|
|
|
|
|
| Arsenic Distribution, Species, and Its Effect on Maize Growth Treated with Arsenate |
| CI Xiao-ke, LIU Hua-lin, HAO Yu-bo, LIU Peng, DONG Shu-ting |
1.State Key Laboratory of Crop Biology, Shandong Agricultural University, Tai’an 271018, P.R.China
2.Circulation Industry Promotion Center, Ministry of Commerce, Beijing 100731, P.R.China
3.Institute of Crop Sciences, Chinese Academy of Agricultural Sciences, Beijing 100081, P.R.China |
|
|
|
摘要 A pot experiment was conducted to investigate the effect of different arsenic (As) levels on maize (Zea mays L.) growth and As accumulation and species in different parts of maize plants, as a guideline for production of maize in As-polluted areas with the objective of preventing As from entering the food chain, and improving understanding of the mechanisms of effect of As on plant. Zhengdan 958 was grown at five As levels added to soil (0, 12.5, 25, 50, and 100 mg kg-1 As). As concentration in maize tissues increased in the order of grain<stalk<leaf<<root. The As concentration in maize grain exceeded the maximum permissible concentration of 0.7 mg kg-1 in China at levels of 50 and 100 mg kg-1. As species were presented in root, stalk, and grain, but organic As was the major As species identified in the grain. Maize plants were able to reduce arsenate to arsenite. Low As levels of 12.5 and 25 mg kg-1 improved maize growth and grain nutrition quality, while high levels of As 50 or 100 mg kg-1 inhibited them. Yield reduction at high As levels resulted mainly from reduced ear length, kernel number per row, and kernel weight.
Abstract A pot experiment was conducted to investigate the effect of different arsenic (As) levels on maize (Zea mays L.) growth and As accumulation and species in different parts of maize plants, as a guideline for production of maize in As-polluted areas with the objective of preventing As from entering the food chain, and improving understanding of the mechanisms of effect of As on plant. Zhengdan 958 was grown at five As levels added to soil (0, 12.5, 25, 50, and 100 mg kg-1 As). As concentration in maize tissues increased in the order of grain<stalk<leaf<<root. The As concentration in maize grain exceeded the maximum permissible concentration of 0.7 mg kg-1 in China at levels of 50 and 100 mg kg-1. As species were presented in root, stalk, and grain, but organic As was the major As species identified in the grain. Maize plants were able to reduce arsenate to arsenite. Low As levels of 12.5 and 25 mg kg-1 improved maize growth and grain nutrition quality, while high levels of As 50 or 100 mg kg-1 inhibited them. Yield reduction at high As levels resulted mainly from reduced ear length, kernel number per row, and kernel weight.
|
|
Received: 09 January 2011
Accepted:
|
| Fund: This study was supported by the 973 Program of China (2006CB10701-11), the National Natural Science Foundation of China (30871476), the Agro-Scientific Research Fund from the Ministry of Agriculture, China (NYHYZX07-003), t h e P r o j e c t f o r H i g h - Yi e l d i n g C r o p , C h i n a (2006BADOZA09), and the Project for Improved Variety (2007lucainong100). |
|
Corresponding Authors:
Correspondence DONG Shu-ting, Tel: +86-10-8241591, E-mail:stdong@sdau.edu.cn
E-mail: stdong@sdau.edu.cn
|
| About author: CI Xiao-ke, E-mail: xkc_99@yahoo.com.cn; LIN Hua-lin, E-mail: Liuhualin@mofcom.gov.cn; |
Cite this article:
CI Xiao-ke, LIU Hua-lin, HAO Yu-bo, LIU Peng, DONG Shu-ting.
2012.
Arsenic Distribution, Species, and Its Effect on Maize Growth Treated with Arsenate. Journal of Integrative Agriculture, 12(3): 416-423.
|
| [1]Aldrich M V, Peralta-Videa J R, Parsons J G, Gardea-Torresday J L. 2007. Examination of arsenic (III) and (V) uptake by the desert plant species mesquite (Prosopis spp.) using X-ray absorption spectroscopy. Science Total Environment, 379, 249-255. [2]Abedin M J, Feldmann J, Meharg A A. 2002. Uptake kinetics of arsenic species in rice plants. Plant Physiology, 128, 1120-1128. [3]Burló F, Guijarro I, Carbonell-Barrachina A A, Valero D, Martínez-Sánchez F. 1999. Arsenic species: effects on and accumulation by tomato plants. Journal of Agricultural and Food Chemistry, 47, 1247-1253. [4]Cai Y, Georgiadis M, Fourqurean J W. 2000. Determination of arsenic in seagrass using inductively coupled plasma mass spectrometry. Spectrochim Acta (B), 55, 1411-1422. [5]Cao J, Huang R D, Jiang W C, Cao Z Q. 2005. Effect of heavy metal lead and cadmium on grain quality of maize. Journal of Shenyang Agricultural University, 36, 218-220. (in Chinese) [6]Carbonell-Barrachina A A, Aarabi M A, DeLaune R D, Gambrell R P, Patrick W H. 1998. The influence of arsenic chemical form and concentration on Spartens patens and Spartina alterinflora growth and tissue arsenic concentration. Plant Soil, 198, 33-43. [7]Carbonell-Barrachina A A, Burló F, Valero D, López E, Martínez-Romero D, Martínez-Sánchez F. 1999. Arsenic toxicity and accumulation in turnip as affected by arsenic chemical speciation. Journal of Agricultural Food Chemistry, 47, 2288-2294. [8]Carbonell-Barrachina A A, García E, Sánchez Soriano J, Aracil P, Burló F. 2002. Effects of raw materials, ingredients, and production lines on arsenic and copper concentrations in confectionery products. Journal of Agricultural Food Chemistry, 50, 3738-3742. [9]Ci X K, Liu H L, Hao Y B, Zhang J W, Liu P. 2012. The effect of arsenic in soil on plant growth and grain quality of maize cultivar Jingzinuo 218. Journal of Integrative Agriculture. (in press) [10]Dahmani-Muller H, van Oort F, Gélie B, Balabane M. 2000. Strategies of heavy metal uptake by three plant species growing near a metal smelter. Environmental Pollution, 109, 231-238. [11]Dhankher O P, Li Y J, Rosen B P, Shi J, Salt D, Senecoff J F, Sashti N A, Meagher R B. 2002. Engineering tolerance and hyperaccumulation of arsenic in plants by combining arsenate reductase and l-glutamylcysteine synthetase expression. Nature Biotechnology, 20, 1140-1145. [12]Dong S T. 2006. Variation of physiological characteristics of maize during variety replacement. Eco-Physiology and Formation of Yield and Quality in Maize. Higher Education Press, Beijing. (in Chinese) [13]Gulz P, Gupta S K. 2000. Arsenaufnahme von Kulturpflanzen. Agrarforschung, 7, 360-365. [14]Gulz P A, Gupta S K, Schulin R. 2005. Arsenic accumulation of common plants from contaminated soils. Plant Soil, 272, 337-347. [15]He Z. 1985. Analysis Technique for Grain of Cereal and Oils. China Agriculture Press, Beijing. (in Chinese) He M, Yang J. 2002. Characteristic of binding forms of arsenic in polluted rice seed and their stability. Chinese Journal of Applied Ecology, 13, 1141-1144. (in Chinese) [16]Jin Y L, Liang C R, He G L. 2003. Investigation to the distribution of local arsenic poisoning in China. Health Research, 32, 519-540. [17]Juhasz A L, Smith E, Weber J, Rees M, Rofe A, Kuchel T, Sansom L, Naidu R. 2006. In vivo assessment of arsenic bioavailability in rice and its significance for human health risk assessment. Environment Health Perspect, 114, 1826-1831. [18]Koch I, Wang L, Ollson C A, Cullen W R, Reimer K J. 2000. The predominance of inorganic arsenic species in plants from Yellowknife, Northwest Territories, Canada. Environment Science Technology, 34, 22-26. [19]Kuehnelt D, Lintschinger J, Goessler W. 2000. Arsenic compounds in terrestrial organisms. IV. Green plants and lichens from an old arsenic smelter site in Austria. Applied Organomet Chemistry, 14, 411-420. [20]Malouf R B, Hoseney R C. 1992. Wheat hardness I. A method to measure endosperm tensile strength using tablets made from wheat flour. Cereal Chemistry, 69, 164-168. [21]Meharg A A, Hartley-Whitaker J. 2002. Arsenic uptake and metabolism in arsenic resistant and nonresistant plant species. New Phytology, 154, 29-43. [22]Odanaka Y, Tsuchiya N, Matano O, Goto S. 1985. Characterization of arsenic metabolites in rice plant treated with DSMA (disodium methanearsonate). Journal of Agricultural and Food Chemistry, 33, 757-763. [23]Peng M, Gao M, Abdel-Aal E S M, Hucl P, Chibbar R N. 1999. Separation and characterization of A-and B-type starch granules in wheat endosperm. Cereal Chemistry, 76, 375-379. [24]Peterson P J, Girling C A, Benson L M, Zieve R. 1981. Metalloids. In: Lepp N W, ed., Effect of Heavy Metal Pollution on Plants. vol. 1. Applied Science, London. Requejo R, Tena M. 2006. Maize response to acute arsenic toxicity as revealed by proteome analysis of plant shoots. Proteomics, 6, 156-162. [25]SAS Institute. 2009. SAS system for windows. ver. 9.1.3. SAS Inst., Inc. Cary. NC. Shao Y, Jiang L N, Li W C, Li C X, Li X L. 2009. Toxic effects of As and Pb to wheat seedling and scanning electron microscopic observation on nether epidermis of leaves. Acta Agriculturae Boreali-Occidentalis Sinica, 18, 133-138. (in Chinese) [26]Sharples J M, Meharg A A, Chambers S M, Cairney J W G. 2000. Evolution: Symbiotic solution to arsenic contamination. Nature, 404, 951-952. [27]Smedley P L, Kinniburgh D G. 2002. A review of the source, behaviour and distribution of arsenic in natural waters. Applied Geochemistry, 17, 517-568. [28]Smith E, Juhasz A L, Weber J, Naidu R. 2008. Arsenic uptake and speciation in rice plants grown under greenhouse conditions with arsenic contaminated irrigation water. Science Total Environment, 392, 277-283. [29]Stoeva N, Berova M, Zlatev Z. 2003. Physiological response of maize to arsenic contamination. Biologia Plantarum, 47, 449-452. [30]Tamaki S, Frankenberger W T. 1992. Environmental biochemistry of arsenic. Reviews of Environment Contamination Toxicology, 124, 79-110. [31]Wang Y, Guo H, Yan S. 2004. Geochemical Evolution of Shallow Groundwater Systems and Their Vulnerability to Contaminants: A Case Study at Datong Basin, Shanxi Province, China. Science Press, Beijing. (in Chinese) Xu XY, McGrath S P, Zhao F J. 2007. Rapid reduction of arsenate in the medium mediated by plant roots. New Phytology, 176, 590-599. [32]Yong G. 1984. Scanning Electron Microscooe Biological Sample Preparation. Science Press, Beijing. (in Chinese) Zavala Y J, Gerads R, Gürleyük H, Duxbury J M. 2008. Arsenic in rice: II. Arsenic speciation in USA grain and implications for human health. Environment Science Technology, 42, 3861-3866. [33]Zhang W, Cai Y, Tu C, Ma LQ. 2002. Arsenic speciation and distribution in an arsenic hyperaccumulating plant. Science Total Environment, 300, 167-177. [34]Zhou Y. 2003. Methods for Material Analysis. Mechanical Industry Press, Beijing. (in Chinese) |
| No Suggested Reading articles found! |
|
|
Viewed |
|
|
|
Full text
|
|
|
|
|
Abstract
|
|
|
|
|
Cited |
|
|
|
|
| |
Shared |
|
|
|
|
| |
Discussed |
|
|
|
|
