Groundwater Modeling Calculation for the Cone of Depression
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Drawdown Analysis of the Local Middle and Lower Trinity Aquifers
TECHNICAL MEMORANDUM TO: Mr. Dirk Aaron, General Manager, CUWCD FROM: Michael R. Keester, P.G. SUBJECT: Drawdown Analysis of the Local Middle and Lower Trinity Aquifers DATE: October 5, 2018 As noted in previous analyses of water level changes, District constituents have expressed concerns regarding declining water levels in the Trinity Aquifer. In addition, in response to proposed mining operations in northern Williamson County, landowners reached out to the District to better understand Trinity Aquifer conditions and how the pumping by the mine operators may affect their wells. To assess the current conditions of the aquifer, we built upon previous analyses of the changes in water levels in the Middle Trinity Aquifer in southern Bell and northern Williamson counties. As part of our analysis, we expanded our evaluation to include an assessment of the water level conditions for the Lower Trinity Aquifer. Methodology We began by assembling the most recent water level data collected in 2018. Within Bell County, we relied primarily on the water level measurements collected by District staff or from continuous monitoring wells maintained by the Texas Water Development Board. These water levels and locations were the most reliable as the water levels are collected regularly and the aquifer designation for the well has been reviewed by District staff and multiple hydrogeologists. To supplement the water level data available from the District’s database, we also collected records from the Submitted Driller’s Report database. This database provides a record of well completions as reported by licensed water well drillers. Data associated with the report includes the location of the well, the depth and completion interval of the well, and the water level in the well at the time of completion. -
Ground Water Introduction and Demonstration
Ground Water Introduction and Demonstration Page Content By Kimberly Mullen, CPG http://www.ngwa.org/Fundamentals/teachers/Pages/Ground-Water-Introduction-and- Demonstration.aspx Objective Students will be able to define terms pertaining to groundwater such as permeability, porosity, unconfined aquifer, confined aquifer, drawdown, cone of depression, recharge rate, Darcy’s law, and artesian well. Students will be able to illustrate environmental problems facing groundwater, (such as chemical contamination, point source and nonpoint source contamination, sediment control, and overuse). Introduction Looking at satellite photographs of the planet Earth can illustrate the fact that the majority of the Earth’s surface is covered with water. Earth is known as the “Blue Planet.” Seventy-one percent of the Earth’s surface is covered with water. There also is water beneath the surface of the Earth. Yet, with all of the water present on Earth, water is still a finite source, cycling from one form to another. This cycle, known as the hydrologic cycle, is an important concept to help understand the water found on Earth. In addition to understanding the hydrologic cycle, you must understand the different places that water can be found—primarily above the ground (as surface water) and below the ground (as groundwater). Today, we will be starting to understand water below the ground. General definitions and discussion points “What is groundwater?” Groundwater is defined as water that is found beneath the water table under Earth’s surface. “Why is groundwater important?” Groundwater, makes up about 98 percent of all the usable fresh water on the planet, and it is about 60 times as plentiful as fresh water found in lakes and streams. -
A New Approach to the Step-Drawdown Test
A new approach to the step-drawdown test Dr. Gianpietro Summa Ph.D. in Environmental and Applied Geology Monticchio Bagni 85028 Rionero in Vulture (Potenza), Italy e-mail: [email protected] Abstract In this paper a new approach to perform step-drawdown tests in presented. Step-drawdown tests known so far are performed strictly keeping the value of the pumping rates constant through all the steps of the test. Current technology allows us to let the submerged electric pumps work at a specific revolution per minute (rpm) and allows us to suitably modify the rotation velocity at every step. Our approach is based on the idea of keeping the value of rpm fixed at every step of the test, instead of keeping constant the value of the discharge. Our technique has been experimentally applied to a well and a description of the operations and results are thoroughly presented. Our approach, in this peculiar case, has made possible to understand how actually the discharge Q varies in function of the drawdown sw . It has also made possible to monitor the approaching of the equilibrium between Q and sw , using both the variation of Q and that of sw with time. Moreover, we have seen that for the well studied in this paper the ratio Q/ sw remains almost constant within each step. Keywords characteristic curve - pumping test - equipment/field techniques - hydraulic testing Introduction Step-drawdown tests are nowadays quite popular: they are the most frequently performed tests in the case of single well (Kawecki 1995). There are various reasons why they are performed: in the case of exploration wells, they allow to determine the proper discharge rate for the subsequent aquifer test; in the case of exploitation wells they allow, among other things, to understand the behavior of the well during the pumping, to determine the optimum production capacity and to analyze the well performance over time (Boonstra and Kselik 2001). -
American Water Works Association California-Nevada Section Annual Fall Conference 2015 Las Vegas, Nevada – October 27, 2015 1
Russell J. Kyle, MS, PG, CHG Associate Hydrogeologist Wood Rodgers, Inc. American Water Works Association California-Nevada Section Annual Fall Conference 2015 Las Vegas, Nevada – October 27, 2015 1. Basics of Pumping Wells 2. Types of Pumping Tests 3. Test Procedures 4. Data Analysis 5. Summary Basics of a Pumping Well Discharge Ground Surface Static Water Level Aquifer Loss Cone of Depression Well Loss Pumping Water Level Aquifer Cone of Depression Pumping Depression (1 Well) Specific Capacity Discharge Rate (gpm) Ground Surface Static Water Level Aquifer Loss Drawdown (ft) Well Loss Aquifer Specific Capacity (gpm/ft) = Discharge Rate / Drawdown Specific Capacity Specific capacity (Q/s) defines the relationship between drawdown in the well and its discharge rate. gallons per minute per foot (gpm/foot) of drawdown Often used as a metric of well performance Varies with both time and flow rate. Lower specific capacities will result in deeper pumping water levels, resulting in higher energy costs to pump. Example Calculation Q = 1,793 gpm Static water level = 114.07 feet Pumping water level = 160.3 feet Q/s = 1,793 gpm / (160.3 ft – 114.07 ft) = 39 gpm/ft Well Efficiency Discharge Rate (gpm) Ground Surface Static Water Level Aquifer Loss Drawdown (ft) Well Loss Aquifer Well Efficiency (%) = Aquifer Loss / Total Drawdown Well Interference Discharge Ground Surface Static Water Level Cone of Depression Interference Aquifer Well Interference Coalescing Pumping Depressions (2 Wells) 1. 2. Types of Pumping Tests 3. 4. 5. Typical Pumping -
Table of Common Symbols Used in Hydrogeology
Common Symbols used in GEOL 473/573 A Area [L2] b Saturated thickness of an aquifer [L] d Diameter [L] e void ratio (dimensionless) or e1 is a constant = 2.718281828... f Number of head drops in a flow of net F Force [M L T-2 ] g Acceleration due to gravity [9.81 m/s2] h Hydraulic head [L] (Total hydraulic head; h = ψ + z) ho Initial hydraulic head [L], generally an initial condition or a boundary condition dh/dL Hydraulic gradient [dimensionless] sometimes expressed as i 2 ki Intrinsic permeability [L ] K Hydraulic conductivity [L T-1] -1 Kx, Ky , Kz Hydraulic conductivity in the x, y, or z direction [L T ] L Length from one point to another [L] n Porosity [dimensionless] ne Effective porosity [dimensionless] q Specific discharge [L T-1] (Darcy flux or Darcy velocity) -1 qx, qy, qz Specific discharge in the x, y, or z direction [L T ] Q Flow rate [L3 T-1] (discharge) p Number of stream tubes in a flow of net P Pressure [M L-1T-2] r Radial coordinate [L] rw Radius of well over screened interval [L] Re Reynolds’ number [dimensionless] s Drawdown in an aquifer [L] S Storativity [dimensionless] (Coefficient of storage) -1 Ss Specific storage [L ] Sy Specific yield [dimensionless] t Time [T] T Transmissivity [L2 T-1] or Temperature (degrees) u Theis’ number [dimensionless} or used for fluid pressure (P) in engineering v Pore-water velocity [L T-1] (Average linear velocity) V Volume [L3] 3 VT Total volume of a soil core [L ] 3 Vv Volume voids in a soil core [L ] 3 Vw Volume of water in the voids of a soil core [L ] Vs Volume soilds in a soil -
Sinkhole Physical Models to Simulate and Investigate Sinkhole Collapses
SINKHOLE PHYSICAL MODELS TO SIMULATE AND INVESTIGATE SINKHOLE COLLAPSES Mohamed Alrowaimi Doctoral Student, Civil, Environmental and Construction Engineering, University of Central Florida, 4000 Central Florida Blvd., Orlando, Florida, 32816, USA, [email protected] Hae-Bum Yun Assistant professor, Civil, Environmental and Construction Engineering, University of Central Florida, 4000 Central Florida Blvd., Orlando, Florida, 32816, USA, [email protected] Manoj Chopra Professor, Civil, Environmental and Construction Engineering, University of Central Florida 4000 Central Florida Blvd., Orlando, Florida, 32816, USA, [email protected] Abstract Introduction Florida is one of the most susceptible states for sinkhole Sinkhole is a ground surface depression that occurs with collapses due to its karst geology. In Florida, sinkholes or without any surface indication. Sinkholes commonly are mainly classified as cover subsidence sinkholes that occur in a very distinctive terrain called karst terrain. result in a gradual collapse with possible surface signs, This terrain mainly has a bedrock of a carbonate rocks and cover collapse sinkholes, which collapse in a sudden such as limestone, dolomite, or gypsum. Sinkholes and often catastrophic manner. The future development develop when the carbonate bedrocks are subjected of a reliable sinkhole prediction system will have to dissolution with time to form cracks, conduits, and the potential to minimize the risk to life, and reduce cavities in the underground bedrock. These features delays in construction due to the need for post-collapse allow the overburden soils (on top of the carbonate remediation. In this study, different versions of small- bedrock) to transport through them to the underground scale sinkhole physical models experimentally used cavities, which results in surface collapse due to the to monitor the water levels in a network of wells. -
Low-Flow (Minimal Drawdown) Ground-Water Sampling Procedures
United States Office of Office of Solid Waste EPA/540/S-95/504 Environmental Protection Research and and Emergency April 1996 Agency Development Response Ground Water Issue LOW-FLOW (MINIMAL DRAWDOWN) GROUND-WATER SAMPLING PROCEDURES by Robert W. Puls1 and Michael J. Barcelona2 Background units were identified and sampled in keeping with that objective. These were highly productive aquifers that The Regional Superfund Ground Water Forum is a supplied drinking water via private wells or through public group of ground-water scientists, representing EPA’s water supply systems. Gradually, with the increasing aware- Regional Superfund Offices, organized to exchange ness of subsurface pollution of these water resources, the information related to ground-water remediation at Superfund understanding of complex hydrogeochemical processes sites. One of the major concerns of the Forum is the which govern the fate and transport of contaminants in the sampling of ground water to support site assessment and subsurface increased. This increase in understanding was remedial performance monitoring objectives. This paper is also due to advances in a number of scientific disciplines and intended to provide background information on the improvements in tools used for site characterization and development of low-flow sampling procedures and its ground-water sampling. Ground-water quality investigations application under a variety of hydrogeologic settings. It is where pollution was detected initially borrowed ideas, hoped that the paper will support the production of standard methods, and materials for site characterization from the operating procedures for use by EPA Regional personnel and water supply field and water analysis from public health other environmental professionals engaged in ground-water practices. -
Basic Equations
- The concentration of salt in the groundwater; - The concentration of salt in the soil layers above the watertable (i.e. in the unsaturated zone); - The spacing and depth of the wells; - The pumping rate of the wells; i - The percentage of tubewell water removed from the project area via surface drains. The first two of these factors are determined by the natural conditions and the past use of the project area. The remaining factors are engineering-choice variables (i.e. they can be adjusted to control the salt build-up in the pumped aquifer). A common practice in this type of study is to assess not only the project area’s total water balance (Chapter 16), but also the area’s salt balance for different designs of the tubewell system and/or other subsurface drainage systems. 22.4 Basic Equations Chapter 10 described the flow to single wells pumping extensive aquifers. It was assumed that the aquifer was not replenished by percolating rain or irrigation water. In this section, we assume that the aquifer is replenished at a constant rate, R, expressed as a volume per unit surface per unit of time (m3/m2d = m/d). The well-flow equations that will be presented are based on a steady-state situation. The flow is said to be in a steady state as soon as the recharge and the discharge balance each other. In such a situation, beyond a certain distance from the well, there will be no drawdown induced by pumping. This distance is called the radius of influence of the well, re. -
Hydrological Behavior of a Deep Sub-Vertical Fault in Crystalline
Hydrological behavior of a deep sub-vertical fault in crystalline basement and relationships with surrounding reservoirs Cl´ement Roques, Olivier Bour, Luc Aquilina, Benoit Dewandel, Sarah Leray, Jean Michel Schroetter, Laurent Longuevergne, Tanguy Le Borgne, Rebecca Hochreutener, Thierry Labasque, et al. To cite this version: Cl´ement Roques, Olivier Bour, Luc Aquilina, Benoit Dewandel, Sarah Leray, et al.. Hydrological behavior of a deep sub-vertical fault in crystalline basement and relation- ships with surrounding reservoirs. Journal of Hydrology, Elsevier, 2014, 509, pp.42-54. <10.1016/j.jhydrol.2013.11.023>. <insu-00917278> HAL Id: insu-00917278 https://hal-insu.archives-ouvertes.fr/insu-00917278 Submitted on 11 Dec 2013 HAL is a multi-disciplinary open access L'archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destin´eeau d´ep^otet `ala diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publi´esou non, lished or not. The documents may come from ´emanant des ´etablissements d'enseignement et de teaching and research institutions in France or recherche fran¸caisou ´etrangers,des laboratoires abroad, or from public or private research centers. publics ou priv´es. 1 HYDROLOGICAL BEHAVIOR OF A DEEP SUB-VERTICAL FAULT IN 2 CRYSTALLINE BASEMENT AND RELATIONSHIPS WITH 3 SURROUNDING RESERVOIRS 4 C. ROQUES*(1), O. BOUR(1), L. AQUILINA(1), B. DEWANDEL(2), S. LERAY(1), JM. 5 SCHROETTER(3), L. LONGUEVERGNE(1), T. LE BORGNE(1), R. HOCHREUTENER(1), -
What Are the Ecological Impacts of Groundwater Drawdown?
What are the ecological impacts of groundwater drawdown? Research commissioned by the Department of the Environment and Energy provides new insights into the ecological impacts of groundwater drawdown. The findings strengthen the scientific knowledge base that informs the regulation of coal seam gas extraction and coal mining in Australia. What is groundwater drawdown? Groundwater is a critical resource for society and the environment. Groundwater is water found underground where it saturates soil and fills spaces in rock. This water may flow underground and naturally re-surface at different locations, such as springs or streams. It may also be extracted for agriculture, industrial purposes or drinking water. Any activity that extracts groundwater may cause groundwater drawdown, which can have important ecological consequences. Coal seam gas extraction, mining, and pumping of groundwater for irrigation are examples of such activities. In the case of coal seam gas extraction, groundwater is pumped to the surface in order to release natural gas that is trapped in an underground formation of coal. The Department of the Environment and Energy commissioned A simple example of the hydrologic cycle, where precipitation a team of Australia’s leading freshwater researchers to conduct creates runoff that travels over the ground surface and replenishes a study investigating the role of groundwater in supporting surface and ground water. vegetation, intermittent streams, streambed environments and Great Artesian Basin spring wetlands. This fact sheet summarises the key findings of the study. For more information, refer to the full project report.1 1 Andersen M, Barron O, Bond N, Burrows R, Eberhard S, Emelyanova I, Fensham R, Froend R, Kennard M, Marsh N, Pettit N, Rossini R, Rutlidge R, Valdez D & Ward D, (2016) Research to inform the assessment of ecohydrological responses to coal seam gas extraction and coal mining, Department of the Environment and Energy, Commonwealth of Australia. -
A Sketchy Teacher's Guide To
Kansas Geological Survey A PRELIMINARY TEACHER’S GUIDE TO THE INTERACTIVE GROUND-WATER TUTOR By P. Allen Macfarlane, M.A. Townsend, G. Bohling, S. Case, and A. Reber Kansas Geological Survey Open File Report 2003-65 The University of Kansas, Lawrence, KS 66047 (785) 864-3965; www.kgs.ukans.edu KANSAS GEOLOGICAL SURVEY OPEN-FILE REPORTS >>>>>>>>>>>NOT FOR RESALE<<<<<<<<<< Disclaimer The Kansas Geological Survey made a conscientious effort to ensure the accuracy of this report. However, the Kansas Geological Survey does not guarantee this document to be completely free from errors or inaccuracies and disclaims any responsibility or liability for interpretations based on data used in the production of this document or decisions based thereon. This report is intended to make results of research available at the earliest possible date, but is not intended to constitute final or formal publication. Kansas Geological Survey A PRELIMINARY TEACHER’S GUIDE TO THE INTERACTIVE GROUND-WATER TUTOR By P. Allen Macfarlane, M.A. Townsend, G. Bohling, S. Case, and A. Reber Kansas Geological Survey Open File Report 2003-65 The University of Kansas, Lawrence, KS 66047 (785) 864-3965; www.kgs.ukans.edu Preface The Interim Teacher’s Guide to the Ground-water Tutor is designed for use with the interactive ground-water tutor during the alpha and beta testing and development stages in the formulation of the prototype, eventually Web-based software. In its final form, the manual will contain more information on assessment rubrics that can be used by teachers to evaluate student science learning as well as well as the results of the evaluations conducted as part of this NSF-funded project. -
Further Discussion on the Influence Radius of a Pumping Well
water Review Further Discussion on the Influence Radius of a Pumping Well: A Parameter with Little Scientific and Practical Significance That Can Easily Be Misleading Yuanzheng Zhai , Xinyi Cao , Ya Jiang * , Kangning Sun, Litang Hu , Yanguo Teng, Jinsheng Wang and Jie Li * Engineering Research Center for Groundwater Pollution Control, Remediation of Ministry of Education of China, College of Water Sciences, Beijing Normal University, Beijing 100875, China; [email protected] (Y.Z.); [email protected] (X.C.); [email protected] (K.S.); [email protected] (L.H.); [email protected] (Y.T.); [email protected] (J.W.) * Correspondence: [email protected] (Y.J.); [email protected] (J.L.); Tel.: +86-151-6658-7857 (Y.J.); Fax: +86-010-58802736 (J.L.) Abstract: To facilitate understanding and calculation, hydrogeologists have introduced the influence radius. This parameter is now widely used, not only in the theoretical calculation and reasoning of well flow mechanics, but also in guiding production practice, and it has become an essential parameter in hydrogeology. However, the reasonableness of this parameter has always been disputed. This paper discusses the nature of the influence radius and the problems of its practical application based on mathematical reasoning and analogy starting from the Dupuit formula and Thiem formula. It is found that the influence radius is essentially the distance in the time–distance problem in physics; Citation: Zhai, Y.; Cao, X.; Jiang, Y.; therefore, it is a function of time and velocity and is influenced by hydrogeological conditions and Sun, K.; Hu, L.; Teng, Y.; Wang, J.; Li, pumping conditions.