多摩河流域土地利用与河流水质的关系

S. Kimura, M. Okazaki
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引用次数: 1

摘要

为了优化生态系统中的活性氮循环,必须开发提高氮利用效率和减少氮排放的技术。在流域生态系统中,具有净化能力的土地利用可以成为减轻非点源氮负荷的有力工具。本研究分析了土地利用方式对日本典型城市河流多摩河流域硝酸盐浓度的影响。上游地区以森林为主,下游地区以城市用地为主。在塔玛河流域,59%的土地利用是森林;23%是市区;只有5%是农业用地。市区分布在中游下游。2004年平均硝态氮(NO3—N)浓度由上游向下游呈上升趋势,上游为0.7 mg N - L-1,下游为6.0 mg NO3—N - L-1。河流水体NO3——N浓度与城市土地利用比例呈正相关,与森林比例呈负相关。然而,尽管土地利用高度城市化,但一些小流域的NO3—N浓度值较低。与其他子流域相比,稻田面积占总面积的比例较高,在0.3 ~ 3.0%之间,水体面积占比较高,在8.3 ~ 30.6%之间。这可能反映了水体和稻田的净化能力。距离河流水面0 ~ 50 m范围内的土地利用影响了水质,森林和其他水体降低了硝酸盐浓度。人工湿地或河岸森林的建设将减少进入河流的氮负荷。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Relation between Land Use and River Water Quality of the Tama River Watershed
To optimize the reactive nitrogen cycle in an ecosystem, technologies to increase nitrogen use efficiency and reduce emissions of nitrogen must be developed. In a watershed-ecosystem, land uses with purification abilities can be a powerful tool to mitigate nitrogen loads from nonpoint sources. This study analyzes the influence of land use on nitrate concentration in the watershed of the Tama River, a typical urban river in Japan. The upstream area is occupied by forest, while the downstream area is dominated by urban land use. In the Tama River watershed, 59% of the total land use is forest ; 23% is urban area ; and, only 5% is occupied by agricultural land. Urban areas are distributed downstream from the middle reaches. The average nitrate nitrogen (NO3--N) concentration in 2004 increased from upstream to downstream: it was 0.7 mg N L-1 in the upstream area, while it rose to 6.0 mg NO3--N L-1 in the downstream area. The river water NO3--N concentration showed a positive correlation with the proportion of urban land use, while it showed a negative correlation with the proportion of forest. However, some small sub-watersheds have low values for NO3--N concentration despite highly urbanized land use. These sub-watersheds are characterized by higher proportions of paddy rice fields to the total area, ranging from 0.3 to 3.0%, and higher proportions of water body areas, ranging from 8.3 to 30.6%, compared to other sub-watersheds. This might indicate the purification ability of the water bodies and paddy rice fields. Land use within 0 to 50 m from the river water surface influenced water quality and forest and other water bodies reduced nitrate concentration. Construction of artificial wetlands or riparian forests would decrease the N load into the river.
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