Impacts of hydrous manganese oxide on the retention and lability of dissolved organic matter

IF 0.9 4区 地球科学 Q4 GEOCHEMISTRY & GEOPHYSICS
Jason W. Stuckey, Christopher Goodwin, Jian Wang, Louis A. Kaplan, Prian Vidal-Esquivel, Thomas P. Beebe Jr., Donald L. Sparks
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引用次数: 40

Abstract

Minerals constitute a primary ecosystem control on organic C decomposition in soils, and therefore on greenhouse gas fluxes to the atmosphere. Secondary minerals, in particular, Fe and Al (oxyhydr)oxides—collectively referred to as “oxides” hereafter—are prominent protectors of organic C against microbial decomposition through sorption and complexation reactions. However, the impacts of Mn oxides on organic C retention and lability in soils are poorly understood. Here we show that hydrous Mn oxide (HMO), a poorly crystalline δ-MnO2, has a greater maximum sorption capacity for dissolved organic matter (DOM) derived from a deciduous forest composite Oi, Oe, and Oa horizon leachate (“O horizon leachate” hereafter) than does goethite under acidic (pH 5) conditions. Nonetheless, goethite has a stronger sorption capacity for DOM at low initial C:(Mn or Fe) molar ratios compared to HMO, probably due to ligand exchange with carboxylate groups as revealed by attenuated total reflectance-Fourier transform infrared spectroscopy. X-ray photoelectron spectroscopy and scanning transmission X-ray microscopy–near-edge X-ray absorption fine structure spectroscopy coupled with Mn mass balance calculations reveal that DOM sorption onto HMO induces partial Mn reductive dissolution and Mn reduction of the residual HMO. X-ray photoelectron spectroscopy further shows increasing Mn(II) concentrations are correlated with increasing oxidized C (C=O) content (r?=?0.78, P?<?0.0006) on the DOM–HMO complexes. We posit that DOM is the more probable reductant of HMO, as Mn(II)-induced HMO dissolution does not alter the Mn speciation of the residual HMO at pH 5. At a lower C loading (2?×?102?μg?C?m?2), DOM desorption—assessed by 0.1?M NaH2PO4 extraction—is lower for HMO than for goethite, whereas the extent of desorption is the same at a higher C loading (4?×?102?μg?C?m?2). No significant differences are observed in the impacts of HMO and goethite on the biodegradability of the DOM remaining in solution after DOM sorption reaches steady state. Overall, HMO shows a relatively strong capacity to sorb DOM and resist phosphate-induced desorption, but DOM–HMO complexes may be more vulnerable to reductive dissolution than DOM–goethite complexes.

Abstract Image

含水氧化锰对溶解有机物的滞留性和稳定性的影响
矿物构成了土壤中有机碳分解的主要生态系统控制,从而控制了温室气体向大气的通量。次生矿物,特别是铁和铝(氧合)氧化物——以下统称为“氧化物”——是有机碳通过吸附和络合反应防止微生物分解的重要保护剂。然而,锰氧化物对有机碳在土壤中的保留和稳定性的影响尚不清楚。研究表明,在酸性(pH 5)条件下,含水氧化锰(HMO) (δ-MnO2结晶性较差)对来自落叶林复合层渗滤液(以下简称“O层渗滤液”)的溶解有机物(DOM)的最大吸附能力大于针铁矿。尽管如此,与HMO相比,针铁矿在低初始C:(Mn或Fe)摩尔比下对DOM的吸附能力更强,这可能是由于衰减全反射-傅里叶变换红外光谱显示的与羧酸基的配体交换。x射线光电子能谱和扫描透射x射线显微镜-近边缘x射线吸收精细结构能谱结合Mn质量平衡计算表明,DOM吸附在HMO上引起了残余HMO的部分Mn还原溶解和Mn还原。x射线光电子能谱进一步表明,Mn(II)浓度的增加与DOM-HMO配合物上氧化C (C=O)含量的增加相关(r = 0.78, P = 0.0006)。我们假设DOM更可能是HMO的还原剂,因为Mn(II)诱导的HMO溶解不会改变pH 5下残余HMO的Mn形态。在较低的碳负荷(2 × 102 μg - cm2)下,DOM解吸率为0.1 μg - cm2。HMO对NaH2PO4的提取率低于针铁矿,而在较高的C负荷下(4 × 102 μg C·M·2),其解吸程度相同。在DOM吸附达到稳态后,HMO和针铁矿对溶液中剩余DOM生物降解性的影响无显著差异。总体而言,HMO表现出较强的吸附DOM和抵抗磷酸盐诱导解吸的能力,但DOM - HMO配合物可能比DOM -针铁矿配合物更容易受到还原性溶解的影响。
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来源期刊
Geochemical Transactions
Geochemical Transactions 地学-地球化学与地球物理
CiteScore
3.70
自引率
4.30%
发文量
2
审稿时长
>12 weeks
期刊介绍: Geochemical Transactions publishes high-quality research in all areas of chemistry as it relates to materials and processes occurring in terrestrial and extraterrestrial systems.
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