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Nutrient removal capacity of wood residues for the Agro-environmental safety of ground and surface waters

机译:去除木材残留物对地下水和地表水农业环境安全的营养去除能力

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摘要

The aim of this study was to determine the effectiveness of wood residues in the removal of nutrients (ammonium-N; NH4-N) from nutrient-rich (NH4-N) waters. The water holding capacity of the wood materials was also determined. Carried out at Rothamsted Research, North Wyke, UK, this controlled laboratory experiment tested two wood residues; in length, one being 1-2cm and the other from 150 μm (microns) to 9.5mm. Although a wide range of studies have shown the effectiveness and performance of various absorbent materials as animal beddings, such as straw (cereal straw), woodchip (sawdust, bark or wood shavings), bracken and rushes, only few have focused on the NH4-N sorption/desorption capacity. The depuration capacity of wood residues from nutrient-rich effluents such as those from cattle bedded on woodchip or straw will be controlled by processes such as sorption (adsorption-absorption) and desorption of nutrients. Studies have reported the nitrogen removal capacity of woodchip materials and biochar from woodchip as well as removal of NH4+-N from domestic and municipal wastewater, farm dirty water, landfill and industry effluents. These studies have observed that the mechanism of removal of nitrogen is by either increasing NO3--N removal form leachate by enhancing N2O losses via denitrification (biochar as carbon source for denitrifiers) or by decreasing NH4+-N in leachate through adsorption to negatively charged sites. Results showed that although the cation exchange capacity (CEC) and surface area (SA) are both fundamental properties of adsorbent materials, no correlation was found with CEC and adsorption or desorption. Nor did changes in pH appear to be sufficiently important to cause changes in CEC. For this reason, osmotic pressure appeared to be a more predominant parameter controlling processes of adsorption and desorption of NH4+-N in both wood residues. Thus, Wood residues high in NH4+-N should be avoided, as they could have an opposite effect in the adsorption of nutrients from nutrient-rich effluents.udThe results also showed that some wood residues (G30) had great capacity to adsorb NH4+-N to levels up to nearly 90% whilst demonstrating low desorption capacity of NH4+-N (less than 1%). These are ideal relevant features for an adsorbent material for the removal of nutrients (or heavy metals) from contaminated waters such us farm o industrial effluents, or for the depuration of eutrophic watercourses. This could help reduce the concentration of farm effluents making them more manageable, subsequently contributing towards the compliance of new environmental regulations.
机译:这项研究的目的是确定木材残留物在从营养丰富的(NH4-N)水中去除营养物质(铵态氮; NH4-N)的有效性。还确定了木质材料的持水量。该受控实验室实验在英国北怀克的Rothamsted Research进行,测试了两种木材残留物。长度为1-2cm,另一个为150μm(微米)至9.5mm。尽管广泛的研究表明,各种吸收性材料作为动物床上用品的有效性和性能,例如稻草(谷物稻草),木片(木屑,木屑或刨花),蕨菜和草皮,但很少有人关注NH4-氮的吸附/解吸能力。来自营养丰富的废水(例如,躺在木片或稻草上的牛的废水)中的木材残留物的净化能力将通过诸如养分的吸收(吸附-吸收)和解吸过程来控制。研究报道了木片材料和生物炭中木片材料的脱氮能力,以及生活和市政废水,农场污水,垃圾填埋场和工业废水中NH4 + -N的去除。这些研究已经观察到,氮的去除机理是通过通过反硝化作用(生物炭作为反硝化剂的碳源)增加N2O的损失来增加从渗滤液中去除NO3--N的作用,或者是通过吸附到带负电荷的位置来减少渗滤液中的NH4 + -N。 。结果表明,尽管阳离子交换容量(CEC)和表面积(SA)都是吸附材料的基本特性,但未发现与CEC和吸附或解吸相关。 pH的变化似乎也不足以引起CEC的变化。因此,渗透压似乎是控制两种木材残留物中NH4 + -N吸附和解吸的更主要的参数控制过程。因此,应避免使用NH4 + -N含量高的木材残留物,因为它们可能对富含养分的废水中养分的吸附产生相反的作用。 ud结果还表明,某些木材残留物(G30)具有很大的吸附NH4 +-的能力。氮水平高达近90%,同时表明NH4 + -N的解吸能力低(小于1%)。这些是吸附材料的理想相关特性,用于从工业废水等污染水中去除营养物(或重金属),或用于富营养化河道的净化。这可以帮助降低农业废水的浓度,使其更易于管理,从而有助于遵守新的环境法规。

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