294-7: Effects of Polyacrylamide (PAM) Treated Soils on Water Seepage in Unlined Water Delivery Canals Jianting (Julian) Zhu 1, Michael H. Young 2 and.

Slides:



Advertisements
Similar presentations
Engineering properties of soils and materials
Advertisements

Yhd Subsurface Hydrology
Groundwater Flow Equations
Yhd Soil and Groundwater Hydrology
Introduction to Environmental Engineering Lecture 15 Water Supply and Groundwater.
Flow through Soils (ch7)
STABILITY ANALYSIS IN PRESENCE OF WATER Pore pressures Rainfall Steady state flow and transient flow.
z = -50 cm, ψ = -100 cm, h = z + ψ = -50cm cm = -150 cm Which direction will water flow? 25 cm define z = 0 at soil surface h = z + ψ = cm.
Estimating Streamflow Channel Losses with the Green-Ampt Model Neil Hutten Ag Eng 558 April 20, 2001.
Features of POLLUSOL Flow model Flow model Homogeneous, Isotropic, Heterogeneous and Anisotropic medium Homogeneous, Isotropic, Heterogeneous and Anisotropic.
Field Hydrologic Cycle Chapter 6. Radiant energy drives it and a lot of water is moved about annually.
Water Movement in Soil and Rocks. Two Principles to Remember:
Continuum Equation and Basic Equation of Water Flow in Soils January 28, 2002.
Infiltration Introduction Green Ampt method Ponding time
1 Next adventure: The Flow of Water in the Vadose Zone The classic solutions for infiltration and evaporation of Green and Ampt, Bruce and Klute, and Gardner.
HYDRUS_1D Sensitivity Analysis Limin Yang Department of Biological Engineering Sciences Washington State University.
Lecture ERS 482/682 (Fall 2002) Infiltration ERS 482/682 Small Watershed Hydrology.
1 Steady Evaporation from a Water Table Following Gardner Soil Sci., 85: , 1958 Following Gardner Soil Sci., 85: , 1958.
Infiltration into Soils
1 Steady Evaporation from a Water Table Following Gardner Soil Sci., 85: , 1958 Following Gardner Soil Sci., 85: , 1958.
Watershed Hydrology, a Hawaiian Prospective; Groundwater Ali Fares, PhD Evaluation of Natural Resource Management, NREM 600 UHM-CTAHR-NREM.
The Effect of Soil Hydraulic Properties and Deep Seepage Losses on Drainage Flow using DRAINMOD Debjani Deb 26 th April, 2004.
A Process-Based Transfer Function Approach to Model Tile Drain Hydrographs Mazdak Arabi, Jennifer Schmidt and Rao S. Govindaraju World Water & Environmental.
Groundwater Hydraulics Daene C. McKinney
8. Permeability (Das, chapter 7)
1 GROUNDWATER HYDROLOGY AND CONTAMINANT TRANSPORT CEVE 518 P.C. de Blanc C.J. Newell 1.Porosity and Density Continued 2.Saturation and Water Content 3.Darcy.
Cross Section of Unconfined and Confined Aquifers
Lab 10 - Soil Water Movement Flow Model Experiment 1 –Red dye is added to the waste lagoon and to a well in the unconfined aquifer. –Green dye is added.
Presented by: 1. A measure of how easily a fluid (e.g., water) can pass through a porous medium (e.g., soils) 2 Loose soil - easy to flow - high permeability.
CE 394K.2 Hydrology Infiltration Reading AH Sec 5.1 to 5.5 Some of the subsequent slides were prepared by Venkatesh Merwade.
Lecture Notes Applied Hydrogeology
Unsaturated-Zone Case Study at the Idaho National Engineering and Environmental Laboratory: Can Darcian Hydraulic Properties Predict Contaminant Migration?
Darcy’s Law and Flow CIVE Darcy allows an estimate of: the velocity or flow rate moving within the aquifer the average time of travel from the head.
Surface Water Hydrology: Infiltration – Green and Ampt Method
Subsurface Water unit volume of subsurface consists of soil/rock, and pores which may be filled with water and/or air total porosity= volume voids/total.
CE 394K.2 Hydrology Infiltration Reading for Today: AH Sec 4.3 and 4.4 Reading for Thurs: AH Sec 5.1 to 5.5 Subsequent slides prepared by Venkatesh Merwade.
ATM 301 Lecture #7 (sections ) Soil Water Movements – Darcy’s Law and Richards Equation.
PRINCIPLES OF GROUNDWATER FLOW. I.Introduction “Groundwater processes energy in several forms”
CE 3354 Engineering Hydrology Lecture 21: Groundwater Hydrology Concepts – Part 1 1.
Groundwater Supply Dr. Martin T. Auer Michigan Tech Department of Civil & Environmental Engineering.
Groundwater Supply Dr. Martin T. Auer Michigan Tech Department of Civil & Environmental Engineering.
Groundwater Systems D Nagesh Kumar, IISc Water Resources Planning and Management: M8L3 Water Resources System Modeling.
Counter-current flows in liquid-liquid boundary layers II. Mass transfer kinetics E. Horvath 1, E. Nagy 1, Chr. Boyadjiev 2, J. Gyenis 1 1 University.
Soil Stress and Pore Water Pressure
Soil Physics David Zumr room: b608 Lecture (and seminar) notes will be available: -
Groundwater movement Objective To be able to calculate the hydraulic conductivity of a sample given measurements from a permeameter To be able to evaluate.
Soil Water Balance Reading: Applied Hydrology Sections 4.3 and 4.4
1. CHAPTER 3 SUB-SURFACE DRAINAGE THEORY ERNST EQUATION 2.
Soil wetting patterns under porous clay pipe subsurface irrigation A. A. Siyal 1 and T. H. Skaggs 2 1 Sindh Agriculture University, Tandojam, Sindh, Pakistan.
Redistribution. the continued movement of soil water after infiltration ends rate decreases over time influences plant available water influences solute.
Groundwater movement Objective
Groundwater Review Aquifers and Groundwater Porosity
Water in Soil Learning objectives
Darcy’s Law and Richards Equation
AIM AIM point-scale plot-scale hillslope-scale
Infiltration and unsaturated flow (Mays p )
Basic Hydrology & Hydraulics: DES 601
Infiltration and unsaturated flow
Water in Soil Learning objectives
Infiltration and unsaturated flow
Methods Used to Determine Hydraulic Conductivity
Next adventure: The Flow of Water in the Vadose Zone
Green and Ampt Infiltration
Applied Hydrology Infiltration
Chapter-4 Infiltration
Groundwater Learning objectives
Applied Hydrology Infiltration
INFILTRATION The downward flow of water from the land surface into the soil medium is called infiltration. The rate of this movement is called the infiltration.
Some Quiz Questions Unit: Subsurface Flow.
Department of Civil & Environmental Engineering
Presentation transcript:

294-7: Effects of Polyacrylamide (PAM) Treated Soils on Water Seepage in Unlined Water Delivery Canals Jianting (Julian) Zhu 1, Michael H. Young 2 and Ernesto Moran 3 Desert Research Institute, Division of Hydrologic Sciences, Las Vegas, NV ( Introduction Objectives Acknowledgment: The financial support by U.S. Bureau of Reclamation, under cooperative agreement 05-FC , is greatly appreciated. Contents do not reflect the views of this agency. Viscosity / Surface sealing / Plugging of pores Experiments were designed to explain Ks reduction by quantifying role of viscosity changes, conductivity of PAM layer, and plugging of large soil pores. Analysis of Steady State Infiltration When PAM is added to full-scale canal, it hydrates, reacts with suspended sediment and settles to the bottom of canal ‘prism.’ Flocculate reduces infiltration and thus seepage loss. Full-scale canals can exhibit seepage in bottom and sidewalls – this analysis considers only vertical infiltration. 1D flow process considers two-layer soils with distinct and contrasting hydraulic properties (see figure on the right). For steady state conditions, Darcy’s law through each layer gives The saturated hydraulic conductivities before PAM treatment and effective hydraulic conductivities after PAM treatment were determined from constant head experiments. Experimental design included 3 suspended concentrations of kaolinite, and soils of 3 textures (Moran, 2006), including: C33 coarse sand #70 mesh sand Loam-textured soil Graphs on left are averaged Ks values for given experimental conditions. Ks decreases with increases in both PAM application rates (expressed in lbs/acre) and suspended sediment concentrations (SSC). Largest reduction in Ks observed in C33 and #70 mesh sand. Small reduction observed in loam. Results Using Laboratory Data Laboratory Experiments to Determine Hydraulic Conductivities of PAM Treated Soils where z 1 is the height of the layer 1:layer 2 interface above the water table, z 1 =L-d, where d is the thickness of PAM-treated layer. When d<<L, z 1 ~ L, and the equation governing infiltration rate into a two-layer soil becomes where  =  2 /  1,  =K s2 /K s1. i.e., the ratios of hydraulic parameters after and before PAM treatments of soils. The infiltration rate, p, can be obtained solving iteratively for p/K s1 For special cases where  = 1,  = 1 and d = 0, the result reduces to one-layer scenario (i.e., without PAM [WOP]). Substituting (6) into (5) and manipulating, we obtain For another special case where  = 1, but K s2 < K s1, Equation (8) reduces to The ratio of seepage rates for the two-layer system can be defined as where z is the elevation,  is the suction head (a positive quantity for unsaturated soil),  =  i at location z i, q is the Darcian velocity (flux rate) and K(  ) the unsaturated hydraulic conductivity function. Using the Gardner model for hydraulic conductivity function: where Ks is the saturated hydraulic conductivity, and  is a parameter. For Gardner hydraulic conductivity function, the general solution can be shown as (see the above figure for symbol meaning) For the bottom layer with no PAM, the steady state flow equation can be written as: where q is the vertical flux rate of water which is the same for both layers (for infiltration, q is positive). For the top (PAM treated) layer, the steady state flow equation can be written as where L-z 1 is equal to the thickness of PAM-treated soil layer, d = L-z 1. In the case of ponding,  2 equals the negative ponding depth. From Equation (4), we can obtain Note that infiltration rate (q) is negative, i.e., p = -q, and that negative suction at canal bottom is replaced with ponding depth h, i.e.,  2 = -h. (1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) The ratio, r, in Equation (11) can be considered as a measure of efficacy of PAM applications for reducing water seepage loss. Smaller r values correspond to higher efficiency of PAM application. We assume typical values of  for the 3 soil types used in the experiments; Carsel and Parrish (1988) suggest  = (1/cm) for C33 sand, and  = (1/cm) for loam. We assume a value of 0.1 (1/cm) for the #70 mesh sand, which is between C33 sand and loam groups but is closer to the sand group. Graphs below illustrate predicted seepage ratio for several combinations of PAM and SSC concentrations. For each graph, water table depth L=400 (cm) and canal water depth h = 50 (cm).  Results show that seepage loss rates are quite sensitive to . Some method should be developed to characterize  for the thin PAM layer.  Groundwater table depth does not affect seepage loss ratio between PAM-treated and untreated soils, but depth to water table and water depth in canal would influence the actual water seepage loss. The groundwater table depth is only important for determining seepage loss ratio when water table depth converges on canal bottom.  Canal water depth influences seepage loss ratio of PAM-treated and untreated soils, if  values of the two layers differ. Concluding Remarks Ks ratio after PAM treatment: (a) C33 sand, (b) #70 mesh sand, (c) loam soil Seepage ratio vs. canal water depth for C33 sand for the scenario of PAM = 40 lbs/acre and SSC = 300ppm Investigate the effects of applying a thin PAM layer at the bottom of water delivery canals on water seepage into subsurface material. Determine the parameter sensitivity for reducing water seepage loss through canal bottoms. Persistent drought in the west and mid-west US has created a significant need to improve efficiency of water delivery canal systems. Polyacrylamide (PAM) has been used extensively in furrow irrigation applications, but recently is undergoing scientific scrutiny as a potential water conservation tool for unlined canals. Laboratory, field and numerical experiments are being conducted to better understand the benefits (efficacy, longevity) and risks (environmental and human impacts) of PAM usage in canals. The research described herein uses laboratory results and a new analytical approach for estimating seepage loss reduction after PAM is applied to soil. Sensitivity Analysis PAM layer thickness d = 0.1 (cm) PAM layer thickness d = 0.05 (cm) (i = 1, 2)