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比较污泥和猪粪衍生生物炭去除硫化氢的效果。

Comparison of sewage sludge- and pig manure-derived biochars for hydrogen sulfide removal.

机构信息

School of Environmental Science and Engineering, Shanghai Jiao Tong University, Shanghai 200240, China.

School of Environmental Science and Engineering, Shanghai Jiao Tong University, Shanghai 200240, China.

出版信息

Chemosphere. 2014 Sep;111:296-303. doi: 10.1016/j.chemosphere.2014.04.014. Epub 2014 May 13.

Abstract

Biochars derived from pig manure and sewage sludge were evaluated for their abilities to remove hydrogen sulfide (H2S) from gas phase. The pig manure biochar had higher capacities for H2S sorption than sewage sludge biochar in both dynamic and static systems, and moisture improves H2S removal. Increasing the biochar moisture to 25 wt% and 100 wt% in the static system increased the pig manure biochar removal capacities by 15.9% and 58.9%, respectively, compared to the dry biochar (0 wt% moisture). The sewage sludge biochar similarly increased the removal by 1.04 and 3.30 times for 25 wt% and 100 wt% moisture, respectively. The catalytic conversion to elemental S(0) and SO4(2)(-) was the main route of H2S removal. The complete oxidation of H2S into SO4(2)(-) mainly occurred on the biochar surface, while H2S underwent incomplete oxidation into elemental S(0) in the biochar pores. The SO4(2)(-) was the dominant form in both biochars, especially for the pig manure biochar which contained 53.9% of the total sulfur at 100 wt% moisture. The SO4(2)(-) was mainly present as CaSO4 precipitate in the sewage sludge biochar, while SO4(2)(-) in the pig manure biochar was mostly soluble (K, Na)2SO4. The results indicated the waste biomass can be converted into value-added biochar as a sorbent for H2S, especially at high moisture that promotes complete oxidation of H2S into SO4(2)(-). Strong alkalinity and rich inorganic minerals originated in the biochar play an important role in its high H2S sorption ability and the final sulfur forms.

摘要

从猪粪和污水污泥中制备的生物炭被评估用于从气相中去除硫化氢(H2S)的能力。在动态和静态系统中,猪粪生物炭对 H2S 的吸附能力均高于污水污泥生物炭,并且水分可以提高 H2S 的去除率。与干生物炭(0 wt%水分)相比,在静态系统中将生物炭的水分提高到 25wt%和 100wt%,分别使猪粪生物炭的去除能力提高了 15.9%和 58.9%。污水污泥生物炭的水分分别提高到 25wt%和 100wt%时,去除能力分别提高了 1.04 倍和 3.30 倍。H2S 的主要转化途径是生成元素 S(0)和 SO4(2)(-)。H2S 完全氧化成 SO4(2)(-)主要发生在生物炭表面,而 H2S 在生物炭孔中发生不完全氧化生成元素 S(0)。SO4(2)(-)是两种生物炭中的主要形式,特别是在 100wt%水分时,猪粪生物炭中总硫的 53.9%以 SO4(2)(-)的形式存在。SO4(2)(-)主要以污水污泥生物炭中的 CaSO4 沉淀形式存在,而猪粪生物炭中的 SO4(2)(-)主要是可溶性的(K,Na)2SO4。结果表明,废生物质可以转化为增值生物炭,用作 H2S 的吸附剂,特别是在高水分条件下,可以促进 H2S 完全氧化成 SO4(2)(-)。生物炭中固有的强碱性和丰富的无机矿物质对其高 H2S 吸附能力和最终硫形态起着重要作用。

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