Abstract
The influx of arsenate, arsenite and dimethyl arsinic acid (DMA) were studied in 7-day-old excised maize roots (Zea mays L.), and then related to arsenate, arsenite and DMA toxicity. Arsenate, arsenite and DMA influx was all found concentration dependent with significant genotypic differences for arsenite and DMA. Arsenate influx in phosphate starved plants best fitted the four-parameter Michaelis–Menten model corresponding to an additive high and low affinity uptake system, while the uptake of phosphate replete plants followed the two parameter model of Michaelis–Menten kinetics. Arsenite influx was well described by the two parameter model of ‘Michaelis–Menten’ kinetics. DMA influx was comprised of linear phase and a hyperbolic phase. DMA influx was much lower than that for arsenite and arsenate. Arsenate and DMA influx decreased when phosphate was given as a pre-treatment as opposed to phosphate starved plants. The +P treatment tended to decrease influx by 50% for arsenate while this figure was 90% for DMA. Arsenite influx increasing slightly at higher arsenite concentrations in P starved plants but at lower arsenite concentrations, there was little or no difference in arsenite uptake. Low toxicity was found for DMA on maize compared with arsenate and arsenite and the relative toxicity of arsenic species was As(V) > As(III) >> DMA.
Similar content being viewed by others
References
Abedin MJ, Meharg AA (2002) Relative toxicity of arsenite and arsenate on germination and early seedling growth of rice (Oryza sativa L.). Plant Soil 243:57–66
Abedin MJ, Feldmann J, Meharg AA (2002) Uptake kinetics of arsenic species in rice (Oryza sativa L.) plants. Plant Physiol 128:1120–1128
Bleeker PM, Hakvoort HWJ, Bliek M, Souer E, Schat H (2006) Enhanced arsenate reduction by a CDC25-like tyrosine phosphatase explains increased phytochelatin accumulation in arsenate-tolerant Holcus lanatus. Plant J 45:917–929
Burló F, Guijarro I, Carbonell-Barrachina AA, Valero D, Martínez-Sánchez F (1999) Arsenic species: effects on and accumulation by tomato plants. J Agric Food Chem 47:1247–1253
Carbonell AA, Aarabi MA, DeLaune RD, Gambrell RP, Patrick WH (1998) Arsenic in wetland vegetation: availability, phytotoxicity, uptake and effects on plant growth and nutrition. Sci Total Environ 217:189–199
Carbonell-Barrachina AA, Aarabi MA, DeLaune RD, Gambrell RP, Patrick WH (1998) The influence of arsenic chemical form and concentration on Spartina patens and Spartina alterniflora growth and tissue arsenic concentration. Plant Soil 198:33–43
Carbonell-Barrachina AA, Burlo F, Valero D, Lopez E, Martinez-Romero D, Martinez-Sanchez F (1999) Arsenic toxicity and accumulation in turnip as affected by arsenic chemical speciation. J Agric Food Chem 47:2288–2294
Dasgupta T, Hossain SA, Meharg AA, Price AH (2004) An arsenate tolerance gene on chromosome 6 of rice. New Phytol 163:45–49
De Koe T, Jaques NMM (1993) Arsenate tolerance in Agrostis castellane and Agrostis delicatula. Plant Soil 151:185–191
Geng CN, Zhu YG, Hu Y, Williams P, Meharg AA (2006) Arsenate causes differential acute toxicity to two P-deprived genotypes of rice seedlings (Oryza sativa L.). Plant Soil 279:297–306
Hartley-Whitaker J, Ainswort G, Meharg AA (2001) Copper and arsenate induced oxidative stress in Holcus lanatus L. clones with differential sensitivity. Plant Cell Environ 24:713–722
Hood RD (1985) Cacodylic acid: agricultural uses, biologic effects, and environmental fate. V. A. Monograph. 171 pp Avail. from Sup Documents, US Government Printing Office, Washington, DC, 20402
Jamali MK, Kazi TG, Arain MB, Afridi HI, Jalbani N, Adil RS (2006) The correlation of total and extractable heavy metals from soil and domestic sewage sludge and their transfer to maize (Zea mays L.) plants. Toxicol Environ Chem 88:619–632
Marcus-Wyner L, Rains DW (1982) Uptake, accumulation, and translocation of arsenical compounds by cotton. J Environ Qual 11:715–719
Marin AR, Masscheleyn PH, Patrick WH (1992) The influence of chemical form and concentration of arsenic on rice growth and tissue arsenic concentration. Plant Soil 139:175–183
Meharg AA, Hartley-Whitaker J (2002) Arsenic uptake and metabolism in arsenic resistant and non-resistant plant species. New Phytol 154:29–43
Meharg AA, Jardine L (2003) Arsenite transport into paddy rice (Oryza sativa) roots. New Phytol 157:39–44
Meharg AA, Macnair MR (1992) Suppression of the high-affinity phosphate-uptake system—a mechanism of arsenate tolerance in Holcus lanatus L. J Exp Bot 43:519–524
Qin J, Rosen BP, Zhang Y, Wang G, Franke S, Rensing C (2006) Arsenic detoxification and evolution of trimethylarsine gas by a microbial arsenite S-adenosylmethionine methyltransferase. Proc Natl Acad Sci USA 103:2075–2080
Raab A, Feldmann J, Schat H, Meharg AA (2005) Uptake, translocation and transformation of arsenate and arsenite in sunflower (Helianthus annuus)—Part I: formation of arsenic–phytochelatin complexes during exposure to high arsenic concentrations. New Phytol 168:551–558
Raab A, Ferreira K, Meharg AA, Feldmann J (2007a) Can arsenic-phytochelatin complex formation be used as an indicator for toxicity in Helianthus annuus? J Ex Bot 58:1333–1338
Raab A, Williams PW, Meharg AA, Feldmann J (2007b) Uptake and translocation of inorganic and methylated arsenic species by plants. Environ Chem 4:197–203
Rahman MA, Hasegawa H, Rahman MM, Islam MN, Miah MAM, Tasmen A (2007) Effect of arsenic on photosynthesis, growth and yield of five widely cultivated rice (Oryza sativa L.) varieties in Bangladesh. Chemosphere 67:1072–1079
Sadiq M (1986) Solubility relationships of arsenic in calcareous soils and its uptake by corn. Plant Soil 91:241–248
US Environmental Protection Agency EPA (2005) Mode of carcinogenic action for cacodylic acid (dimethylarsinic acid, DMAV) and recommendations for dose response extrapolation. Available at: http://www.epa.gov/oppsrrd1/reregistration/cacodylic_acid/dma_moa.pdf
US Environmental Protection Agency EPA (2006) Reregistration eligibility decision for MSMA, DSMA, CAMA, and cacodylic ccid. Available at: http://www.epa.gov/pesticides/reregistration/REDs/organic_arsenicals_red.pdf
Wang J, Zhao FJ, Meharg AA, Raab A, Feldmann J, McGrath SP (2002) Mechanisms of arsenic hyperaccumulation in Pteris vittata. uptake kinetics, interactions with phosphate, and arsenic speciation. Plant Physiol 130:1552–1561
Williams PN, Price AH, Raab A, Hossain SA, Feldmann J, Meharg AA (2005) Variation in arsenic speciation and concentration in paddy rice related to dietary exposure. Environ Sci Technol 39:5531–5540
Woolson EA, Axley JH, Kearney PC (1971) Correlation between available soil arsenic, estimated by six methods, and response of corn (Zea mays L.). Soil Sci Soc Am Proc 35:101–105
Wysocki R, Chery CC, Wawrzycka D, Van Hulle M, Cornelis R, Thevelein J, Tamas MJ (2001) The glycerol channel Fps1p mediates the uptake of arsenite and antimonite in Saccharomyces cerevisiae. Mol Microbiol 40:1391–1401
Yan WG, Dilday RH, Tai TH, Gibbons JW, McNew RW, Rutger JN (2005) Differential response of rice germplasm to straighthead induced by arsenic. Crop Sci 45:1223–1228
Zaman K, Pardini RS (1996) An overview of the relationship between oxidative stress and mercury and arsenic. Toxic Subst Mech 15:151–181
Author information
Authors and Affiliations
Corresponding author
Additional information
Responsible Editor: Henk Schat
Rights and permissions
About this article
Cite this article
Abbas, M.H.H., Meharg, A.A. Arsenate, arsenite and dimethyl arsinic acid (DMA) uptake and tolerance in maize (Zea mays L.). Plant Soil 304, 277–289 (2008). https://doi.org/10.1007/s11104-008-9549-9
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s11104-008-9549-9