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    DOM from non-treated sludge had a greater effect on chlorotoluron toxicity to wheat than DOM from heat-expanded sludge.
    含有绿麦隆的两种来源DOM对两类小麦的毒性有增强作用,来源于原始污泥的DOM作用高于来源于热喷污泥的DOM。
    The order of ability of inhibiting to Cd adsorption is found as following: CS DOM>DS DOM≈WS DOM>RS DOM>PM DOM in neutral soils, and CS DOM>DS DOM>RS DOM≈PM DOM>WS DOM in alkaline soils.
    碱性土壤中 ,5种DOM同样表现为对Cd吸附的抑制作用 ,抑制效果由大到小顺序为 :堆腐污泥DOM >消化污泥DOM >脱水污泥DOM≈猪粪DOM >小麦秸杆DOM
    The dissolved organic carbon in excess of 400 and 150 mg/L was inhibitory to the bacterial growth using sludge DOM and manure DOM,respectively.
    当污泥DOM和猪粪DOM中水溶性有机碳浓度分别高于400mg/L和150mg/L时,就表现出对硫杆菌的不可修复的抑制作用.
    The apparent water solubility of Phe in the presence of 150 mg·L -1 could increased by 20.39 folds for Tween-80, and 2.08, 1.84 or 1.55 folds for DOM from pig manure, sewage sludge and green manure, respectively.
    当DOM浓度为150mg·L-1(以DOC计)时,在含Tween80、猪粪DOM、污泥DOM和绿肥DOM的体系中菲的表观溶解度分别是纯水体系的20.39、2.082、1.838和1.549倍.
    The solubilizing sequence among DOM was Tween-80>pig manure DOM>sewage sludge DOM>green manure DOM.
    回归直线的斜率可以用来表征DOM对菲的增溶效果,本试验4种体系中DOM的增溶效果大小依次为表面活性剂Tween80>猪粪DOM>污泥DOM>绿肥DOM.
    DOM reduced sorption of napropamide significantly onto thetested soils, which consequently facilitated the transport of napropamide exhibited by soilcolumn experiment.
    结果表明,在供试DOM浓度范围内两种DOM均能提高草萘胺的溶解度,并且绿肥DOM的影响比污泥DOM的更显著。
    Within the selected concentration range of the napropamide and DOM napropamidesorption isotherm could be described well by the Freundlich equation.
    污泥DOM比绿肥DOM更易被土壤吸附,其在土壤中的分配系数(K_d)分别比对应的绿肥DOM的高出14.4%(黄棕壤)和165.3%(潮土)。
    The adsorption of Cd and Zn was decreased by 18.2% and 9.1% in soil 2. In the composite adsorption system, the adsorption of Cd and Zn was increased by 450% and 325% in soil 1;
    3.在20℃下向土壤中分别添加稻秆DOM、污泥DOM和菜叶DOM后,单一吸附中,3种DOM对Cd、Zn在1号土上吸附的促进作用为菜叶DOM>污泥DOM>稻秆DOM,而对Cd、Zn在2号土上吸附的抑制作用为稻秆DOM>污泥DOM>菜叶DOM。
 

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