The Effect of Glufosinate Ammonium in Three Different Textured Soil Types under Malaysian Tropical Environment

被引:3
作者
Tayeb, M. A. [1 ]
Ismail, B. S. [1 ]
Mardiana-Jansar, K. [1 ]
机构
[1] Univ Kebangsaan Malaysia, Fac Sci & Technol, Ctr Earth Sci & Environm, Ukm Bangi 43600, Selangor Dand E, Malaysia
来源
SAINS MALAYSIANA | 2019年 / 48卷 / 12期
关键词
Adsorption; desorption; glufosinate ammonium; linear equation; sorption isotherm; AMINOMETHYLPHOSPHONIC ACID; OIL PALM; LIQUID-CHROMATOGRAPHY; GLYPHOSATE; DEGRADATION; ADSORPTION; DESORPTION; WATER; DELTAMETHRIN; DISSIPATION;
D O I
10.17576/jsm-2019-4812-01
中图分类号
O [数理科学和化学]; P [天文学、地球科学]; Q [生物科学]; N [自然科学总论];
学科分类号
07 ; 0710 ; 09 ;
摘要
Glufosinate ammonium is a broad spectrum, non-selective, contact and organophosphate herbicide which is commonly used in Malaysian oil palm plantations. Research area was one of the oil palm growing areas of Malaysia is located adjacent to the Tasik Chini, Pahang. Farmers use this herbicide to control several types of unwanted plants which could compete with the oil palm for nutrients. Rain water and the sprayed solution are easily adsorbed by soil particles. The glufosinate ammonium sorption was determined by the batch equilibrium technique. The collected soil samples (0-50 cm depth) divided into five groups at 10 cm depth intervals. Glufosinate ammonium adsorption coefficients were correlated with the soil pH, organic matter (Om), clay content, and cation exchange capacity (cEc). Series of glufosinate ammonium standard were as 0.01, 0.1,0 25, 05,1, 3, 5, and 10 mu m/mL. The Linear and Freundlich equations were fitted for obtaining the adsorption and desorption isotherms. The result of the analyses showed that adsorption of glufosinate ammonium was correlated to the clay content. The clay fraction of the soil is the main absorbent of the glufosinate ammonium. Desorption from the soil was indicated by the high binding strength of the adsorbed glufosinate ammonium.
引用
收藏
页码:2605 / 2612
页数:8
相关论文
共 40 条
[1]   Influence of insecticidal toxins from Bacillus thuringiensis subsp kurstaki on the degradation of glyphosate and glufosinate-ammonium in soil samples [J].
Accinelli, C ;
Screpanti, C ;
Vicari, A ;
Catizone, P .
AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 2004, 103 (03) :497-507
[2]  
Alison L.E., 1965, Methods of soil analysis, P1372, DOI DOI 10.2134/AGRONMONOGR9.2.C39
[3]   FATE OF THE HERBICIDE GLUFOSINATE-AMMONIUM IN THE SANDY, LOW-ORGANIC-CARBON AQUIFER AT CFB BORDEN, ONTARIO, CANADA [J].
ALLENKING, RM ;
BUTLER, BJ ;
REICHERT, B .
JOURNAL OF CONTAMINANT HYDROLOGY, 1995, 18 (02) :161-179
[4]  
BEHRENDT H, 1990, ENVIRON TOXICOL CHEM, V9, P541, DOI [10.1897/1552-8618(1990)9[541:LATOGA]2.0.CO
[5]  
2, 10.1002/etc.5620090502]
[6]   Analysis of glyphosate, glufosinate and aminomethylphosphonic acid by capillary electrophoresis with indirect fluorescence detection [J].
Chang, SY ;
Liao, CH .
JOURNAL OF CHROMATOGRAPHY A, 2002, 959 (1-2) :309-315
[7]   Weed efficacy evaluations for bromoxynil, glufosinate, glyphosate, pyrithiobac, and sulfosate [J].
Corbett, JL ;
Askew, SD ;
Thomas, WE ;
Wilcut, JW .
WEED TECHNOLOGY, 2004, 18 (02) :443-453
[8]   Toxicity of a glufosinate- and several glyphosate-based herbicides to juvenile amphibians from the Southern High Plains, USA [J].
Dinehart, Simon K. ;
Smith, Loren M. ;
McMurry, Scott T. ;
Anderson, Todd A. ;
Smith, Philip N. ;
Haukos, David A. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2009, 407 (03) :1065-1071
[9]   Optimization of extraction procedure and chromatographic separation of glyphosate, glufosinate and aminomethylphosphonic acid in soil [J].
Druart, Coline ;
Delhomme, Olivier ;
de Vaufleury, Annette ;
Ntcho, Evodie ;
Millet, Maurice .
ANALYTICAL AND BIOANALYTICAL CHEMISTRY, 2011, 399 (04) :1725-1732
[10]  
EPA, 1986, United States Environ. Prot. Agency SW-846