Instituto de Ecología, A. C.,Veracruz, Xalapa, Mexico.
Environ Manage. 2010 Aug;46(2):213-24. doi: 10.1007/s00267-010-9517-z. Epub 2010 Jun 26.
This study addressed the effects of land use and slope position on soil inorganic nitrogen and was conducted in small watersheds. The study covered three land use types: tropical cloud forest, grassland, and coffee crop. To conduct this research, typical slope small watersheds were chosen in each land use type. Slopes were divided into three positions: shoulder, backslope, and footslope. At the center of each slope position, soil sampling was carried out. Soil inorganic nitrogen was measured monthly during a period of 14 months (July 2005-August 2006) with 11 observations. Significant differences in soil NH(4) (+)-N and NO(3) (-)-N content were detected for both land use and sampling date effects, as well as for interactions. A significant slope position-by-sampling date interaction was found only in coffee crop for NO(3) (-)-N content. In tropical cloud forest and grassland, high soil NH(4) (+)-N and low NO(3) (-)-N content were recorded, while soil NO(3) (-)-N content was high in coffee crop. Low NO(3) (-)-N contents could mean a substantial microbial assimilation of NO(3) (-)-N, constituting an important mechanism for nitrogen retention. Across the entire land use set, the relationship between soil temperature and soil inorganic N concentration was described by an exponential decay function (N = 33 + 2459exp(-0.23T), R (2) = 0.44, P < 0.0001). This study also showed that together, soil temperature and gravimetric soil water content explained more variation in soil inorganic N concentration than gravimetric soil water content alone.
本研究探讨了土地利用和坡度位置对土壤无机氮的影响,研究地点位于小流域。研究涵盖了三种土地利用类型:热带云雾林、草地和咖啡种植园。为了进行这项研究,在每种土地利用类型中选择了具有代表性的坡面小流域。坡面分为三个位置:坡肩、坡中和坡脚。在每个坡度位置的中心进行了土壤采样。在 14 个月(2005 年 7 月至 2006 年 8 月)期间每月进行土壤无机氮测量,共进行了 11 次观测。土地利用和采样日期效应以及相互作用均对土壤 NH(4) (+)-N 和 NO(3) (-)-N 含量存在显著差异。仅在咖啡种植园中发现了显著的坡度位置与采样日期相互作用,对 NO(3) (-)-N 含量有影响。在热带云雾林和草地中,记录到了高土壤 NH(4) (+)-N 和低 NO(3) (-)-N 含量,而咖啡种植园中则具有高土壤 NO(3) (-)-N 含量。低 NO(3) (-)-N 含量可能意味着大量的 NO(3) (-)-N 被微生物同化,这是氮素保留的一个重要机制。在整个土地利用类型中,土壤温度和土壤无机氮浓度之间的关系可以用指数衰减函数来描述(N = 33 + 2459exp(-0.23T),R (2) = 0.44,P < 0.0001)。本研究还表明,土壤温度和土壤重量含水量一起可以比单独的土壤重量含水量更好地解释土壤无机氮浓度的变化。