水管理

采出水处理压力日益增大

二叠纪盆地的油井产生大量的水。其中大部分被注入盆地主要石油和天然气生产区上方和下方的处理区。当水被注入这些处置区域时,压力会增加,主要是因为没有流体同时被去除。压力的增加是否令人担忧?数据表明是的。

水力压裂钻机晚上在德克萨斯州西部戏剧性的天空下拍摄,草原上有沉淀池
资料来源:grandriver/Getty Images

350亿桶。1.5万亿加仑。1 托莱多本德水库(德克萨斯州最大的湖泊)。

这大约是自美国页岩革命开始以来注入地下进行处理的二叠纪盆地油田产出水(即石油和天然气开采过程中产生的水)的体积。尽管更多地使用这些产出水来完成新的油气井,但排入地下的水量逐年增加(图 1),从 2010 年的略低于 9 亿桶增加到 2022 年的超过 50 亿桶,几乎增加六倍。B3 Insight 的数据显示,到 2030 年,这一数字预计将增长至约 70 亿桶。

压力_Fig1.jpg
图1—二叠纪 盆地油田逐年产水处理量。
来源:B3 Insight

目前,二叠纪盆地85%的采出水通过二叠纪盆地非常规油气开发的优势区特拉华和米德兰次盆地的2000多口注入井得到处理(图2)。

压力_Fig2.jpg
图 2——特拉华州和米德兰子盆地的活跃 处置井,符号用颜色区分子盆地和深度。
来源:B3 Insight

由于水源地储层岩石的渗透性较低,未使用的采出水不容易注入生产地层中。相反,绝大多数被注入“浅层”处置区(例如特拉华次盆地的特拉华山群和米德兰次盆地的圣安德烈斯组)和“深层”处置区(例如、Fusselman 地层、泥盆系地层和 Ellenburger 地层)分别位于二叠纪盆地主要非常规石油和天然气生产地层的上方和下方(图 3)。

压力_Fig3.jpg
图3-特拉华次流域和米德兰次流域油田产水和处理示意图。浅层处置区位于主要非常规石油和天然气生产地层上方,而深层处置区位于其下方。

在所指出的 2,000 多口注入井中,大约 80% 目前用于将油田产出水注入浅层处理区,特拉华和米德兰子盆地之间的比例大致相等(图 4a 和 4c)。而且,虽然与深层区域相比,相关水量的相似百分比(75%)被注入浅层处理区,但总水量(两个子流域的浅层和深层)的一半以上被注入浅层处理区。特拉华次盆地的地层(图4b和4d)。

压力_Fig4.jpg
图4’ a ) 2010年以来特拉华和米德兰次盆地活跃浅层和深层处置井数量。 b) 2010年以来特拉华和米德兰次盆地浅层和深层处置油田采出水量。 c) 2022 年特拉华和米德兰次盆地活跃浅层和深层处置井的百分比。 d) 2022 年特拉华和米德兰次盆地浅层和深层处理油田采出水量的百分比。
来源:B3 Insight

压力响应
当水注入这些处置区域时,压力会增加(图 5a),这主要是因为没有流体同时被排出(与同时生产石油、天然气和水的注水作业不同)。在主动注入过程中,在井筒处和远离井筒处会形成压力锥,其大小和形状由许多因素决定,包括注入速度;注射历史;水、井和岩石的特性;以及其他主动注入的存在[压力在重叠的压力锥之间相加(图5b)]。

压力_Fig5.jpg
5’a )主动注入之前、期间和之后的压力分布图。b) 多个活跃注入井之间重叠的压力累积锥体的描述。

一旦井停止注入,只要有足够的时间,这些动态压力锥就会消散,压力返回到其初始背景状态。然而,如果注入足够大的体积,背景压力(即,没有主动注入时的压力)也会显着增加,因为结构和地层变化限制了流体的持续运移并阻碍了压力耗散。本质上,该系统的行为就像一个密封罐。

虽然与活跃注入井周围更局部和突然的压力扰动相比,这种背景压力往往变化相对缓慢和稳定(因此图5a中使用术语“伪静态”),但由此产生的压力增加在空间和范围上更广泛。可能会持续更长时间,甚至超出油田开发的时间范围。因此,虽然运营商可以通过减少注入来主动管理活跃注入井附近的高压(尽管这引入了一系列单独的后勤挑战,将水重定向到备用处理地点),但几乎没有立即采取措施来减少背景中更隐蔽的上升。压力。从本质上讲,水箱已满,但无法快速清空。

压力是一个问题吗?
数据明确表明是的。水处理对地层压力最明显的影响是二叠纪盆地地震频率和震级的急剧上升(图6)。虽然浅层处置、深层处置和水力压裂都可能导致区域地震活动,但自 2021 年以来,德克萨斯铁路委员会 (RRC) 为减轻诱发地震事件所做的尝试主要集中在限制指定地震响应区域 (SRA) 内的深层处置。此外,今年 2 月,RRC 宣布将对新的二叠纪盆地处置井许可证增加额外要求, “以协助该机构和行业监测和应对可能有利于诱发地震活动的注入和储层条件” ”这包括在二叠纪盆地所有新的深处置井和 SRA 内的所有新浅处置井上安装井底压力监测计。

压力_Fig6.jpg
图6——2017年至今二叠纪盆地地震事件的位置 、震级和频率。

浅层压力的影响:调节器
但是为什么首先要将油田水处理到深层地层中呢?较浅的井通常更容易钻探和完井,资本和运营成本较低。这在很大程度上解释了前面提到的浅层处置井的激增。

钻深井的一个主要理由是管理和保持浅层压力。新墨西哥州监管机构已采取积极措施来实现这一结果。2016年,新墨西哥州能源、矿产和自然资源部的石油保护部门实际上暂停了浅层处置,因为担心地层压力升高和水流会对新生产井的钻探产生不利影响。通过比较新墨西哥州钻探的浅处置井比例与德克萨斯州直接跨越边境钻探的浅井比例的历史趋势,这一监管行动的结果是显而易见的(图7)。然而,RRC 也承认浅层压力是一个令人担忧的问题。在 2020 年发给处置井许可证申请人的“索取更多数据”信函中,RRC 表示,圣安德烈斯流层“值得关注 H 2 S 流量和超压”。

压力_Fig7.jpg
图 7“特拉华州为浅层处置而钻探的新次盆地处置井的百分比 (按州区分)。
来源:B3 Insight

注入井压力测量证实了浅层处理区背景压力正在增加的观点。过去 5 年进行的步进注入测试的注入前井底压力汇总数据(即伪静态背景压力)表明压力梯度(即标准化为深度的压力)正在增加,特别是在特拉华次盆地内(图8)。此外,数据还显示了压力梯度与注入区断裂梯度(即岩石开始破裂的压力)的接近程度,后者的数据也来自步进注入测试。B3 Insight 通过使用训练有素的机器学习模型将步进注入测试数据与注入井施工/完井、注入量和地表压力数据相集成,在其地下层压模型中验证并进一步完善了这些结果。对 2017 年至 2023 年注入的分析显示,特拉华次盆地的全流域浅层背景压力平均增加了 9%,米德兰次盆地增加了 3%。

压力_Fig_8_3.jpg
资料来源:B3 Insight 数据

浅层压力影响:勘探和生产公司
对浅层压力和缓解措施的担忧不仅仅局限于监管机构。一些运营商公开承认对钻井时地层完整性的担忧,以及需要额外的套管柱来控制压力。Pioneer Natural Resources在 2018 年 2 月的投资者介绍中指出,在米德兰次盆地使用四管柱套管设计“消除了使用三管柱套管设计时遇到的平衡高压层段和低压层段之间泥浆重量的挑战, “中间套管从地面穿过高压处理区设置。”

Guidon Energy(2021 年被 Diamondback Energy 收购)在题为“圣安德烈斯问题”的演讲中描述了它如何修改米德兰次盆地生产井的套管设计,以 60 万美元的增量成本添加额外的衬管,以管理钻探位于“压力过大”的 San Andres 地层与较弱的底层 Clearfork 和 Upper Spraberry 地层之间(JPT 也在 2019 年 2 月报道过)。Guidon Energy进一步指出,循环漏失和差异卡滞事件有所增加,并表示担心,随着压力上升,圣安德烈斯压井泥浆很快就会使岩石破裂。

对建井历史的分析,特别是所用套管柱的数量,证实了这些公开声明。虽然压力本身并不能决定所使用的套管柱的数量,但数据确实显示在过去十年中使用四个或更多套管柱钻探的水平井有所增加,特别是在米德兰次盆地。自 2014 年以来,特拉华次盆地使用 4 根或更多管柱钻探的井的比例普遍徘徊在 40% 至 50% 之间,而米德兰次盆地的比例已从 10% 增加到近 30%。 %。在同一时间范围内,平均钻探深度没有明显变化(图 9)。

压力_Fig9.jpg
图 9——特拉华州和米德兰次盆地水平生产井使用的套管柱数量趋势 。
来源:B3 Insight

浅压力影响:处置井运营商
从采出水处置的角度来看,压力增加也意味着处置能力减少。在德克萨斯州,每口处置井的运营均受到 RRC 制定的特定井允许的最大日注入量和最大井口压力的限制。而且,在二叠纪盆地,油井通常在达到最大注入速度之前就达到了允许的最大注入压力。在其他条件相同的情况下,初始压力越高,注入时井达到最大允许压力的速度就越快。因此,虽然德克萨斯州浅井处置井运营商在米德兰子流域和特拉华子流域平均分别使用了总许可率的约 25% 和 15%,但他们平均使用了 60% 和 60%。允许压力的 45%。

二叠纪盆地之外
水和压力管理的关系不仅仅是二叠纪盆地的问题。德克萨斯州东南部和东部、俄克拉荷马州和北达科他州的运营商也面临着水处理对地层压力和地震活动影响的挑战。石油天然气开发是一个高度关联的企业;一家公司的行为可能会严重影响另一家公司的运营。问题是,该行业能否努力实现长期压力维持的共同目标,从而在区域受到长期损害之前将运营和环境风险降至最低?

此外,随着活动围绕碳捕获和封存展开,应用从油田采出水注入中吸取的经验教训至关重要,特别是对于地质CO 2封存、水处理和生产作业可能邻近甚至重叠的地区。对地下孔隙空间进行深思熟虑、信息灵通和沟通良好的合作监督和管理对于确保作业的长期可行性和有效性至关重要,否则可能会产生相互竞争的目标和结果。

原文链接/jpt
Water management

The Growing Pressures of Produced Water Disposal

Permian Basin oil wells produce a lot of water. Much of it is injected into disposal zones above and below the basin’s primary oil- and gas-producing zone. When water is injected into these disposal zones, the pressure increases, mainly because no fluid is concurrently removed. Is this increase in pressure a concern? The data would suggest yes.

Fracking Drilling Rig Evening Shot under dramatic Sky in West Texas with Settling Ponds on the Prairie
Source: grandriver/Getty Images

35 billion barrels. 1.5 trillion gallons. 1 Toledo Bend Reservoir (the largest lake in Texas).

That’s roughly the volume of Permian Basin oilfield produced water (i.e., water produced during oil and gas extraction) that has been injected underground for disposal since the beginning of the US shale revolution. Despite greater use of this produced water to complete new oil and gas wells, the amount of water disposed into the subsurface has increased yearly (Fig. 1), from just under 900 million bbl in 2010 to over 5 billion bbl in 2022, a nearly sixfold increase. This number is forecast to grow to about 7 billion bbl by 2030, according to data from B3 Insight.

Pressure_Fig1.jpg
Fig. 1—Permian Basin oilfield produced water disposal volume by year.
Source: B3 Insight

Currently, 85% of the Permian Basin’s produced water is disposed of via more than 2,000 injection wells in the Delaware and Midland sub-basins, the predominant areas of Permian Basin unconventional oil and gas development (Fig. 2).

Pressure_Fig2.jpg
Fig. 2—Active disposal wells in the Delaware and Midland sub-basins, symbols colored to distinguish sub-basins and depths.
Source: B3 Insight

Because of the low permeability of the reservoir rocks where the water originated, the unused produced water is not easily injected back into the producing formations. Instead, the vast majority is injected into “shallow” disposal zones (e.g., the Delaware Mountain Group in the Delaware sub-basin and the San Andres Formation in the Midland sub-basin) and “deep” disposal zones (e.g., the Fusselman, Devonian, and Ellenburger formations) situated above and below, respectively, the Permian Basin’s primary unconventional oil- and gas-producing formations (Fig. 3).

Pressure_Fig3.jpg
Fig. 3—Illustration of Delaware sub-basin and Midland sub-basin oilfield water production and disposal. Shallow disposal zones lie above the principal unconventional oil- and gas-producing formations, while deep zones lie beneath.

Of the over 2,000 injection wells noted, approximately 80% are currently used to inject oilfield produced water into shallow disposal zones, with roughly an equal split between the Delaware and Midland sub-basins (Figs. 4a and 4c). And, while a similar percentage (75%) of the associated water volume is injected into the shallow disposal zones versus deep zones, more than half of the total water volume (both shallow and deep in both sub-basins) is injected into the shallow formations of the Delaware sub-basin (Figs. 4b and 4d).

Pressure_Fig4.jpg
Fig. 4—a) Number of active shallow and deep disposal wells in the Delaware and Midland sub-basins since 2010. b) Volume of oilfield produced water disposed into shallow and deep zones in the Delaware and Midland sub-basins since 2010. c) Percentage of active shallow and deep disposal wells in the Delaware and Midland sub-basins for 2022. d) Percentage of oilfield produced water volume disposed into shallow and deep zones in the Delaware and Midland sub-basins for 2022.
Source: B3 Insight

The Pressure Response
When water is injected into these disposal zones, the pressure increases (Fig. 5a), mainly because no fluid is concurrently removed (unlike waterflooding operations, where oil, gas, and water are simultaneously produced). During active injection, a cone of pressure buildup develops at and away from the wellbore, the size and shape of which are dictated by a host of factors including the injection rate; the injection history; properties of the water, well, and rock; and the presence of other active injection [pressure is additive among overlapping pressure cones (Fig. 5b)].

Pressure_Fig5.jpg
Fig. 5—a) Illustration of the pressure distribution before, during, and after active injection. b) Depiction of overlapping cones of pressure buildup among multiple actively injecting wells.

Once wells stop injecting, given enough time, these dynamic pressure cones dissipate and pressure returns to its initial background state. However, if a large enough volume is injected, the background pressure (i.e., the pressure in the absence of active injection) also measurably increases as structural and stratigraphic changes restrict continued fluid migration and hinder pressure dissipation. In essence, the system behaves like a sealed tank.

While this background pressure tends to change relatively slowly and steadily (hence the terminology “pseudo-static” used in Fig. 5a) compared with the more local and abrupt pressure perturbations around active injection wells, the resulting pressure increase is broader spatially and potentially much longer-lasting, even extending beyond the timescale of field development. So, while operators can actively manage the elevated pressure near active injection wells by curtailing injection (though this introduces a separate set of logistical challenges to redirect the water to alternate disposal locations), there is little immediate recourse to reduce the more insidious rise in background pressure. In essence, the tank fills up without a way to empty quickly.

Is Pressure a Concern?
The data would suggest unequivocally yes. The most discernable impact of water disposal affecting formation pressure is the steep rise in the frequency and magnitude of Permian Basin earthquakes (Fig. 6). While shallow disposal, deep disposal, and hydraulic fracturing may all contribute to area seismicity, attempts since 2021 by the Texas Railroad Commission (RRC) to mitigate induced seismic events have focused primarily on restricting deep disposal within designated seismic response areas (SRAs). Furthermore, in February of this year, the RRC announced that it would add additional requirements to new Permian Basin disposal well permits “… to assist the agency and industry in monitoring and responding to injection and reservoir conditions that may be conducive to induced seismicity.” This includes installing bottomhole pressure monitoring gauges on all new deep disposal wells in the Permian Basin and all new shallow disposal wells within the SRAs.

Pressure_Fig6.jpg
Fig. 6—Location, magnitude, and frequency of Permian Basin seismic events, 2017 to present.

Shallow Pressure Impacts: Regulators
But why dispose of oilfield water into deep formations in the first place? Shallower wells generally are more straightforward to drill and complete, with lower capital and operating costs. And this explains, in large part, the proliferation of shallow disposal wells noted previously.

A principal justification for drilling deep wells is to manage and preserve shallow pressure. New Mexico regulators have taken proactive measures to achieve this outcome. In 2016, the Oil Conservation Division of New Mexico’s Energy, Minerals, and Natural Resources Department effectively placed a moratorium on shallow disposal over concerns of elevated formation pressure and water flows adversely affecting the drilling of new production wells. The result of this regulatory action is evident when comparing historical trends in the fraction of shallow disposal wells drilled in New Mexico against the fraction of shallow wells drilled immediately across the border in Texas (Fig. 7). The RRC, however, has also acknowledged shallow pressure as a concern. In a 2020 “Request for Additional Data” letter sent to a disposal well permit applicant, the RRC stated that the San Andres “is a formation of concern for H2S flows and overpressure.”

Pressure_Fig7.jpg
Fig. 7—Percentage of new Delaware sub-basin disposal wells drilled for shallow disposal, distinguished by state.
Source: B3 Insight

The notion that the background pressure is increasing in the shallow disposal zones is substantiated by injection well pressure measurements. Aggregated pre-injection bottomhole pressure data (i.e., pseudo-static background pressure) from step-rate injection tests conducted over the past 5 years suggests the pressure gradient (i.e., pressure normalized to depth) is increasing, particularly within the Delaware sub-basin (Fig. 8). Additionally, the data show how close the pressure gradient is to the injection zone fracture gradient (i.e., the pressure at which the rocks begin to break), with the latter data also derived from the step-rate injection tests. B3 Insight has validated and further refined these results in its Subsurface Interval Pressure model by integrating the step-rate injection test data with injection well construction/completion, injection volume, and surface pressure data using trained machine learning models. Analysis of 2017–2023 injection shows a basinwide average increase in shallow background pressure of 9% for the Delaware sub-basin and 3% for the Midland sub-basin.

Pressure_Fig_8_3.jpg
Source: Data from B3 Insight

Shallow Pressure Impacts: Exploration and Production Companies
Concerns about shallow pressure and the measures to mitigate are not just confined to regulators. Several operators have publicly acknowledged concerns about formation integrity while drilling and the need for extra strings of casing to manage pressure. Pioneer Natural Resources, in a February 2018 investor presentation, noted that using a four-string casing design in the Midland sub-basin “eliminates the challenges of balancing mud weights between high and low pressured intervals experienced utilizing a three-string casing design,” where the “… intermediate casing is set from the surface through the higher-pressured disposal zone.”

Guidon Energy (acquired by Diamondback Energy in 2021) described in a presentation titled “The San Andres Problem” how it modified the casing design for Midland sub-basin production wells, adding an extra liner at a $600,000 incremental cost, to manage drilling between the "over-pressured" San Andres formation and the weaker underlying Clearfork and Upper Spraberry formations (also reported by JPT in February 2019). Guidon Energy further noted increased lost circulation and differential sticking events and expressed worry that, as pressure rises, San Andres kill mud will soon fracture the rock.

Analysis of well construction history, particularly the number of casing strings used, corroborates these public statements. While pressure alone does not dictate the number of casing strings used, the data does show an increase in horizontal wells drilled with four or more casing strings over the past decade, particularly in the Midland sub-basin. While the percentage of the wells in the Delaware sub-basin drilled with four or more strings has generally hovered between 40% and 50% dating back to 2014, the percentage of wells in the Midland sub-basin has increased from 10% to nearly 30%. Over the same timeframe, there has been no appreciable change in average drilling depth (Fig. 9).

Pressure_Fig9.jpg
Figure 9—Trends in the number of casing strings used for Delaware and Midland Sub-basin horizontal production wells.
Source: B3 Insight

Shallow Pressure Impacts: Disposal Well Operators
From a produced water disposal perspective, increasing pressure also means less disposal capacity. In Texas, each disposal well’s operation is constrained by a well-specific permitted maximum daily injection rate and maximum wellhead pressure established by the RRC. And, in the Permian Basin, wells generally reach the permitted maximum injection pressure before reaching the maximum injection rate. All else being equal, the higher the initial pressure, the more quickly a well will reach its maximum permitted pressure when injecting. So, while Texas shallow-well disposal well operators are, on average, using approximately 25% and 15% of the total permitted rate in the Midland sub-basin and Delaware sub-basin, respectively, they are using an average of 60% and 45% of the permitted pressure.

Beyond the Permian Basin
The nexus of water and pressure management is not just a Permian Basin concern. Operators in southeast and east Texas, Oklahoma, and North Dakota also face challenges with the influence of water disposal on formation pressure and seismicity. Oil and gas development is a highly interconnected enterprise; one company’s actions can significantly affect another’s operations. The question is, can the industry work toward a common goal of long-term pressure maintenance that minimizes operational and environmental risk before areas are compromised long-term?

Furthermore, as activity builds around carbon capture and storage, it will be crucial to apply the lessons learned from oilfield produced water injection, particularly to areas where geologic CO2 sequestration, water disposal, and production operations may be in proximity, or even overlap. Well-considered, well-informed, and well-communicated cooperative oversight and management of the subsurface pore space will be essential to ensure the long-term viability and effectiveness of operations with possibly otherwise competing objectives and outcomes.