化学破乳剂(Separol NF.36和Servo C.6602)污染土壤的硝化作用和氮矿化

Amadi Amadi
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引用次数: 3

摘要

用0、25、50、100和1000 ppm浓度的化学破乳剂污染红树林淡水环境中的砂壤土,研究它们对氮转化的影响。通过监测处理土壤中NH4+-N、NO2−-N和NO3−-N水平的变化,测定了28天处理土壤中硝化作用和N矿化率的变化。施用Separol NF.36和Servo C.6602抑制了氨化作用,处理土壤的NH4+- n水平高于未处理的对照,但不显著。破乳剂浓度为1000 ppm时对氨化的抑制作用最大,表现为高水平的NH4+-N,而破乳剂浓度为25 ppm时对污染土壤中NH4+-N还原的影响最小。所使用浓度的分离醇NF.36和伺服C.6602不能完全抑制硝化速率。硝酸盐氮含量非常低;不同破乳剂浓度对NO2−-N水平的影响差异不显著,NO2−-N迅速转化为NO3−-N是整个研究期间NO3−-N水平升高的原因。然而,所有浓度的化学破乳剂对土壤NO3-N的抑制作用持续到第14天,而对Servo C.6602处理的土壤则持续到第7天。1000和100 ppm破乳剂处理对硝化和氮矿化的抑制作用最大,而25和50 ppm破乳剂处理对氮转化的促进作用最大,特别是在分离ol NF.36处理土壤第14天后和Servo C.6602处理土壤第7天后。Separol NF.36和Servo C.6602的效果没有显著差异。处理后土壤总矿质氮含量变化趋势与NO3−-N变化趋势一致。
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Nitrification and N mineralization in chemical demulsifier (Separol NF.36 and Servo C.6602) contaminated soil

A sandy loam soil from a mangrove freshwater environment was contaminated with 0, 25, 50, 100 and 1000 ppm concentrations of chemical demulsifiers to determine their effect on nitrogen transformation. Changes in nitrification and N mineralization rates were determined by monitoring the changes in the levels of NH4+-N, NO2-N and NO3-Nin the treated soilsfor a period of 28 days. Application of Separol NF.36 and Servo C.6602 inhibited ammonfication as shown by the increase in NH4+-Nlevels in the treated soil above the untreated control, though not significantly. A demulsifier concentration of 1000 ppm inhibited ammonfication most, as shown by the high level of NH4+-N, while a 25 ppm concentration showed the least adverse effect on NH4+-N reduction in the contaminated soils. Separol NF.36 and Servo C.6602 at the concentrations used did not result in the complete inhibition of nitrification rates. Nitrate-N levels were very minute; the effect of different concentrations of demulsifiers on NO2-N levels did not vary significantly, the NO2-N being rapidly converted to NO3-N accounting for the increases in the NO3-N levels throughout the period of investigation.

However, all concentrations of the chemical demulsifier used depressed NO3-N levels until the 14th day in Separol NF.36 and the 7th day in the Servo C.6602 treated soils. Treatments with 1000 and 100 ppm of demulsifier depressed nitrification and N mineralization most, while 25 and 50 ppm concentrations stimulated nitrogen transformation most, especially after the 14th day in the Separol NF.36 treated soil and after the 7th day in the Servo C.6602 treated soils. The effect of Separol NF.36 and Servo C.6602 when compared, did not vary significantly. Changes in total mineral nitrogen level in the treated soils exhibited the same trend as NO3-N.

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