中国农业科学 ›› 2005, Vol. 38 ›› Issue (02): 341-349 .

• 土壤肥料.节水灌溉 • 上一篇    下一篇

几种粉煤灰的特性及其硅、磷的农业化学行为研究

冯跃华,胡瑞芝   

  1. 湖南农业大学资源环境学院
  • 收稿日期:2004-10-15 修回日期:1900-01-01 出版日期:2005-02-10 发布日期:2005-02-10
  • 通讯作者: 冯跃华

A Study on Physical and Chemical Properties of Several Fly Ashes and Their Agrochemical Behaviors of Silicon and Phosphorus

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  1. 湖南农业大学资源环境学院
  • Received:2004-10-15 Revised:1900-01-01 Online:2005-02-10 Published:2005-02-10

摘要: 对采自湖南省的几种粉煤灰特性及其硅、磷农业化学行为的研究结果表明,粉煤灰颗粒组成以砂粒(1~0.05 mm)和粗粉粒(0.05~0.01 mm)为主,平均分别占34.37 % 和38.56 %。容重较小,仅为土壤的1/2~1/3,除采自长沙电厂的粉煤灰外,pH一般大于10.0,可以用作粘质酸性土壤改良剂。粉煤灰水溶性硅和有效硅含量与土壤相差不明显,不能把粉煤灰直接作硅肥使用。粉煤灰的全钾含量和土壤大致相同,但其游离态铁比土壤低3 ~ 4倍。粉煤灰中硅的释放量随时间变化的关系可以用Elovich方程和Freundlich方程进行较好的描述,其相应的参数b和k反映了硅的释放能力,b、k值越大,硅释放能力越强。不同来源粉煤灰的b、k值不同,其大小顺序为:湘潭电厂(1539.3,2139.3)、岳阳纸厂(1602.4,1274.0)>华能电厂(1325.7,1181.6)>长沙电厂(1250.6,915.9)>洞庭氮肥厂(751.9,565.6)>株洲电厂(555.5,454.4);粉煤灰中硅在100 h内释放量比土壤高3.0~25.0倍,能为作物提供一定数量的硅营养,故可把粉煤灰作为一种硅肥添加剂,其中以湘潭电厂和岳阳纸厂的粉煤灰为好。粉煤灰的全磷含量和有效磷含量一般比土壤高,它对磷的吸附量随着加入溶液磷的浓度的增加而增加,但其吸附率随着加入溶液磷的浓度的增加而减少;粉煤灰的吸磷率比土壤高,但其解吸率低。Langmuir方程、Freundlich方程和Temkin方程都能很好地拟合粉煤灰对磷的吸附,其相应的参数Xm、a和k2都可以表征粉煤灰对磷的吸附能力。粉煤灰对磷的吸附主要是专性吸附和化学沉淀反应,所以在施用粉煤灰改良土壤或利用粉煤灰作添加剂制造复混肥时,必须考虑粉煤灰对磷的固定作用。

关键词: 粉煤灰, 土壤改良剂, 硅的释放量, 吸磷率, 农业化学行为

Abstract: The physical and chemical properties and silicon releasing pattern and phosphate adsorption-desorption of fly ashes derived from six power stations in Hunan province were studied. The results showed that fly ashes could be used as soil amendments because the fly ashes were mostly composed by sand(1-0.05 mm)and coarse silt particle(0.05-0.01mm)accounting for 16.13 %- 85.68 % and 13.03 %-49.64 %, respectively. The bulk density of fly ashes was 2- to 3-fold lower than that of soils. The fly ashes generally have high alkalinity (pH 10.3-12.1, 1︰2.5 in H2O extract) except that the fly ashes of Changsha power factory derived from high sulfur coal have low acidity(pH 7.5, 1︰2.5 in H2O extract). No obvious difference in contents of water-soluble and available silicon between fly ashes and soils was observed, so fly ashes can not be used directly as Si fertilizer. The contents of total potassium in fly ashes were approximately the same as in soils, but the contents of free iron oxide in fly ashes were 3- to 4-fold lower than those in soils. The releasing processes of Si in fly ashes and soils could be well described with Elovich equation and Freundlich equation ,in which the parameter b value and k value could express the releasing capacity of Si in fly ashes and soils .The larger the b and k values, the more the Si will be released from the fly ashes. The b value and k value in 5 fly ashes derived from various locations in order of magnitude is Xiangtan power factory (1539.3,2139.3)and Yueyang paper factory (1602.4,1274.0)>Huaneng power factory (1325.7,1181.6)>Changsha power factory(1250.6,915.9)>Dongting nitrogenous fertilizer factory (751.9,565.6)>Zhuzhou power factory (555.5,454.4). The fly ashes can supply certain Si nutrition for crop growth because the amount of silicon released in fly ashes were 3.0-25.0 times higher within 100 hours than those in the soils, thus the fly ashes can be a kind of Si fertilizer additive when manufacturing Si fertilizer. Furthermore, the fly ashes derived from Xiangtan power factory and Yueyang paper factory are fairly good Si fertilizer additives. The contents of total P and available P in fly ashes were generally higher than those in soils. The adsorption capacity of P in fly ashes increased with increasing P added,but the rates of P adsorbed in fly ashes decreased with increasing P added. The rates of P adsorbed in fly ashes were higher than those in soils, but the rates of P desorbed in fly ashes were lower than those in soils. The sorption processes of P in fly ashes could be also well described with Langmuir equation and Freundlich equation and Temkin equation, in which parameter Xm value and a value and k2 value can be used as a comprehensive index to characterize the potential phosphate sorptivity of fly ashes. The phosphate adsorption in fly ashes were mainly specific adsorption and chemical precipitation, thus it is suggested that the fixation of P must be considered when fly ash is used as soil amendments or filling substances of compound fertilizers.

Key words: Fly ashes, Soil amendants, The amount of silicon releasing, The rates of P adsorbed, Agrochemical behaviors