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Standard Practice for (Analytical Procedure) for Determining Transmissivity of Confined Nonleaky Aquifers by Underdamped Well Response to Instantaneous Change in Head (Slug Test) 用欠阻尼井对水头瞬时变化的响应测定承压无渗漏含水层透射率的标准实施规程(分析程序)(段塞试验)
发布日期: 2020-05-15
1.1 本规程涵盖从测量井含水层系统平衡水位的阻尼振荡到井中水位突然变化的透射率测定。井中水位对水位突变的欠阻尼响应的特征是围绕静态水位的振荡波动,波动幅度减小,并恢复到初始水位。欠阻尼响应可能发生在开采高渗透性承压含水层的油井和具有长水柱的深井中。 1.2 该分析程序与现场程序测试方法结合使用 D4044/D4044M 用于收集测试数据。 1.3 限制- 段塞试验被认为是对承压含水层透射率的估计。 本试验方法要求已知储能系数。这种做法的假设规定了一口完全穿透的井(在含水层的整个厚度上打开的井),但段塞测试方法通常使用部分穿透的井进行。在含水层分层且水平导水率远大于垂直导水率的条件下,可以接受这种做法。在这种情况下,测试将被视为代表与井开放区间相邻的含水层部分的平均导水率。该方法假设层流,适用于初始水位位移小于静态水柱长度的0.1或0.2的段塞试验。 1.4 本文所述的分析实践由van der Kamp推导而来 ( 1. ) 2. 基于欠阻尼响应与指数阻尼正弦响应的近似。Kipp对水井对水位突然变化的响应进行了更严格的分析 ( 2. ) 表明van der Kamp提出的方法 ( 1. ) 匹配Kipp的解决方案 ( 2. ) 当阻尼参数值小于约0.2且时间大于振荡第一个峰值时 ( 2. ) . 1.5 单位- 以国际单位制或英寸-磅单位表示的数值应单独视为标准值。每个系统中的值可能不是精确等价的;因此,每个系统应独立使用。将两个系统的值合并可能会导致不符合标准。 以国际单位制以外的单位报告试验结果不应视为不符合本惯例。 1.6 所有观察值和计算值应符合实践中确定的有效数字和舍入准则 D6026 . 1.7 本实践提供了一组用于执行一个或多个特定操作的说明。本文件不能取代教育或经验,应与专业判断一起使用。并非实践的所有方面都适用于所有情况。本ASTM标准不代表或取代必须根据其判断给定专业服务的充分性的谨慎标准,也不应在不考虑项目的许多独特方面的情况下应用本文件。本文件标题中的“标准”一词仅表示该文件已通过ASTM共识程序获得批准。 1.8 本标准并非旨在解决与其使用相关的所有安全问题(如有)。本标准的用户有责任在使用前制定适当的安全、健康和环境实践,并确定监管限制的适用性。 1.9 本国际标准是根据世界贸易组织技术性贸易壁垒(TBT)委员会发布的《关于制定国际标准、指南和建议的原则的决定》中确立的国际公认标准化原则制定的。 ====意义和用途====== 6.1 物理系统的假设如下: 6.1.1 含水层厚度均匀,由上下不透水层限制。 6.1.2 含水层具有恒定的均匀孔隙度和基质压缩性,具有均匀和各向同性的导水性。 6.1.3 圆柱坐标系的原点位于含水层顶部的井筒轴上。 6.1.4 含水层被完全屏蔽。 6.2 定义动量平衡的假设如下: 6.2.1 在井筒段上,井中的平均水流速度近似恒定。 6.2.2 流体为层流,通过井网的流体产生的摩擦水头损失可忽略不计。 6.2.3 通过井网的水流均匀分布在整个含水层厚度上。 6.2.4 从穿过筛网的径向流到井中的垂直流的水流速度的动量变化可以忽略不计。 6.2.5 系统响应是一个指数衰减的正弦函数。 注3: 本标准产生的结果的质量取决于执行该标准的人员的能力,以及所用设备和设施的适用性。符合实践标准的机构 D3740 通常认为能够胜任和客观的测试/采样/检查等。本标准的用户应注意遵守惯例 D3740 本身并不能保证可靠的结果。可靠的结果取决于许多因素;实践 D3740 提供了一种评估其中一些因素的方法。
1.1 This practice covers determination of transmissivity from the measurement of the damped oscillation about the equilibrium water level of a well-aquifer system to a sudden change of water level in a well. Underdamped response of water level in a well to a sudden change in water level is characterized by oscillatory fluctuation about the static water level with a decrease in the magnitude of fluctuation and recovery to initial water level. Underdamped response may occur in wells tapping highly transmissive confined aquifers and in deep wells having long water columns. 1.2 This analytical procedure is used in conjunction with the field procedure Test Method D4044/D4044M for collection of test data. 1.3 Limitations— Slug tests are considered to provide an estimate of transmissivity of a confined aquifer. This test method requires that the storage coefficient be known. Assumptions of this practice prescribe a fully penetrating well (a well open through the full thickness of the aquifer), but the slug test method is commonly conducted using a partially penetrating well. Such a practice may be acceptable for application under conditions in which the aquifer is stratified and horizontal hydraulic conductivity is much greater than vertical hydraulic conductivity. In such a case the test would be considered to be representative of the average hydraulic conductivity of the portion of the aquifer adjacent to the open interval of the well. The method assumes laminar flow and is applicable for a slug test in which the initial water-level displacement is less than 0.1 or 0.2 of the length of the static water column. 1.4 This practice for analysis presented here is derived by van der Kamp ( 1 ) 2 based on an approximation of the underdamped response to that of an exponentially damped sinusoid. A more rigorous analysis of the response of wells to a sudden change in water level by Kipp ( 2 ) indicates that the method presented by van der Kamp ( 1 ) matches the solution of Kipp ( 2 ) when the damping parameter values are less than about 0.2 and time greater than that of the first peak of the oscillation ( 2 ) . 1.5 Units— The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values in each system may not be exact equivalents; therefore each system shall be used independently of the other. Combining values from the two systems may result in non-conformance with the standard. Reporting of test results in units other than SI shall not be regarded as nonconformance with this practice. 1.6 All observed and calculated values shall conform to the guidelines for significant digits and rounding established in Practice D6026 . 1.7 This practice offers a set of instructions for performing one or more specific operations. This document cannot replace education or experience and should be used in conjunction with professional judgment. Not all aspects of the practice may be applicable in all circumstances. This ASTM standard is not intended to represent or replace the standard of care by which the adequacy of a given professional service must be judged, nor should this document be applied without the consideration of a project’s many unique aspects. The word “Standard” in the title of this document means only that the document has been approved through the ASTM consensus process. 1.8 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. 1.9 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee. ====== Significance And Use ====== 6.1 The assumptions of the physical system are given as follows: 6.1.1 The aquifer is of uniform thickness and confined by impermeable beds above and below. 6.1.2 The aquifer is of constant homogeneous porosity and matrix compressibility and of homogeneous and isotropic hydraulic conductivity. 6.1.3 The origin of the cylindrical coordinate system is taken to be on the well-bore axis at the top of the aquifer. 6.1.4 The aquifer is fully screened. 6.2 The assumptions made in defining the momentum balance are as follows: 6.2.1 The average water velocity in the well is approximately constant over the well-bore section. 6.2.2 Flow is laminar and frictional head losses from flow across the well screen are negligible. 6.2.3 Flow through the well screen is uniformly distributed over the entire aquifer thickness. 6.2.4 Change in momentum from the water velocity changing from radial flow through the screen to vertical flow in the well are negligible. 6.2.5 The system response is an exponentially decaying sinusoidal function. Note 3: The quality of the result produced by this standard is dependent on the competence of the personnel performing it, and the suitability of the equipment and facilities used. Agencies that meet the criteria of Practice D3740 are generally considered capable of competent and objective testing/sampling/inspection/etc. Users of this standard are cautioned that compliance with Practice D3740 does not in itself assure reliable results. Reliable results depend on many factors; Practice D3740 provides a means of evaluating some of those factors.
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