储层孔隙结构对CO2地质封存井周围盐沉淀作用的影响机制

Mechanisms underlying the impacts of reservoir pore structures on near-well salt precipitation in CO2 geological storage

  • 摘要:
    目的和方法 良好的储层可注入性是优质CO2地质封存场所的必备条件,注入井周围盐水溶解于CO2造成的盐沉淀作用是导致CO2可注入性损害的关键因素之一。为探究不同类型储层盐沉淀发育机制和储层损害程度的差异,选取具有显著孔隙结构差异的砂岩样品,开展基于高温高压流体驱替系统的盐沉淀作用模拟实验,结合铸体薄片、扫描电镜及能谱、微区X射线荧光光谱、高压压汞、核磁共振、相对渗透率等测试分析,旨在揭示储层初始孔隙结构特征对盐沉淀晶体特征和分布规律的影响机制。
    结果和结论 孔隙发育的高孔高渗型储层具有盐晶体数量少、尺寸小、分散单晶体为主的盐沉淀特征,盐沉淀含量最高仅约为0.2%。随着孔喉大小、分选性和连通性变差,盐晶体数量、尺寸以及盐集合体含量增加,盐沉淀含量最高可达约4.7%。随着储层孔隙结构由均质大孔喉型向非均质小孔喉型变化,盐沉淀分布规律呈现盐水溶解主导形成的弱盐沉淀均质分布模式—盐水毛细回流主导形成的局部强盐沉淀非均质分布模式—盐水毛细回流和盐溶质扩散共同控制的强盐沉淀均质分布模式的转变过程。盐沉淀作用增强导致对井周围储层孔隙结构和可注入性的损害程度显著增加,孔渗损害率由大孔喉型储层的约1%上升至小孔喉型储层的26%和38%。不同初始孔隙结构储层具有不同的盐沉淀发育模式和可注入性损害风险,为咸水层CO2地质封存过程中储层损害的缓解提供理论依据,助力CO2地质封存的高效部署。

     

    Abstract:
    Objective and Method  High CO2 injectivity in reservoirs is essential for high-quality sites of CO2 geological storage (CGS). Salt precipitation in the vicinity of injection wells due to brine dissolution in CO2 emerges as a critical factor impairing CO2 injectivity. To explore the differences in the mechanisms behind salt precipitation and damage degree across various reservoirs, this study conducted salt precipitation simulation experiments on sandstone samples with distinct pore structures using a high-temperature and high-pressure fluid displacement system. By combining methods such as cast thin section observations, scanning electron microscopy and resulting spectra, micro-X-ray fluorescence (micro-XRF) spectroscopy, mercury injection capillary pressure (MICP), nuclear magnetic resonance (NMR), and relative permeability tests, this study aims to clarify the mechanisms underlying the impacts of initial reservoir pore structures on the crystal characteristics and distribution patterns of salt precipitation.
    Results and Conclusions  Salt precipitation in high-porosity, high-permeability porous reservoirs was characterized by a low number of small salt crystals dominated by dispersed single crystals, with a maximum salt precipitation content of merely about 0.2%. Decreases in the pore throat size, sorting, and connectivity corresponded to increases in the number and size of salt crystals, as well as the salt aggregate content. Accordingly, the maximum salt precipitation content reached up to approximately 4.7%. As the reservoir pore structures shifted from homogeneous large pore throats to heterogeneous small pore throats, the distribution patterns of salt precipitation evolved through three stages: a homogeneous distribution pattern of weak salt precipitation primarily induced by brine dissolution, a heterogeneous distribution pattern characterized by local strong salt precipitation mainly due to capillary brine reflux, and a homogeneous distribution pattern of strong salt precipitation under the joint control of capillary brine reflux and salt solute diffusion. Intensified salt precipitation significantly increased the damage to the pore structures and CO2 injectivity of reservoirs in the vicinity of injection wells. The porosity-permeability damage rate increased from about 1% in reservoirs with large pore throats to 26% and 38% in reservoirs with small pore throats. Reservoirs with varying initial pore structures exhibited different developmental patterns of salt precipitation and varying injectivity impairment risks. The results of this study will provide a theoretical basis for mitigating damage to reservoirs during CO2 geological storage in saline aquifers, thereby facilitating the efficient deployment of CO2 geological storage.

     

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