Measurement of Groundwater Table & Pore Water Pressure in Deep
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Dewatering Behavior of a Wood-Cellulose Nanofibril
www.nature.com/scientificreports OPEN Dewatering Behavior of a Wood- Cellulose Nanofbril Particulate System Received: 6 May 2019 Ezatollah (Nima) Amini1, Mehdi Tajvidi1, Douglas W. Bousfeld2, Douglas J. Gardner1 & Accepted: 26 September 2019 Stephen M. Shaler1 Published: xx xx xxxx The novel use of aqueous suspensions of cellulose nanofbrils (CNF) as an adhesive/binder in lignocellulosic-based composite manufacture requires the removal of a considerable amount of water from the furnish during processing, necessitating thorough understanding of the dewatering behavior referred to as “contact dewatering”. The dewatering behavior of a wood-CNF particulate system (wet furnish) was studied through pressure fltration tests, centrifugation, and characterization of hard-to- remove (HR) water, i.e. moisture content in the wet furnish at the transition between constant rate part and the falling rate part of evaporative change in mass from an isothermal thermogravimetric analysis (TGA). The efect of wood particle size thereby particle specifc surface area on the dewatering performance of wet furnish was investigated. Permeability coefcients of wet furnish during pressure fltration experiments were also determined based on Darcy’s law for volumetric fow through a porous medium. Results revealed that specifc particle surface area has a signifcant efect on the dewatering of wet furnish where dewatering rate signifcantly increased at higher specifc particle surface area levels. While the permeability of the systems decreased over time in almost all cases, the most signifcant portion of dewatering occurred at very early stages of dewatering (less than 200seconds) leading to a considerable increase in instantaneous dewatering when CNF particles come in contact with wood particles. -
Instrumentation for Monitoring Consolidation of Soft Soil 1
ONE STOP MONITORING SOLUTIONS | HYDROLOGY | GEOTECHNICAL | STRUCTURAL | GEODETIC Over 50 years of excellence through ingenuity APPLICATION NOTE INSTRUMENTATION FOR MONITORING CONSOLIDATION OF SOFT SOIL 1. Introduction Considerable settlement may occur when constructing projects such as highway embankments, bridge approaches, dikes, dams, large storage areas, tanks, airport runways or buildings on soft compressible soil, due to the consolidation of soil under the superimposed load. To avoid serious and potentially expensive problems due to such settlement, it is desirable to cause the consolidation to occur at the outset of the project, and in the shortest possible time during construction period. Construction of a facility on top of a soft soil foundation will normally be delayed until there is assurance that it will not be damaged by settlement that occurs during subsequent consolidation. If the predicted delay is not acceptable, the time required for consolidation can be reduced by surcharging and/or by installation of vertical drains. 1.1 Consolidation In case a saturated soil experiences a steady pressure due to the weight of overlying soil or pre-loading from an embankment, its volume will decrease with time. Soil particles as well as the water in the voids being almost incompressible at the pressures encountered, any change in volume can only occur if the water between the voids is forced out. This reduces the size of the voids enabling the solid particles to become wedged closer together. The process is illustrated in figures 1.1 and 1.2 below: Im posed Stress h W a t e r Figure 1.1 Im posed Stress h W a t e r Figure 1.2 Surcharging (or pre-loading) involves placement of fill materials to a level higher than that required for the foundation or embankment, so that consolidation proceeds more quickly. -
Bedrock Dewatering for Construction of Marmet and Soo Lock Projects
Bedrock Dewatering for Construction of Marmet and Soo Lock Projects Michael Nield Engineering Geologist Dam Safety Production Center, Huntington, WV August 2012 US Army Corps of Engineers BUILDING STRONG® BEDROCK DEWATERING FOR CONSTRUCTION OUTLINE 1. Marmet Lock Replacement Project (construction) - Project Description - Site Geology - Permeability and Groundwater Inflow - Dewatering Provisions 2. Soo Lock Replacement Project (design) - Project Description - Site Geology - Permeability and Predicted Groundwater Inflow - Impact to Design BUILDING STRONG® MARMET LOCK - PROJECT DESCRIPTION . Located on Kanawha River, OHIIO RIVER near Charleston, West GREAT LAKES DIVISION Virginia. Permits economic river transportation of coal, MARMET aggregate and chemicals. LOCKS & DAM . Construction of the new replacement lock was completed in 2009 BUILDING STRONG® “Busiest Lock in USA” Prior to New Lock Twin 56’ X 360’ Chambers Completed in 1934 Aerial View – Original Locks BUILDING STRONG® New 110’ X 800’ Lock Chamber Original Locks New Guard Wall New Guide Walls Aerial View – New Replacement Lock BUILDING STRONG® MARMET LOCK - SITE GEOLOGY . 157 TOTAL BORINGS . 10,200’ TOTAL DRILLING . 3,700’ ROCK CORE . 294 PRESSURE TESTS Subsurface Exploration – Boring Location Plan BUILDING STRONG® General Geology . Soil thickness 40 to 60 feet . Relatively flat top of rock surface at elev. 552 ± 3’ . Sedimentary rock of the Pennsylvanian-aged Kanawha Formation Sandstone member (23 to 43 feet thick) Shale member (19 to 33 feet thick) . Low angled bedding with 0o-10o dip to the Northwest . Slightly fractured with occasional high angled joints (70o-90o) BUILDING STRONG® Bedrock Units - Sandstone Member . Light gray . Moderately hard to hard . Medium to fine grained . Average unconfined compressive strength 8,442 psi . -
Piezometer Installation 2017
Revision 2016-1-1 Copyright ©, 2016 by HMA Group. The information contained in this document is subject to change without prior notice. Contents 1. Introduction:................................................................................................................................................................ 3 2. Specifications: ............................................................................................................................................................. 4 3. Vibrating Wire Piezometer Operation .............................................................................................................. 5 4. Calibration and Interpreting Readings ............................................................................................................. 6 4.1 Electrical Connection ............................................................................................................................................. 6 4.2 Calibration Sheet Interpretation ...................................................................................................................... 7 4.3 Data Reduction ......................................................................................................................................................... 8 4.4 Pressure Head/Water Level Calculation ....................................................................................................... 9 4.5 Barometric Compensation ................................................................................................................................. -
Method 9100: Saturated Hydraulic Conductivity, Saturated Leachate
METHOD 9100 SATURATED HYDRAULIC CONDUCTIVITY, SATURATED LEACHATE CONDUCTIVITY, AND INTRINSIC PERMEABILITY 1.0 INTRODUCTION 1.1 Scope and Application: This section presents methods available to hydrogeologists and and geotechnical engineers for determining the saturated hydraulic conductivity of earth materials and conductivity of soil liners to leachate, as outlined by the Part 264 permitting rules for hazardous-waste disposal facilities. In addition, a general technique to determine intrinsic permeability is provided. A cross reference between the applicable part of the RCRA Guidance Documents and associated Part 264 Standards and these test methods is provided by Table A. 1.1.1 Part 264 Subpart F establishes standards for ground water quality monitoring and environmental performance. To demonstrate compliance with these standards, a permit applicant must have knowledge of certain aspects of the hydrogeology at the disposal facility, such as hydraulic conductivity, in order to determine the compliance point and monitoring well locations and in order to develop remedial action plans when necessary. 1.1.2 In this report, the laboratory and field methods that are considered the most appropriate to meeting the requirements of Part 264 are given in sufficient detail to provide an experienced hydrogeologist or geotechnical engineer with the methodology required to conduct the tests. Additional laboratory and field methods that may be applicable under certain conditions are included by providing references to standard texts and scientific journals. 1.1.3 Included in this report are descriptions of field methods considered appropriate for estimating saturated hydraulic conductivity by single well or borehole tests. The determination of hydraulic conductivity by pumping or injection tests is not included because the latter are considered appropriate for well field design purposes but may not be appropriate for economically evaluating hydraulic conductivity for the purposes set forth in Part 264 Subpart F. -
Dewatering Mechanisms of Compressible Filter Cakes
Dewatering mechanisms of compressible filter cakes Sarah Strubel, Harald Anlauf, Hermann Nirschl, Institute of Mechanical Process Engineering (MVM), Karlsruhe Institute of Technology (KIT) For designing filtration processes, a correlation between applied pressure and filter cake saturation is required. This correlation is provided by the capillary pressure curve, and depends on the pore size distribution of the filter cake. Many materials form compressible filter cakes: The porosity - and pore size distribution - changes with applied pressure. To determine the capillary pressure curve, a saturated filter cake is dewatered by gradually increasing the gas pressure. Below the capillary entry pressure the filter cake will consolidate. Above, desaturation of pores will occur in addition to further consolidation. In industrial filtration processes in contrary, the filter cake is subjected to constant gas pressure and therefore consolidation and desaturation occur simultaneously. With desaturation though, the tensile strength of the filter cake and therefore the resistance to consolidation increases. It is therefore interesting to investigate, if desaturation of an already consolidated cake, as in a capillary pressure experiment, will actually result in the same porosity and saturation as in a conventional filtration experiment, where both mechanisms occur at once. In this work, filter cake porosity, saturation and residual moisture are compared for two sets of filtration experiments. The first experiment is a standard filtration test, where the filter cake is formed and desaturated by gas pressure. In the second experiment a filter cake is first formed and consolidated and subsequently desaturated by applying gas pressure to the filter cake. The obtained results show a difference in porosity for the two types of experiments with in all other respects comparable filtration conditions. -
Dewatering – Deep Well Systems
Dewatering – Deep well systems GEO-SLOPE International Ltd. | www.geo-slope.com 1200, 700 - 6th Ave SW, Calgary, AB, Canada T2P 0T8 Main: +1 403 269 2002 | Fax: +1 888 463 2239 Introduction The objective of dewatering is to lower the groundwater table to prevent significant groundwater flow into an excavation, and/or to ensure slope stability. The preferred dewatering system will depend on hydrogeological conditions and construction requirements. In the case of slopes and excavations, the groundwater table can be lowered using a combination of methods, such as deep wells, wellpoints, vacuum wells, and horizontal wells. Deep well systems are often used for dewatering slopes and excavations when large drawdowns are required. This type of system generally consists of an array of pumping wells located near the excavation or slope. The combined effect of the array lowers the groundwater table over a wide area. The active pumping system must be set below the groundwater table whereas the bottom of the wells must be set deep enough to allow flow without excessive head loss. The objective of this example is to illustrate how to model deep well systems in three-dimensional environments, and to verify the water-flow formulation against a well-known benchmark. To do so, the example will discuss a specific deep well system, and provide insight into an approach for modeling pumping wells. Numerical Simulation The deep well system, taken from Mansur and Kaufman’s (1962) chapter on dewatering, consists of a large, 770 foot-long by 370 foot-wide, 40 foot-deep excavation in a 90 foot-deep unconfined sandy aquifer. -
2 Basic Concepts and Definitions
2 Basic concepts and definitions This chapter summarises some basic concepts and definitions of terms rele- vant to the hydraulic properties of water-bearing layers and the discussions which follow. 2.1 Types of water-bearing layers Water-bearing layers are classified according to their water-transmitting properties into aquifers, aquitards or aquicludes. With regard to the flow to pumped wells the following definitions are commonly used. -An aquifer is a water-bearing layer in which the vertical flow component is so small with respect to the horizontal flow component that it can be neg- lected. The groundwater flow in an aquifer is assumed to be predominantly horizontal. -An aquitard is a water-bearing layer in which the horizontal flow compo- nent is so small with respect to the vertical flow component that it can be neglected. The groundwater flow in an aquitard is assumed to be predomi- nantly vertical. - An aquiclude is a water-bearing layer in which both the horizontal and ver- tical flow components are so small that they can be neglected. The ground- water flow in an aquiclude is assumed to be zero. Common aquifers are geological formations of unconsolidated sand and gravel, sandstone, limestone, and severely fractured volcanic and crystalline rocks. Examples of common aquitards are clays, shales, loam, and silt. 2.2 Aquifer types The four types of aquifer distinguished (Figure 2.1) are: confined, unconfined, leaky and multi-layered. A confined aquifer is a completely saturated aquifer bounded above and below by aquicludes. The pressure of the water in confined aquifers is usually higher than atmospheric pressure, which is why when a well is bored into the aquifer the water rises up the well tube, to a level higher than the aquifer (Figure 2.1.A). -
Installing Monitoring Wells in Soils Version 1.0 August 2008
Installing Monitoring Wells in Soils Version 1.0 August 2008 USDA – Natural Resources Conservation Service National Soil Survey Center Lincoln, Nebraska Correct document citation: Sprecher, S.W. 2008. Installing monitoring wells in soils (Version 1.0). National Soil Survey Center, Natural Resources Conservation Service, USDA, Lincoln, NE. Cover Figure: Schematic diagram of a standard design for an installed water-table monitoring well. Use of trade or firm names is for reader information only, and does not constitute endorsement or recommended use by the U.S. Department of Agriculture of any commercial product or service. The United State Department of Agriculture (USDA) prohibits discrimination in its programs on the basis of race, color, national origin, sex, religion, age, disability, political beliefs, and marital or familial status. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA's TARGET Center at 202-720-2600 (Voice and TDD). To file a complaint, write the Secretary of Agriculture, U.S. Department of Agriculture, Washington, D.C. 20250 or call 1-800-245-6340 (voice) or (202) 720-1127 (TDD). USDA is an equal employment opportunity employer. Acknowledgements This technical note is a compilation of concepts and procedures that have been evolving within pedology and Soil Survey for at least three decades. Few of the ideas presented originated with myself. It is an honor to recognize and thank my main teachers concerning these procedures, Lawson Smith (US Army Engineer Waterways Experiment Station, Vicksburg, Mississippi, deceased) and Jim Richardson (North Dakota State University and NRCS National Soil Survey Center in Lincoln, Nebraska, retired). -
Hvorslev (1951)
TIME LAG AND SOIL PERMEABILITY IN GROUND-WATER OBSERVATIONS BULLETIN NO. 36 WATERWAYS EXPERIMENT STATION CORPS OF ENGINEERS, U. S. ARMY VICKSBURG, MISSISSIPPI TIME LAG AND SOIL PERMEABILITY IN GROUND-WATER OBSERVATIONS BULLETIN NO. 36 WATERWAYS EXPERIMENT STATION CORPS OF ENGINEERS, U. S. ARMY VICKSBURG, MISSISSIPPI APRIL 1951 ARMY - MRC VICKSBURG, MISS. 111 CONTENTS Page PREFACE . i ACKNOWLEDGEMENTS. ii NOTATION. v INTRODUCTION . 1 PART I: GROUND-WATER CONDITIONS AND OBSERVATIONS Irregularities and Variations. 3 Sources of Error in Measurements. 3 Hydrostatic time lag. 4 Stress adjustment time lag. 4 General instrument errors. 4 Seepage along conduits . 4 Interface of liquids. .. 6 Gas bubbles in open systems . 6 Gas bubbles in closed systems . 6 Gas bubbles in soil. 7 Sedimentation and clogging. 7 Erosion and development. 7 Summary comments . 8 PART II: THEORY OF TIME LAG The Basic Hydrostatic Time Lag . 9 Applications for Constant Ground-Water Pressure. 10 Applications for Linearly Changing Pressures . 13 Applications for Sinusoidal Fluctuating Pressures. 16 Corrections for Influence of the Hydrostatic Time Lag. 19 Influence of the Stress Adjustment Time Lag . 21 Initial disturbance and stress changes . 22 Transient consolidation or swelling of soil . 23 Volume changes of gas in soil . 26 Normal operating conditions. 28 iv CONTENTS (Cont’d) Page PART III: DATA FOR PRACTICAL DETERMINATION AND USE OF TIME LAG Flow through Intakes and Well Points . 30 Influence of Anisotropic Permeability . 32 Computation of Time Lag for Design Purposes . 35 Examples of Field Observations and Their Evaluation . 38 Logan International Airport, Boston. 38 Vicinity of Vicksburg, Mississippi. 39 Determination of Permeability of Soil in Situ . -
Groundwater Flow in Low-Permeability Environments
WATER RESOURCES RESEARCH, VOL. 22, NO. 8, PAGES 1163-1195, AUGUST 1986 Groundwater Flow in Low-Permeability Environments Water Resources Division, U.S. Geological Survey, Reston, Virginia Certain geologic media are known to have small permeability; subsurface environments composed of these media and lacking well developed secondary permeability have groundwat'er flow sytems with many distinctive characteristics. Moreover, groundwater flow in these environments appears to influence the evolution of certain hydrologic, geologic, and geochemical systems, may affect the accumulation of pertroleum and ores, and probably has a role in the structural evolution of parts of the crust. Such environments are also important in the context of waste disposal. This review attempts to synthesize the diverse contributions of various disciplines to the problem of flow in low-permeability environments. Problems hindering analysis are enumerated together with suggested approaches to overcoming them. A common thread running through the discussion is the significance of size- and time-scale limitations of the ability to directly observe flow behavior and make measurements of parameters. These limitations have resulted in rather distinct small- and large-scale approaches to the problem. The first part of the review considers experimental investigations of low-permeability flow, including in situ testing; these are generally conducted on temporal and spatial scales which are relatively small compared with those of interest. Results from this work have provided increasingly detailed information about many aspects of the flow but leave certain questions unanswered. Recent advances in laboratory and in situ testing techniques have permitted measurements of permeability and storage properties in progressively "tight- er" media and investigation of transient flow under these conditions. -
Rotary Vacuum-Drum Filter
Rotary vacuum-drum filter Rotary vacuum filter drum consists of a drum rotating in a tub of liquid to be filtered. The technique is well suited to slurries, and liquids with a high solid content, which could clog other forms of filter. The drum is pre-coated with a filter aid, typically of diatomaceous earth (DE) or Perlite. After pre-coat has been applied, the liquid to be filtered is sent to the tub below the drum. The drum rotates through the liquid and the vacuum sucks liquid and solids onto the drum pre-coat surface, the liquid portion is "sucked" by the vacuum through the filter media to the internal portion of the drum, and the filtrate pumped away. The solids adhere to the outside of the drum, which then passes Oliver-type rotary vacuum-drum filter. a knife, cutting off the solids and a small portion of the filter media to reveal a fresh media surface that will enter the liquid as the drum rotates. The knife advances automatically as the surface is removed. Contents Basic fundamentals Rotary vacuum drum filter Range of application Advantages and limitations Advantages Disadvantages Designs available Belt discharge Scraper discharge Roll discharge String discharge Pre coat discharge Main process characteristics and assessment Heuristics design process Basic operation parameters heuristics Discharge mechanism adjustment heuristics Endless belt Scraper Roll String Pre coat Pre coat filter operation heuristics Advanced blade Necessary post treatment for waste stream for thicker Chlorination UV radiation Ozonation Necessary post treatment for waste stream for clarifier Land reclamation Incineration New Development See also References Further reading External links Basic fundamentals Rotary vacuum drum filter Rotary vacuum drum filter (RVDF), patented in 1872,[1] is one of the oldest filters used in the industrial liquid-solids separation.