Mycorrhizal Colonization Affects the Survival of Vetiveria zizanioides (L.) Nash Grown in Water Containing As(III)

被引:2
作者
Srivastava, Jatin [1 ]
Shukla, Dinesh [2 ]
Chand, Vishal [3 ]
Naraian, Ram [4 ]
Chandra, Harish [5 ]
Nautiyal, Anant R. [6 ]
机构
[1] Chhatrapati Shahu Ji Maharaj Univ, Dept Environm Sci, Kanpur, Uttar Pradesh, India
[2] MIMT, Dept Biotechnol, Greater Noida, Uttar Pradesh, India
[3] Chhatrapati Shahu Ji Maharaj Univ, Dept Biotechnol, Kanpur, Uttar Pradesh, India
[4] Chhatrapati Shahu Ji Maharaj Univ, Dept Microbiol, Kanpur, Uttar Pradesh, India
[5] Gayatri Inst Biomed Sci, Dept Microbiol, Dehra Dun, Uttarakhand, India
[6] HNB Garhwal Univ, High Altitude Plant Physiol Res Ctr, Garrhwal, Uttarakhand, India
关键词
Arsenite; Hydroponics; Mycorrhizal colonization; Mycorrhizal intensity; Vetiveria zizanioides; PTERIS-VITTATA; PHOSPHATE-TRANSPORT; UPTAKE KINETICS; ARSENATE; FUNGI; SOIL; COMMUNITIES; TOLERANCE; REMOVAL;
D O I
10.1002/clen.200900252
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The presence of arsenic (As) in water is of great public concern. Arsenic exists in three common valence states viz., As(0) metalloid arsenic, As(III) (arsenite) and As(V) (arsenate). Arsenite [As(III)] is the most toxic form among arsenicals which, predominates in anaerobic conditions, generally in flooded soils and in the water with high BOD. Experiments were conducted to investigate the effect of As(III) on the mycorrhization in vetiver (Vetiveria zizanioides (L.) Nash) grass in hydroponics. Studies showed significant alteration in the mycorrhizal colonization in the roots of vetiver exposed to higher concentrations of As(III) starting from 1.0, 2.0, 3.0, 4.0 to 5.0 mg/L prepared in 5% Hoagland nutrient solution without addition of phosphate ions. Considerable reduction in the mycorrhizal intensity (M) was observed in all the treatment sets as compared to the control suggesting a negative impact of the As(III) on the mycorrhizal association. Simultaneously, the study also showed that, As(III) is toxic to the vetiver plants having mycorrhizal association however plants with non-mycorrhizal (cleansed) roots were found to be able to survive for a longer period exposed to As(III).
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页码:771 / 774
页数:4
相关论文
共 30 条
[1]   ARSENIC UPTAKE BY BARLEY SEEDLINGS [J].
ASHER, CJ ;
REAY, PF .
AUSTRALIAN JOURNAL OF PLANT PHYSIOLOGY, 1979, 6 (04) :459-466
[2]  
Beever R. E., 1980, Advances in Botanical Research, V8, P127, DOI 10.1016/S0065-2296(08)60034-8
[3]   A mesocosm study of aerobic mineralization of seven aquatic macrophytes [J].
Bianchini, I., Jr. ;
Peret, A. M. ;
Cunha-Santino, M. B. .
AQUATIC BOTANY, 2006, 85 (02) :163-167
[4]  
BRUNDRETT M, 1996, ACIAR MONOGR, V32, P373
[5]   Effects of arbuscular mycorrhizal inoculation on uranium and arsenic accumulation by Chinese brake fern (Pteris vittata L.) from a uranium mining-impacted soil [J].
Chen, BD ;
Zhu, YG ;
Smith, FA .
CHEMOSPHERE, 2006, 62 (09) :1464-1473
[6]   Enhanced uptake of As, Zn, and Cu by Vetiveria zizanioides and Zea mays using chelating agents [J].
Chiu, KK ;
Ye, ZH ;
Wong, MH .
CHEMOSPHERE, 2005, 60 (10) :1365-1375
[7]   ARSENIC SPECIATION IN THE ENVIRONMENT [J].
CULLEN, WR ;
REIMER, KJ .
CHEMICAL REVIEWS, 1989, 89 (04) :713-764
[8]   Phosphate transport by communities of arbuscular mycorrhizal fungi in intact soil cores [J].
Jakobsen, I ;
Gazey, C ;
Abbott, IK .
NEW PHYTOLOGIST, 2001, 149 (01) :95-103
[9]   Application of biological processes for the removal of arsenic from groundwaters [J].
Katsoyiannis, IA ;
Zouboulis, AI .
WATER RESEARCH, 2004, 38 (01) :17-26
[10]  
Lavania UC, 2004, CURR SCI INDIA, V86, P11