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Reactions of nitrite with goethite and surface Fe(Ⅱ)-goethite complexes

机译:亚硝酸盐与霉菌和表面Fe的反应(Ⅱ) - 乙腈复合物

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摘要

Chemodenitrification-the abiotic (chemical) reduction of nitrite (NO~-_2 ) by iron (Ⅱ)-plays an important role in nitrogen cycling due in part to this process serving as a source of nitrous oxide (N_2O). Questions remain about the fate of NO~-_2 in the presence of mineral surfaces formed during chemodenitrifkation, such as iron(Ⅲ) (hydr) oxides, particularly relative to dissolved iron(Ⅱ). In this study, stirred-batch kinetic experiments were conducted under anoxic conditions (to mimic iron(Ⅲ)-reducing conditions) from pH 5.5-8 to investigate NO~-_2 reactivity with goethite (FeOOH_(s)) and Fe(Ⅱ)-treated goethite using wet chemical and attenuated total reflectance-Fourier transform infrared (ATR-FTIR) spectroscopy. Nitrite removal from solution by goethite was more rapid at pH 5.5 than at pH 7 and 8. Spectral changes upon nitrite adsorption imply an inner-sphere surface interaction (monodentate and bidentate) at pH 5.5 based on ATR-FTIR spectra of the nitrite-goethite interface over time. In iron(Ⅱ)-amended experiments at pH 5.5 with high aqueous Fe(Ⅱ) in equilibrium with goethite, nitrous oxide was generated, indicating that nitrite removal involved a combination of sorption and reduction processes. The presence of a surface complex resembling protonated nitrite (HONO) with an IR peak near ~1258 cm~(-1) was observed in goethite-only and iron(Ⅱ)-goethite experiments, with a greater abundance of this species observed in the latter treatment. These results might help explain gaseous losses of nitrogen where nitrite and iron( Ⅱ)/goethite coexist, with implications for nutrient cycling and release of atmospheric air pollutants.
机译:Chemodenitrification-非生物(化学)还原亚硝酸盐(NO〜-_2)由铁(Ⅱ)部分由于此过程中作为一氧化二氮(N_2O)的源-plays在氮循环中起重要作用。问题仍然NO〜命运-_2中矿物的存在chemodenitrifkation期间表面上形成,如铁(Ⅲ)(氢)氧化物,特别是相对于溶解的铁(Ⅱ)。在这项研究中,搅拌分批动力学实验在缺氧条件下在pH 5.5-8进行(以模拟铁(Ⅲ)还原条件下),以调查NO〜-_2反应性的针铁矿(FeOOH_(S))和Fe(Ⅱ) - 处理的针铁矿使用湿化学和衰减全反射 - 傅立叶变换红外光谱(ATR-FTIR)光谱。从由针铁矿溶液亚硝酸盐去除在pH 5.5是更快速的比pH 7和8的光谱在亚硝酸盐吸附在改变基于ATR-FTIR光谱的亚硝酸盐的针铁矿的pH 5.5的暗示的内球表面相互作用(单齿和二齿)接口随着时间的推移。在具有高含水的Fe(Ⅱ),其与针铁矿平衡pH 5.5在铁(Ⅱ)-amended实验中,产生的一氧化二氮,表明亚硝酸盐去除涉及吸附和还原过程的组合。表面复杂外形酷似质子化亚硝酸盐(HONO)的具有IR峰存在邻近〜1258厘米〜(-1)在针铁矿仅和铁(Ⅱ)-goethite实验中观察到,与此物种中观察到的更大的丰度后者的治疗。这些结果可能有助于解释气态氮损失,其中亚硝酸盐,铁(Ⅱ)/针铁矿共存,与养分循环和大气排放污染物的影响。

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