Aase J K, Bjorneberg D L, Westermann D T
USDA-ARS, Northwest Irrigation and Soils Research Lab, Kimberly, ID 83341, USA.
J Environ Qual. 2001 Jul-Aug;30(4):1315-23. doi: 10.2134/jeq2001.3041315x.
Phosphorus (P) in irrigation runoff may enrich offsite water bodies and streams and be influenced by irrigation water quality and antecedent soil surface conditions. Runoff, soil loss, and P fractions in runoff using reverse osmosis (RO) water or mixed RO and well water (RO/ Tap) were studied in a laboratory sprinkler study to evaluate water source effects on P transport. A top- or subsoil Portneuf silt loam (coarse-silty, mixed, superactive, mesic Durinodic Xeric Haplocalcid), either amended or not amended with manure and/or with cheese whey, with Olsen P from 20 to 141 mg kg(-1) and lime from 108 to 243 g kg(-1), was placed in 1.5 x 1.2 x 0.2-m-deep containers with 2.4% slope and irrigated three times from a 3-m height for 15 min, applying 20 mm of water. The first irrigation was on a dry loose surface, the second on a wet surface, and the third on a dry crusted surface. Surface (ca. 2 cm) soil samples, prior to the first irrigation, were analyzed for Olsen P, water-soluble P (Pws), and iron-oxide impregnated paper-extractable P (FeO-P) analyses. Following each irrigation we determined runoff, sediment, dissolved reactive phosphorus (DRP) in a 0.45-microm filtered sample, and FeO-P and total P in unfiltered samples. Soil surface conditions had no effect on P runoff relationships. Water source had no significant effect on the relationship between DRP or FeO-P runoff and soil test P, except for DRP in RO runoff versus water-soluble soil P (r2 = 0.90). Total P in RO runoff versus soil P were not related; but weakly correlated for RO/Tap (r2 < 0.50). Water source and soil surface conditions had little or no effect on P runoff from this calcareous soil.
灌溉径流中的磷(P)可能会使场外水体和溪流富营养化,并受到灌溉水质和先前土壤表面状况的影响。在一项实验室喷灌研究中,研究了使用反渗透(RO)水或RO水与井水混合(RO/自来水)时的径流、土壤流失以及径流中的磷组分,以评估水源对磷迁移的影响。将一种表土或底土波特纳夫粉质壤土(粗粉质、混合、超活性、中度干旱的钙积干旱土),分别用粪便和/或奶酪乳清进行改良或未改良, Olsen磷含量为20至141毫克/千克(-1),石灰含量为108至243克/千克(-1),放置在坡度为2.4%、深1.5×1.2×0.2米的容器中,从3米高度进行三次灌溉,每次15分钟,施加20毫米的水。第一次灌溉是在干燥松散的表面上,第二次是在湿润的表面上,第三次是在干燥结壳的表面上。在第一次灌溉之前,对表层(约2厘米)土壤样本进行了Olsen磷、水溶性磷(Pws)和氧化铁浸渍纸可提取磷(FeO-P)分析。每次灌溉后,我们测定了径流、沉积物、0.45微米过滤样品中的溶解活性磷(DRP)以及未过滤样品中的FeO-P和总磷。土壤表面状况对磷径流关系没有影响。除了RO径流中的DRP与水溶性土壤磷之间的关系(r2 = 0.90)外,水源对DRP或FeO-P径流与土壤测试磷之间的关系没有显著影响。RO径流中的总磷与土壤磷无关;但RO/自来水的总磷与土壤磷之间相关性较弱(r2 < 0.50)。水源和土壤表面状况对这种钙质土壤的磷径流影响很小或没有影响。