硝磺草酮在黑土和红壤中的吸附-解吸特性

孙约兵, 徐应明, 孙扬, 秦旭. 硝磺草酮在黑土和红壤中的吸附-解吸特性[J]. 环境化学, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802
引用本文: 孙约兵, 徐应明, 孙扬, 秦旭. 硝磺草酮在黑土和红壤中的吸附-解吸特性[J]. 环境化学, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802
SUN Yuebing, XU Yingming, SUN Yang, QIN Xu. Adsorption-desorption characteristics of mesotrione in phaiozem and red soils[J]. Environmental Chemistry, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802
Citation: SUN Yuebing, XU Yingming, SUN Yang, QIN Xu. Adsorption-desorption characteristics of mesotrione in phaiozem and red soils[J]. Environmental Chemistry, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802

硝磺草酮在黑土和红壤中的吸附-解吸特性

  • 基金项目:

    国家自然科学基金(21107056)

    公益性行业(农业)科研专项(201203045)

    中央级公益性科研院所基本科研业务费专项资助.

Adsorption-desorption characteristics of mesotrione in phaiozem and red soils

  • Fund Project:
  • 摘要: 采用批量平衡实验, 研究了硝磺草酮在黑土和红壤中吸附-解吸行为.结果表明, 硝磺草酮在两种土壤中的吸附分为快速线性分配和慢速吸附两个阶段, 2 h后, 基本达到动态平衡.然而, 其吸附速率随时间的延长而降低, 且初始浓度和土壤性质对硝磺草酮吸附速率的变化率没有明显影响.硝磺草酮在红壤和黑土中吸附和解吸过程均能用Freundlich模型进行很好的拟合, 拟合系数R2分别为0.999和0.993(黑土)、0.991和0.962(红壤).硝磺草酮在土壤中的吸附等温线呈现"L"型, 以物理性吸附为主.硝磺草酮在两种土壤上的解吸过程存在一定的滞后现象, 且随着硝磺草酮初始浓度增加, 其解吸等温线的滞后系数也随之降低.黑土中硝磺草酮的吸附和解吸滞后强度均大于红壤.
  • 加载中
  • [1] 陶波, 李晓薇, 韩玉军.不同吸附剂对土壤中氟磺胺草醚修复/解吸的影响[J].土壤通报, 2010, 41(4): 965-969
    [2] Wu C X, Zhang S Z, Nie G, et al. Adsorption and desorption of herbicide monosulfuron-ester in Chinese soil[J]. Journal of Environmental Sciences, 2011, 23(9): 1524-1532
    [3] MANY L, BARRIUSO E. Desorption and time-dependent sorption of herbicides in soils[J]. European Journal of Soil Science, 2007, 58, 174-187
    [4] 孙约兵, 徐应明, 孙扬, 等.新型除草剂硝磺草酮在玉米和土壤中的残留及降解行为研究[J]. 环境化学, 2013, 32(1): 144-149
    [5] Crouzet O, Wisziowski J, Donnadieu F, et al. Dose-dependent effects of the herbicide mesotrione on soil cyanobacterial communities[J]. Archives of Environmental Contamination and Toxicology, 2013, 64 (1): 23-31
    [6] Crouzet O, Batisson I, Besse-Hoggan P, et al. Response of soil microbial communities to the herbicide mesotrione: A dose-effect microcosm approach[J]. Soil Biology and Biochemistry, 2010, 42 (2): 193-202
    [7] OECD. OECD guidelines for testing of chemicals, test guideline 106: adsorption/desorption using a batch equilibrium method [M].Paris: Revised Draft Document OECD, 2000: 1-45
    [8] Tang Y L, Guan X H, Wang J M, et al. Fluoride adsorption onto granular ferric hydroxide: Effects of ionic strength, pH, surface loading, and major co-existing anions[J]. Journal of Hazardous Materials, 2009, 171: 774-779
    [9] Bradder P, Ling S K, Wang S B, et al. Dye adsorption on layered graphite oxide[J]. Journal of Chemical & Engineering, 2011, 56: 138-141
    [10] Li X H, Zhou Q X, Wei S H. et al. Adsorption and desorption of carbendazim and cadmium in typical soils in northeastern China as affected by temperature[J]. Geoderma, 2011, 160: 347-354
    [11] 孔德洋, 许静, 韩志华, 等七种农药在3种不同类型土壤中的吸附及淋溶特性[J]. 农药学学报, 2012, 14(5): 545-550
    [12] 王静, 赵莲莲, 刘子圣, 等.丁吡吗啉在土壤中的吸附及淋溶特性[J]. 农业环境科学学报2010, 29(11): 2128-2132
    [13] Flores C, Morgante V, GonzáLez M, et al. Adsorption studies of the herbicide simazine in agricultural soils of the Aconcagua valley, central Chile[J]. Chemosphere, 2009, 74: 1544-1549
    [14] 张玉超, 梅向东, 胡继业, 等. 新农药呋喃虫酰肼在四种土壤中吸附行为的研究[J]. 现代农药, 2009, 8(3): 11-14
    [15] 吴星卫, 单正军, 孔德洋, 等. 2, 4-二氯苯氧基乙酸在土壤中的吸附淋溶特性[J]. 农业环境科学学报, 2009, 28(4): 691-695
    [16] Calvet R. Adsorption of organic chemicals in soil[J]. Environmental Health Perspectives, 1989, 83:145-177
    [17] Pinna M V, Braschi I, Blasioli S, et al. Hydrolysis and adsorption of cyhalofop-butyl and cyhalofop-acid on soil colloids[J]. Journal of Agriculture and Food Chemistry, 2008, 56: 5273-5277.
    [18] SINGH N. Sorption behavior of triazole fungicides in Indian soils and its correlation with soil properties[J]. Journal of Agriculture and Food Chemistry, 2002, 50: 6434-6439
    [19] 彭炳先, 李兰, 陈翠, 等. 江西稻田红壤中丙溴磷的移动特性及其主要影响因素[J]. 环境化学, 2014, 33(9): 1456-1461
    [20] 赖作旺, 邓新平, 王小天, 等. 啶虫脒和阿维菌素在4种不同类型土壤中的吸附及迁移[J]. 农药学学报 2010, 12(3): 361-366
    [21] Weber W J, Leboeuf E J, Young T M, et al. Contaminant interactions with geosorbent organic matter: Insight drawn from polymer sciences [J]. Water Research, 2001, 35: 853- 868
    [22] Chiou C T, Kile D E, Rutheford D, et al. Sorption of selected organic compound s from water to a peat soil and its humic-acid and humin fractions: potential sources of the sorption non linearity[J]. Environmental Science & Technology, 2000, 34(7): 1254-1258
    [23] 李俊国, 李存国, 孙红文, 芘在土壤中的吸附和解吸行为研究[J].农业环境科学学报, 2005, 4(增刊): 268-272
    [24] Barriuso E, Laired D A, Koskinen W C, et al. Atrazine desorption from smectites[J]. Soil Science Society of American Journal, 1994, 58: 1632-1638
  • 加载中
计量
  • 文章访问数:  1275
  • HTML全文浏览数:  1188
  • PDF下载数:  366
  • 施引文献:  0
出版历程
  • 收稿日期:  2015-04-28
  • 刊出日期:  2015-10-15
孙约兵, 徐应明, 孙扬, 秦旭. 硝磺草酮在黑土和红壤中的吸附-解吸特性[J]. 环境化学, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802
引用本文: 孙约兵, 徐应明, 孙扬, 秦旭. 硝磺草酮在黑土和红壤中的吸附-解吸特性[J]. 环境化学, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802
SUN Yuebing, XU Yingming, SUN Yang, QIN Xu. Adsorption-desorption characteristics of mesotrione in phaiozem and red soils[J]. Environmental Chemistry, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802
Citation: SUN Yuebing, XU Yingming, SUN Yang, QIN Xu. Adsorption-desorption characteristics of mesotrione in phaiozem and red soils[J]. Environmental Chemistry, 2015, 34(10): 1832-1838. doi: 10.7524/j.issn.0254-6108.2015.10.2015042802

硝磺草酮在黑土和红壤中的吸附-解吸特性

  • 1.  农业部环境保护科研监测所, 农业部产地环境质量重点实验室, 天津, 300191;
  • 2.  农业部环境保护科研监测所, 中国农科院农田重金属污染修复创新团队, 天津, 300191
基金项目:

国家自然科学基金(21107056)

公益性行业(农业)科研专项(201203045)

中央级公益性科研院所基本科研业务费专项资助.

摘要: 采用批量平衡实验, 研究了硝磺草酮在黑土和红壤中吸附-解吸行为.结果表明, 硝磺草酮在两种土壤中的吸附分为快速线性分配和慢速吸附两个阶段, 2 h后, 基本达到动态平衡.然而, 其吸附速率随时间的延长而降低, 且初始浓度和土壤性质对硝磺草酮吸附速率的变化率没有明显影响.硝磺草酮在红壤和黑土中吸附和解吸过程均能用Freundlich模型进行很好的拟合, 拟合系数R2分别为0.999和0.993(黑土)、0.991和0.962(红壤).硝磺草酮在土壤中的吸附等温线呈现"L"型, 以物理性吸附为主.硝磺草酮在两种土壤上的解吸过程存在一定的滞后现象, 且随着硝磺草酮初始浓度增加, 其解吸等温线的滞后系数也随之降低.黑土中硝磺草酮的吸附和解吸滞后强度均大于红壤.

English Abstract

参考文献 (24)

返回顶部

目录

/

返回文章
返回