROL XL 心血管药物 口服缓释片剂 琥珀酸美托洛尔 metoprolol succinate
32 794 562 11
A L P R A Z O L A M 抗焦虑药 口服片剂 阿普唑仑
22 020 478 26
C E L E B R E X 非甾体消炎镇痛剂 口服胶囊 塞来昔布 c e l e c o x i b
21 916 220 27
FLUOXETINE HCL 抗抑郁药 口服片剂 盐酸氟西汀
21 752 487 28
FOSAMAX 骨质疏松症治疗药 口服片剂 阿仑膦酸钠 alendronate sodium
24 616 014 18
A M B I E N 安眠镇静剂 口服片剂 唑吡坦 z o l p i d e m
24 494 669 19
C E P H A L E X I N 抗生素 口服胶囊 头孢氨苄
23 665 172 20
NEXIUM 抗溃疡药 口服缓释胶囊 艾美拉唑 e s o m e p r a z o l e
27 234 005 15
M E T F O R M I N H C L 2 型糖尿病药 口服片剂 盐酸二甲双胍
25 472 580 16
I B U P R O F E N 消炎镇痛剂 口服片剂 混悬液 布洛芬
25 188 051 17
TRIAMTERENE W/HCTZ 利尿药 日服一次胶囊 氨苯蝶啶 / 氢氯噻嗪
18 523 548 37
PROTONIX 抗溃疡药 口服缓释片剂 泮托拉唑钠 pantoprazole sodium

植物忍耐低磷胁迫机理的研究进展

植物忍耐低磷胁迫机理的研究进展

Abstract: Studies on physiological adaptability of root morphology, root excretion, transportation of P across plasma membrane
and P translocation of plants under phosphorus deficiency stress were summarized. Researches on the basis of molecular biology re lated to excavation of plant s phosphorus high nutrition efficiency were also discussed. It would be helpful for understanding the adaptation mechanisms of plants to phosphorus deficiency stress.
[ 8] [ 7] [ 5]
泌有机酸的 性能 看作是 数量 遗传性 状, 通常 采用 QTLs 技术来研究其分子遗传[ 10] 。Pyan 等[ 11] 发现不 同小麦细胞分泌苹果酸的差异主要取决于质膜上阴 离子通道转运速率 , 而非细胞内苹果酸合成速度 , 发 现 ALT1 位点可能编码苹果酸通道或非专一性阴离 子通道, 但 ALT 1 位点编码产物的功能 目前尚未明 确 , 低磷和高铝胁迫都能诱导其表达。白羽扇豆常 作为研究根系分泌有机酸的模式植物, 其排根细胞 内积累的柠檬 酸通过质膜上的阴离子 通道转运出 来 , 释放量也主要受阴离子通道的调节, 合成柠檬酸 所需要的碳源主要来自非光合作用的碳固定途径, 其中磷酸烯醇丙酮酸羧化酶是这一碳供应途径的限 速酶。磷酸烯醇丙酮酸羧化酶的基因已经被成功克 隆 , 该基因在排根皮层细胞中表达, 并在低磷条件下 增强表达[ 12] 。

2004年美国药物研究与开发回顾-续完

2004年美国药物研究与开发回顾-续完

2004年美国药物研究与开发回顾-续完
张字(摘)
【期刊名称】《国外药讯》
【年(卷),期】2005(000)010
【摘要】Amgen/Abgenix公司正在合作开发直接作用于表皮生长因子受体(EGFR)的新一类治疗药panitumumab。

这个产品目前正作为单独和与其他药物连用用于各种类型的癌,处于Ⅱ和Ⅲ期临床试验中,包括结直肠、肺和肾癌。

它是用Abgenix公司的XenoMouse技术创造的,这个抗体没有鼠蛋白并可能导致滴注反应、免疫原性和过敏反应低发生率的更有利的安全性。

4月份开始的一项Ⅲ临床试验旨在评估将panitumumab每隔周加入到Avastin和Eloxatin基或Camptosar基化疗方案中作为转移性结直肠癌一线治疗的潜在利益。

【总页数】2页(P49-50)
【作者】张字(摘)
【作者单位】无
【正文语种】中文
【中图分类】R975.4
【相关文献】
1.毒品及滥用药物的HPLC、GC分析方法——美国新泽西州法医局部分毒物标准化分析方法简介(续完) [J], 高利生
2.美国创新药物研究与开发对我国的启示 [J], 徐守军;张永祥;高波;赵达生
3.美国环境监测一百年历史回顾及其借鉴(续完) [J], 王炳华
4.2004年美药物研究与开发回顾 [J], 张宇(摘)
5.美国肿瘤治疗药物研究与开发的最新进展 [J], 王以光
因版权原因,仅展示原文概要,查看原文内容请购买。

2004国际仪器展讯

2004国际仪器展讯

2004国际仪器展讯
佚名
【期刊名称】《现代仪器》
【年(卷),期】2004(10)1
【总页数】1页(P62-62)
【正文语种】中文
【中图分类】TH
【相关文献】
1.第九届中国国际纺机展(CITME 2004)纺织测试仪器展出概况(续) [J], 宋湛华
2.2004年国际医疗仪器设备展览会——2004年4月26日---29日中国国际展览中心 [J],
3.2004年2月-6月国际花展讯息 [J],
4.第51届中国国际医瘸器械博览会(2004武汉) 2004年国际医疗仪器设备展览会(CHINA MED 2004北京) [J], 无
5.2004(第五届)西南地区自动化及仪器仪表国际展览会纪要——2004年4月8~11日成都国际会议展览中心 [J], 无
因版权原因,仅展示原文概要,查看原文内容请购买。

2004年9-10月欧洲批准和上市的新产品

2004年9-10月欧洲批准和上市的新产品

2004年9-10月欧洲批准和上市的新产品
章鸣
【期刊名称】《国外药讯》
【年(卷),期】2004(000)012
【摘要】Cellegy公司的Rectogesic(nitroglycerin,硝酸甘油软膏)在英国获准,用于慢性肛裂相关性疼痛的治疗。

申请资料显示,在8周治疗期间,每天给药2
次其疼痛减轻作用统计学上优于安慰剂。

英国是欧盟相互承认审批程序的参考成员国。

此药已在澳大利亚、新西兰和韩国获准,
【总页数】3页(P3-5)
【作者】章鸣
【作者单位】无
【正文语种】中文
【中图分类】R657
【相关文献】
1.01010 2004年10~11月份欧洲批准和上市的新产品 [J], 刘静
2.2004年11~12月欧洲批准和上市的新产品 [J], 张宇
3.2004年2-3月份欧洲批准和上市的新产品 [J], 刘敏
4.2003年12月-2004年1月欧洲批准和上市的新产品 [J], 章鸣
5.2004年4—5月份欧洲批准和上市的新产品 [J], 刘敏
因版权原因,仅展示原文概要,查看原文内容请购买。

以色列野生二粒小麦与光稃野燕麦远缘杂种的分子标记鉴定

以色列野生二粒小麦与光稃野燕麦远缘杂种的分子标记鉴定

Vai ain o eP o e isF o W i e C o sL r e i mme l t ft r g n e rm d r s sa lW l E d o h d r
× Ar n t a L. r Glb aa P tb lc lrM a k r e a Fa u Va . a r t a y Moe u a r es
Ab t a t T e v l ain O h y r s f m d r s e sa lw l mme × A e a F t a L V r g a rt s r c : h a i t f e h b d r wi e c o s s I r e i e d o t i o d t r n a u . a . lb aa
关键词 : 野生二粒小麦 ;光稃野燕麦 ; 远缘杂交 ; D A间隔序列 ; R P 5Sr N SA
中 图 分 类 号 : S / 91 5 1 ; S52 5 0 . 5 3 I 1 文献 标 志 码 : A 文 章 编 号 : 10 — 7 5 2 0 )40 3 -3 0 1 4 0 (0 9 0 -0 50
rs l h we a ep me arP I PI p o u e ep tr a p cf r esi eh bis a d teh — eut s o dt t r r i / rd c d t aen l e icmak r nt y r . n y s h t i h p I h s i h d h
研 究报告
耿广东 等 : 以色列野生二粒小麦与光稃野燕麦远缘杂 种的分子标记 鉴定
以色 列 野 生二 粒 小 麦 与 光稃 野燕 麦远 缘 杂 种 的 分 子 标 记 鉴 定
耿 广 东 , 张素勤 , 李 松桃 , 贾开 家 , 程剑 平 , 张庆 勤

2000年以来天然放射增敏剂概览(英文)

2000年以来天然放射增敏剂概览(英文)

2000年以来天然放射增敏剂概览(英文)
卢佳;邵宏
【期刊名称】《中国药学:英文版》
【年(卷),期】2003(12)3
【总页数】4页(P160-163)
【关键词】放射增敏剂;天然产物;肿瘤;放射疗法
【作者】卢佳;邵宏
【作者单位】北京大学基础医学院放射医学基础教研室;北京大学药学院药事管理与临床药学系
【正文语种】中文
【中图分类】R979.19;R730.55
【相关文献】
1.肿瘤放射增敏剂及增敏机制研究进展 [J], 周厚清;邢成;李伯南
2.放射增敏剂的增敏机制 [J], 高春玲;高春丽;宋维芳;谢立青
3.2000年以来放射增敏剂 (化学合成剂和基因治疗剂 )概览(英文) [J], 邵宏;卢佳因版权原因,仅展示原文概要,查看原文内容请购买。

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Overexpression of OsRAA1Causes Pleiotropic Phenotypes in Transgenic Rice Plants,includingAltered Leaf,Flower,and Root Developmentand Root Response to Gravity1Lei Ge,Hui Chen,Jia-Fu Jiang,Yuan Zhao,Ming-Li Xu,Yun-Yuan Xu,Ke-hui Tan,Zhi-Hong Xu,and Kang Chong*Research Center for Molecular and Developmental Biology,Key Laboratory of Photosynthesis and Environmental Molecular Physiology,Institute of Botany,The Chinese Academy of Sciences,Beijing100093,ChinaThere are very few root genes that have been described in rice as a monocotyledonous model plant so far.Here,the OsRAA1 (Oryza sativa Root Architecture Associated1)gene has been characterized molecularly.OsRAA1encodes a12.0-kD protein that has58%homology to the AtFPF1(Flowering Promoting Factor1)in Arabidopsis,which has not been reported as modulating root development yet.Data of in situ hybridization and OsRAA1::GUS transgenic plant showed that OsRAA1expressed specifically in the apical meristem,the elongation zone of root tip,steles of the branch zone,and the young lateral root. Constitutive expression of OsRAA1under the control of maize(Zea mays)ubiquitin promoter resulted in phenotypes of reduced growth of primary root,increased number of adventitious roots and helix primary root,and delayed gravitropic response of roots in seedlings of rice(Oryza sativa),which are similar to the phenotypes of the wild-type plant treated with auxin.With overexpression of OsRAA1,initiation and growth of adventitious root were more sensitive to treatment of auxin than those of the control plants,while their responses to9-hydroxyfluorene-9-carboxylic acid in both transgenic line and wild type showed similar results.OsRAA1constitutive expression also caused longer leaves and sterileflorets at the last stage of plant development.Analysis of northern blot and GUS activity staining of OsRAA1::GUS transgenic plants demonstrated that the OsRAA1expression was induced by auxin.At the same time,overexpression of OsRAA1also caused endogenous indole-3-acetic acid to increase.These data suggested that OsRAA1as a new gene functions in the development of rice root systems, which are mediated by auxin.A positive feedback regulation mechanism of OsRAA1to indole-3-acetic acid metabolism may be involved in rice root development in nature.The growth and development of crops depend on their roots to take up water and nutrient material from soil.The root system of rice(Oryza sativa)consists of embryonic and postembryonic roots.The rice embry-onic roots,originating from the radical,emerge after germination.They develop into two forms,one pri-mary root and several seminal roots.Postembryonic roots include adventitious roots that are formed from nodes of the plant and lateral roots that develop on all root types.As is known,plant hormone auxin(indole-3-acetic acid[IAA])plays an important role in controlling root development,such as inhibiting elongation of a pri-mary root and promoting formation of adventitious roots,lateral roots,and root hairs.In Arabidopsis,it has been reported that genes involved in the auxin signal transduction pathway are able to control the development of roots.For example,mutants of the AUX/IAA gene family,such as SHY2/IAA3,SLR1/ IAA14,IAA28,and MSG2/IAA19,show reduced lateral roots or no lateral roots(for review,see Reed,2001). Overexpression of AUX1,TIR1,or NAC1can promote lateral root development(Gray et al.,1999;Xie et al., 2000;Marchant et al.,2002).Overexpression of SINAT5 produces fewer lateral roots,whereas overexpression of a dominant-negative C49S(Cys-49to Ser)mutant of SINAT5develops more lateral roots.The lateral root phenotypes correlate with the expression of NAC1 (Xie et al.,2002).As a central regulator,auxin regulates cell division,expansion,and differentiation.It also functions in many other aspects of plant growth and development,such as promoting hypocotyl and stem elongation,mediating root and shoot gravitropism, maintaining apical dominance,and promoting vascu-lar pattern formation(Thimann,1977;Sachs,1991; Estelle and Klee,1994;Hobbie,1998).Auxin is possibly synthesized in young leaves and root meristem(Thimann,1977)and can be transported1This work was supported by the Major State Basic Research Program of China(grant no.G1*******),by the Innovation Grand of CAS,National Nature Science Foundation of China(NSFC;grant no. 30270143),and by the State Project of Transgenic Plant(J99–A–024) as well as the State High-Tech Project(2001AA222281).*Corresponding author;e-mail chongk@;fax86–10–8259–4821.Article,publication date,and citation information can be found at /cgi/doi/10.1104/pp.104.041996.from young leaves to the roots.In the root tip,it is transported from down to up in the cortex(Doerner, 2000).The polarity in transportation causes the gradi-ent of auxin concentration,which then contributes not only to embryonic patterning and vascular differenti-ation(Goldsmith,1977;Thimann,1977;Sachs,1991; Liu et al.,1993;Przemeck et al.,1996;Uggla et al.,1998; Sabatini et al.,1999),but also to the cell-patterning process within the root meristem(Sabatini et al., 1999).In Arabidopsis,many genes,such as the AUX/IAA family,the SAUR(small auxin up-regulated RNA) family,and the GH3family(Hagen et al.,1984; McClure and Guilfoyle,1989;Abel and Theologis, 1996),are regulated by auxin.Some auxin-regulated genes show tissue-specific expression patterns(Key, 1989;Crowell and Amasino,1994;Gray et al.,1998).A sequence motif of5#-TGTCTC-3#,which is necessary for auxin response factor binding,is found in pro-moters of many auxin-regulated genes(Liu et al.,1994; Ulmasov et al.,1997a,1997b,1999a,1999b;Guilfoyle et al.,1998).Previous studies have confirmed that auxin can give auxin response a feedback regulation by inducing SCF TIR1-dependent degradation of AUX/ IAA proteins(del Pozo and Estelle,1999;Gray et al., 1999,2001).Moreover,the auxin signal transduction pathway may be conserved between monocot and dicot plants.Eleven rice genes that encode the homol-ogous protein sequences to the auxin response factors of Arabidopsis were isolated(Sato et al.,2001). OsIAA1,a monocot member of the AUX/IAA family, was demonstrated to be regulated by auxin and light in rice(Thakur et al.,2001).In monocot plants,the molecular mechanism that establishes the morphology of root systems is blurry so far.Only a small number of mutants related to root formation were found in monocots.For example,rtcs mutant is completely devoid of all adventitious roots (Hetz et al.,1996);rt1mutant forms few or no crowns and brace roots(Jenkins,1930);asr1mutant forms defective seminal roots(De Miranda,1980);and slr1 mutant and slr2mutant display short lateral roots (Hochholdinger et al.,2001).Although the genes corresponding to these mutants have not been cloned, studies of the characters of mutants are useful to understand the mechanism of grass root development. Concerning effects of ethylene on the development of adventitious roots,it has been proposed that sub-mergence or treatment with ethylene can induce the growth of adventitious roots of deepwater rice (Vergera et al.,1976;Suge,1985;Bleecker et al.,1986, 1987).So far,genes related to root development in rice have not yet been studied thoroughly.In this paper,we used a reverse genetics approach to study the functions of a novel auxin-induced gene regulating root development in rice.Based on the database of expression sequence tag(EST)and genomic sequences,a cDNA and its promoter sequence were cloned.Its expression patterns and phenotypes of over-expression in transgenic plants were analyzed.RESULTSOsRAA1Gene Encodes a Small Protein and Is Conserved in PlantsBased on the EST database,an unknown small pro-tein gene corresponding to an EST(AU071162)was identified in rice(BAB07982).A PAC clone(P0462H08) containing the EST was screened from the database of DDBJ/GenBank/EMBL.The RACE strategy was uti-lized to amplify the full-length cDNA in rice.The full-length cDNA consists of725nucleotides containing a327-nucleotide open reading frame(ORF). The5#-upstream untranslated region is82-bp long,and the3#-downstream untranslated region is339-bp long. The ORF was predicted to encode a109-amino acid polypeptide with a calculated molecular mass of12kD and a pI of9.45(Fig.1A).There are three amino acids that are slightly rich in protein:Ser,Val,and Leu.It was named OsRAA1(Oryza sativa Root Architecture Associ-ated1)since our data suggested that its functions are related to root morphology development in -parative analysis between sequences of the cDNA and those of the PAC clone(P0462H08)at chromosome1in rice suggested that the OsRAA1gene has no intron. The results of BLAST in the GenBank showed that OsRAA1shared a58%sequence homology of amino acids with AtFPF1(Flowering Promoting Factor1; Y11988).A series of ESTs,including MossFPF1 (AW699964)from moss(Physcomitrella patens);ChrFPF1 (BE034410)and ChrFPF2(BE033961)from chrysanthe-mum root;MuFPF1(Y11987)from mustard;ZeTaP1 (BE552830)from the cDNA library of maize tassel pri-mordia;WhRoP1(BE428690)and WhRoP2(BE428819) from the wheat root library;and BaLeP1(BE421936), BaSpP1(BG342901),and BaSpP2(BE196402)from the barley leaf library and spike library,were also obtained from the database(Fig.1,B and D).The anal-ysis showed that homologous genes of OsRAA1exist ubiquitously from the lower plant(such as moss)to the higher plant(such as chrysanthemum).It indi-cates that this gene family may play important roles in plant development.Comparative alignments analysis of the OsRAA1 sequence suggested that four conserved domains pre-sented in these proteins.Thefirst motif is-GVWV/IF-in the N-terminal part;the second one is-GWERYY-in the middle part;and the third and fourth ones are -DLIS/ALP-and-H/YMYDI/VVV/I-in the near C-terminal part,respectively(Fig.1C).Interestingly, the conservative domains except for the second one appear in the hydrophobic region on the hydropho-bicity plot(data not shown).Besides that,there were seven Leu conserved.There are at least three members of this gene family in Arabidopsis(Y11988,T04505,and T49976).In rice, there is another EST(AU070455)shared sequence with OsRAA1.The complete sequence corresponding to the EST was obtained from the GenBank(contig AAAA01001788.1).At rice chromosome7(AP003982), Overexpression of OsRAA1Controls Rice Root DevelopmentFigure1.The analysis of the OsRAA1gene and its protein sequence.A,Nucleotide and putative protein sequence of OsRAA1 cDNA.B,Protein sequence multiple alignment of OsRAA1.BaLeP1(BE421936),BaSpP1(BG342901),and BaSpP2(BE196402) are from barley leaf and spike;MuFPF1(Y11987)is from mustard;WhRoP1(BE428690)and WhRoP2(BE428819)are from wheat root;ChrFPF1(BE034410)and ChrFPF2(BE033961)are from chrysanthemum;MossFPF1(AW699964)is from moss (Physcomitrella patens);AtFPF1(Y11988)is from Arabidopsis;ZeaTaP2(BE552830)is from maize.C,Protein multialignment of rice putative OsRAA1/FPF1family genes.OsRAAL1(OsRAA like)is from rice contig AAAA01001788.1,which contains EST AU070455;OsRAAL2is from rice chromosome7(AP003982).D,The phylogenetic tree of the FPF1/OsRAA1gene family processed by software DNAMAN.In the phylogenetic tree at bottom,the numbers of amino acid substitutions per alignment site are indicated on the branches.E,OsRAA1promoter structure.TAACAAA/TTTGTTA is a gibberellin response element;TGTCTC isan AuRE.Bar5100bp.there is a fragment of genomic sequence,which can also be deduced to a protein with high homology with OsRAA1(Fig.1C).These three sequences in rice belong to three different subfamilies (data not shown).Phylogenetic analysis of the AtFPF1/OsRAA1gene family indicated that homologs were divided into three branches.It also showed there are different members expressed even in the same organ (Fig.1D).For example,there are two ESTs (WhRoP1and WhRoP2)from the wheat root library,and they are located at different branches of the phylogenetic tree.Another two ESTs (BaSpP1and BaSpP2)are in the barley spike library,which belong to a different sub-family.OsRAA1is located in a branch that was different from those of AtFPF1.The OsRAA1promoter sequence of 1,987bp was isolated and analyzed.Elements of GA and auxin response were involved in the promoter region.The conservative GA response complex consists of pyrim-idine box (C/TCTTTTC/T),GA response element (TAACAAA),and element of TATCCA.Those ele-ments appeared in the promoter region (Fig.1E),but it was a very weak response to GA 3treatment (data not shown).There is an auxin response element (AuRE)core sequence 5#-TGTCTC-3#located at 2150to 2145(Fig.1E).In reverse orientation,another AuRE (5#-CTCTGT-3#)is located at 2158to 2153.The pre-sence of two AuRE motifs suggested that the OsRAA1gene is probably regulated by auxin.The expression pattern of OsRAA1was investigated as to its localization.Northern analysis showed that the OsRAA1mRNA was specifically transcripted in the organs of roots and spikes (Fig.2A).No signal was detected in either young shoots or leaves.Data of RNA in situ hybridization showed a more distinct expres-sion pattern.As shown in Figure 2,F and G,signals of OsRAA1were detected in the root apex,including quiescent center and dividing cells.Stronger signals were shown in the cortex of root apical meristem and pericycle of root apex.On the contrary,no distinct signal could be detected in the cortex of the mature zone.A transcript of OsRAA1was also present in lateral roots,especially in the lateral root primordia and the pericycles of the branch zones (Fig.2,B and C).In situ hybridization also showed that OsRAA1mRNA is expressed in the apical meristem of young spikes (Fig.2E).Besides that,there is a distinct signal in the collenchyma cells of margin vascular bundles between shoot and roots (Fig.2D).As is known,the adventi-tious roots are differentiated from these collenchyma cells (Fujii,1959).To further confirm the expression patterns,an ex-pression vector of GUS (b -glucuronidase)driven by OsRAA1promoter was constructed andtransformedFigure 2.OsRAA1expression patterns.A,OsRAA1northern blot of RNA from tissues of young shoots,roots,young spikes,and leaves in wild-type plants.Y oung spikes were harvested from 70-d-old plants grown in a growth chamber.The remaining materials were from plants grown for 14d.Ethidium bromide (EtBr)staining shows equal RNA loading.B to G,In situ localization of OsRAA1transcript in wild-type rice with an antisense probe.B,Longitudinal section of young root with lateral root.C,Longitudinal section of young root with lateral root primordium.D,Longitudinal section of young shoot,including the junction part between shoot and roots.E,Longitudinal section of young spike.F,Longitudinal sections of root tip.G,Details of young root meristem zone.b,e,and g are the control sections with a sense probe of OsRAA1corresponding to B,E,and G sections,respectively.C and D photos were taken after mounting of slides using resin,so signals are blue.The remaining photos were taken before mounting of the slide,therefore,signals are brown.Overexpression of OsRAA1Controls Rice Root Developmentinto rice plants.The transgenic plants showed the patterns of GUS staining in the roots,which are similar to the data of in situ hybridization described above.Figure 3A showed that strong signals were detected in lateral roots and their primordia.It was clear that there were staining signals of GUS activity in the division and elongation zones of the root apex,while there was no signal detected in root cap (Fig.3B).GUS activity appeared in the palea/lower palea vascular strands (Fig.3C).The conjugated part between anther and filament also showed a strong signal in the GUS trans-genic plant driven by the OsRAA1promoter (Fig.3E).Although a few signals appeared at some parts of young leaves,they were irregular and unstable (Fig.3D).Therefore,mRNA of OsRAA1is present in the rapidly growing zones,which indicates its possible roles in the cell growth and/or division.Interestingly,its expression pattern in the root was similar to that of AUX1(Marchant et al.,2002)and TIR1and NAC1in Arabidopsis (Gray et al.,1999;Xie et al.,2000),whichare involved in auxin transport or signal transduction pathway.OsRAA1Overexpression in the Root Results in Reduced Growth of Primary Root,Increased Formation of Adventitious Roots,and Helix RootsThere were 20independent Ubi ::OsRAA1transgenic lines with characters of a tolerance to hygromycin and a positive staining of GUS marker to be obtained from the different transformed rice callus in the experiments.Longer flag leaves of the transgenic plants were a clear phenotype in comparison with the wild-type control without a hygromycin treatment.To investigate its role in root development,the seeds of 12independent transgenic lines with the longest flag leaveswereFigure 3.The localization of OsRAA1::GUS gene expression in the transgenic rice.A,A primary root with lateral root.B,Apical region of a primary root.C,Mature spikelet.D,Y oung shoot with some young leaves.E,Floral organs of a spikelet.Arrow is a morphogenesis site of lateral root with GUSactivity.Figure 4.The expression pattern of OsRAA1and the phenotype of root in the Ubi ::OsRAA1overexpression transgenic rice.A,Northern-blot anal-ysis for a representative Ubi ::OsRAA1transgenic plant to show an over-expression.Ethidium bromide (EtBr)staining shows equal RNA loading.B,Statistical analysis of primary root growth in Ubi ::OsRAA1transgenic plant.More than 10seedlings were examined for each point.C,Roots of 12-d-old seedlings grown in the half-strength MS medium.CK,control.OsRAA1,Representative of Ubi ::OsRAA1transgenic line.D,Mature roots at flowering stage.E,The wild-type plant roots (CK),transgenic line 8(OsRAA1-8),and transgenic line 11(OsRAA1-11)at 9d after germination in the half-strength MS medium.Arrow is a primary root.Ge et al.harvested.More than50seeds of these lines were germinated in the half-strength MS medium with75mg L21hygromycin,respectively.Leaves of these seedlings were cut and stained with5-bromo-4-chloro-3-indolyl-b-D-GlcUA(X-Gluc).Seedlings with positive staining signals were chosen for analysis of phenotypes(data not shown).The transgenic plants of Ubi::OsRAA1with positive GUS staining also showed a stronger hybrid-ization signal either in leaf or root before any signal appeared in the untransformed control in the northern-blot analysis(Fig.4A).Results of the northern blot suggested that OsRAA1displayed constitutive over-expression patterns in transgenic plants.As shown in Table I and Figure4,C to E,the transgenic plants had more adventitious roots than the untransformed con-trol plants under the same growth conditions.When the seedling grew for9d,a transgenic plant had two more roots than the wild-type control on the average. Moreover,roots of the transgenic plants were almost longer by0.5cm.At the same time,primary roots in transgenic rice were shorter than that of the wild-type control(Table I).It was also observed that although the lateral roots of primary roots in the transgenic plants were shorter than those of the wild-type control plant, the lateral roots of the remaining roots were much longer(Fig.4C).This suggests that OsRAA1may pro-mote formation of the lateral roots.When the plants developed to the heading stage,the transgenic plants of Ubi::OsRAA1had grown more roots than the wild-type control(Fig.4D).Besides that,another clear root phenotype with a helix appeared in the transgenic plant.In representative lines,such as OsRAA1-8and OsRAA1-11,the primary roots formed a helix to various extents,while the wild-type plants had a normal pri-mary root under the same conditions(Fig.4E).The phenotypes,such as reduced growth of primary root and increased adventitious roots and lateral roots,are very similar to that of overexpression of TIR1and NAC1 in Arabidopsis(Gray et al.,1999;Xie et al.,2000).Constitutive Expression of OsRAA1Results in Longer Leaves and FilamentsWhen the transgenic plants of Ubi::OsRAA1grew for 2weeks after germinating from a solution of hygro-mycin(75mg L21),they were transferred into the soil and then cultured in a greenhouse.The OsRAA1gene expressed constitutively in leaf and root in the trans-genic plants.During thefirst month after transfer,the transgenic plants grew more slowly than the wild-type controls without a hygromycin treatment.But just before the booting stage,the leaves of the transgenic plant were longer than those of the wild-type control. Especially at the heading stage,theflag leaves of the transgenic plants were distinguished as longer than those of the control plants.As shown in Table II and Figure5A,theflag leaves of the transgenic plants were about44cm(up to60cm in some independent lines)in length on the average,while those of the wild-type controls were about31cm.The leaf length of transgenic plants was1.4times longer than the control.The results of a scan electronic microscope showed that silica cell length of the transgenic plant was longer than that of the control,which was supported by statistical tests (P,0.05;Fig.5D).There werefive silica cells in the limited area in theflag leaf of the transgenic plants on the average,while six cells appeared at the same size area in the wild-type control(Fig.5,B and C).In other words,the cell length of transgenic plants was1.2times larger than the wild-type control based on the scan electronic microscope data.The difference between the wild-type control and the transgenic plant reached a significant level in statistics(P,0.05;Table II).It was suggested that the length increase offlag leaves in the transgenic plant might be caused by both extension of cells and an increase in cell numbers.Extension of cells, however,contributed more than increase of cell num-bers to leaf extension in transgenic plants. Abnormalflorets appeared in the spikes of the transgenic plant(Fig.5,F and G).The yellow and plump anthers of the wild-type control plant were just above penniform carpels at that stage(Fig.5E).Con-versely,stamens of the transgenic plants with OsRAA1 constitutive expression resulted in abnormally longer filaments with white and shrunken anthers(Fig.5,F and G).Actually,somefilaments were too long to be peeled off from the palea;they curved and attached tightly to the palea.Auxin Regulates the Transcription of the OsRAA1Gene Based on the AuRE sequence in OsRAA1promoter, the expression patterns in roots,and the phenotypesTable I.The comparative analysis of root numbers between thetransgenic plants and the wild-type controlWild-TypeControlUbi::OsRAA1PRoot numbers 6.0861.567.8262.48*0.0064Root numbers(.0.5cm)4.1761.71 6.9162.67* 1.35E–4Asterisks indicate the significance of difference between the controland the Ubi::OsRAA1transgenic plant populations as determined byrepeated-measures analysis of variance(two samples t test proceededby Origin6.0;P,0.05).The numbers are the mean6SE.Table II.The comparative analysis of leaf length between thetransgenic plants and the wild-type controlWild-TypeControlUbi::OsRAA1PLength of aflag leaf(cm)31.6464.7944.5368.13* 4.76E–10Length of a lastsecond leaf(cm)49.3868.4158.9665.03* 2.63E25Asterisks indicate the significance of difference between the controland the Ubi::OsRAA1transgenic plant populations as determined byrepeated-measures analysis of variance(two samples t test proceededby Origin6.0;P,0.05).The numbers are the mean6SE.Overexpression of OsRAA1Controls Rice Root Developmentof transgenic plants with constitutive expression of OsRAA1,we hypothesize that expression of OsRAA1gene is regulated by auxin.Northern blot showed that the OsRAA1mRNA was increased from treatment of 1025M IAA.More than double expression was induced by the treatment of 1024M IAA (Fig.6A).The GUS staining data of the OsRAA1::GUS transgenic plant showed that auxin induced a stronger signal in the transgenic plant,while a weaker blue signal appeared in the untreated control (Fig.6B).Suppression of the inhibitor of auxin polar transport on GUS staining clearly occurred as the treatment time went on (Fig.6B).The inhibitor experiment may support an explanation that decrease of endogenous auxin weakened GUS expression-driven OsRAA1promoter.The results sug-gested that expression of the OsRAA1gene in nature is induced by auxin.The effect of auxin on root development was ob-served (Fig.6).Interesting phenotypes occurred in the wild-type roots treated with 1-napthaleneacetic acid (NAA).Growth of the roots was strongly inhibited by auxin as compared with untreated wild-type control (Fig.6,C and D;Table III).The numbers of adventitious roots,however,increased up to 11in a treated seedling plant.In the untreated control,there were five adven-titious roots under the same conditions (Table III).All of the treated plants had helix-like primary roots (Fig.6D).The phenotypes were similar to those status in tomato that auxin stimulated lateral root growth at a concen-tration at which primary root growth was inhibited (Muday and Haworth,1994).In the Ubi ::OsRAA1transgenic plant,results of auxin treatment showed that a promotion role on the adven-titious root initiation induced by IAA was more distin-guished than that in the wild-type control (Fig.7A).However,the adventitious root initiation responses to 9-hydroxyfluorene-9-carboxylic acid (HFCA),a polar auxin transport inhibitor,between the transgenic plants and the wild-type control exhibited similar phenotype (Fig.7B).Results of auxin level determined showed that IAA level either in shoot or root was obviously higher in the transgenic plant of Ubi ::OsRAA1than that in the wild-type control (Fig.8).And IAA of the transgenic shoot was 2.8times greater than the wild-type control,while those of the root were 1.9times greater.It suggested overexpression of OsRAA1resulted in accu-mulating a higher level of IAA in the transgenic plant.It is well known that gravitropism is a phenomenon mainly regulated by auxin.The seedlings were re-oriented horizontally in the darkness to check their gravitropic response.Until reoriented for 3h,any gravitropic response of the overexpression line was not detected,while the wild-type control showed a distinct response (Fig.9,A,B,and D).In fact,the transgenic lines with extreme overexpression com-pletely lost gravitropic response until reoriented for 20h.The kinetics of gravitropic curvature showed a vigorous graviresponse from 3h after gravistimula-tion in the transgenic plant (Fig.9D).Results inFigureFigure 5.The phenotypes of Ubi ::OsRAA1constitutive expression transgenic rice plant.A,Flag leaf of wild-type control plant (left)and the Ubi ::OsRAA1transgenic plant (right).B,Silica cells of flag leaf of wild-type control plant.C,Silica cells of flag leaf of the transgenic plant.D,Statistical analysis of the length of silica cells in the flag leaves (P ,0.05;two samples t test proceeded by Origin 6.0).More than 50cells were examined for each bar.E,Flowers of wild-type control plant.F and G,The transgenic plant with different lines (D–F)to show longerfilaments.Figure 6.OsRAA1expression is regulated by auxin.A,Northern-blot analysis for OsRAA1expression treated with IAA of different concen-tration.Ethidium bromide staining (EtBr)shows equal RNA loading in the blot.The bar shows a relative amount of the gene expression at the bottom.B,Effect of GUS staining on treatment of 1m M NAA (no.2)and water as a control (no.1)and on treatment of the auxin polar transport inhibitor (HFCA,0.5m M )for 0,1,2,and 4h (corresponding to nos.3,4,5,and 6,respectively).Data of auxin (nos.1and 2)and HFCA (nos.3–6)were from different experiments.C,Roots of wild-type plant (14d).D,Effect of NAA (1m M )on root growth of the wild-type plant.The seedling was incubated for 14d after germination.Arrows show primary roots.Ge et al.。

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