首页> 外文会议>International Conference on Greenhouse Gas Control Technologies; 20040905-09; Vancouver(CA) >EVALUATION OF THE SPREAD OF ACID-GAS PLUMES INJECTED IN DEEP SALINE AQUIFERS IN WESTERN CANADA AS AN ANALOGUE FOR CO_2 INJECTION INTO CONTINENTAL SEDIMENTARY BASINS
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EVALUATION OF THE SPREAD OF ACID-GAS PLUMES INJECTED IN DEEP SALINE AQUIFERS IN WESTERN CANADA AS AN ANALOGUE FOR CO_2 INJECTION INTO CONTINENTAL SEDIMENTARY BASINS

机译:加拿大西部深层盐岩层中注入的酸性气体柱的扩散评估,作为向陆相沉积盆地中注入CO_2的类似物

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For the past 15 years, oil and gas producers in the Alberta Basin in western Canada have increasingly turned to disposal of acid gas (H_2S and CO_2, with minor traces of hydrocarbons) by injection into deep geological formations. By the end of 2003, more than 4.5 Mt of acid gas, ranging in composition from 2% H_2S and 95% CO_2 to 83% H_2S and 14% CO_2, have been injected at 39 locations. The acid gas is injected into deep saline aquifers at 24 sites, and into depleted oil or gas reservoirs at the remainder, at rates that range from 1x10~3 to 500x10~3 m~3/d. At in situ conditions, the flow of the injected acid gas is driven and controlled by the hydrodynamic force due to injection and by differences in density and viscosity between the injected gas and the formation water. In a sedimentary basin extensively drilled for hydrocarbon exploration and production like the Alberta Basin there are wells that penetrate the disposal aquifer in the vicinity of the injection well that can be reached by a migrating plume of acid gas. Thus, the acid-gas disposal operations in western Canada represent an analogue for CO_2 storage in geological media in mature continental sedimentary basins like those in North America where oil has been discovered and produced since the 19th century and where many wells can be encountered by a plume of injected CO_2.rnTo assess the potential for upward leakage along improperly completed and/or abandoned wells, it is necessary to estimate the evolution and spread of the plume of injected acid gas and identify the existing wells within the plume's reach. A semi-analytical solution has been developed and applied to the radial spread of a plume of injected acid gas around an injection well. The flow of the injected acid gas is driven by the injection hydrodynamic force and by the density difference between the acid gas and formation water (buoyancy), and is controlled by the mobility ratio between the two fluids. The analytical derivation explicitly shows that the plume evolution and speed of spread depend on two classes of parameters: aquifer characteristics, such as porosity, permeability and thickness; and injection and fluid characteristics, such as injection rate, and fluid density and mobility. The effect of buoyancy is small and the plume evolution is controlled by the mobility ratio between the injected gas and the formation water, with gravitational forces playing a minor role in segregating the two fluids, when acid gas of high mobility contrast is injected at a high injection rate (strong hydrodynamic force) into a thin aquifer with low permeability and porosity. Buoyancy is important and even may dominate the transport problem in the case of low injection rates of light acid gas into thick aquifers with high porosity and permeability. An immediate and simple application of this semi-analytical solution is the explicit prediction of the maximum extent of an injection plume, which depends on the mobility contrast between the two fluids, on injection rate, on the length of time since the start of injection, and on aquifer thickness and porosity. Application to the case of acid-gas injection operations in western Canada shows that the respective acid-gas plumes have probably spread at distances that, depending on the particular case, range from approximately 150 m to less than 2100 m from the injection well. This method allows for the easy identification of existing wells that may be reached by a plume of injected CO_2 or acid gas.
机译:在过去的15年中,加拿大西部艾伯塔盆地的石油和天然气生产商越来越多地通过注入深层地质构造来处置酸性气体(H_2S和CO_2,其中含有少量的碳氢化合物)。到2003年底,已经在39个位置注入了超过4.5 Mt的酸性气体,其组成从2%H_2S和95%CO_2到83%H_2S和14%CO_2不等。酸性气体以1x10〜3至500x10〜3 m〜3 / d的速率注入到24个位置的深层盐水层中,其余部分注入枯竭的油气藏中。在原位条件下,注入的酸性气体的流动由注入引起的流体动力以及注入的气体与地层水之间的密度和粘度差异来驱动和控制。在像阿尔伯塔盆地那样为碳氢化合物勘探和生产而广泛钻探的沉积盆地中,有一些井可渗透注入井附近的处置含水层,而酸性气体的羽状流可以到达该沉积井。因此,加拿大西部的酸性气体处置业务代表了成熟大陆沉积盆地地质介质中CO_2的存储类似物,例如北美地区,自19世纪以来就发现和生产了石油,而北美可能遇到许多油井。为了评估沿未完工和/或废弃井的向上泄漏的潜力,有必要估算注入的酸性气体的羽流的演化和扩散,并确定羽流范围内的现有井。已开发出一种半分析解决方案,并将其应用于围绕注入井的注入酸性气体羽流的径向扩散。注入的酸性气体的流动由注入流体动力和酸性气体与地层水之间的密度差(浮力)驱动,并由两种流体之间的迁移率控制。分析推导明确表明,羽状流的演化和扩散速度取决于两类参数:含水层特征,例如孔隙度,渗透率和厚度;含水量特征。以及注入和流体特性,例如注入速率,流体密度和流动性。浮力的影响很小,并且羽流的演化受注入的气体与地层水之间的迁移率控制,当以高迁移率对比的酸性气体以高注入率注入时,重力对分离两种流体的作用较小。向低渗透率和低孔隙率的薄含水层中注入速度(强水动力)。在将轻酸气体以低孔隙度和高渗透率注入到厚含水层中时,浮力很重要,甚至可能主导运输问题。这种半分析解决方案的直接而简单的应用是显着预测注入羽流的最大范围,这取决于两种流体之间的流动性对比,注入速率,自注入开始以来的时间长度,以及含水层的厚度和孔隙率。在加拿大西部的酸性气体注入作业中的应用表明,根据特定情况,各个酸性气体羽流的散布距离视注入井而定,范围约为150 m至小于2100 m。此方法可以轻松识别通过注入的CO_2或酸性气体羽流可能到达的现有井。

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