利用生物炭净化城市化流域道路边缘的径流:一项大规模现场渗滤仪研究

K. Kuoppamäki , M. Hagner , M. Valtanen , H. Setälä
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引用次数: 16

摘要

来自交通区域的城市径流是污染的主要来源,它降低了邻近地表水的质量。城市边缘地区大量路边土地提供的绿色基础设施可用于更好地管理和渗透城市径流。在建立城市绿地时,应优先使用回收材料,以实现经济上可行和对环境负责的解决方案。例如,欧盟内部的废水处理厂产生大量含有营养物质和金属的固体,需要以可持续的方式加以利用。然而,由这些污水污泥堆肥而成的土壤被广泛用于建设绿色基础设施,如公园和道路边缘,这可能会危及其用于雨水管理的用途,尽管尚未对道路边缘的污水污泥对径流水质的影响进行科学研究。有人建议,生物炭可以保留污染物,也可能符合可回收材料的标准。我们在芬兰南部寒冷气候条件下的大型野外渗滤仪中建立了模拟道路边缘的人工生物过滤器结构,以研究生物炭保留从堆肥污水污泥中浸出的污染物和从人工雨水中渗透的污染物的能力。最上面的15 cm由天然泥炭(peat)或由污水污泥混合桦树衍生生物炭(体积3%)或不混合这种生物炭(Comp+bc和Comp)的土壤堆肥组成的有机层组成。在第1个生长期结束时,在溶渗池中生长的禾草吸收了含有堆肥的表层土壤中高达32%的磷。磷的淋溶量在不同处理之间没有差异,而氮的淋溶量是泥炭的10倍。重金属,如镍和铜,从堆肥土壤中浸出也明显高于泥炭,但生物炭显著减少了从堆肥中浸出的金属(高达50%)。建成两年后,利用模拟交通繁忙的道路径流的人工雨水灌溉溶渗仪。与泥炭相比,堆肥浸出了更多的氮。然而,生物炭显著降低了通过堆肥渗透的氮负荷44%。将污水污泥堆肥与生物炭混合,并在有机土层下添加5 cm厚的生物炭层,可显著减少氮和重金属的淋滤。然而,鉴于城市边缘地区有大量的路边,应仔细考虑在这些地区广泛使用污水污泥和其他富氮材料。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Using biochar to purify runoff in road verges of urbanised watersheds: A large-scale field lysimeter study

Urban runoff from traffic areas is a major source of pollution that degrades the quality of adjacent surface waters. Green infrastructure provided by the substantial amount of roadside land at urban fringe areas can be used to better manage and infiltrate this urban runoff. When establishing urban green areas, recycled materials should be preferred in order to achieve economically feasible and environmentally responsible solutions. Wastewater treatment plants within e.g. the EU yield substantial amounts of solids containing nutrients and metals that need to be utilised in a sustainable way. However, soil composted from such sewage sludge is being used widely in constructing green infrastructure, such as parks and road verges, which may jeopardise their use for stormwater management even though the effects of sewage sludge at road verges on the quality of runoff waters have not been subjected to scientific examination. Biochar has been suggested to retain pollutants and may also meet the criteria of being recycled material. We established artificial biofilter structures, mimicking road verges, in large-scale field lysimeters under cold climatic conditions in southern Finland to study the ability of biochar to retain pollutants leaching from composted sewage sludge and from infiltrating artificial stormwater. The topmost 15 cm consisted of an organic layer of either natural peat (Peat) or soil composted from sewage sludge either mixed with birch-derived biochar (3% by volume) or without this biochar (Comp+bc and Comp, respectively). At the end of the 1st growing period grasses growing in the lysimeters had taken up to 32% of phosphorus in the top soil containing compost. Leaching of phosphorus did not differ between the treatments, while nitrogen (N) leaching was ten time larger from Comp than Peat. Leaching of heavy metals, such as nickel and copper, was also significantly higher from compost soils than peat, but biochar significantly reduced metal leaching from compost (up to 50%). Two years after establishment, lysimeters were irrigated with artificial stormwater mimicking runoff from roads with heavy traffic. Comp leached more N compared to Peat. However, biochar significantly reduced N load infiltrated through the compost by 44%. Mixing sewage sludge-originated compost with biochar, and adding a 5 cm thick layer of biochar underneath the organic soil layer can substantially reduce leaching of N and heavy metals. However, given the substantial amount of roadsides in urban fringe areas, the extensive use of sewage sludge and other N-rich materials in such areas should be considered carefully.

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