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Experimental investigations of the effects of acid gas (H_2S/CO_2) exposure under geological sequestration conditions

机译:地质封存条件下酸性气体(H_2S / CO_2)暴露的实验研究

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Acid gas (mixed CO_2 and H_2S) injection into geological formations is increasingly used as a disposal option. For example, more than 40 acid gas injection projects are currently operating in Alberta, Canada [1]. In contrast to pure CO_2 injection, there is little understanding of the possible effects of acid gases under geological sequestration conditions on exposed materials ranging from reactions with reservoir minerals to the stability of proppants injected to improve oil recovery to the possible failure of wellbore cements. The number of laboratory studies investigating effects of acid gas has been limited by safety concerns and the difficulty in preparing and maintaining single-phase H_2S/CO_2 mixtures under the experimental pressures and temperatures required. In an effort to address the lack of experimental data addressing the potential effects of acid gas injection, the Plains CO_2 Reduction Partnership (PCOR) in the United States has developed approaches using conventional syringe pumps (ISCO 260D pumps) and reactor vessels (Parr Instruments) to prepare and maintain H_2S/CO_2 mixtures under relevant sequestration conditions of temperature, pressure, and exposure to water and dissolved salts. Exposures up to several months can be conducted at temperatures and pressures up to 350°C and 414 bar (6000 psi) using any desired H_2S/CO_2 mole ratio. Up to 16 individual samples racked in separate glass vials can be exposed at one time, and the use of separate glass vessels allows different salt brine concentrations to be evaluated. In addition to performing static exposure experiments, the pumps and vessels are sufficiently leakfree that reaction rates can be determined by monitoring mass flow at the pumps. Interestingly, this is much easier to perform for reactions with H_2S than with CO_2, because H_2S is much less compressible and has lower Joule–Thompson heating/cooling effects than CO_2. Thus, obtaining accurate values for the mass of CO_2 used during an experiment based on pump volume is much more difficult than for H_2S, although controlling the pump cylinder temperature with a water jacket allows reasonable measurements to be made. These systems have been used to determine reaction rates of model systems, such as the formation of magnesium carbonate from magnesium silicate and the formation of pyrite from iron oxide (Fe_3O_4). For example, the use of H_2S (as measured at the pump) was steady at ca. 0.5 grams per day (for 18.6 grams of Fe_3O_4) until the reaction was complete. The half-life of the reaction was 20 days, and the mass balance (0.54 moles H_2S actual compared to 0.48 moles theoretical) was reasonable.
机译:将酸性气体(混合CO_2和H_2S)注入地质构造越来越多地用作处置选择。例如,目前在加拿大艾伯塔省运营了40多个酸性气体注射项目[1]。与纯CO_2注射相比,几乎没有了解酸性气体在地质封存条件下的可能影响,这些内容物料从与储存器矿物质的反应的反应到注射的支撑剂的稳定性,以改善井筒水泥的可能失败。调查酸性气体影响的实验室研究的数量受到安全问题的限制,并且在实验压力和温度下制备和维持单相H_2S / CO_2混合物的难题。为了解决缺乏寻址酸气液注入的潜在影响的实验数据,美国在美国的平原CO_2减少伙伴关系(PCOR)采用常规注射器泵(ISCO 260D泵)和反应堆血管(Parr Instruments)开发了方法。在温度,压力和暴露于水和溶解盐的相关封存条件下制备和维持H_2S / CO_2混合物。高达几个月的暴露可以在温度下进行,并且使用任何所需的H_2S / CO_2摩尔比在温度下进行高达350°C和414巴(6000psi)。在单独的玻璃小瓶中最多16个单独的样品可以一次暴露,并且使用单独的玻璃容器允许评估不同的盐水浓度。除了进行静态曝光实验之外,泵和容器足以通过监测泵上的质量流量来确定反应速率。有趣的是,对于H_2S而言,这比用CO_2更容易地表演,因为H_2S不可压缩并具有比CO_2更低的焦耳 - 汤普森加热/冷却效果。因此,基于泵体积的实验期间使用的CO_2质量的精确值比H_2S更困难,尽管用水套控制泵缸温度允许进行合理的测量。这些系统已被用于确定模型系统的反应速率,例如从硅酸镁中形成碳酸镁和来自氧化铁(Fe_3O_4)的硫铁矿的形成。例如,使用H_2S(如泵在泵中测量)在CA稳定。每天0.5克(为18.6克Fe_3O_4),直至反应完成。反应的半衰期为20天,质量平衡(0.54摩尔H_2S,实际与0.48摩尔)合理。

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