Esteller M V, Martínez-Valdés H, Garrido S, Uribe Q
Universidad Autónoma del Estado de México, Cerro Coatepec S/N Toluca, Estado de México, 50130 México, Mexico.
Waste Manag. 2009 Jun;29(6):1936-44. doi: 10.1016/j.wasman.2008.12.025. Epub 2009 Feb 13.
The use of organic wastes in agriculture may increase the production of crops by incorporating organic matter and nutrients into the soil, and by improving its physical characteristics; however, this use may cause environmental problems such as the leaching of certain ions. The objective of this study was to establish possible nitrogen and phosphorus leaching under real field conditions in Phaeozem soils. The experimental work was performed in a corn (Zea mays L.) field where three plots were conditioned with inorganic fertilizer, three plots with 4.5 Mgha(-1) of biosolids on dry basis, and three plots with the same amount of composted biosolids. The quality of biosolids and composted biosolids complied with the Mexican Official Standards. Soil water samples were collected with suction cups during two agricultural cycles and were analysed. Soil samples were also taken and analysed. The N-NO(3) concentrations in soil water fluctuated between 0.9 and 98mgL(-1) in the composted biosolid treatment, between 0.7 and 64 mgL(-1) in the biosolid treatment, and between 1 and 61 mgL(-1) in the inorganic fertilizer treatment. The maximum concentration of N-NO(2) and N-NH(3) in soil water was 1.02 and 2.65 mgL(-1), respectively. The greatest percentage of nitrogen leached is produced when inorganic fertilizer is used (37.4% and 24.0% N leached in the first and second years, respectively), followed by composted biosolids (17.1% and 13.5% N leached in the first and second years, respectively) and last by biosolids (11% for both years). This difference could be related to the form in which nitrogen is present in the fertilizers, while commercial fertilizer is as inorganic nitrogen, organic wastes are basically presented as organic nitrogen. The maximum PO(4)(3-) concentration in soil water was 1.9 mgL(-1) in the composted biosolid treatment, 1.7mgL(-1) in the biosolid treatment and 0.9 mgL(-1) in the inorganic fertilizer treatment. The estimated percentage of leached phosphorus was less than 1% for all treatments. The minimum leaching that occurred seemed to be due to a sorption-precipitation process.
在农业中使用有机废物,通过向土壤中添加有机物质和养分以及改善土壤物理特性,可能会提高作物产量;然而,这种使用可能会引发环境问题,比如某些离子的淋溶。本研究的目的是确定在黑钙土的实际田间条件下可能出现的氮和磷淋溶情况。实验工作在一片玉米(Zea mays L.)田进行,设置了三个施用无机肥料的地块、三个施用干基含量为4.5 Mg ha⁻¹生物固体废弃物的地块以及三个施用等量堆肥化生物固体废弃物的地块。生物固体废弃物和堆肥化生物固体废弃物的质量符合墨西哥官方标准。在两个农业周期内,用吸盘采集土壤水样并进行分析。同时采集土壤样品并进行分析。在堆肥化生物固体废弃物处理中,土壤水中N-NO₃浓度在0.9至98 mg L⁻¹之间波动,在生物固体废弃物处理中为0.7至64 mg L⁻¹,在无机肥料处理中为1至61 mg L⁻¹。土壤水中N-NO₂和N-NH₃的最大浓度分别为1.02和2.65 mg L⁻¹。使用无机肥料时淋溶的氮比例最大(第一年和第二年分别为37.4%和24.0%的氮被淋溶),其次是堆肥化生物固体废弃物(第一年和第二年分别为17.1%和13.5%的氮被淋溶),最后是生物固体废弃物(两年均为11%)。这种差异可能与肥料中氮的存在形式有关,商业肥料中的氮为无机氮,而有机废物中的氮基本以有机氮形式存在。在堆肥化生物固体废弃物处理中,土壤水中PO₄³⁻的最大浓度为1.9 mg L⁻¹,在生物固体废弃物处理中为1.7 mg L⁻¹,在无机肥料处理中为0.9 mg L⁻¹。所有处理中磷的淋溶估计百分比均小于1%。发生的最低淋溶似乎是由于吸附沉淀过程。