Borin Maurizio, Tocchetto Davide
Dipartimento di Agronomia Ambientale e Produzioni Vegetali, Università di Padova, Italy.
Sci Total Environ. 2007 Jul 15;380(1-3):38-47. doi: 10.1016/j.scitotenv.2006.12.039. Epub 2007 Jan 30.
The performance of a constructed surface flow wetland in reducing diffuse N pollution coming from croplands is being investigated in an ongoing experiment, begun in 1998 in NE Italy. The 0.32 ha wetland is vegetated with Phragmites australis (Cav.) Trin. and Typha latifolia (L.). It receives drainage water from 6 ha of land managed for an experiment on drainage systems, where maize, sugarbeet, winter wheat and soybean are cultivated. During the period 1998-2002, the wetland received from 4698 to 8412 mm of water per year (on average, about 9 times the environmental rainfall); its water regimen was discontinuous and flooding occurred on a variable number of days per year (from 13 to 126). Nitric nitrogen was the most important form of element load. Its concentration in the inflow water over time was rather discontinuous, with median values ranging from 0.2 (in 2001) to 4.5 (in 2000) mg L(-1). Inflow nitric N concentrations were occasionally in the 5-15 mg L(-1) range. Concentrations reduced passing through the wetland, with a more evident effect in the last year. Over 5 years, the wetland received slightly more than 2000 kg ha(-1) of nitrogen, 87% in nitric form mostly from farmland drainage. The remaining 13% of N was applied as organic slurry directly onto the wetland, with 5 distributions during 1998 to assess wetland performance in treating occasional organic loads. Field drainage loads had a discontinuous time pattern and occurred mostly during autumn-winter, with the exception of the 2001-2002 season which was a very dry. The wetland discharged 206 kg ha(-1) of N, over the 5-year period, with an apparent removal efficiency of about 90%. The disappearance was mostly due to plant uptake (1110 kg ha(-1)) and soil accumulation (570 kg ha(-1)), with the contribution of denitrification being estimated at around 7%.
1998年在意大利东北部开始的一项正在进行的实验,正在研究人工构建的地表流湿地在减少来自农田的面源氮污染方面的性能。这个0.32公顷的湿地植被为芦苇(Phragmites australis (Cav.) Trin.)和香蒲(Typha latifolia (L.))。它接收来自6公顷进行排水系统实验的土地的排水,在这片土地上种植玉米、甜菜、冬小麦和大豆。在1998 - 2002年期间,湿地每年接收4698至8412毫米的水(平均约为环境降雨量的9倍);其水位变化不连续,每年发生洪水的天数不同(从13天到126天)。硝态氮是元素负荷的最重要形式。其在流入水中的浓度随时间变化相当不连续,中值范围从0.2(2001年)到4.5(2000年)毫克/升。流入的硝态氮浓度偶尔在5 - 15毫克/升范围内。通过湿地后浓度降低,在最后一年效果更明显。在5年时间里,湿地接收了略超过2000千克/公顷的氮,其中87%为硝态形式,主要来自农田排水。其余13%的氮以有机泥浆的形式直接施用于湿地,在1998年期间进行了5次分布,以评估湿地处理偶尔有机负荷的性能。田间排水负荷具有不连续的时间模式,主要发生在秋冬季节,2001 - 2002年季节是个非常干旱的年份除外。在5年期间,湿地排放了206千克/公顷的氮,表观去除效率约为90%。氮的消失主要归因于植物吸收(1110千克/公顷)和土壤积累(570千克/公顷),反硝化作用的贡献估计约为7%。