This document describes numerical flow modeling and analysis of observation well data carried out to study seepage at Hidden Dam. Five flow simulation scenarios are analyzed using a 2D model that incorporates the dam geometry, foundation geology, and downstream topography. The scenarios vary parameters like the reservoir level, presence of horizontal drains, and properties of subsurface layers. Predicted seepage rates, piezometric levels, and other outputs are compared to historical observation well data to validate the simulations. The modeling aims to better understand how seepage at the dam is influenced by variations in hydrogeologic conditions.
1) A hydrogeophysical survey was conducted on an earthen dam to investigate factors contributing to its long-term successful operation without apparent seepage issues. 2) Geophysical methods including seismic refraction, self-potential, and electrical resistivity tomography were used to map the subsurface hydrostratigraphy and groundwater flow patterns. 3) The data indicated a preferential flow pathway beneath the dam, corresponding to a sandy-gravel layer that connects the reservoir to a downstream seepage zone. This layer may explain the dam's success by providing a controlled pathway for seepage.
This document summarizes an HEC-HMS hydrologic model of the Cherry Creek basin in Colorado, which drains into Cherry Creek Lake. The 22-subbasin model was created using geospatial data and streamflow records. Land use was classified from 1954 to 2004 using maps and aerial photos. The Green-Ampt method was used to simulate rainfall-runoff processes, accounting for soil properties and initial moisture conditions. Key events in 1965, 1973, and 2006 were used to calibrate soil parameters for each subbasin. Storage functions were developed for impoundments and the reservoir based on surveys. The completed model simulates the precipitation-runoff process and outflow to Cherry Creek Lake.
Landscape Consequences of Natural Gas Extraction in Fayette and Lycoming Coun...Marcellus Drilling News
A report published in June 2013 by the U.S. Geological Survey titled, "Landscape Consequences of Natural Gas Extraction in Fayette and Lycoming Counties, Pennsylvania, 2004–2010." The USGS considers the effects of both conventional and unconventional (shale) drilling and their combined affect on local forestlands and vegetation in two PA counties.
Diurnal Patterns and Microclimatological Controls on Stomata Conductance and ...heidenjoy
This master's thesis examines diurnal patterns and microclimatic controls on stomatal conductance and transpiration at High Creek Fen in Colorado. It includes 3 chapters that provide background on evapotranspiration processes, describe the study site and vegetation, and outline the study hypotheses. Methods of data collection and results are presented for 3 problem statements comparing physiological responses within and between plant species under different microclimate conditions. Statistical analyses show significant effects of plant height, soil moisture, and species on stomatal conductance and transpiration. The discussion and conclusion sections interpret the results in the context of the literature.
This document summarizes geophysical field investigations carried out at Hidden Dam in Raymond, California to better understand subsurface hydrogeology and seepage conditions. Known seepage areas on the northwest right abutment of the downstream side of the dam prompted the study. Self-potential and direct current resistivity surveys were conducted to identify present-day seepage and subsurface geologic structures that may control flow. The focus was the downstream right abutment, where a 1980 study found significant seepage. Preliminary results from the geophysical methods aim to improve understanding of seepage patterns through dam construction, geology, and groundwater data.
Thesis: Geophysical Investigation of Carrizo Formation by Using Two- Dimensio...Zach Ghalayini
Ghalayini, Zachary. Bachelor of Science, University of South Florida, Fall 2014;
Master of Business Administration Spring 2018; Master of Science, the
University of Louisiana at Lafayette, Fall 2018
Major: Geology Title of Thesis: Geophysical Investigation of Carrizo Formation by Using Two-
Dimensional Seismic Surveys in the Tullos-Urania Oilfield in LaSalle Parish, LA
Thesis Director: Dr. Rui Zhang Pages in Thesis: 77; Words in Abstract: 298
Abstract
The upper Wilcox group in the Tullos-Urania oilfield has not been imaged with enough resolution for interpretation. Prior seismic data collected in the area was designed for formations much deeper than the Wilcox Group. The purpose of this investigation was to produce an image of the subsurface and identify formations of interest for production of oil and gas by applying different processing methods. With an optimal processing workflow and use of limited well logs, an interpretation of the data was provided to the oil company.
The advantage of using an accelerated weight-drop source is the shallow horizons, ranging from 1,500 to 3,000 feet in-depth, become distinct with higher resolution. The acquisition achieved a dominant frequency averaging around 45-65 Hz compared to a nearby pre-existing 3D survey volume with a dominant frequency range of 15-35 Hz. Refracted waves dominated the unprocessed shot records from this data. Consequently, the field records had a significantly low signal-noise ratio. Therefore, the most critical processing steps focused on signal processing and velocity analysis. Without enough ground roll and noise suppression, the velocity analysis would not have been coherent. Some obstacles faced with processing the data included a sparse horizontal sampling and a lack of velocity logs along the seismic line.
64
The results of this study included a set of stacked lines, velocity models, and an optimal processing workflow for future high-frequency shallow seismic exploration surveys in the vicinity of LaSalle, LA. These results have concluded seismic surveying with an accelerated weight-drop source is a cost-effective method to produce a high-resolution cross-section of the high and low-velocity sand and shale channels of the fluvial Wilcox strata of Northern Louisiana. Further research should look to build on these results and gather a 3D survey to image the structure of the Tullos-Urania oilfield and identify hydrocarbons-in-place.
This document presents a methodological toolkit for conducting field assessments of artisanally mined alluvial diamond deposits. The toolkit provides guidance on project planning, fieldwork planning and preparation, fieldwork methods, and reporting results. It outlines approaches for developing a research plan, literature review, stakeholder identification, field site identification, logistical preparation, and data collection through direct observations, interviews, and photographs. It also discusses tools for field map preparation and summarizes a case study applying the toolkit to assess Guinea's artisanally mined diamond deposits. The case study demonstrates the implementation and multistakeholder approach to data collection and highlights challenges encountered.
Behaviour and Analysis of Large Diameter Laterally Loaded PilesHenry Pik Yap Sia
75% of UK offshore wind turbines are supported on monopile foundations (Doherty and Gavin, 2012). The piles are subjected to large lateral loading from wind and tide surges as well as seabed movement. British Standards (BS EN 61400-3:2009) suggested p-y curve to predict the behaviour of laterally loaded offshore piles. P-y curve has certain assumptions including negligible rotational resistance along the pile length.
This report presents our investigation on the effect of rotational resistance on a typical large diameter pile. It also describes how the finite difference (FD) program has been written from first principles, the Winkler’s Method and Euler-Bernoulli Beam theory. To calculate the rotational resistance, the slice method proposed by McVay and Niraula (2004) is implemented in our model. Our linear-elastic FD model calculates the displacement, bending moment, shear force and soil pressure for laterally loaded piles for two cases: (a) when rotational resistance is considered and (b) when rotational resistance is neglected. The later represents the values used in the industry.
Sensitivity study, through our model produced good results within its scope. The results suggested that the change in the soil and pile properties was found to be dependent on the length-to-depth (L/D) ratio of the pile and the stiffness of the soil next to the pile. In other words, when reached critical ratio, the rotational resistance becomes very significant, specifically for short, rigid piles. Therefore, we computed curves to recommend the range of L/D values where rotational resistance can be safely neglected.
Recommendations and suggestions are made to improve the model and research to fully encapsulate the behaviour of offshore monopiles, such as cyclic loading, elastic continuum, plasticity and non-linearity.
Lastly, we have sufficient confidence from this research to conclude that rotational resistance of a laterally loaded large diameter pile are important and that current design standards for offshore monopiles are conservative.
1) A hydrogeophysical survey was conducted on an earthen dam to investigate factors contributing to its long-term successful operation without apparent seepage issues. 2) Geophysical methods including seismic refraction, self-potential, and electrical resistivity tomography were used to map the subsurface hydrostratigraphy and groundwater flow patterns. 3) The data indicated a preferential flow pathway beneath the dam, corresponding to a sandy-gravel layer that connects the reservoir to a downstream seepage zone. This layer may explain the dam's success by providing a controlled pathway for seepage.
This document summarizes an HEC-HMS hydrologic model of the Cherry Creek basin in Colorado, which drains into Cherry Creek Lake. The 22-subbasin model was created using geospatial data and streamflow records. Land use was classified from 1954 to 2004 using maps and aerial photos. The Green-Ampt method was used to simulate rainfall-runoff processes, accounting for soil properties and initial moisture conditions. Key events in 1965, 1973, and 2006 were used to calibrate soil parameters for each subbasin. Storage functions were developed for impoundments and the reservoir based on surveys. The completed model simulates the precipitation-runoff process and outflow to Cherry Creek Lake.
Landscape Consequences of Natural Gas Extraction in Fayette and Lycoming Coun...Marcellus Drilling News
A report published in June 2013 by the U.S. Geological Survey titled, "Landscape Consequences of Natural Gas Extraction in Fayette and Lycoming Counties, Pennsylvania, 2004–2010." The USGS considers the effects of both conventional and unconventional (shale) drilling and their combined affect on local forestlands and vegetation in two PA counties.
Diurnal Patterns and Microclimatological Controls on Stomata Conductance and ...heidenjoy
This master's thesis examines diurnal patterns and microclimatic controls on stomatal conductance and transpiration at High Creek Fen in Colorado. It includes 3 chapters that provide background on evapotranspiration processes, describe the study site and vegetation, and outline the study hypotheses. Methods of data collection and results are presented for 3 problem statements comparing physiological responses within and between plant species under different microclimate conditions. Statistical analyses show significant effects of plant height, soil moisture, and species on stomatal conductance and transpiration. The discussion and conclusion sections interpret the results in the context of the literature.
This document summarizes geophysical field investigations carried out at Hidden Dam in Raymond, California to better understand subsurface hydrogeology and seepage conditions. Known seepage areas on the northwest right abutment of the downstream side of the dam prompted the study. Self-potential and direct current resistivity surveys were conducted to identify present-day seepage and subsurface geologic structures that may control flow. The focus was the downstream right abutment, where a 1980 study found significant seepage. Preliminary results from the geophysical methods aim to improve understanding of seepage patterns through dam construction, geology, and groundwater data.
Thesis: Geophysical Investigation of Carrizo Formation by Using Two- Dimensio...Zach Ghalayini
Ghalayini, Zachary. Bachelor of Science, University of South Florida, Fall 2014;
Master of Business Administration Spring 2018; Master of Science, the
University of Louisiana at Lafayette, Fall 2018
Major: Geology Title of Thesis: Geophysical Investigation of Carrizo Formation by Using Two-
Dimensional Seismic Surveys in the Tullos-Urania Oilfield in LaSalle Parish, LA
Thesis Director: Dr. Rui Zhang Pages in Thesis: 77; Words in Abstract: 298
Abstract
The upper Wilcox group in the Tullos-Urania oilfield has not been imaged with enough resolution for interpretation. Prior seismic data collected in the area was designed for formations much deeper than the Wilcox Group. The purpose of this investigation was to produce an image of the subsurface and identify formations of interest for production of oil and gas by applying different processing methods. With an optimal processing workflow and use of limited well logs, an interpretation of the data was provided to the oil company.
The advantage of using an accelerated weight-drop source is the shallow horizons, ranging from 1,500 to 3,000 feet in-depth, become distinct with higher resolution. The acquisition achieved a dominant frequency averaging around 45-65 Hz compared to a nearby pre-existing 3D survey volume with a dominant frequency range of 15-35 Hz. Refracted waves dominated the unprocessed shot records from this data. Consequently, the field records had a significantly low signal-noise ratio. Therefore, the most critical processing steps focused on signal processing and velocity analysis. Without enough ground roll and noise suppression, the velocity analysis would not have been coherent. Some obstacles faced with processing the data included a sparse horizontal sampling and a lack of velocity logs along the seismic line.
64
The results of this study included a set of stacked lines, velocity models, and an optimal processing workflow for future high-frequency shallow seismic exploration surveys in the vicinity of LaSalle, LA. These results have concluded seismic surveying with an accelerated weight-drop source is a cost-effective method to produce a high-resolution cross-section of the high and low-velocity sand and shale channels of the fluvial Wilcox strata of Northern Louisiana. Further research should look to build on these results and gather a 3D survey to image the structure of the Tullos-Urania oilfield and identify hydrocarbons-in-place.
This document presents a methodological toolkit for conducting field assessments of artisanally mined alluvial diamond deposits. The toolkit provides guidance on project planning, fieldwork planning and preparation, fieldwork methods, and reporting results. It outlines approaches for developing a research plan, literature review, stakeholder identification, field site identification, logistical preparation, and data collection through direct observations, interviews, and photographs. It also discusses tools for field map preparation and summarizes a case study applying the toolkit to assess Guinea's artisanally mined diamond deposits. The case study demonstrates the implementation and multistakeholder approach to data collection and highlights challenges encountered.
Behaviour and Analysis of Large Diameter Laterally Loaded PilesHenry Pik Yap Sia
75% of UK offshore wind turbines are supported on monopile foundations (Doherty and Gavin, 2012). The piles are subjected to large lateral loading from wind and tide surges as well as seabed movement. British Standards (BS EN 61400-3:2009) suggested p-y curve to predict the behaviour of laterally loaded offshore piles. P-y curve has certain assumptions including negligible rotational resistance along the pile length.
This report presents our investigation on the effect of rotational resistance on a typical large diameter pile. It also describes how the finite difference (FD) program has been written from first principles, the Winkler’s Method and Euler-Bernoulli Beam theory. To calculate the rotational resistance, the slice method proposed by McVay and Niraula (2004) is implemented in our model. Our linear-elastic FD model calculates the displacement, bending moment, shear force and soil pressure for laterally loaded piles for two cases: (a) when rotational resistance is considered and (b) when rotational resistance is neglected. The later represents the values used in the industry.
Sensitivity study, through our model produced good results within its scope. The results suggested that the change in the soil and pile properties was found to be dependent on the length-to-depth (L/D) ratio of the pile and the stiffness of the soil next to the pile. In other words, when reached critical ratio, the rotational resistance becomes very significant, specifically for short, rigid piles. Therefore, we computed curves to recommend the range of L/D values where rotational resistance can be safely neglected.
Recommendations and suggestions are made to improve the model and research to fully encapsulate the behaviour of offshore monopiles, such as cyclic loading, elastic continuum, plasticity and non-linearity.
Lastly, we have sufficient confidence from this research to conclude that rotational resistance of a laterally loaded large diameter pile are important and that current design standards for offshore monopiles are conservative.
The study aims to better understand formation invasion around wellbores. During drilling, mud filtrate invades the formation, displacing native fluids and altering properties in the invaded zone. This zone is often assumed cylindrical but its true shape is unknown, especially in horizontal wells where density differences can cause gravity segregation. The goals are to use ground penetrating radar (GPR) to image invasion geometries in a physical model and provide data to develop mathematical models. Comparisons of visual observations, GPR images, and numerical simulations show promise for characterizing invasion and correcting borehole measurements.
This report provides an updated engineering evaluation of remaining natural gas reserves in Cook Inlet, Alaska. It was authored by three petroleum reservoir engineers from the Alaska Division of Oil and Gas and edited by the Resource Evaluation Section Manager. The report finds that as of December 31, 2014, 3.9 trillion cubic feet of gas had been produced from Cook Inlet fields, with an estimated 3.4 trillion cubic feet of reserves remaining under existing economic and technical conditions. Of the remaining reserves, 1.7 trillion cubic feet require additional investment to be produced.
This document introduces Technical Release 55 (TR-55) which provides simplified procedures for estimating runoff and peak discharges in small urban and urbanizing watersheds. Urbanization increases runoff and peak discharges by reducing infiltration and decreasing travel time through increased impervious surfaces. TR-55 presents methods to estimate runoff, time of concentration, peak discharge, and hydrographs based on measurable watershed characteristics that are affected by urban development such as soil type, slope, and land cover.
This document analyzes a 23-year wave hindcast dataset for 12 locations around the Isles of Scilly to assess the wave energy resource. It finds large temporal and spatial variation in wave power, with locations to the southwest experiencing a mean annual power of 37.5kW/m compared to 6.7kW/m on the sheltered east side. Monthly mean power varies from 3-7kW/m in summer to over 100kW/m in winter at energetic sites. Extreme wave analysis shows a potential 1 in 100 year wave of almost 20m significant height. However, utilizing wave power is constrained by the islands' sensitive marine environment and electrical grid capacity.
USGS Report on the Impact of Marcellus Shale Drilling on Forest Animal HabitatsMarcellus Drilling News
A report issued March 25, 2013 by the U.S. Geological Survey titled "Landscape Consequences of Natural Gas Extraction in Allegheny and Susquehanna Counties, Pennsylvania, 2004–2010." The report, using a series of maps and data, purports to show that drilling has lead to "carving up" wildlife habitats in some forests.
The USF team reviewed a geophysical investigation of the Kar Kar region conducted by WesternGeco in 2011. They found that WesternGeco's magnetotelluric (MT) data and models were of high quality. Both the WesternGeco and USF MT models identified a low resistivity zone at 300m depth that correlates with a water-bearing zone found in Borehole 4. USF performed gravity modeling which identified a north-south trending basin reaching 1500m depth, consistent with mapped faults. A preliminary hydrothermal model suggested observed temperatures could result from deep circulation of meteoric waters in the basin without needing a localized heat source. Additional geophysical data is recommended around the Jermaghbyur hot springs to
This thesis examines the influence of irrigation water use efficiencies on the sustainability of irrigation at the global scale. The student developed a global hydrological model, PCR-GLOBWB, to simulate irrigation water requirements and consumption under different climate change scenarios from 1960-2099. The model was forced with output from several general circulation models to account for climate uncertainty. Results showed irrigation requirements generally increasing over time, with significant regional variations, highlighting the need to improve irrigation efficiencies to ensure sustainable water resources for agriculture worldwide.
Flood Handbook Analysis and Modeling Eslamian 2022.pdfsandipanpaul16
This document provides an introduction and table of contents for a book titled "Flood Handbook: Analysis and Modeling". The book contains 19 chapters organized into 7 parts covering various topics related to flooding such as flood observation and modeling, flood modeling and forecasting, floods and river restoration, flood optimization and simulation, flood software, flood regionalization, and flood soft computing. The book is edited by Saeid Eslamian and Faezeh Eslamian and published by CRC Press in 2022.
This report analyzes baseline groundwater conditions in three basins in Cape Verde - Mosteiros, Ribeira Paul, and Ribeira Fajã - based on existing data and new data collected in 2005-2006. Key findings include:
1) Groundwater levels varied between basins and over time, with some wells showing fluctuations of up to 1.8 meters.
2) Measured groundwater discharge was approximately 220,000 cubic meters/year in Mosteiros, 1,600,000 cubic meters/year in Ribeira Paul, and 150,000 cubic meters/year in Ribeira Fajã.
3) Groundwater ages ranged from over 50 years to within
EPA/Chesapeake Energy Study: Impact of Fracking on Water in Bradford County, PAMarcellus Drilling News
Preliminary results from water samples taken from an area of Pennsylvania where there is a lot of hydraulic fracturing of Marcellus Shale gas wells. The water samples were compared with samples taken prior to fracking in the area, and the results show no measurable impact of fracking on drinking water supplies. This is part of the EPA's multi-year study of fracking.
Dr Dev Kambhampati | EPA Proceedings- Hydraulic Fracturing Study- Water Resou...Dr Dev Kambhampati
This document provides an overview of the agenda and presentations given at the EPA Technical Workshop on Water Resources Management for the Hydraulic Fracturing Study held on March 29-30, 2011. The workshop consisted of three themes: 1) Water Use & Sustainability, 2) Flowback Recovery & Water Reuse, and 3) Disposal Practices. Over the two days, 22 presentations and 2 posters were given on topics such as determining appropriate water sources, water quantity analysis, flowback characterization, treatment technologies, and disposal practices. The goal was to inform EPA's study of potential impacts of hydraulic fracturing on drinking water resources.
This document provides a summary of a report on teleportation physics. The report proposes several theoretical models for teleportation based on engineering spacetime or the vacuum electromagnetic parameters. It reviews quantum teleportation and its technological progress. It also documents reports of anomalous teleportation phenomena. The report identifies promising theoretical concepts and experimental research to advance understanding of teleportation.
This document summarizes a student's dissertation on slope stability analysis and rockfall hazard zonation in Royat, France. The student conducted fieldwork to collect data on rock discontinuities and geological features. Stereographic projections and rockfall modeling were used to analyze slope stability hazards. This resulted in a hazard zonation map showing the areas of highest rockfall risk around Royat Park. The modeling found the perimeter of the park to have the highest hazard, while the center had the lowest.
This dissertation discusses observations of terrestrial gamma flashes (TGFs) made by the TETRA and LAGO detectors between 2010 and 2014. Chapter 1 provides an introduction to the topic. Chapter 2 discusses the motivation for studying TGFs. Chapter 3 describes the TETRA detector and its configuration. Chapter 4 presents an analysis of TGF event candidates detected by TETRA between 2010 and 2013, identifying 24 candidate events. Chapter 5 provides an updated analysis through 2014, identifying 28 candidate events. Chapter 6 analyzes the thunderstorm conditions associated with several TGF events. Chapter 7 describes the LAGO detector. Chapter 8 discusses plans for a next-generation TETRA detector. The dissertation concludes in Chapter 9.
This document analyzes water quality at three streams in Haliburton Forest where road crossings are present. Benthic invertebrate communities and chemical parameters were used to assess water quality at two study sites - K-1 and W-2. Results from biological indices showed no indication of impairment between reference and exposure units at both sites, suggesting the road crossings did not negatively impact water quality. While additional research is needed, this study provides initial evidence that organic pollution from rural developments may not significantly impact these streams.
This document provides the Wetlands Delineation Manual published in 1987 by the U.S. Army Corps of Engineers. The manual establishes technical guidelines and methods for identifying and delineating wetlands subject to regulatory jurisdiction under the Clean Water Act. It requires evidence of hydrophytic vegetation, hydric soils, and wetland hydrology to designate an area as a wetland. The manual also describes characteristics and indicators used to identify these three wetland parameters and provides detailed methods for routine, comprehensive, and atypical wetland determinations.
This thesis examines shallow gas anomalies in the North Sea using AVO analysis and seismic inversion. The author creates a wedge model to estimate the thickness of a thin gas sand detected at 520ms that shows high amplitudes on seismic data. AVO cross-plotting shows the anomaly deviates from the background trend into quadrant III, indicating a Class III gas effect. Tuning curves from the wedge model suggest the anomaly is affected by both gas saturation and tuning effects. Seismic inversion enhances interpretation by showing anomalous low impedance associated with the high amplitude anomaly.
This document analyzes changes to forest cover and landscape patterns in Bradford and Washington Counties, Pennsylvania between 2004-2010 resulting from natural gas extraction. Using aerial imagery and GIS, the researchers mapped disturbed areas from well pads, roads, and pipelines. They calculated landscape metrics to quantify forest fragmentation, edge effects, and interior forest loss. Key findings include: 1) Over 6,000 acres of forest were disturbed by natural gas development. 2) Forest cover declined in both counties while fragmentation increased. 3) Interior forest decreased substantially, particularly near Marcellus Shale extraction sites.
This technical report evaluates the surface water and geomorphological impacts of the proposed Pioneer Aggregates Mining Expansion and North Sequalitchew Project. The report describes the existing environment including Sequalitchew Creek, Fort Lewis Diversion Canal, springs, wetlands and Puget Sound. It finds that construction and operation of the expanded mine would impact these water bodies and alter creek and wetland geomorphology. The report recommends mitigation and monitoring measures to minimize impacts to water quality and channel form during mining and ensure restoration after reclamation.
This document provides guidance on designing and constructing welded steel penstocks. It discusses factors to consider such as location, economics, head losses, stresses, supports, bends, accessories, materials, fabrication, installation, specifications, and corrosion control. Welded steel penstocks are well-suited for transmitting water from reservoirs or dams to hydroelectric turbines due to their strength and flexibility. They are designed according to codes like the ASME Boiler and Pressure Vessel Code to ensure safety. The document is intended to help designers solve problems and construct penstocks safely and efficiently.
The study aims to better understand formation invasion around wellbores. During drilling, mud filtrate invades the formation, displacing native fluids and altering properties in the invaded zone. This zone is often assumed cylindrical but its true shape is unknown, especially in horizontal wells where density differences can cause gravity segregation. The goals are to use ground penetrating radar (GPR) to image invasion geometries in a physical model and provide data to develop mathematical models. Comparisons of visual observations, GPR images, and numerical simulations show promise for characterizing invasion and correcting borehole measurements.
This report provides an updated engineering evaluation of remaining natural gas reserves in Cook Inlet, Alaska. It was authored by three petroleum reservoir engineers from the Alaska Division of Oil and Gas and edited by the Resource Evaluation Section Manager. The report finds that as of December 31, 2014, 3.9 trillion cubic feet of gas had been produced from Cook Inlet fields, with an estimated 3.4 trillion cubic feet of reserves remaining under existing economic and technical conditions. Of the remaining reserves, 1.7 trillion cubic feet require additional investment to be produced.
This document introduces Technical Release 55 (TR-55) which provides simplified procedures for estimating runoff and peak discharges in small urban and urbanizing watersheds. Urbanization increases runoff and peak discharges by reducing infiltration and decreasing travel time through increased impervious surfaces. TR-55 presents methods to estimate runoff, time of concentration, peak discharge, and hydrographs based on measurable watershed characteristics that are affected by urban development such as soil type, slope, and land cover.
This document analyzes a 23-year wave hindcast dataset for 12 locations around the Isles of Scilly to assess the wave energy resource. It finds large temporal and spatial variation in wave power, with locations to the southwest experiencing a mean annual power of 37.5kW/m compared to 6.7kW/m on the sheltered east side. Monthly mean power varies from 3-7kW/m in summer to over 100kW/m in winter at energetic sites. Extreme wave analysis shows a potential 1 in 100 year wave of almost 20m significant height. However, utilizing wave power is constrained by the islands' sensitive marine environment and electrical grid capacity.
USGS Report on the Impact of Marcellus Shale Drilling on Forest Animal HabitatsMarcellus Drilling News
A report issued March 25, 2013 by the U.S. Geological Survey titled "Landscape Consequences of Natural Gas Extraction in Allegheny and Susquehanna Counties, Pennsylvania, 2004–2010." The report, using a series of maps and data, purports to show that drilling has lead to "carving up" wildlife habitats in some forests.
The USF team reviewed a geophysical investigation of the Kar Kar region conducted by WesternGeco in 2011. They found that WesternGeco's magnetotelluric (MT) data and models were of high quality. Both the WesternGeco and USF MT models identified a low resistivity zone at 300m depth that correlates with a water-bearing zone found in Borehole 4. USF performed gravity modeling which identified a north-south trending basin reaching 1500m depth, consistent with mapped faults. A preliminary hydrothermal model suggested observed temperatures could result from deep circulation of meteoric waters in the basin without needing a localized heat source. Additional geophysical data is recommended around the Jermaghbyur hot springs to
This thesis examines the influence of irrigation water use efficiencies on the sustainability of irrigation at the global scale. The student developed a global hydrological model, PCR-GLOBWB, to simulate irrigation water requirements and consumption under different climate change scenarios from 1960-2099. The model was forced with output from several general circulation models to account for climate uncertainty. Results showed irrigation requirements generally increasing over time, with significant regional variations, highlighting the need to improve irrigation efficiencies to ensure sustainable water resources for agriculture worldwide.
Flood Handbook Analysis and Modeling Eslamian 2022.pdfsandipanpaul16
This document provides an introduction and table of contents for a book titled "Flood Handbook: Analysis and Modeling". The book contains 19 chapters organized into 7 parts covering various topics related to flooding such as flood observation and modeling, flood modeling and forecasting, floods and river restoration, flood optimization and simulation, flood software, flood regionalization, and flood soft computing. The book is edited by Saeid Eslamian and Faezeh Eslamian and published by CRC Press in 2022.
This report analyzes baseline groundwater conditions in three basins in Cape Verde - Mosteiros, Ribeira Paul, and Ribeira Fajã - based on existing data and new data collected in 2005-2006. Key findings include:
1) Groundwater levels varied between basins and over time, with some wells showing fluctuations of up to 1.8 meters.
2) Measured groundwater discharge was approximately 220,000 cubic meters/year in Mosteiros, 1,600,000 cubic meters/year in Ribeira Paul, and 150,000 cubic meters/year in Ribeira Fajã.
3) Groundwater ages ranged from over 50 years to within
EPA/Chesapeake Energy Study: Impact of Fracking on Water in Bradford County, PAMarcellus Drilling News
Preliminary results from water samples taken from an area of Pennsylvania where there is a lot of hydraulic fracturing of Marcellus Shale gas wells. The water samples were compared with samples taken prior to fracking in the area, and the results show no measurable impact of fracking on drinking water supplies. This is part of the EPA's multi-year study of fracking.
Dr Dev Kambhampati | EPA Proceedings- Hydraulic Fracturing Study- Water Resou...Dr Dev Kambhampati
This document provides an overview of the agenda and presentations given at the EPA Technical Workshop on Water Resources Management for the Hydraulic Fracturing Study held on March 29-30, 2011. The workshop consisted of three themes: 1) Water Use & Sustainability, 2) Flowback Recovery & Water Reuse, and 3) Disposal Practices. Over the two days, 22 presentations and 2 posters were given on topics such as determining appropriate water sources, water quantity analysis, flowback characterization, treatment technologies, and disposal practices. The goal was to inform EPA's study of potential impacts of hydraulic fracturing on drinking water resources.
This document provides a summary of a report on teleportation physics. The report proposes several theoretical models for teleportation based on engineering spacetime or the vacuum electromagnetic parameters. It reviews quantum teleportation and its technological progress. It also documents reports of anomalous teleportation phenomena. The report identifies promising theoretical concepts and experimental research to advance understanding of teleportation.
This document summarizes a student's dissertation on slope stability analysis and rockfall hazard zonation in Royat, France. The student conducted fieldwork to collect data on rock discontinuities and geological features. Stereographic projections and rockfall modeling were used to analyze slope stability hazards. This resulted in a hazard zonation map showing the areas of highest rockfall risk around Royat Park. The modeling found the perimeter of the park to have the highest hazard, while the center had the lowest.
This dissertation discusses observations of terrestrial gamma flashes (TGFs) made by the TETRA and LAGO detectors between 2010 and 2014. Chapter 1 provides an introduction to the topic. Chapter 2 discusses the motivation for studying TGFs. Chapter 3 describes the TETRA detector and its configuration. Chapter 4 presents an analysis of TGF event candidates detected by TETRA between 2010 and 2013, identifying 24 candidate events. Chapter 5 provides an updated analysis through 2014, identifying 28 candidate events. Chapter 6 analyzes the thunderstorm conditions associated with several TGF events. Chapter 7 describes the LAGO detector. Chapter 8 discusses plans for a next-generation TETRA detector. The dissertation concludes in Chapter 9.
This document analyzes water quality at three streams in Haliburton Forest where road crossings are present. Benthic invertebrate communities and chemical parameters were used to assess water quality at two study sites - K-1 and W-2. Results from biological indices showed no indication of impairment between reference and exposure units at both sites, suggesting the road crossings did not negatively impact water quality. While additional research is needed, this study provides initial evidence that organic pollution from rural developments may not significantly impact these streams.
This document provides the Wetlands Delineation Manual published in 1987 by the U.S. Army Corps of Engineers. The manual establishes technical guidelines and methods for identifying and delineating wetlands subject to regulatory jurisdiction under the Clean Water Act. It requires evidence of hydrophytic vegetation, hydric soils, and wetland hydrology to designate an area as a wetland. The manual also describes characteristics and indicators used to identify these three wetland parameters and provides detailed methods for routine, comprehensive, and atypical wetland determinations.
This thesis examines shallow gas anomalies in the North Sea using AVO analysis and seismic inversion. The author creates a wedge model to estimate the thickness of a thin gas sand detected at 520ms that shows high amplitudes on seismic data. AVO cross-plotting shows the anomaly deviates from the background trend into quadrant III, indicating a Class III gas effect. Tuning curves from the wedge model suggest the anomaly is affected by both gas saturation and tuning effects. Seismic inversion enhances interpretation by showing anomalous low impedance associated with the high amplitude anomaly.
This document analyzes changes to forest cover and landscape patterns in Bradford and Washington Counties, Pennsylvania between 2004-2010 resulting from natural gas extraction. Using aerial imagery and GIS, the researchers mapped disturbed areas from well pads, roads, and pipelines. They calculated landscape metrics to quantify forest fragmentation, edge effects, and interior forest loss. Key findings include: 1) Over 6,000 acres of forest were disturbed by natural gas development. 2) Forest cover declined in both counties while fragmentation increased. 3) Interior forest decreased substantially, particularly near Marcellus Shale extraction sites.
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1. Prepared in cooperation with the U.S. Army Corps of Engineers
Geophysical Investigations at Hidden Dam, Raymond,
California—Flow Simulations
By Burke J. Minsley and Scott Ikard
Open-File Report 2010–1153
U.S. Department of the Interior
U.S. Geological Survey
2. U.S. Department of the Interior
KEN SALAZAR, Secretary
U.S. Geological Survey
Marcia K. McNutt, Director
U.S. Geological Survey, Reston, Virginia: 2010
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Suggested citation:
Minsley, B.J., and Ikard, Scott, 2010, Geophysical investigations at Hidden Dam, Raymond, California—Flow
simulations: U.S. Geological Survey Open-File Report 2010–1153, 64 p.
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3. Geophysical investigations at Hidden Dam—Flow simulations iii
Contents
Introduction.................................................................................................................................................................... 1
Background ................................................................................................................................................................... 2
Location and Geology................................................................................................................................................ 2
Summary of Previous Work ....................................................................................................................................... 3
Hidden Dam Flow Simulations....................................................................................................................................... 3
Description of Model .................................................................................................................................................. 3
Scenario 1: Baseline Model, Profile A........................................................................................................................ 6
Scenario 2: Baseline Model, Profile B........................................................................................................................ 8
Scenario 3: Profile A, No Horizontal Drainage Fill.....................................................................................................10
Scenario 4: Profile A, Baseline Model with Near-Surface Sediment Layer ...............................................................11
Scenario 5: Profile A, Baseline Model with Deep Sediment Channel........................................................................12
Comparison with Selected Observation-Well Data.......................................................................................................13
Conclusions..................................................................................................................................................................14
Acknowledgments ........................................................................................................................................................16
References Cited..........................................................................................................................................................16
Appendix.......................................................................................................................................................................18
Governing Variably Saturated Flow Equations..........................................................................................................18
Determination of Variably Saturated Model Input Parameters ..................................................................................18
Electrokinetic Coupling to Determine the Self-Potential Response...........................................................................19
Figures..........................................................................................................................................................................21
4. Geophysical investigations at Hidden Dam—Flow simulationsiv
Figures
Figure 1. Location (inset) and aerial photo of Hidden Dam ....................................................................................... 2
Figure 2. Inverted sections for DC resistivity (A) line 1 and (B) line 2........................................................................ 4
Figure 3. Geometry of Hidden Dam and downstream topography along profile A in figure 1 .................................... 5
Figure 4. Geometry of Hidden Dam and downstream topography along profile B in figure 1 .................................... 5
Figure 5. Flow model results for the profile A baseline model and reservoir elevation of 485 ft
(flow scenario 1) .......................................................................................................................................................... 21
Figure 6. Flow model results for the profile A baseline model and reservoir elevation of 510 ft
(flow scenario 1) .......................................................................................................................................................... 22
Figure 7. Flow model results for the profile A baseline model and reservoir elevation of 540 ft
(flow scenario 1) .......................................................................................................................................................... 23
Figure 8. Seepage (foot per second) through the downstream embankment and ground surface as a
function of distance for the three different reservoir elevations illustrated in figures 5–7 (flow scenario 1).................. 24
Figure 9. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground
surface (red) per foot along the length of the dam as a function of reservoir elevation (flow scenario 1) .................... 25
Figure 10. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream
toe for flow scenario 1.................................................................................................................................................. 26
Figure 11. Self-potential (millivolts) values predicted along the downstream embankment and ground
surface for the three different reservoir elevations illustrated in figures 5–7 for flow scenario 1.................................. 27
Figure 12. Electrical resistivity (ohm-meters) predicted for flow scenario 1 at a reservoir elevation of 510 feet ...... 28
Figure 13. Flow model results for the profile B baseline model and reservoir elevation of 485 ft
(flow scenario 2) .......................................................................................................................................................... 29
Figure 14. Flow model results for the profile B baseline model and reservoir elevation of 510 ft
(flow scenario 2) .......................................................................................................................................................... 30
5. Geophysical investigations at Hidden Dam—Flow simulations v
Figure 15. Flow model results for the profile B baseline model and reservoir elevation of 540 ft
(flow scenario 2) .......................................................................................................................................................... 31
Figure 16. Seepage (foot per second) through the downstream embankment and ground surface as a
function of distance for the three different reservoir elevations illustrated in figures 13–15 (flow scenario 2).............. 32
Figure 17. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground
surface (red) per foot along the length of the dam as a function of reservoir elevation for flow scenario 2.................. 33
Figure 18. Predicted water levels in observation wells 15 feet (left) and 300 feet (right) from the downstream
toe for flow scenario 2.................................................................................................................................................. 34
Figure 19. Self-potential (millivolts) values predicted along the downstream embankment and ground
surface for the three different reservoir elevations illustrated in figures 13–15 for flow scenario 2 .............................. 35
Figure 20. Flow model results for the profile A model with no horizontal-drainage fill and reservoir
elevation of 485 ft (flow scenario 3)............................................................................................................................. 36
Figure 21. Flow model results for the profile A model with no horizontal-drainage fill and reservoir
elevation of 510 ft (flow scenario 3)............................................................................................................................. 37
Figure 22. Flow model results for the profile A model with no horizontal-drainage fill and reservoir
elevation of 540 ft (flow scenario 3)............................................................................................................................. 38
Figure 23. Seepage (foot per second) through the downstream embankment and ground surface as a
function of distance for the three different reservoir elevations illustrated in figures 20–22 (flow scenario 3).............. 39
Figure 24. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground
surface (red) per foot along the length of the dam as a function of reservoir elevation for flow scenario 3.................. 40
Figure 25. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream
toe for flow scenario 3.................................................................................................................................................. 41
Figure 26. Self-potential (millivolts) values predicted along the downstream embankment and ground
surface for the three different reservoir elevations illustrated in figures 20–22 for flow scenario 3 .............................. 42
6. Geophysical investigations at Hidden Dam—Flow simulationsvi
Figure 27. Saturated hydraulic-conductivity values for scenario 4 are identical to scenario 1 (figure 3),
with the addition of a higher conductivity near-surface layer in the downstream portion of the model......................... 43
Figure 28. Flow model results for the profile A baseline model with an additional near-surface sediment
layer and reservoir elevation of 485 ft (flow scenario 4)............................................................................................... 44
Figure 29. Flow model results for the profile A baseline model with an additional near-surface sediment
layer and reservoir elevation of 510 ft (flow scenario 4)............................................................................................... 45
Figure 30. Flow model results for the profile A baseline model with an additional near-surface sediment
layer and reservoir elevation of 540 ft (flow scenario 4)............................................................................................... 46
Figure 31. Seepage (feet per second) through the downstream embankment and ground surface as a
function of distance for the three different reservoir elevations illustrated in figures 28–30 (flow scenario 4).............. 47
Figure 32. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground
surface (red) per foot along the length of the dam as a function of reservoir elevation for flow scenario 4.................. 48
Figure 33. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream
toe for flow scenario 4.................................................................................................................................................. 49
Figure 34. Self-potential (millivolts) values predicted along the downstream embankment and ground
surface for the three different reservoir elevations illustrated in figures 28–30 for flow scenario 4 .............................. 50
Figure 35. Electrical resistivity (ohm-meters) predicted for flow scenario 4 at a reservoir elevation of 510 feet ...... 51
Figure 36. Saturated hydraulic-conductivity values for scenario 5 are identical to scenario 1 (figure 3),
with the addition of a higher conductivity channel that extends to several hundred feet depth and connects
the upstream and downstream portions of the model.................................................................................................. 52
Figure 37. Flow model results for the profile A baseline model with an additional deep sediment channel
and reservoir elevation of 485 ft (flow scenario 5) ....................................................................................................... 53
Figure 38. Flow model results for the profile A baseline model with an additional deep sediment channel
and reservoir elevation of 510 ft (flow scenario 5) ....................................................................................................... 54
7. Geophysical investigations at Hidden Dam—Flow simulations vii
Figure 39. Flow model results for the profile A baseline model with an additional deep sediment channel
layer and reservoir elevation of 540 ft (flow scenario 5)............................................................................................... 55
Figure 40. Seepage (feet per second) through the downstream embankment and ground surface as a
function of distance for the three different reservoir elevations illustrated in figures 37–39 (flow scenario 5).............. 56
Figure 41. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground
surface (red) per foot along the length of the dam as a function of reservoir elevation for flow scenario 5.................. 57
Figure 42. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream
toe for flow scenario 5.................................................................................................................................................. 58
Figure 43. Self-potential (millivolts) values predicted along the downstream embankment and ground
surface for the three different reservoir elevations illustrated in figures 37–39 for flow scenario 5 .............................. 59
Figure 44. Historical record of reservoir elevation (top) and water levels relative to ground surface
(negative values are below ground) for observation wells OW-22 and OW-7.............................................................. 60
Figure 45. Detailed view of reservoir elevation and observation-well data for OW-22 and OW-7
from 2001–2004 .......................................................................................................................................................... 61
Figure 46. Crossplots of reservoir elevation and observation-well water level data for OW-22 (A)
and OW-7 (B), along with model-predicted results from the various flow scenarios in this study ................................ 62
Figure 47. Gradation curves for primary Hidden Dam model units.......................................................................... 63
Figure 48. Soil-water retention curves for primary Hidden Dam model units........................................................... 64
8. Geophysical investigations at Hidden Dam—Flow simulationsviii
Tables
Table 1. Baseline parameters for each Hidden Dam unit used in the variably saturated flow model......................... 6
Table 2. Summary of gradation and soil-water retention data for Hidden Dam model units..................................... 19
9. Geophysical investigations at Hidden Dam—Flow simulations ix
Conversion Factors
Inch/Pound to SI
Multiply By To obtain
Length
inch (in.) 2.54 centimeter (cm)
foot (ft) 0.3048 meter (m)
mile (mi) 1.609 kilometer (km)
Area
acre 4,047 square meter (m2
)
acre 0.004047 square kilometer (km2
)
square mile (mi2
) 2.590 square kilometer (km2
)
Volume
gallon (gal) 0.003785 cubic meter (m3
)
acre-foot (acre-ft) 1,233 cubic meter (m3
)
Flow rate
foot per day (ft/d) 0.3048 meter per day (m/d)
cubic foot per day (ft3
/d) 0.02832 cubic meter per day (m3
/d)
gallon per minute (gal/min) 0.06309 liter per second (L/s)
gallon per day (gal/d) 0.003785 cubic meter per day (m3
/d)
Mass
pound, avoirdupois (lb) 0.4536 kilogram (kg)
Pressure
pound-force per square foot (lb/ft2
) 0.04788 kilopascal (kPa)
Density
pound per cubic foot (lb/ft3
) 16.02 kilogram per cubic meter
(kg/m3
)
Acceleration
foot per square second (ft/s2
) 0.3048 meter per square second (m/s2
)
Hydraulic conductivity
foot per day (ft/d) 0.3048 meter per day (m/d)
Vertical coordinate information is referenced to North American Vertical Datum of 1988 (NAVD 88).
Horizontal coordinate information is referenced to the North American Datum of 1983 (NAD 83).
Elevation, as used in this report, refers to distance above the vertical datum.
10. Geophysical investigations at Hidden Dam—Flow simulationsx
Electrical Conductivity and Electrical Resistivity
Multiply By To obtain
Electrical conductivity
siemens per meter (S/m) 1,000 millisiemens per meter (mS/m)
siemens per meter (S/m) 10,000 microsiemens per meter (µS/cm)
Electrical resistivity
ohm-meters (ohm-m) 0.001 kiloohm-meters (kohm-m)
Electrical conductivity σ in siemens per meter (S/m) can be converted to electrical resistivity ρ in ohm-meters (ohm-m) as
follows: ρ = 1/ σ.
Electrical resistivity ρ in ohm-meters (ohm-m) can be converted to electrical conductivity σ in siemens per meter (S/m) as
follows: σ = 1/ ρ.
11. Geophysical Investigations at Hidden Dam, Raymond,
California—Flow Simulations
By Burke J. Minsley and Scott Ikard
Introduction
Numerical flow modeling and analysis of
observation-well data at Hidden Dam are
carried out to supplement recent geophysical
field investigations at the site (Minsley and
others, 2010). This work also is complementary
to earlier seepage-related studies at Hidden Dam
documented by Cedergren (1980a, b). Known
seepage areas on the northwest right abutment
area of the downstream side of the dam was
documented by Cedergren (1980a, b).
Subsequent to the 1980 seepage study, a
drainage blanket with a sub-drain system was
installed to mitigate downstream seepage. Flow
net analysis provided by Cedergren (1980a, b)
suggests that the primary seepage mechanism
involves flow through the dam foundation due
to normal reservoir pool elevations, which
results in upflow that intersects the ground
surface in several areas on the downstream side
of the dam. In addition to the reservoir pool
elevations and downstream surface topography,
flow is also controlled by the existing
foundation geology as well as the presence or
absence of a horizontal drain in the downstream
portion of the dam.
The current modeling study is aimed at
quantifying how variability in dam and
foundation hydrologic properties influences
seepage as a function of reservoir stage. Flow
modeling is implemented using the COMSOL
Multiphysics software package, which solves
the partially saturated flow equations in a two-
dimensional (2D) cross-section of Hidden Dam
that also incorporates true downstream
topography. Use of the COMSOL software
package provides a more quantitative approach
than the flow net analysis by Cedergren (1980a,
b), and allows for rapid evaluation of the
influence of various parameters such as
reservoir level, dam structure and geometry, and
hydrogeologic properties of the dam and
foundation materials. Historical observation-
well data are used to help validate the flow
simulations by comparing observed and
predicted water levels for a range of reservoir
elevations. The flow models are guided by, and
discussed in the context of, the geophysical
work (Minsley and others, 2010) where
appropriate.
12. Geophysical investigations at Hidden Dam—Flow simulations2
Background
Location and Geology
Hidden Dam is located on the Fresno River
in the Sierra Nevada foothills, approximately 15
miles northeast of Madera, California (figure 1).
Detailed information regarding the dam
construction and local geology and hydrology,
summarized below, is provided by the U.S.
Army Corps of Engineers (1977) as well as
Cedergren (1980a, b). Hidden Dam is a rolled
earthfill dam constructed between 1972 and
1975, with a crest length of approximately
5,700 ft, a maximum height above streambed of
184 ft, and a crest elevation of 561 ft. At gross
pool (elevation of 540 ft), the impounded lake
has a surface area of about 1,570 acres and a
storage capacity of 90,000 acre-feet. Relief at
the dam site is approximately 180 ft with
elevations ranging between about 400 ft at the
streambed to approximately 580 ft on the right
and left abutments. This topography is
characterized by gently rolling, rounded hills
with scattered rock outcrops.
Figure 1. Location (inset) and aerial photo of Hidden Dam. Colored lines indicate topographic profiles that are used
in the flow modeling study. Observation wells discussed in this report are labeled.
The area in the vicinity of Hidden Dam is
underlain by what is generally described as
granitic and associated metamorphic rocks
derived from the Sierra Nevada batholith,
though there is some variability in composition,
texture, and color (U.S. Army Corps of
Engineers, 1977). Granitic rocks are overlain
by residual soil, slope wash, and alluvium,
ranging in thickness from zero to approximately
30 ft and varying in composition between sands,
13. Geophysical investigations at Hidden Dam—Flow simulations 3
silts, and clays. Beneath the overburden, to
total depths of up to 60 ft, the granite is
decomposed such that it is easily crumbled or
broken. Fresh rock occurs below the
decomposed granite, though decomposed
materials are occasionally interspersed up to
depths of 140 ft. Jointing was observed
throughout the foundation area during
excavation, though the profusion of joints and
the extent to which they are clay-filled varies
throughout the site.
Summary of Previous Work
Studies carried out by Cedergren (1980a, b)
highlighted the right, or northwest, side of the
dam as the primary area of seepage concern.
Part of these studies included several flow net
calculations based on different characteristic
sections of the dam that capture variability in
downstream topography and horizontal drainage
in the downstream portion of the dam. Initial
estimates of hydraulic conductivity for the
foundation and core materials resulted in
seepage rates that did not match observed
values, and revised hydraulic conductivity
values were determined that provided a match
between observed and predicted seepage
(Cedergren, 1980a). A second set of flow net
calculations were calibrated to new observation-
well data, and predicted substantially higher
water levels in several downstream locations for
gross pool (540 ft) conditions. All of the flow
net calculations were presented for gross pool
conditions and did not incorporate any effect of
the grout curtain located beneath the dam
foundation.
More recently, geophysical surveys
conducted in May 2009 at Hidden Dam focused
on (1) assessing seepage through the use of self-
potential measurements and (2) characterizing
heterogeneity in the subsurface that might
influence seepage patterns using direct current
(DC) resistivity measurements (Minsley and
others, 2010). The reservoir elevation at the
time of the self-potential survey was
approximately 490 ft, resulting in significantly
less seepage than expected when the reservoir is
at or near gross pool. The self-potential data
highlighted several diffuse seepage areas on the
right side of the dam that were consistent with
the areas of previously known seepage.
Additionally, one area of potentially focused
seepage was identified above the outlet works.
There was no evidence for significant amounts
of seepage on the left side of the dam, which is
also consistent with previous observations from
the site (Cedergren, 1980a).
The DC resistivity data showed a resistive
feature at approximately 0- to 80- ft depths
along most of the right side of the dam, which
was interpreted to be relatively unweathered and
low-porosity granitic bedrock (figure 2). In
general, this bedrock is expected to have
relatively low hydraulic conductivity, but it is
possible that there are localized seepage
pathways in this unit due to the presence of
joints. At the surface, lower resistivity values
were interpreted as a combination of alluvial
overburden and decomposed, or weathered,
granitic bedrock that likely have higher
hydraulic conductivity. One notable feature in
the resistivity data is the presence of a wide
(300–400 ft), intermediate-resistivity channel on
the right side of the dam, which may be a
significant pathway for increased flow
underneath the dam. This feature is coincident
with the broad self-potential anomaly in the
low-topography area on the right side of the
dam, which lends further evidence to the fact
that this is an area of enhanced seepage.
Hidden Dam Flow Simulations
Description of Model
Two-dimensional (2D) numerical models of
variably saturated flow at Hidden Dam were
constructed using the COMSOL Multiphysics
3.5a finite element modeling software. The
models simulate pressure head and flow
distributions in the dam and surrounding
foundation materials by solving the steady-state
14. Geophysical investigations at Hidden Dam—Flow simulations4
Richards equation (Freeze and Cherry, 1979),
where the van Genuchten (1980)
parameterization is used to describe the
saturation-dependent hydraulic properties (see
Appendix). The models are used to assess the
potential for seepage at the dam for several
scenarios that include variability in the reservoir
Figure 2. Inverted sections for DC resistivity (A) line 1 and (B) line 2 (from Minsley and others, 2010) at 1:1 scale.
Location E, observed on both lines, is interpreted to be a deep alluvial valley between bedrock highs; locations F
are highly resistive features that may represent competent granitic highs with complex geometry; and locations G
illustrate high near-surface resistivity associated with large granite outcrops.
elevation, internal dam structure, and
foundation structure. The DC resistivity survey
results (Minsley and others, 2010) are used to
help inform likely scenarios for subsurface
hydraulic conductivity variability.
Additionally, self-potential signals are predicted
for the various flow models by incorporating
electrokinetic coupling in COMSOL, as
described in the Appendix.
The basic model geometry was constructed
to match the dam design specifications (U.S.
Army Corps of Engineers, 1977; Cedergren,
1980a) as closely as possible, and downstream
topographic profiles were extracted from a 30-ft
resolution digital elevation model (DEM) of the
surrounding terrain. The model geometries
shown in figure 3 and 4 correspond to profiles
A and B shown in figure 1, where the elevation
at the downstream toe is approximately 450 and
470 ft, respectively. Each model includes
subdomains representing bedrock (BR), the
central impervious core (IC), the outer shell
comprising random fill materials (RF),
transition and outer shell zones comprising
select fill materials (SF), the vertical chimney
drain comprising drainage fill materials (DF),
and the impervious grout curtain (GC) beneath
the dam foundation.
The model geometries in figure 3 and 4 and
the hydrologic parameters for each unit
summarized in table 1 are used as the ‘baseline’
models for this study. Saturated hydraulic
conductivity values were taken from Cedergren
(1980a), with the exception of the grout curtain,
which was not incorporated in previous studies.
The saturated and residual moisture content, as
well as parameters a (related to the air entry
pressure head and desorption behavior of the
soil) and n (related to the pore-size distribution
of the soil), were derived according to the
15. Geophysical investigations at Hidden Dam—Flow simulations 5
procedure discussed in the Appendix from
information in the foundation report (U.S. Army
Corps of Engineers, 1977) and Cedergren
(1980a) for all units except for the bedrock and
grout curtain, which did not have the necessary
input data. Default values have been used for
the hydrologic parameters where no information
was available. Results from these baseline
models, as well as several variations on the
geometry and hydrologic properties, are
discussed in the following sections. For
convenience, the figures from all of the
scenarios have been placed together at the end
of this report..
Figure 3. Geometry of Hidden Dam and downstream topography along profile A in figure 1. Color scale indicates
the baseline saturated hydraulic conductivity values used in this study.
Figure 4. Geometry of Hidden Dam and downstream topography along profile B in figure 1. Color scale indicates
the baseline saturated hydraulic conductivity values used in this study.
16. Geophysical investigations at Hidden Dam—Flow simulations6
Table 1. Baseline parameters for each Hidden Dam unit used in the variably saturated flow model.
Saturated
hydraulic
conductivity, Ks
(ft/day)
Saturated
moisture
content, θs
(volume
fraction)
Residual
moisture
content, θr
(volume
fraction)
a
(1/ft)
n
Water
density, ρ
(lb/ft3
)
Fluid
source, Qs
(1/s)
Bedrock (BR) 0.1 0.150 0.050 0.2000 2.000
62.42 0
Impervious
core (IC)
0.02 0.418 0.210 0.2013 1.9923
Random fill
(RF)
1.0 0.372 0.015 0.2399 3.9218
Select fill (SF) 2.0 0.375 0.014 0.2453 3.3088
Drainage fill
(DF)
8,000.0 0.425 0.020 0.7165 3.5952
Grout curtain
(GC)
0.01 0.05 0.005 0.2000 2.0000
Scenario 1: Baseline Model, Profile A
This first scenario illustrates the difference
in flow for the baseline model along profile A at
reservoir elevations between 480 and 540 ft.
The baseline models have identical material
properties for the various dam and bedrock units
(table 1), but differ in downstream topography
profiles. The elevation at the downstream toe
on profile A is 450 ft, and there is a low-
topography area approximately 100 ft from the
toe of the dam, or at about 350 ft downline
distance on the model. This geometry and
parameters for this scenario are similar to flow
net number 2 produced by Cedergren (1980a).
Figure 5–7 show the flow model results for
profile A with reservoir elevations 485, 510,
and 540 ft. Increasing saturation and flow
through the dam are evident as the reservoir
elevation increases. In each of these figures, the
length of the white arrows represent relative
variations in flow velocity in a model, but do
not indicate absolute differences in flow
velocity between models. The effectiveness of
the high-hydraulic-conductivity horizontal-
drainage fill on the downstream side of the dam
is evident in these figures, as the drainage fill
prevents increased water levels and redirects
upward flow in the foundation materials out
toward the toe. Saturation in the high-
topography areas downstream of the dam can
also be seen to increase as the reservoir
elevation increases. Focused seepage is also
evident in the low-topography area at
approximately 350 ft downline distance , and
becomes more enhanced at higher reservoir
elevations. This observation of focused seepage
in the low-topography area is consistent with
observations of seepage at Hidden Dam
(Cedergren, 1980a).
Seepage through the downstream
embankment and ground surface is quantified in
figure 8, which shows the rate of seepage (ft/s)
along the surface model boundary as a function
of distance for the models shown in figure 5–7.
The sharp spike at a distance of approximately
260 ft corresponds to the outward flow through
the conductive drainage-fill material at the toe
of the dam. Discrete zones of seepage are
evident in the low-topography areas from 300–
400 ft, as well as 900–1,000 ft. This latter
seepage zone is another low-topography area,
which can be seen in figure 3. As expected, the
rate of seepage increases with reservoir
elevation. In some cases (just past 400 ft, for
example), seepage only begins at the higher
reservoir elevations.
Further quantification of seepage for this
model is shown in figure 9, which shows
volumetric flow (gal/min) through the
17. Geophysical investigations at Hidden Dam—Flow simulations 7
downstream embankment (blue) and ground
surface (red) per foot along the length of the
dam as a function of reservoir elevation. The
volumetric flow is calculated by integrating the
seepage along both the downstream
embankment and ground surface boundaries in
the model. An increasing proportion of flow
through the dam can be seen with increasing
reservoir elevation, to a maximum of
approximately 0.055 gal/min per ft of total
seepage at gross pool. This is consistent with,
but slightly greater than, the approximately 0.04
gal/min per ft for flow net number 2 produced
by Cedergren (1980a).
Figure 10 illustrates simulated observation-
well data that can be obtained from the flow
model results. Each panel shows the predicted
water level in an observation well relative to the
ground surface, where positive values are higher
than the ground surface, for different reservoir
elevations and any well depth between zero and
50 feet. That is, for a given observation well
depth and reservoir elevation, the predicted
water level in the well can be found on one of
the curves in the figure. The panel on the left is
for an observation-well approximately 15 ft
from the downstream toe, which is a typical
location for a number of observation wells at
Hidden Dam. The panel on the right is for an
observation well approximately 90 ft from the
downstream toe, which corresponds to a low-
topography area of focused seepage.
The model-predicted water levels are
consistent with observation-well data reported
in the 1980 seepage study (Cedergren, 1980b).
Although the observed and model-predicted
water levels are consistent, some discrepancy
can be expected due to (1) the fact that the
ground surface elevations for the flow model do
not exactly match the observation wells, (2)
hydrogeologic heterogeneity is not captured in
the flow model, and (3) the three-dimensional
nature of flow is not captured in the two-
dimensional flow model.
For example, water levels in observation
wells OW-9 and OW-10, which are located in
areas of relatively low topography away from
the downstream toe (figure 1), were 2–5 ft
above ground surface at the reservoir elevation
of approximately 484 ft (see table 1 in
Cedergren, 1980b). Given the well depth of
approximately 22 ft for these wells, the model-
predicted water level on the right panel in figure
10 is around 4 ft above the ground surface for
the curve that corresponds to a reservoir
elevation of 485 ft. Observed water levels in
wells OW-7A/B and OW-8A/B, which are close
to the downstream toe, were approximately 2 ft
and –2ft with respect to the ground surface,
respectively. The model-predicted water level
for wells close to the downstream toe at a
reservoir elevation of 485 ft is less than 1 ft
below ground surface (figure 10, left panel),
which is consistent with the observed values. A
key benefit of the flow modeling is that water
levels can be predicted for any reservoir
elevation or observation-well depth. As can be
seen in figure 10, the maximum expected water
level for this model geometry is approximately
8 ft above the ground surface for a 50-ft-deep
well located 90 ft from the downstream toe.
Figure 11 shows the self-potential values
predicted along the ground surface and
downstream embankment for the flow depicted
in figure 5–7 (reservoir elevations 485, 510, and
540 ft). The self-potential values are calculated
by incorporating electrokinetic coupling into the
COMSOL model, as described in the Appendix.
The self-potential values depend on the flow
velocity, electrical resistivity structure, and
excess charge in the pore space. The latter two
values are automatically calculated using
empirical relationships that are also discussed in
the Appendix. The self-potential values
displayed in figure 11 are relative to an arbitrary
reference location, which was chosen at the
crest of the dam (distance equals 0 ft).
There are four main components to the self-
potential signal that can be attributed to details
in the flow model:
1. General trend of increasing potentials with
distance: This trend represents the expected
18. Geophysical investigations at Hidden Dam—Flow simulations8
response of increasing self-potentials in the
direction of flow (Morgan and others, 1989;
Minsley and others, 2010).
2. Trend of increasing potentials with
increasing reservoir level: Because the self-
potentials are proportional to flow, as
described in equation (6) in the Appendix,
increased flow due to higher reservoir
elevations leads to increased self-potentials
3. Positive “kicks” superimposed on the
general trend: Seepage outflow areas are
expected to result in positive self-potential
anomalies. This is related to item (1) above,
as the seepage areas represent localized flow
terminations and, correspondingly,
maximum self-potentials at those locations.
4. Sharp trend in self-potentials between 0–100
ft, increasing with reservoir elevation, and a
negative center at the highest reservoir
elevation: This trend near the dam crest is
due to the increasing downward component
of flow as seepage passing through the
impervious core is rapidly transported
through the drainage fill. In contrast with
the seepage outflow areas that generate a
positive anomaly, this downward flow-zone
generates a negative anomaly. Because the
flow magnitude increases with increasing
reservoir elevation, the strength of the
negative self-potential anomaly increases
proportionally.
The self-potential data collected at Hidden
Dam (Minsley and others, 2010) clearly indicate
localized positive anomalies on the order of 30–
70 mV in the low-topography seepage areas,
which is consistent with the coupled flow
modeling result. The data do not clearly
indicate an overall trend of increasing potentials
in the downstream direction, though this is
difficult to identify due to the location of survey
lines, which were primarily in the dam-parallel
direction. Additionally, there is clearly a three-
dimensional component to the flow and
corresponding self-potentials due to variations
in the ground-surface topography both along
and perpendicular to the dam strike.
An example of the electrical resistivity
structure determined from the flow model at a
reservoir elevation of 510 ft is shown in figure
12. The resistivity values are calculated using
equation (7) in the Appendix, where a constant
water resistivity of 20 ohm-m and cementation
factor, m, of 1.7 are assumed. The bedrock
resistivity of 500 ohm-m is similar to the values
observed during the geophysical surveys at
Hidden Dam (Minsley and others, 2010),
though the field data suggest a primarily two-
layer model with lower near-surface resistivity,
which is investigated in modeling scenarios 4
and 5. Very high resistivities (greater than
10,000 ohm-m) are observed in the unsaturated
portions of the dam. The resistivity information
is an important part of calculating self-potential
values, but could also be used to guide future
geophysical investigations at the site.
Scenario 2: Baseline Model, Profile B
This flow scenario follows the same
modeling procedures as with the previous
example, but uses the model geometry for
profile B (figure 4) along with the baseline
model parameters (table 1). Profile B is located
closer to the right abutment than profile A
(figure 1), and therefore has higher ground
surface elevations (470 ft at the downstream
toe) than profile A. A second difference with
this profile is the details of the downstream
topography. Along profile B, the ground
surface dips only slightly near the downstream
toe, then rises again over one of the rounded
hills found in the right abutment area before
dropping approximately 20 ft to a low-
topography area that coincides with the area
covered by the drainage blanket. As with
scenario 1, the low-topography areas are
significant factors in the distribution of seepage.
Figure 13–15 show results from the flow
model at 485-, 510-, and 540-ft-reservoir
elevations. As with scenario 1, the
effectiveness of the horizontal drainage fill is
evident as it redirects upward seepage beneath
19. Geophysical investigations at Hidden Dam—Flow simulations 9
the dam toward the downstream toe rather than
into the dam structure. The main difference
with this flow scenario is the distribution of
seepage in low-topography areas; particularly
between 450–650 ft, but also somewhat near the
downstream toe. Additionally, the uppermost
part of the hill between 250–450 ft remains
unsaturated at the lower reservoir elevations,
but becomes almost entirely saturated at gross
pool.
Seepage through the downstream
embankment and ground surface is quantified in
figure 16, which shows the rate of seepage (ft/s)
along the surface model boundary as a function
of distance for the models shown in figure 13–
15. The sharp spike at a distance of
approximately 220 ft corresponds to the
outward flow through the conductive drainage-
fill material at the toe of the dam. Discrete
zones of seepage are evident on either side of
the hill area from 220–280 ft and 450–600 ft, as
well as another low-topography area farther
downstream at 900–1,000 ft. As expected, the
rate of seepage increases with reservoir
elevation.
Figure 17 shows the volumetric flow
(gal/min) through the downstream embankment
(blue) and ground surface (red) per foot along
the length of the dam as a function of reservoir
elevation. As with scenario 1, an increasing
proportion of flow through the dam can be seen
with increasing reservoir elevation, to a
maximum of approximately 0.0425 gal/min per
ft at gross pool. This is also very consistent
flow net number 2 produced by Cedergren
(1980a), which predicted approximately 0.04
gal/min per ft. The reduced seepage compared
with scenario 1 is due to the higher downstream
elevation in this case. For the lowest reservoir
elevation (480 ft), virtually all of the seepage is
through the downstream ground surface.
Figure 18 illustrates simulated observation-
well data that can be obtained from the flow
model results. Each panel shows the predicted
water level in an observation well relative to the
ground surface, where positive values are higher
than the ground surface (that is, artesian
conditions), for different reservoir elevations
and any well depth between 0 and 50 ft. That
is, for a given observation-well depth and
reservoir elevation, the predicted water level in
the well can be found on one of the curves in
the figure. The panel on the left is for an
observation well approximately 15 ft from the
downstream toe, which is a typical location for
a number of observation wells at Hidden Dam.
The panel on the right is for an observation well
approximately 300 ft from the downstream toe,
which corresponds to a low-topography area of
focused seepage.
The simulated observation-well results are
similar to those for scenario 1, with a few minor
differences. For example, the water level
predicted for any well depth at the location 15 ft
downstream from the toe is approximately 2 ft
below ground surface for the 480-ft reservoir
elevation in scenario 2, whereas it is much
closer to the ground surface in scenario 1.
Additionally, at a reservoir elevation of 485 ft,
the predicted water level on the left panel of
figure 18 is above the ground surface, whereas
the corresponding curve in figure 10 indicates a
water level slightly below ground surface. This
is somewhat counterintuitive as one might
expect the lower topography scenario (scenario
1) to have the higher predicted water levels, and
highlights the nonlinearity in predicted water
level as a function of model geometry.
Figure 19 shows the self-potential values
predicted along the ground surface and
downstream embankment for the flow depicted
in figure 13–15 (reservoir elevations 485, 510,
and 540 ft). The self-potential values displayed
in figure 19 are relative to an arbitrary reference
location, which was chosen at the crest of the
dam (distance equals 0 ft).
20. Geophysical investigations at Hidden Dam—Flow simulations10
Scenario 3: Profile A, No Horizontal Drainage
Fill
This flow scenario is identical to scenario 1,
with the exception that there is no horizontal
drainage-fill material along the downstream
base of the dam, and is similar to flow net 1
produced by Cedergren (Cedergren, 1980a).
Absence of the high-hydraulic-conductivity
horizontal-drainage fill results in elevated water
levels in the downstream portion of the dam,
which can be seen in the flow model results in
figure 20–22. This increased flow through the
dam, as well as elevated hydraulic pressure
relative to the baseline models, could be a
mechanism for internal erosion over long
periods of time.
Although there is clearly a larger region of
seepage in the dam and downstream
embankment, the seepage pattern along the
downstream topography is not significantly
different. This is quantified in figure 23, which
shows the rate of seepage (ft/s) along the model
boundary as a function of distance for the
models shown in figure 20–22. In this scenario,
the increased seepage face along the
downstream embankment is evident as a
broader zone of flow between 240–260 ft in
figure 23, compared with the very sharp outflow
spike at the downstream toe in figure 8.
Discrete zones of seepage are evident in the
low-topography areas from 300–400 ft, as well
as 900–1,000 ft, and are similar in magnitude to
scenario 1. One interesting feature is the
increased seepage areas between 400–500 ft
compared with scenario 1. This is likely due to
the fact that the net hydraulic conductivity of
the dam is reduced with the removal of the
drainage-fill material, which partitions a greater
amount of seepage into the foundation below
the dam that exits further downstream.
Figure 24 shows the volumetric flow
(gal/min) through the downstream embankment
(blue) and ground surface (red) per foot along
the length of the dam as a function of reservoir
elevation. As with scenario 1, an increasing
proportion of flow through the dam can be seen
with increasing reservoir elevation, to a
maximum of approximately 0.0425 gal/min per
ft at gross pool. It is interesting that the total
seepage in scenario 3 is less than scenario 1 at
all reservoir elevations (0.055 gal/min at gross
pool for scenario 1 versus 0.0425 gal/min at
gross pool for scenario 3). Additionally, a
much greater proportion of seepage in scenario
3 flows through the ground surface instead of
the downstream embankment compared with
scenario 1. This can be explained by the fact
that, while the seepage face along the
downstream embankment is wider in scenario 3,
the high-hydraulic conductivity drainage-fill
material in scenario 1 drains significantly more
water through the dam.
The predicted observation-well water levels
in figure 25 are elevated with respect to the
predicted water levels for scenario 1 (figure 10),
and this difference becomes more pronounced
as the well depth and/or reservoir elevation
increases. Significant pressures at depth
corresponding to water levels of 10–12 ft above
the ground surface are predicted for the highest
reservoir elevations. This observation is
consistent with the argument that the reduced
net-hydraulic conductivity of the dam due to the
lack of horizontal-drainage fill causes more
seepage to be partitioned into the subsurface
beneath the dam, contributing to increased
pressure at depth. It is possible that an analysis
of observation-well data could be used to assess
the effectiveness of the horizontal drain along
the length of the dam, though it is important to
note that other factors such as local
hydrogeologic heterogeneity can influence these
observations.
Figure 26 shows the self-potential values
predicted along the ground surface and
downstream embankment for the flow depicted
in figure 20–22 (reservoir elevations 485, 510,
and 540 ft). The self-potential values displayed
in figure 26 are relative to an arbitrary reference
21. Geophysical investigations at Hidden Dam—Flow simulations 11
location, which was chosen at the crest of the
dam (distance equals 0 ft).
The self-potentials for scenario 3 are very
similar to scenario 1 (figure 11), with a few
exceptions. First, the magnitude of the seepage-
related self-potential anomalies between 250–
450 ft are more pronounced in scenario 3, again
reflecting the increased amount of subsurface
flow relative to scenario 1. Second, the shape
of the self-potential curves from 0–250 ft are
different for the two scenarios, reflecting the
difference in internal flow patterns in the dam
structure and shallow foundation.
Measurements in this area could be very
diagnostic about flow in the dam structure,
though good measurements are difficult to make
over the dam structure due to the difficulty in
obtaining good electrical contact over riprap-
covered surfaces (Minsley and others, 2010).
Scenario 4: Profile A, Baseline Model with
Near-Surface Sediment Layer
Flow scenario 4 uses the profile A baseline
model as in scenario 1, but with the addition of
a variable-thickness layer in the near-surface on
the downstream portion of the model that has a
higher saturated hydraulic conductivity than the
bedrock (figure 27). Justification for the
addition of this layer comes from the known
presence of residual soil, slope wash, alluvial
sediments, and decomposed granite that overlie
bedrock (U.S. Army Corps of Engineers, 1977;
Cedergren, 1980a), as well as the two-layer
resistivity model observed over the downstream
portion of the dam foundation (Minsley and
others, 2010) that is consistent with higher
hydraulic conductivity sedimentary overburden.
Hydraulic parameters used for this sediment
layer are: Ks = 0.5 ft/day, s = 0.25, r = 0.015,
a = 0.2399 1/ft, n = 3.9218.
The flow modeling results in figure 28–30
are similar to those in scenario 1 (figure 5–7)
with a few minor exceptions. Although the
drainage-fill material still serves as an effective
cutoff for upward flow coming from the
foundation, an increased amount of
downstream-oriented seepage is focused in the
sediment layer due to its elevated hydraulic
conductivity with respect to the bedrock.
Additionally, the elevated hydraulic
conductivity and saturated moisture content of
the sediment layer limits the saturation in some
of the high-topography hill areas downstream of
the dam, even at gross pool.
The rate of seepage (ft/s) along the model
boundary as a function of distance for the
models shown in figure 28–30 is illustrated in
figure 31. Compared with the corresponding
image for scenario 1 (figure 8), it is clear that
the impact of the high-hydraulic-conductivity
sediment layer has not significantly altered the
distribution of seepage, but the seepage rate has
increased by a factor of 2–3.
Figure 32 shows the volumetric flow
(gal/min) through the downstream embankment
(blue) and ground surface (red) per foot along
the length of the dam as a function of reservoir
elevation. The maximum of approximately
0.057 gal/min at gross pool is close to the
scenario 1 value of 0.055 gal/min (figure 9), and
the total rate of seepage at other reservoir
elevations are also comparable between the two
models. In scenario 4, however, it is apparent
that a greater amount of the volumetric seepage
occurs through the downstream ground surface
rather than the embankment when compared
with scenario 1. This is again consistent with
the observation that the elevated hydraulic
conductivity of the sediment layer directs an
increased amount of flow in the downstream
direction away from the dam.
The predicted observation-well water levels
for scenario 4 are illustrated in figure 33. The
water levels are significantly reduced with
respect to scenario 1 (figure 10), with a
maximum predicted water level of
approximately 4 ft above ground surface at
gross pool for a 50-ft-deep well. The ‘kink’ in
the curves at approximately 40-ft depth
corresponds to the transition from the sediment
22. Geophysical investigations at Hidden Dam—Flow simulations12
layer to bedrock. The reduced water levels
predicted for scenario 4 are a direct result of the
elevated hydraulic conductivity, which acts to
reduce hydraulic pressure in the subsurface.
Figure 34 shows the self-potential values
predicted along the ground surface and
downstream embankment for the flow depicted
in figure 28–30 (reservoir elevations 485, 510,
and 540 ft). The self-potential values are
relative to an arbitrary reference location, which
was chosen at the crest of the dam (distance
equals 0 ft). The self-potential response for
scenario 4 is very similar to scenario 1 (figure
11), both in character and magnitude, though
the self-potential values in flow scenario 4 are
slightly smaller. This is somewhat non-intuitive
due to the increased seepage rate with respect to
scenario 1 (figure 31), but results from the fact
that the elevated hydraulic conductivity
sediment layer leads to reduced excess charge in
equation (8) and the elevated saturated moisture
content of the sediment layer leads to reduced
electrical resistivity according to equation (7),
both of which lead to reduced self-potential
values as described in the Appendix.
The electrical resistivity profile for this flow
model derived using equation (7) and a
reservoir elevation of 510 ft is shown in figure
35. The resistivity of the near-surface sediment
layer is approximately 200 ohm-m, which is
consistent with the values reported from the
geophysical field survey (Minsley and others,
2010). One important factor that is not
accurately accounted for in this flow model is
the thickness profile of this sediment layer.
Because the resistivity surveys were oriented
parallel to the dam, this information could not
be incorporated into the flow models beyond the
use of a ‘typical’ thickness observed from the
resistivity profiles.
Scenario 5: Profile A, Baseline Model with
Deep Sediment Channel
Flow scenario 5 uses the profile A baseline
model as in scenario 1, but with the addition of
a thick (several hundred feet) sediment channel
that extends from the upstream to downstream
portions of the model (figure 36). Justification
for the addition of this deep channel comes
from the resistivity survey at Hidden Dam
(Minsley and others, 2010) that identified a
wide (300–400 ft), low-resistivity channel that
extends to depths of several hundred feet over a
portion of the low-topography area downstream
of the dam (figure 2). Hydraulic parameters
used for this sediment channel are the same as
those used in scenario 4: Ks = 0.5 ft/day, s =
0.25, r = 0.015, a = 0.2399 1/ft, n = 3.9218.
The flow modeling results in figure 37–39
are more similar to those in scenario 1 (figure
5–7) than to the sediment layer case in scenario
4 (figure 28–30). In scenario 5 the hydraulic
conductivity in the foundation is controlled
mainly by the sediment channel (Ks = 0.5
ft/day), compared with scenario 1, where the
foundation is bedrock (Ks = 0.1 ft/day). One
similarity with scenario 4, however, is the
reduced saturation in the high-topography hill
area downstream of the dam due to the elevated
hydraulic conductivity.
The rate of seepage (ft/s) along the model
boundary as a function of distance for the
models shown in figure 37–39 is illustrated in
figure 40. The seepage pattern is similar to
scenario 1 (figure 8), but the magnitude of the
rate of seepage is similar to (but somewhat
larger than) scenario 4 (figure 31). The high-
hydraulic-conductivity sediment channel that
extends to the upstream side of the dam results
in seepage rates that are approximately 3–4
times greater than the baseline case in
scenario 1.
Figure 41 shows the volumetric flow
(gal/min) through the downstream embankment
(blue) and ground surface (red) per foot along
23. Geophysical investigations at Hidden Dam—Flow simulations 13
the length of the dam as a function of reservoir
elevation. The maximum of approximately
0.162 gal/min at gross pool is significantly
larger than the scenario 1 or scenario 5 values of
approximately 0.055 gal/min (figure 9 and 32).
This increased volumetric rate of seepage is
consistent with the value of 0.108 gal/min
reported by Cedergren (1980a, table 6) for a
slightly lower foundation hydraulic conductivity
of 0.25 ft/day.
The predicted observation-well water levels
for scenario 5 are illustrated in figure 42. The
water levels are very similar to those predicted
in scenario 1 (figure 10), with a maximum
predicted water level of approximately 7 ft
above ground surface at gross pool for a 50-ft-
deep well. Although the seepage rate is much
higher than in scenario 1, the effect of the
elevated hydraulic conductivity reduces
pressures at depth and results in similar
predicted water levels.
Figure 43 shows the self-potential values
predicted along the ground surface and
downstream embankment for the flow depicted
in figure 37–39 (reservoir elevations 485, 510,
and 540 ft). The self-potential values are
relative to an arbitrary reference location, which
was chosen at the crest of the dam (distance
equals 0 ft). The self-potential response for
scenario 5 is very similar to scenario 1 (figure
11) and scenario 4 (figure 34), both in character
and magnitude, though the self-potential values
in flow scenario 5 are slightly smaller. This is
due to the same effect discussed in scenario 4,
where the reduced excess charge in equation (8)
and the reduced electrical resistivity according
to equation (7) counteract the increased seepage
rate and leads to reduced self-potential
magnitudes as described in the Appendix.
Comparison with Selected
Observation-Well Data
Historical reservoir elevation data, along
with measurements from observation wells,
piezometers, and weirs, were obtained for the
Hidden Dam site (K. Hazleton, written
commun., 2009). These records provide useful
information regarding the connection between
reservoir elevation and downstream water levels
and seepage at the site. Here, we focus on the
records for two observation wells on the right
abutment drainage blanket area with elevations
that are comparable to the surface elevations on
the two profiles used in this study (figure 1).
OW-22 has an elevation of approximately 450
feet, with a screened depth between 15–20 feet.
OW-7 has an elevation of approximately 470
feet, with a screened depth interval between 30–
40 feet. Figure 44 shows the historical record
of reservoir elevation (top panel) as well as
water levels relative to the ground surface
(negative values are below ground) for these
wells (lower panels) since 1980.
A more detailed view of these curves is
provided in figure 45, which overlays the
reservoir elevation and observation-well records
for the years 2001–2004. Water levels in the
observation wells are a damped version of the
forcing produced by variations in the reservoir
elevation, with a clear time-shift between the
two curves that indicates a characteristic
reaction time for seepage through the dam.
In figure 46, the reservoir elevation data are
cross-plotted with the observation-well water
levels for OW-22 (A) and OW-7 (B) for the
entire available historical record. As expected,
there is a positive correlation between reservoir
elevation and observed water level, with a slope
of approximately 0.1 and 0.2 in OW-22 and
OW-7, respectively (that is, a 1-ft increase in
reservoir elevation leads to approximately 0.2-ft
increase in observation-well levels in OW-7).
The large number of zero-values and absence of
24. Geophysical investigations at Hidden Dam—Flow simulations14
positive water levels in the OW-22 data indicate
the inability to record water levels that are
higher than the ground surface. Values
extrapolated to gross pool using the slope of 0.2
are approximately 8 ft above ground. In OW-7,
above-ground water levels are measured with
pressure transducers.
Superimposed on the observation-well data
are the model-predicted water levels from the
various flow scenarios in this study taken from
the appropriate well depths in figure 10
(scenario 1), figure 18 (scenario 2), figure 25
(scenario 3), figure 33 (scenario 4), and figure
42 (scenario 5). There is a reasonably good
agreement between the observation-well data
and model-predicted water levels, suggesting
that the flow models in this study provide a
good representation of seepage at Hidden Dam,
though the flow models tend to predict water
levels that are slightly elevated for specific
reservoir elevations. This discrepancy may be
related to inaccuracies in the details of the
model geometry or hydrologic properties, as
well as the fact that there is a 3D component of
flow that is not captured in the 2D models. One
notable feature in the simulated water-level data
is the nonlinear aspect that is apparent as a
decrease in slope at higher reservoir elevations,
which is also apparent in the historical record
data in figure 46B.
In figure 46A, it is evident that the
predictions for the scenario 4 model, which
involves the thin sediment (higher hydraulic
conductivity) layer over bedrock (figure 27),
correspond most closely with the historical
record. The lack of historical data for positive
water levels, however, makes it impossible to
validate this observation for reservoir elevations
above 510 ft. Agreement with the historical
data, along with the fact that scenario 4 is
consistent with the hydrogeologic knowledge of
the site as well as the general character observed
in the DC resistivity models (figure 2) over
much of the right abutment area, suggests that
this is a reasonable model for flow through the
portion of the dam in the vicinity of OW-22.
Conclusions
Quantitative information about seepage and
flow patterns at Hidden Dam is provided by this
numerical modeling study. The flow model
scenarios, dam geometry, and hydrologic
parameters were guided by the foundation
report and initial flow net studies (U.S. Army
Corps of Engineers, 1977; Cedergren, 1980a),
with additional information about subsurface
structural properties inferred from more recent
geophysical work (Minsley and others, 2010).
Implementation of the variably saturated flow
equations in COMSOL allows for quantitative
predictions of seepage rates or volumes, water
levels, and degree of saturation anywhere in the
model as a function of changing reservoir
elevation. This provides a valuable framework
for studying different hydrogeologic or dam-
structure scenarios. The modeling results are
consistent with both the initial flow net studies
(Cedergren, 1980a) as well as data from
observation wells at the site.
Additionally, we have provided a
methodology for coupling the flow results to
geophysical properties investigated by Minsley
and others (2010). The predicted electrical
resistivity model for any flow scenario is
determined through a petrophysical relationship
that incorporates the calculated total moisture
content. This electrical resistivity model is
subsequently used in a second set of equations
that describe the self-potential response to the
various flow scenarios based on electrokinetic
coupling. Predicting the geophysical response
to various hydrogeologic models helps to
validate the field data already acquired, but also
provides useful information for guiding future
geophysical studies. The expected geophysical
response to different flow scenarios can be used
to guide survey locations and acquisition
parameters that will be most sensitive to
subsurface changes of interest.
Several of the main insights gained from
this study are outlined below:
25. Geophysical investigations at Hidden Dam—Flow simulations 15
• Low-topography areas act to focus seepage,
which is consistent with historical
observations at the site. Low-topography
areas can also result in seepage at significant
distances downstream of the dam (for
example, 900–1,000 ft in figure 8).
Cedergren (1980a) identified one such area
approximately 700 ft downstream on the left
side of the dam.
• Predicted water levels are near or above the
ground surface for reservoir elevations
above 480 ft in all of the scenarios studied.
The maximum value in this study is
approximately 12 ft above ground surface
for scenario 3 (no horizontal drainage fill,
figure 25). Water levels do not, however,
reach the extremely high values up to 40
feet above the ground surface at gross pool
predicted in the revised flow net study by
Cedergren (1980b)
• Absence of the horizontal drainage-fill
material in the downstream part of the dam
(scenario 3) results in a broader area of
seepage on the downstream embankment
(figure 20–22), but reduced volumetric
seepage compared with the case where the
drainage fill is present. This is because the
absence of the drainage fill reduces the net
hydraulic conductivity of the dam, which
partitions a greater amount of seepage into
the subsurface (compare figure 24 with
figure 9). None the less, this enhanced area
of flow in the dam may lead to increased
long-term erosion under elevated reservoir
levels.
• The presence of a thin (tens of feet)
sedimentary layer with higher hydraulic
conductivity than the underlying bedrock
results in moderately increased seepage in
the downstream area (compare figure 23
with figure 8) as well as a greater proportion
of seepage in the sediment and bedrock
(compare figure 24 with figure 9), but also
results in lower water levels in observation
wells (compare figure 25 with figure 10).
• The presence of a deep (hundreds of feet)
sedimentary channel under the dam
foundation, suggested by the resistivity
survey carried out by Minsley and others
(2010), leads to substantial increases in
volumetric seepage under the dam (compare
figure 41 with figure 9), though water levels
predicted in observation wells are
comparable to the case without a high-
conductivity channel (compare figure 42
with figure 10). This observation of
increased seepage, but unchanged water
level (pressure), is predicted from normal
Darcy flow (Freeze and Cherry, 1979): the
increased hydraulic conductivity in the
sediment channel leads to increased flow,
but the pressure gradient (defined by the
ratio of flow to hydraulic conductivity)
remains unchanged. This suggests that
water-level data alone may not be a good
indicator of relative amounts of seepage
along the dam if the wells are located in
different geologic structures.
• For a given scenario, the predicted self-
potential response scales with seepage due
to increased flow. However, increased
seepage at one location with elevated
hydraulic conductivity does not necessarily
lead to larger self-potentials than an area
with lower hydraulic conductivity and
reduced seepage (compare figure 43 with
figure 11) due to the counteracting role of
electrical resistivity and excess charge in the
self-potential response. It is clear, however,
that for the same bedrock hydraulic
conductivity, increased self-potentials are
observed when the horizontal-drainage fill is
absent because of increased seepage beneath
the dam (compare figure 26 with figure 11).
• The self-potential response over the
downstream embankment for the case with
26. Geophysical investigations at Hidden Dam—Flow simulations16
no horizontal drainage fill (figure 26) is
different than when the drainage fill is
present (figure 11) and becomes more
apparent at higher reservoir elevations.
While this could be a useful indicator of
locations with effective drainage fill, self-
potential measurements on riprap are
difficult and would likely require dedicated
holes into dam material to make good
electrical contact.
• One limiting factor in this study is that 2D
models are used, which assumes that all
flow is perpendicular to the dam. While this
is a reasonable modeling assumption, the
true downstream topography likely produces
a component of flow that is directed toward
the outflow axis of the dam. Additionally,
variability in internal dam structure (for
example, the presence or absence of
drainage fill) and subsurface heterogeneity
(such as the influence of a deep sediment
channel) may also lead to 3D flow patterns
not captured in this study.
Acknowledgments
This work was carried out with the support
of the U.S. Army Corps of Engineers,
Sacramento District, under the supervision of
Lewis Hunter. We thank Lewis Hunter, Kevin
Hazleton, Beth Burton, and Martin Fahning for
their reviews of the manuscript.
References Cited
Archie, G.E., 1942, The electrical resistivity log
as an aid in determining some reservoir
characteristics: Trans. Amer. Inst. Mining
Metallurgical and Petroleum Engineers, v.
146, p. 54–62.
Cedergren, H.R., 1980a, Seepage study of
Hidden Dam, Fresno River, California:
Prepared for Department of the Army,
Sacramento District, Corps of Engineers,
210 p.
Cedergren, H.R., 1980b, Seepage study of
Hidden Dam, Fresno River, California:
Analysis of data from observation wells put in
right abutment seepage areas in 1980:
Prepared for Department of the Army,
Sacramento District, Corps of Engineers,
31 p.
Freeze, R.A., and Cherry, J.A., 1979,
Groundwater: Englewood Cliffs, New Jersey,
Prentice Hall, 604 p.
Ishido, T., and Mizutani, H., 1981,
Experimental and theoretical basis of
electrokinetic phenomena in rock-water
systems and its applications to geophysics:
Journal of Geophysical Research, v. 86, no.
NB3, p. 1763–1775.
Jardani, A., Revil, A., Boleve, A., and Dupont,
J.P., 2008, Three-dimensional inversion of
self-potential data used to constrain the
pattern of groundwater flow in geothermal
fields: Journal of Geophysical Research-Solid
Earth, v. 113, B09204.
Lesmes, D.P., and Friedman, S.P., 2005,
Relationships between the electrical and
hydrogeological properties of rocks and soils,
in Rubin, Y., and Hubbard, S.S., eds.,
Hydrogeophysics: Netherlands, Springer,
p. 87–128.
Minsley, B.J., Burton, B.L., Ikard, S., and
Powers, M.H., 2010, Geophysical
investigations at Hidden Dam, Raymond, CA:
Summary of fieldwork and preliminary data
analysis U.S. Geological Survey Open-File
Report 2010-1013, 25 p.
Morgan, F.D., Williams, E.R., and Madden,
T.R., 1989, Streaming potential properties of
Westerly Granite with applications: Journal of
Geophysical Research-Solid Earth and
Planets, v. 94, no. B9, p. 12449–12461.
Revil, A., Pezard, P.A., and Glover, P.W.J.,
1999, Streaming potential in porous media 1.
Theory of the zeta potential: Journal of
Geophysical Research-Solid Earth, v. 104,
no. B9, p. 20021–20031.
27. Geophysical investigations at Hidden Dam—Flow simulations 17
Saxton, K.E., and Rawls, W.J., 2006, Soil water
characteristic estimates by texture and organic
matter for hydrologic solutions: Soil Science
Society of America Journal, v. 70, no. 5,
p. 1569–1578.
U.S. Army Corps of Engineers, 1977,
Foundation report: Hidden Dam project,
Hensley Lake, Fresno River, California,
Madera County: USACE, Sacramento
District.
van Genuchten, M.T., 1980, A Closed-form
Equation for Predicting the Hydraulic
Conductivity of Unsaturated Soils: Soil
Science Society of America Journal, v. 44.
28. Geophysical investigations at Hidden Dam—Flow simulations18
Appendix
Governing Variably Saturated Flow Equations
The formulation of the steady-state Richards
equation solved by COMSOL Multiphysics is
( )
∇⋅ − ∇ + ∇ =
s r
s
K k
p g z Q
g
(1)
where Ks is the saturated hydraulic conductivity
(ft/s); is the water density, which is set to a
constant 62.42 lb/ft3
; g is the acceleration due to
gravity, equal to 32.2 ft/s2
; p is the state variable
that describes water pressure (lbf/ft2
) throughout
the model; z is elevation (ft), and Qs represents
imposed fluid sources or sinks (1/s). The van
Genuchten equations (van Genuchten, 1980) are
used to describe the relative permeability, kr,
effective saturation, Se, and liquid volume, θ, as
a function of pressure head, which is defined as
pH p g= (ft).
( )( )
2
1/
1 1 0
1 0
m
m
p
r
p
Se Se H
k
H
− − <
=
≥
(2)
( )
1
0
1
1 0
pmn
p
p
H
aHSe
H
< +=
≥
(3)
( ) 0
0
r s r p
s p
Se H
H
+ − <
=
≥
(4)
1
1m
n
= − (5)
Liquid volume ranges from user-specified small
residual value, r, to the total porosity, s.
These bounds, as well as the constants a and n
depend on material properties. The constant a
(1/ft) is related to the air entry pressure head
and desorption behavior of the soil, and n is
related to the pore-size distribution of the soil.
A detailed description of how these values were
determined for the Hidden Dam model is
provided below.
Determination of Variably Saturated Model
Input Parameters
The model input parameters were obtained
from the seepage studies conducted by
Cedergren (1980a, b) and the Soil Plant Air
Water (SPAW) soils database developed by
Saxton and Rawls (2006) and available through
the USDA-NRCS
(http://www.wsi.nrcs.usda.gov/products/W2Q/w
ater_mgt/Water_Budgets/SPAW_Model.html,
last accessed January 2010). Estimates of the
saturated hydraulic conductivity (table 1) and
gradation curves (figure 47) corresponding to
each sub-domain of the dam were provided by
Cedergren (1980a) and the foundation report
(U.S. Army Corps of Engineers, 1977). Grain
size distributions were summarized in terms of
percent gravel, sand, silt and clay, by employing
a standardized grain scale.
Soil-water retention curves (figure 48) and
saturated and residual moisture contents (table
1) for each sub-domain were estimated using
the graphical user interface of Saxton and Rawls
(2006) and the available gradation data.
Percentages were entered into the SPAW
database to obtain estimates of textural
classification (table 1) and statistically based
estimates of soil-water retention curves for each
sub-domain. The retention curves relate matric
suction (Hp < 0) to volumetric moisture content
(volume fraction), and are a key component of
the unsaturated flow models. Soil-water
retention curves were created for matric
suctions ranging between 1,500 kPa (31,328
lbf/ft2
), corresponding to absorbed soil moisture
at the residual moisture condition, and
atmospheric pressure, corresponding to soil
moisture at the saturated condition. The curves
29. Geophysical investigations at Hidden Dam—Flow simulations 19
were produced under the assumption that the
effects of organic matter and osmotic pressures
were negligible. Soil compaction in the SPAW
model was specified as “normal,” implying that
no unnatural changes in soil bulk density had
occurred.
Table 2. Summary of gradation and soil-water retention data for Hidden Dam model units.
Impervious Core Random Fill Select Fill Drainage Fill
Saturated hydraulic
conductivity (ft/day)
0.02 1.0 2.0 8000.0
Gravel
(weight fraction)
0.10 0.25 0.30 1.00
Sand
(weight fraction)
0.45 0.10 0.50 0.00
Silt
(weight fraction)
0.10 0.63 0.18 0.00
Clay
(weight fraction)
0.35 0.02 0.02 0.00
Textural classification Sandy clay Silty loam Sandy loam Sandy gravel
Residual moisture
(volume fraction)
0.21 0.02 0.01 0.02
Saturated moisture
(volume fraction)
0.42 0.37 0.38 0.43
a (1/ft) 0.2013 0.2399 0.2453 0.7165
n 1.9923 3.9218 3.3088 3.5952
The soil-water retention curves are
incorporated into the flow model by
determining the parameters a and n in equations
(3) and (4) that fit each retention curve
produced by the SPAW model. These
parameters define the relative permeability as a
function of saturation in equation (2), which is
incorporated in the variably saturated flow
equation (1). Nominal values a = 0.2 / ft and n
= 2.0 are used for the grout curtain and bedrock
as the necessary input parameters were not
available for these units.
Electrokinetic Coupling to Determine the Self-
Potential Response
Electrokinetic coupling is the mechanism by
which fluid flow in porous media generates
measurable electrical potentials in the earth,
called self-potentials (Ishido and Mizutani,
1981; Morgan and others, 1989; Revil and
others, 1999). The basic concept, summarized
by Minsley and others (2010), involves a small
amount of excess positive charge that is
transported along with fluid flow in porous
materials, generating a “streaming” electric
current density. Because the total electric
current density in the earth must be conserved,
this streaming current density generates a
balancing conduction current density that flows
throughout the earth. As this conduction
current traverses the subsurface electrical
resistivity structure, it results in measurable
electrical potential differences between various
locations, which are called self-potentials.
Mathematically, this phenomenon is written
( ) ( ) 0s c Vj j Q u V∇⋅ + = ∇⋅ − ∇ = (6)
where js and jc represent the streaming and
conduction currents (A/ft2
), respectively. The
streaming current can be defined as the excess
charge density QV in coulombs per cubic foot
(C/ft3
) times the fluid velocity u (ft/s). The
conduction current is defined as the negative of
the electrical conductivity (S/m) times the
electrical potential gradient (V/ft). The
difference in electrical potential, V, between two
locations is the self-potential value (V). By
30. Geophysical investigations at Hidden Dam—Flow simulations20
coupling the electrical problem to the variably
saturated flow problem, the self-potential
response can be calculated for any flow
scenario.
Equation (6) can be solved in COMSOL by
coupling directly to the flow velocity, u, that is
calculated in the solution of Richards equation
discussed previously. The subsurface electrical
conductivity structure () is calculated
dynamically as a function of the liquid volume
content, , in equation (4) using Archie’s law
(Archie, 1942; Lesmes and Friedman, 2005),
m
w = (7)
where w is the electrical conductivity of the
pore water, and is fixed at a value of 0.05 S/m
(20 ohm-m) for this study. The cementation
exponent, m, is fixed at 1.7. An example of the
electrical resistivity (inverse of conductivity)
structure for one flow model is shown in figure
12. The excess charge density, QV, is also
calculated dynamically as a function of the
saturation-dependent hydraulic permeability, k,
using the relationship provided by Jardani and
others (2008):
( ) ( )log 9.2349 0.8219logVQ k= − − (8)
31. Geophysical investigations at Hidden Dam—Flow simulations 21
Figures
Figure 5. Flow model results for the profile A baseline model and reservoir elevation of 485 ft (flow scenario 1). Background colors represent the
effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
32. Geophysical investigations at Hidden Dam—Flow simulations22
Figure 6. Flow model results for the profile A baseline model and reservoir elevation of 510 ft (flow scenario 1). Background colors represent the
effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
33. Geophysical investigations at Hidden Dam—Flow simulations 23
Figure 7. Flow model results for the profile A baseline model and reservoir elevation of 540 ft (flow scenario 1). Background colors represent the
effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
34. Geophysical investigations at Hidden Dam—Flow simulations24
Figure 8. Seepage (foot per second) through the downstream embankment and ground surface as a function of
distance for the three different reservoir elevations illustrated in figure 5–7 (flow scenario 1).
35. Geophysical investigations at Hidden Dam—Flow simulations 25
Figure 9. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground surface
(red) per foot along the length of the dam as a function of reservoir elevation (flow scenario 1).
36. Geophysical investigations at Hidden Dam—Flow simulations26
Figure 10. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream toe for
flow scenario 1. The predicted water level relative to ground surface (positive upwards) is shown for different
reservoir elevations and any well depth between 0 and 50 feet.
37. Geophysical investigations at Hidden Dam—Flow simulations 27
Figure 11. Self-potential (millivolts) values predicted along the downstream embankment and ground surface for the
three different reservoir elevations illustrated in figure 5–7 for flow scenario 1.
38. Geophysical investigations at Hidden Dam—Flow simulations28
Figure 12. Electrical resistivity (ohm-meters) predicted for flow scenario 1 at a reservoir elevation of 510 feet.
39. Geophysical investigations at Hidden Dam—Flow simulations 29
Figure 13. Flow model results for the profile B baseline model and reservoir elevation of 485 ft (flow scenario 2). Background colors represent the
effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
40. Geophysical investigations at Hidden Dam—Flow simulations30
Figure 14. Flow model results for the profile B baseline model and reservoir elevation of 510 ft (flow scenario 2). Background colors represent the
effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
41. Geophysical investigations at Hidden Dam—Flow simulations 31
Figure 15. Flow model results for the profile B baseline model and reservoir elevation of 540 ft (flow scenario 2). Background colors represent the
effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
42. Geophysical investigations at Hidden Dam—Flow simulations32
Figure 16. Seepage (foot per second) through the downstream embankment and ground surface as a function of
distance for the three different reservoir elevations illustrated in figure 13–15 (flow scenario 2).
43. Geophysical investigations at Hidden Dam—Flow simulations 33
Figure 17. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground surface
(red) per foot along the length of the dam as a function of reservoir elevation for flow scenario 2.
44. Geophysical investigations at Hidden Dam—Flow simulations34
Figure 18. Predicted water levels in observation wells 15 feet (left) and 300 feet (right) from the downstream toe for
flow scenario 2. The predicted water level relative to ground surface (positive upwards) is shown for different
reservoir elevations and any well depth between 0 and 50 feet.
45. Geophysical investigations at Hidden Dam—Flow simulations 35
Figure 19. Self-potential (millivolts) values predicted along the downstream embankment and ground surface for the
three different reservoir elevations illustrated in figure 13–15 for flow scenario 2.
46. Geophysical investigations at Hidden Dam—Flow simulations36
Figure 20. Flow model results for the profile A model with no horizontal-drainage fill and reservoir elevation of 485 ft (flow scenario 3). Background
colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
47. Geophysical investigations at Hidden Dam—Flow simulations 37
Figure 21. Flow model results for the profile A model with no horizontal-drainage fill and reservoir elevation of 510 ft (flow scenario 3). Background
colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
48. Geophysical investigations at Hidden Dam—Flow simulations38
Figure 22. Flow model results for the profile A model with no horizontal-drainage fill and reservoir elevation of 540 ft (flow scenario 3). Background
colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative magnitude.
49. Geophysical investigations at Hidden Dam—Flow simulations 39
Figure 23. Seepage (foot per second) through the downstream embankment and ground surface as a function of
distance for the three different reservoir elevations illustrated in figure 20–22 (flow scenario 3).
50. Geophysical investigations at Hidden Dam—Flow simulations40
Figure 24. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground surface
(red) per foot along the length of the dam as a function of reservoir elevation for flow scenario 3.
51. Geophysical investigations at Hidden Dam—Flow simulations 41
Figure 25. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream toe for
flow scenario 3. The predicted water level relative to ground surface (positive upwards) is shown for different
reservoir elevations and any well depth between 0 and 50 feet.
52. Geophysical investigations at Hidden Dam—Flow simulations42
Figure 26. Self-potential (millivolts) values predicted along the downstream embankment and ground surface for the
three different reservoir elevations illustrated in figure 20–22 for flow scenario 3.
53. Geophysical investigations at Hidden Dam—Flow simulations 43
Figure 27. Saturated hydraulic-conductivity values for scenario 4 are identical to scenario 1 (figure 3), with the addition of a higher conductivity
near-surface layer in the downstream portion of the model.
54. Geophysical investigations at Hidden Dam—Flow simulations44
Figure 28. Flow model results for the profile A baseline model with an additional near-surface sediment layer and reservoir elevation of 485 ft
(flow scenario 4). Background colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow
directions and relative magnitude.
55. Geophysical investigations at Hidden Dam—Flow simulations 45
Figure 29. Flow model results for the profile A baseline model with an additional near-surface sediment layer and reservoir elevation of 510 ft
(flow scenario 4). Background colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow
directions and relative magnitude.
56. Geophysical investigations at Hidden Dam—Flow simulations46
Figure 30. Flow model results for the profile A baseline model with an additional near-surface sediment layer and reservoir elevation of 540 ft (flow
scenario 4). Background colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions
and relative magnitude.
57. Geophysical investigations at Hidden Dam—Flow simulations 47
Figure 31. Seepage (feet per second) through the downstream embankment and ground surface as a function of
distance for the three different reservoir elevations illustrated in figure 28–30 (flow scenario 4).
58. Geophysical investigations at Hidden Dam—Flow simulations48
Figure 32. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground surface (red)
per foot along the length of the dam as a function of reservoir elevation for flow scenario 4.
59. Geophysical investigations at Hidden Dam—Flow simulations 49
Figure 33. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream toe for
flow scenario 4. The predicted water level relative to ground surface (positive upwards) is shown for different
reservoir elevations and any well depth between 0 and 50 feet.
60. Geophysical investigations at Hidden Dam—Flow simulations50
Figure 34. Self-potential (millivolts) values predicted along the downstream embankment and ground surface for the
three different reservoir elevations illustrated in figure 28–30 for flow scenario 4.
61. Geophysical investigations at Hidden Dam—Flow simulations 51
Figure 35. Electrical resistivity (ohm-meters) predicted for flow scenario 4 at a reservoir elevation of 510 feet.
62. Geophysical investigations at Hidden Dam—Flow simulations52
Figure 36. Saturated hydraulic-conductivity values for scenario 5 are identical to scenario 1 (figure 3), with the addition of a higher conductivity channel
that extends to several hundred feet depth and connects the upstream and downstream portions of the model.
63. Geophysical investigations at Hidden Dam—Flow simulations 53
Figure 37. Flow model results for the profile A baseline model with an additional deep sediment channel and reservoir elevation of 485 ft
(flow scenario 5). Background colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show
flow directions and relative magnitude.
64. Geophysical investigations at Hidden Dam—Flow simulations54
Figure 38. Flow model results for the profile A baseline model with an additional deep sediment channel and reservoir elevation of 510 ft (flow scenario
5). Background colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions and relative
magnitude.
65. Geophysical investigations at Hidden Dam—Flow simulations 55
Figure 39. Flow model results for the profile A baseline model with an additional deep sediment channel layer and reservoir elevation of 540 ft (flow
scenario 5). Background colors represent the effective saturation, contours indicate hydraulic head (feet), and white arrows show flow directions
and relative magnitude.
66. Geophysical investigations at Hidden Dam—Flow simulations56
Figure 40. Seepage (feet per second) through the downstream embankment and ground surface as a function of
distance for the three different reservoir elevations illustrated in figure 37–39 (flow scenario 5).
67. Geophysical investigations at Hidden Dam—Flow simulations 57
Figure 41. Volumetric flow (gallons per minute) through the downstream embankment (blue) and ground surface (red)
per foot along the length of the dam as a function of reservoir elevation for flow scenario 5.
68. Geophysical investigations at Hidden Dam—Flow simulations58
Figure 42. Predicted water levels in observation wells 15 feet (left) and 90 feet (right) from the downstream toe for
flow scenario 5. The predicted water level relative to ground surface (positive upwards) is shown for different
reservoir elevations and any well depth between 0 and 50 feet.
69. Geophysical investigations at Hidden Dam—Flow simulations 59
Figure 43. Self-potential (millivolts) values predicted along the downstream embankment and ground surface for the
three different reservoir elevations illustrated in figure 37–39 for flow scenario 5.
70. Geophysical investigations at Hidden Dam—Flow simulations60
Figure 44. Historical record of reservoir elevation (top) and water levels relative to ground surface (negative values
are below ground) for observation wells OW-22 and OW-7.
71. Geophysical investigations at Hidden Dam—Flow simulations 61
Figure 45. Detailed view of reservoir elevation and observation-well data for OW-22 and OW-7 from 2001–2004.
72. Geophysical investigations at Hidden Dam—Flow simulations62
Figure 46. Crossplots of reservoir elevation and observation-well water level data for OW-22 (A) and OW-7 (B), along
with model-predicted results from the various flow scenarios in this study. The large number of zero-values and
absence of positive water levels in the OW-22 data indicate the inability to record water levels that are higher than
the ground surface. In OW-7, above-ground water levels are measured with pressure transducers.
73. Geophysical investigations at Hidden Dam—Flow simulations 63
Figure 47. Gradation curves for primary Hidden Dam model units.
74. Geophysical investigations at Hidden Dam—Flow simulations64
Figure 48. Soil-water retention curves for primary Hidden Dam model units.