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Scale Inhibitor Core Floods in Carbonate Cores: the Influence of pH on Phosphonate- Carbonate Interactions

机译:碳酸核核心的规模抑制剂核心:pH对膦酸盐相互作用的影响

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Scale inhibitor core floods were performed using outcrop Jurassic Portlandian chalk cores. The effect of pH on the phosphonate-carbonate interaction was studied by performing core floods at various fixed injected pH values (pH ~6, 4, and 2). The scale inhibitor (SI) used in these core floods was 5000 ppm active DETPMP adjusted to the application pH for that core flood. Effluent concentrations of scale inhibitor, lithium tracer, calcium and magnesium are measured, as are the effluent pH values. This thorough set of measurements makes it possible to interpret the inhibitor/carbonate interaction mechanisms quite clearly. Some carbonate dissolution is evident in all core floods which is quantified in our floods and, as expected, the degree of dissolution increases as pH decreases. The pH 2 core flood (C4) showed the highest carbonate dissolution to the extent that the fluid induced the formation of a worm hole through the core. Flood C3 carried out at pH 4 showed more carbonate dissolution than in floods carried out at pH 6, as well as giving high pH (~7) effluents. There is higher interaction between the injected solutions and the rock material in flood C3 (SI retention, Γ ≈ 4.5 mg/g), and an increase in permeability between the pre-treatment and post treatment stages (~13 %). All floods were modelled using a well established methodology [1, 2]. For the high pH floods (pH 6) the SI return curves were modelled very accurately using an adsorption isotherm which appears to provide an excellent description of the SI/carbonate rock interaction. For the lower pH floods (pH 4 and 2), a reasonably good, but not perfect, match was obtained using a “pseudo-adsorption isotherm” approach. However, a more complete description of the SI /rock interaction involving the role of Ca2+ is required in order to accurately model all of the features of the phosphonate/carbonate interaction.
机译:使用露头侏罗纪波特兰粉核来进行规模抑制剂核心泛滥。通过在各种固定注射的pH值(pH〜6,4和2)下进行核心泛粉来研究pH对膦酸盐 - 碳酸酯相互作用的影响。在这些核心泛洪水中使用的尺度抑制剂(SI)为5000ppm活性DECPMP,调整到该核心洪水的应用pH值。测量污垢抑制剂,锂示踪剂,钙和镁的流出浓度,是流出物pH值。这种彻底的测量值使得可以非常清楚地解释抑制剂/碳酸酯相互作用机制。在我们的洪水中量化的所有核心洪水中,一些碳酸盐溶解是明显的,并且如预期的那样,随着pH降低,溶解度增加。 pH 2核心泛洪(C4)显示出最高的碳酸盐溶解,在范围内,流体诱导通过芯形成蜗杆孔的程度。在pH4中进行的洪水C3显示比在pH6的pH6中进行的洪水中的更多碳酸盐溶解,以及给予高pH(〜7)污水。注射液与洪水C3中的岩石材料之间具有更高的相互作用(Si保留,γ≈4.5mg/ g),并且在预处理和后处理阶段之间的渗透性增加(〜13%)。所有洪水都是使用完整的方法进行建模[1,2]。对于高pH泛洪(pH6),使用吸附等温线非常精确地模拟Si返回曲线,该吸附等温线似乎提供了Si /碳酸酯岩相互作用的优异描述。对于较低的pH洪水(pH4和2),使用“伪吸附等温线”方法获得合理良好但不完美的匹配。然而,需要更完整的Si /岩石相互作用的描述,涉及Ca2 +的作用,以便准确地模拟膦酸盐/碳酸酯相互作用的所有特征。

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