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Macroscopic and microscopic perspectives on dissolution of carbonate minerals.

机译:碳酸盐矿物溶解的宏观和微观观点。

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摘要

Carbonate mineral dissolution and precipitation partially regulate the pH and alkalinity of natural waters, affecting the fate and transport of contaminants. A detailed understanding of the microscopic behavior of these mineral surfaces is essential to the development of quantitative geochemical models. To that end, a series of studies investigating the dissolution of an isostructural series of carbonates, including calcite (CaCO3), magnesite (MgCO3), rhodochrosite (MnCO3), siderite (FeCO 3), and smithsonite (ZnCO3), is conducted by simultaneous atomic force microscopy/flow-though reactor experiments under oxic and anoxic conditions.; Macroscopically, carbonate dissolution occurs by parallel proton- and water-promoted dissolution reactions under anoxic conditions. These reactions are cast mathematically as mechanistic or surface complexation models. Circumneutral dissolution rates vary from 10−5.5 for CaCO3 to 10−8.9 mol m−2 s−1 for MgCO3. Trends in dissolution rates as a function of composition are rationalized by literature water exchange rates and calculated energies.; Microscopically, dissolution occurs by crystallographically-controlled pit formation of and subsequent step retreat. For type I carbonates (CaCO 3 and MnCO3), near rhombohedral pits form at all pH values. For type II carbonates (FeCO3 and MgCO3), rhombohedral pits form for pH > 4. However, for pH 4, steps reorient, resulting in a change in pit morphology. ZnCO3, a type III carbonate, forms distorted pits at pH > 4 and triangular pits at pH 4, possibly due to the formation of tetrahedral Zn2+ surface complexes.; Microscopic dissolution rates derived from the observation of surface microtopographic changes are compared to macroscopic dissolution rates derived from changes in aqueous metal ion concentration. Macroscopic and microscopic dissolution rates agree within a factor of four for type I carbonates at all pH values and for type II carbonates for pH > 4. However, macroscopic and microscopic dissolution rates for type II carbonates diverge for pH 4 to a maximum 30-fold separation.; Oxygen is a critical parameter for the dissolution of redox active carbonates. For MnCO3 under oxic conditions, a tabular Mn2O 3 precipitate forms for 5.8 pH 7.7, while MnOOH hillocks form at pH > 7.7. For FeCO3 for 6.0 pH 10.3, hillock Fe(OH) 3 precipitates form at steps, accompanied by a decrease in macroscopic dissolution rates.
机译:碳酸盐矿物的溶解和沉淀部分地调节了天然水的pH值和碱度,影响了污染物的命运和转移。对这些矿物表面的微观行为的详细了解对于开发定量地球化学模型至关重要。为此,进行了一系列研究,研究了方解石(CaCO 3 ),菱镁矿(MgCO 3 ),菱锰矿(MnCO 3 ),菱铁矿(FeCO 3 )和菱铁矿(ZnCO 3 )是通过同时在氧气中进行原子力显微镜/通流反应器实验而进行的和缺氧条件。宏观上,碳酸盐溶解是在缺氧条件下通过质子和水促进的平行溶解反应发生的。这些反应在数学上被视为机械或表面络合模型。周围神经溶解速率从CaCO 3 的10 -5.5 到10 -8.9 mol m -2 s 3 的> −1 。溶解速率随组成变化的趋势可通过文献中的水交换速率和计算出的能量来合理化。在显微镜下,通过晶体学控制的凹坑形成以及随后的步骤后退而发生溶解。对于I型碳酸盐(CaCO 3 和MnCO 3 ),在所有pH值下均会形成菱面体凹坑。对于II型碳酸盐(FeCO 3 和MgCO 3 ),pH> 4时会形成菱形的凹坑。但是,对于pH <4而言,步骤会重新定向,导致凹坑发生变化形态学。 ZnCO 3 (一种III型碳酸盐)在pH> 4时形成扭曲的凹坑,在pH <4时形成三角形的凹坑,这可能是由于形成了四面体Zn 2 + 表面复合物。 ;将观察到的表面微观形貌变化得出的微观溶解速率与源自含水金属离子浓度变化的宏观溶解速率进行比较。对于所有pH值的I型碳酸盐,对于pH> 4的II型碳酸盐,宏观和微观溶出度均在四倍之内。但是,对于pH <4的II型碳酸盐,宏观和微观的溶出度相差最大30-折叠分离。氧是氧化还原活性碳酸盐溶解的关键参数。对于含氧条件下的MnCO 3 ,在5.8 H <7.7的条件下,会形成板状Mn 2 O 3 沉淀,而MnOOH小丘在pH>时形成。 7.7。对于FeCO 3 在6.0 H <10.3时,小丘Fe(OH) 3 逐步形成沉淀,同时宏观溶解速率降低。

著录项

  • 作者

    Duckworth, Owen William.;

  • 作者单位

    Harvard University.;

  • 授予单位 Harvard University.;
  • 学科 Geochemistry.; Engineering Environmental.
  • 学位 Ph.D.
  • 年度 2003
  • 页码 183 p.
  • 总页数 183
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类 地质学 ; 环境污染及其防治 ;
  • 关键词

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