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Study on Cadmium Tolerance of Seed Germination and Seedlings Growth of Different Rice Varieties

2015-11-08GuiyuanMENGMengyangLlJingZHOUTingTANGShuyingZENG

Agricultural Science & Technology 2015年11期
关键词:幼苗水稻品种

Guiyuan MENG,Mengyang Ll,Jing ZHOU*,Ting TANG,Shuying ZENG

1.College of Agriculture&Biotechnology,Hunan University of Humanities,Science and Technology,Loudi 417000,China;

2.Collaborative Innovation Center for Farmland weeds control of Hunan Province,Loudi 417000,China

Study on Cadmium Tolerance of Seed Germination and Seedlings Growth of Different Rice Varieties

Guiyuan MENG1,2,Mengyang Ll1,Jing ZHOU1,2*,Ting TANG1,Shuying ZENG1

1.College of Agriculture&Biotechnology,Hunan University of Humanities,Science and Technology,Loudi 417000,China;

2.Collaborative Innovation Center for Farmland weeds control of Hunan Province,Loudi 417000,China

The research used bioassay method to explore seed tolerance of Cd in terms of seed germination and seedling growth.Specifically,12 rice varieties of three types were investigated under Cd stress,covering germination rate,shooting index,vigor index,seedling and shoot lengths,and fresh weights.The results showed that as Cd concentration grew,seed germination and seedling growth kept increasingly inhibited;germination index,vigor index,root length,shoot length and fresh weights went down;inhibition effects on seed germination and seedling growth were conventional rice>two-line hybrid rice>three-line hybrid rice.Shenyou 9588,Tianyou 998,Chuanxiang 8,and Y Liangyou 1 performed strongly in Cd tolerance;C Liangyou 651,Nei 5 You 263,Xiangwanxian 16,Huanghuazhan,Xiangwanxian 13,and Zhunliangyou 527 performed poorly in Cd tolerance,and Cd tolerance of rest treatments were moderate.

Variety types;Rice seed;Germination;Seedling growth;Cadmium tolerance

I n Hunan Province,it is a key issue that heavy metal pollution is increasingly deteriorating with industry and development and mineral resources exploitation.For example,Cd,Hg and Pb have become pollutants which are the most dangerous in farmland,posing threats to agricultural production and food safety[1]and more attention is paid to Cd which is easily absorbed by plants and enriches fast in human bodies[2].Rice is the second most-produced cereal after wheat and the most-consumed cereal in China and rice safety has been closely linked to human health.In Hunan,Cd is a most common heavy metal in farmland soils.Specifically,Cd contents of early-season rice and late-season rice reach as high as 5.33 and 9.36 mg/kg[3-4]in severely contaminated ar eas.In Lengshuijiang,Cd content of contaminated soils tends to be volatile in the range of 2.5-181.6 mg/kg.

Currently,much more attentions have been drawn by remediation of heavy-metal polluted soils by superenrichment plants.For instance,Wang and Liu et al.researched that absorption and accumulation on Cd are different upon rice varieties[5-11].The re search on Cd-tolerance of rice seeds is basis of selection and breeding of Cd-tolerant varieties,and the test on heavy-metaltolerance during seed germination stage is applied globally[12-14].Therefore,it is of great importance for selection and cultivating Cd-tolerant rice varieties to explore differences of rice seeds in Cd tolerance.The research investigated effects of Cd stress on seed germination and seedling growth based on 12 rice varieties,providing references for selective breeding of Cd-tolerant rice varieties and for selection of rice varieties with low-absorption capacity of Cd in contaminated farmlands.

Materials and Methods

Test materials

The test materials included local rice,such as Huanghuazhan,Xiangwanxian 13,Xiangwanxian 16,Nongxiang 18;two-line hybrid rice,such as C Liangyou 651,Fengliangyou 4,Zhunliangyou 527,and Y Liangyou 1,and three-line hybrid rice such as Shenyou 9588,Tianyou 998,Chuanxiang 8,Nei 5 You 263.

Test design and treatment

The test was conducted in College of Agriculture&Biotechnology agronomy laboratory of Hunan University of Humanities,Science and Technology. At first,fully-grown rice seeds were selected and washed clean,and then sterilized with 0.5%NaClO for 20 min. Subsequently,the seeds were washed repeatedly and sealed with bags.It is notable that a few holes were pricked on bag bottoms.The seeds were merged for 12 h and collected and drain off for 12 h,which were repeated twice.Then,the seeds were collected and placed into culture dishes containing 10 ml 0.5 mmol/L CdCl2with double-layer filter paper.Every culture dish contained 50 seeds.Additionally,the treatment with distilled water was taken as a control and other treatments were repeated three times.Besides,seed culture was conducted at 26℃for 5 d,and the seeds were illuminated for 14 h and in darkness for 10 h every day.The culture solution was supplemented once every day during culture period.

Measured items and methods

During test period,the number of seed shoots was observed and recorded every day and germination standard was determined when seedling grew the length half of the seed length to compute germination rate.Furthermore,root length,shoot length,fresh weights of root and shoot of seedlings were measured on the 6thd.Subsequently,germination index,vigor index,stress index and comprehensive inhibition effect were calculated of different rice varieties[9].

Germination rate=(The number of germinated seed/The number of test seeds)×100%;

Germination index=Σ(The number of germinated shoots on the specific day/Total germination days)

Vigorindex=The length of seedling length(cm)×Germination index;

Stress index=1-(Treatment value/ Control value).

The comprehensive inhibition effect refers to averaged stress index of seed of the same rice variety.

Data processing

The test data were processed with Excel 2003 and DPS 3.0.

Table 1 Effects of Cd on seed germination rate and index of different rice varieties

Results and Analysis

Effects of Cd on seed germination,germination index and vigor index of different rice varieties

As shown in Table 1,seeds of different rice varieties kept decreasing upon Cd concentration and the decrease of three-line hybrid rice proved the slowest,followed by two-line hybrid rice and common hybrid rice,reducingby26.49%,63.41%and74.53%,respectively,than that of the control,when Cd concentration reached 1.25 mmol/L.Specifically,when Cd concentration was 0.5 mmol/L,germination rates of most seeds maintained higher than 90.0%,except of Huanghuazhan and Chuanxiang 8(below 85.00%),which indicated that most seeds would not be inhibited in germination by Cd at the concentration of 0.5 mmol/L.However,seed germination rates declined in varying degrees as Cd concentration increased.For example,when Cd concentration grew to 1.0 mmol/L,germination rates of mostseeds dropped considerably,with exceptions of Zhunliangyou 527,Shenyou 9588 and Tianyou 998,which suggested that most rice seeds underwent Cd stress significantly of the concentration.In general,germination rates dropped faster of Xiangwanxian 13,Huanghuazhan,Xiangwanxian 16,showing poor tolerance capacity of Cd;germination rates of Shenyou 9588,Tianyou 998,Chuanxiang 8,and Zhunliangyou 527 decreased slowly under Cd stress at a high concentration,showing higher tolerance capacity;germination rates of rest varieties kept moderate.

As shown in Table 1,relative germination index declined in varying de-grees upon Cd concentrations.Specifically,with Cd concentration in the range of 0-1.0 mmol/L,relative germination rates of different rice varieties dropped slowly,which demonstrated that germination speed is less affected by Cd of the concentrations.When Cd concentration grew to 1.25 mmol/L,rice varieties differed significantly in germination index.For instance,germination indices of local rice and twoline hybrid rice went down by 10.78% and 8.17%than those of Cd at former concentration,and three-line hybrid rice reduced by 4.57%,which incorporated that germination index of threeline hybrid rice is less affected by Cd stress.Of the 12 varieties,Huanghuazhan,Xiangwanxian 13,Y Liangyou 1,Nei 5 You 263,C Liangyou 651,and Xiangwanxian 16 declined the most significantly in terms of germination indices,which proved that the varieties are poorly in Cd-tolerance.In contrast,Shenyou 9588,Tianyou 998,and Chuanxiang 8 dropped dramatically in the germination indices,indicating that the varieties perform better in Cd tolerance.The rest varieties kept moderate.

Table 2 Effects of Cd on seed vigor index of different rice varieties

Table 3 Effects of Cd on root and shoot lengths of different rice varieties

As shown in Table 2,vigor index of seeds declined in varying degrees upon Cd concentration.For example,when Cd concentration was lower than 1.0 mmol/L,vigor indices of the three rice varieties'seeds showed little differences,but seeds of local rice and two-line hybrid rice declined dramatically,which indicated that vigor indices of the varieties in the two classifications underwent Cd stress significantly,showing poor tolerance capacity. When Cd concentration grew to 0.5 mmol/L,vigor indices of the 12 rice varieties declined dramatically and the decreases slowed down when Cd concentration increased to 1.0 mmol/L. When Cd concentration enhanced to 1.25 mmol/L,the vigorindices of Huanghuazhan, Xiangwanxian 13,Nongxiang 18,Fengliangyou 4 and Xi-angwanxian 16 dropped considerably,which demonstrated that the varieties performed poorly in Cd tolerance.In contrast,Y Liangyou 1,Shenyou 9588,and Tianyou 998 performed better in Cd tolerance,whose vigor indices reached 5.78%,10.85%and 5.71% with Cd of 1.25 mmol/L,respectively.

Effects of Cd on the length of root and shoot of different rice varieties

As shown in Table 3,both of root and shoot lengths of rice seeds kept decreasing upon Cd concentration,and the higher Cd concentration,the higher inhibition.Specifically,average root lengths differed insignificantly under Cd stresses of different rice varieties,but root length reached maximum of three-line hybrid rice when Cd concentration reached 1.25 mmol/L,which indicated that the varieties performed better in Cd tolerance.In contrast,roots of local rice varieties were shorter,incorporating that the varieties performed poorly in Cd tolerance.On the other hand,shoot lengths from high to low were three-line hybrid rice,two-line hybrid rice and local rice. Generally speaking,with Cd concentration of 1.25 mmol/L,C Liangyou 651 and Shenyou 9588 proved the varieties performed well in Cd tolerance for root lengths reached over 0.4 cm,and Shenyou 9588,Tianyou 998,Nei 5 You 263,Chuanxiang 8,and Y Linagyou 1 also proved well in Cd tolerance,for shoot lengths all reached over 1.3 cm.Besides,root lengths of Huanghuazhan,Xiangwanxiang 13,Nongxiang 18,Fengliangyou 4 were below 0.1 cm,and except of the varieties above with better-grown shoots,shoot lengths of the rest rice varieties were all below 0.6 cm,which suggested that the seedlings are significantly influenced by Cd stresses.

Table 4 Effect of Cd stresses on fresh weight root and shoot of different rice varieties

Effects of Cd on seedlings fresh weight of different rice varieties

As shown in Table 4,fresh weights of seedlings and shoots both kept decreasing upon Cd concentra-tion,which incorporated that Cd stress has effects on seeds of different rice varieties.Although changes of root fresh weight differed insignificantly,the weights from high to low were threeline hybrid rice>two-line hybrid rice>common hybrid rice,with Cd concentration of 0.75 mmol/L.As for shoot fresh weight,the sequence from low to high was common rice<two-line hybrid rice<three-line hybrid rice,and the differences under Cd stress of 0.75 mmol/L were much significant.Specifically,under Cd stress of 1.25 mmol/L,fresh root weights of Shenyou 9588,Chuanxiang 8,and Fengliangyou 4 all kept over 0.3 mg and fresh shoot weights of Shenyou 9588,Tianyou 998,Nei 5 You 263 and Chuanxiang 8 maintained over 3.6 mg.These have demonstrated that seedings of all the rice varieties perform better in tolerance ofCd.In contrast,Huanghuazhan,Xiangwanxian 13,Xiangwanxian 16 and Nongxiang 18 kept below 0.1 mg in terms of both fresh root weight and shoot weight,which incorporated that seedlings of the varieties are significantly influenced by Cd stresses.

Comprehensive evaluations on inhibition effects of Cd on seed germination of different rice varieties

As shown in Table 5,Cd stress on seed germination and seedling growth was the most significant on common rice varieties,followed by two-line hybrid rice and three-line hybrid rice. Specifically,comprehensive inhibition effects were higher (over 0.50)on Huanghuazhan,Xiangwanxian 13,Xiangwanxian 16,C Liangyou 651,Zhunliangyou 527 and Nei 5 You 263,and insignificant (below 0.4)on Y Liangyou 1,Shenyou 9588,Tianyou 998,and Chuanxiang 8.Besides Cd stress on rest seeds kept moderate.

Results and Analysis

Cadmium is a non-essential element for plant growth,and even poses threats to plants if accumulates too much,preventing plant growth[15-16].The test indicated that under Cd stress,seed germination and seedling growth would be both inhibited;germination index,vigor index,root length,shoot length and fresh weights would go down;differences among rice varieties would increase.These coincide with researches available on rice and alfalfa[17-18],possibly caused by decline of activities of cell RNA and DNA and reduction of nucleic acid[19],or inhibited hydrolase vigor by Cd[12,15].

Nevertheless,Cd tolerance of plants,the comprehensive reflection,is under influence of multiple factors. Therefore,it is necessary for exploring seed tolerance of Cd to conduct a comprehensive evaluation on influential factors[20].The research investigated germination rate,shooting index,vigor index,root length,shoot length and fresh weightand the results showed that three-line hybrid rice performed better in terms of seed germination or seedling growth in Cd tolerance.Specifically,seed tolerance of Cd tends to be volatile upon rice varieties.Shenyou 9588,Tianyou 998,Chuanxiang 8,and Y Liangyou 1 performed strongly in Cd tolerance;C Liangyou 651,Nei 5 You 263,Xiangwanxian 16,Huanghuazhan,Xiangwanxian 13,and Zhunliangyou 527 performed poorly in Cd tolerance,and Cd tolerance of rest treatments were moderate.It is researched that Cd stress can be detoxicated by plants through fixing,complexing and antioxidase. Hence,tolerance differences in the research of 12 rice varieties require further exploration in the future.

[1]MELAUGL MJ,PARKER DR,Clarke JM.Metals and micronutrients-food safetyisues[J].Field Crops Research,1999,(60):143-163.

[2]FLORIJN P J,VAN BEUSICHEM M L. Uptake and distribution of cadmium in Maze Inbred Lines[J].Plant and soil,1993,150:25-32.

[3]HUANG DY(黄道友),CHEN HP(陈惠萍),GONG GT(龚高堂),et al.Cd pollution and countermeasures of dominant paddy soils in Hunan province(湖南省主要类型水稻土镉污染改良利用研究)[J]. Research of Agricultural Modernization(农业现代化研究),2000,21(6):364-370.

[4]WANG KR(王凯荣).Cd pollution and treatment countermeasures in China(我国农田镉污染现状及其治理利用对策)[J].Agro-Environmental Protection(农业环境保护),1997,16(6):274-278.

[5]WANG KR(王凯荣),GONG HQ(龚惠群).Differences of Cd absorbing and redistribution of rice varieties with two genotypes(两种基因型水稻对环境镉吸收与再分配差异性比较研究)[J].Agro-Environmental Protection(农业环境保护),1996,15(4):145-149.

[6]YANG JR(杨居荣),ZHA Y(查燕),LIU H(刘虹),et al.The distribution and chemical forms of Cd,Cu,and Pb in polluted seeds(污染稻、麦籽实中Cd、Cu、Pb的分布及其存在形态初探)[J].China Environmental Science(中国环境科学),1990,19(6):500-504.

[7]WU QT(吴启堂),CHEN L(陈卢),WANG GS(王广寿),et al.Differences on Cd uptake and accumulation among rice varieties and its mechanism (水稻不同品种对Cd吸收积累的差异和机理研究)[J].Acta Ecologica Sinica(生态学报),1999,19(1):104-107.

[8]LONG XL(龙小林),XIANg XZ(向珣朝),XU YF (徐艳芳),et al..Absorption,Transfer and Distribution of Cd in indica and japonica Rice under Cd Stress(镉胁迫下籼稻和粳稻对镉的吸收、转移和分配研究)[J].Chinese Journal of Rice Science(中国水稻科学),2014,28(2): 177-184

[9]TANG F(唐非),LEI M(雷鸣),TANG Z(唐贞),et al.Accumulation and dynamic distribution of Cd by rice varieties(不同>水稻品种对镉的积累及其动态分布)[J]. Journal of Agro-Environment Science(农业环境科学学报),2013,32(6):1092-1098

[10]ZHANG XZ(张锡洲),ZHANG HJ(张洪江),LI TX(李廷轩),et al.Differences in Cd-tolerance of rice and screening for Cd low-accumulation rice germplasm resources(水稻镉耐性差异及镉低积累种质资源的筛选)[J].Chinese Journal of Eco-Agriculture(中国生态农业学报),2013,21(11):1434-1440.

[11]LIU ZB(刘昭兵),JI XH(纪雄辉),PENG H(彭华),et al.Characteristics of Cd and Pb absorption and accumulation by rice at different growth stages and the differences between varieties (不同生育期水稻对Cd、Pb的吸收累积特征及品种差异)[J].Chinese Journal of Soil Science(土壤通报),2011,42(5): 1124-1130.

[12]HE JY(何俊瑜),REN YF(任艳芳),ZHU C (朱 诚),et al.Effects of cadmium stress on seed germination,seedling growth and amylase activities in rice(镉胁迫对不同水稻品种种子萌发、幼苗生长和淀粉酶活性的影响)[J].Chinese Journal of Rice Science(中国水稻科学),2008,22(4):399-404.

[13]Abedin M J,Meharg A A.Relative toxicity of arsenite and arsenate on germination and early seedling growth of rice(Oryza sativa L.)[J].Plant and Soil,2002,243:57-66

[14]HE JY(何俊瑜),REN YF(任艳芳),ZHOU GQ (周国强),et al.Study on cadmium tolerance of different varieties of Oryza sativa L.during seedgermination stage(不同水稻品种种子萌发期耐镉性的研究)[J].Acta Agriculturae Boreali-Sinica(华北农学报),2010,52(3):108-112.

[15]HE JY(何俊瑜),REN YF(任艳芳),ZHU C (朱诚),et al.Effects of cadmium stress on reactive oxygen species metabolism and antioxidant enzyme activities in Cd-sensitive mutant rice seedlings(镉胁迫对镉敏感水稻突变体活性氧代谢及抗氧化酶活性的影响)[J]. Ecology and Environment(生态环境),2008,17(3):1004-1008.

[16]CHENG WD(程旺大),YAO HG(姚海根),ZHANG GP(张国平),et al.Effect of cadmium on growth and nutrition metabolism in rice(镉胁迫对水稻生长和营养代谢的影响)[J].Scientia Agricultura Sinica(中国农业科学),2005,38(3):528-537.

[17]ZENG X(曾翔),ZHANG YZ(张玉烛),WANG KR (王凯荣),et al.Effects of cadmium on rice seed germination(镉对水稻种子萌发的影响)[J].Chinese Journal of Applied Ecology(应用生态学报),2007,18(7):1665-1668.

[18]HAN DH(韩多红),MENG HM(孟红梅),WANG J(王进),et al.Effect of Cd2+on physiological characteristics of alfalfa(镉对紫花苜蓿种子萌发等生理特性的影响)[J].Agricultural Research In the Arid Areas(干旱地区农业研究),2007,25(5):151-155.

[19]EUN S,YOUNG HS,LEE Y.Cadmium disturbs microtubule organization in the root meristem of Zea mays[J]. Physiol Plantarum,2000,110:357-365.

[20]AANREI AB,VERA IS,VIKTOR ET,et al.Genetic variability in tolerance to cadmium and accumulation of heavy metals in pea(Pisum sativum L.)[J].E-uphytica,2003,131:25-35.

[21]HALL J L.Cellular mechanisms for heavy metal detoxification and tolerance[J].Journal of Experimental Botany,2002,53(366):1-11.

Responsible editor:Xiaoxue WANG

Responsible proofreader:Xiaoyan WU

不同水稻品种种子萌发及幼苗生长耐镉性研究

孟桂元1,2,李梦阳1,周静1,2*,唐婷1,肖珑1,曾淑英1(1.湖南人文科技学院农业与生物技术学院,湖南娄底 47000;2.湖南省农田杂草防控技术与应用协同创新中心,湖南娄底417000)

为探明不同类型水稻品种种子萌发及幼苗生长耐Cd性差异,采用室内生物测定方法,研究了不同镉(Cd)胁迫处理对3种不同类型12个水稻品种种子的萌发率、发芽指数、活力指数、幼苗根长、芽长及其根芽鲜质量的影响。结果表明,随着镉离子浓度增加,各类型水稻品种种子萌发所受抑制作用明显增强,萌发率、发芽指数、活力指数、根芽长及其鲜重均表现呈下降趋势;不同类型水稻品种种子萌发及幼苗生长受抑制程度均表现以常规水稻品种>两系水稻品种>三系水稻品种。12个水稻品种中,深优9588、天优998、川香8号、Y两优1号等4个品种耐Cd性较强;C两优651、内5优263、湘晚籼16号、黄华占、湘13号、准两优527等6个品种耐Cd性相对较弱,其它为中等耐Cd品种。

品种类型;水稻种子;萌发;幼苗生长;耐镉性

湖南省娄底市科技计划项目(2014-1);杂交水稻国家重点实验室资助;湖南省高校农药无害化应用重点实验室资助。

孟桂元(1977-),男,湖南新邵人,副教授,博士,主要从事作物栽培与生理生态研究,E-mail:mengguiyuan@126.com。*通讯作者,助理研究员,在读博士,主要从事作物栽培与生理生态研究,E-mail:kiki010206@163.com。

2015-08-08

Supported by Loudi City Science and Technology Project(2014-1);State Key Laboratory of Hybrid Rice;Key Laboratory of Pesticide Harmless Application of Hunan Province.

*Corresponding author.E-mail:kiki010206@163.com

Received:August 8,2015 Accepted:October 10,2015

修回日期 2015-10-10

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