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Groundwater flow

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Named for Henri Darcy (1803-1858), chief engineer in Dijon, France ... 'Hydraulic conductivity is equal to intrinsic permeability of the medium times ... – PowerPoint PPT presentation

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Title: Groundwater flow


1
Groundwater flow
  • General principles
  • Important factors affecting flow
  • Application for groundwater protection

2
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3
Gaining and losing streams
  • Most observable flow in perennial streams
    (streams with constant flow) is baseflow
  • Baseflow represents the discharge of groundwater
    along the stream channel
  • Stream reaches may be gaining or losing
  • Gaining streams receive groundwater flow
  • Losing streams recharge groundwater

4
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5
Public and private water supply
  • In Nevada, 99 of the public water supplies rely
    on groundwater
  • 100 of private water supplies (for drinking
    water) rely on groundwater
  • Groundwater also meets demand for irrigation and
    industrial uses

6
Terminology
  • Aquifer a water-bearing subsurface formation
    that can be used for water supply (10 gpm)
  • Unconfined aquifer water-bearing subsurface
    formation that has the upper boundary at
    atmospheric pressure.
  • Confined aquifer formation that is bounded
    above and below by formations that have
    significantly lower hydraulic conductivity

7
Terminology
  • Hydraulic conductivity a proportionality
    constant that represents physical characteristics
    of the geologic formation that are important
    determinants of water movement

8
Aquifer materials
  • Unconsolidated materials (sands, gravels, clays)
  • Rock formations (sedimentary rocks)
  • Igneous and metamorphic rocks
  • Unconsolidated materials are the most exploited
    for water supply because of high yield,
    inexpensive drilling costs and adequate supply

9
Confined and unconfined aquifers
  • Confined aquifers also called artesian aquifers
    (Artois region of France)
  • Recharge area is at a higher elevation than point
    at which water is extracted
  • Elevation pressure head leads to water level in
    well being higher than in aquifer

10
Unconfined aquifers
  • Direct hydraulic connection with overlying
    recharge areas on soil surface
  • Water table aquifers

11
Darcys Law
  • Background
  • Named for Henri Darcy (1803-1858), chief engineer
    in Dijon, France
  • Rapport à Le Maire et au Conseil Municipal, de
    Dijon, sur les Moyens de Fournir L'Eau Nécessaire
    à cette Ville, 1834
  • Law was developed from studies of
    water-filtration to prevent cholera outbreaks

Saturated sand-filled column
12
General principles Darcys law of saturated flow
in porous media
  • The direction and amount of water flow in a
    porous medium is opposite the direction of the
    energy gradient and is determined by
    characteristics of the formation and the change
    in potential energy with distance

Change in energy that is creating flow with
distance
Proportionality constant that represents medium
13
Schematic of System
  • Head (h) consists of pressure and elevation head
  • Dh/Dl represents change in head due to energy
    losses over horizontal distance

14
Energy losses
  • Due to friction effects in interaction with
    grains of porous medium
  • Result leads to decreases in apparent head along
    the horizontal flow path

15
Pressure head
  • h zp/?
  • Total pressure head (l) equals potential energy
    due to differences in elevation pressure
    applied (F/l2) /specific weight of water (g?,
    gravity?density (F/l3)
  • z is always expressed with respect to a datum, or
    point of reference
  • Water flows downhill and from areas of high
    pressure to low pressure

16
Hydraulic conductivity (K)
  • K (l/t)Ki(?/?)
  • Ki (l2) intrinsic permeability, representative
    of the properties of the medium alone
  • ? dynamic viscosity of the fluid (resistance of
    fluid to shearing ?ethanol 10-3 ltlt ?SAE30 oil
    10-1 Ns/m2)
  • Hydraulic conductivity is equal to intrinsic
    permeability of the medium times properties of
    the fluid

17
Focus on medium
  • Assume fluid properties are constant
  • The primary influence on flow is related to the
    medium and resistance and energy loss associated
    with fluid flow through the medium
  • Ki represents the intrinsic permeability Cd2
  • D mean pore diameter
  • KC(D10)2 for grain sizes 0.1-3 mm, with D10
    mean grain diameter in cm

18
Shape factor (C) Coefficient values
120ltClt150
40ltClt80
80ltClt120
19
Hydraulic Conductivity and Texture
20
Other important characteristics
  • Specific yield (Sy) ratio of the total volume of
    water that drains from a saturated formation to
    the total volume of the formation
  • Related to capillary effect because water is
    retained in pores by surface tension against
    gravitational drainage
  • 0ltSylt1

21
Specific yield
  • Related to texture
  • Importance relates to the amount of water that
    can be feasibly extracted from a formation

22
Transmissivity
  • Transmissivity indicator of the ability of
    formation to provide water
  • TKb
  • Transmissivity (l2/t) is the product of hydraulic
    conductivity and thickness of the aquifer (b)

23
Drawdown curves
  • Pumping creates a cone of depression, which
    represents the energy gradient created by
    lowering the water table
  • The extent and shape of the cone may be measured
    with piezometers (observation wells)

24
Assumptions inherent in Darcys Law
  • Homogeneous (material is the same throughout the
    control volume)
  • Isotropic (material has the same permeability in
    all directions within the control volume)
  • Flow in pores is laminar (not turbulent)

25
When Darcys Law is inapplicable (or hard to
apply)
  • Flow with high velocitiesMacropore flow
    (fractures in rocks, large voids in soils or
    sediments)
  • Media with very low permeabilityLow hydraulic
    gradient, low permeability environments (clays,
    solid rock)
  • Heterogeneous, anisotropic and unsteady state
    conditions

26
Application for groundwater protection
  • Travel time estimation
  • Darcys law represents flux through an area (Q/A
    discharge/area)
  • Units are velocity units
  • However, AltAvoid, in which Avoid represents the
    actual amount of space that water has to travel
    through
  • Actual velocity q/?, with 0lt??1

27
Example
  • Two wells 780 meters apart in an unconfined
    aquifer have water levels of 1372.4 m and 1376.3
    m.
  • The formation is composed of sand mixed with silt
  • What is the average velocity of water in the
    formation?

28
Solution
  • q-K(Dh/Dl)
  • K1 m/day (Fig 8-10)
  • Dh/Dl (1372.4-1376.3)/780-.005
  • q.005 m/day
  • ?.44 (Tab 8-1)
  • qe .01 m/day
  • 10 yr travel distance41.5 m

29
Travel time and risk management
  • Many biological and chemical contaminants are
    unstable in the subsurface
  • Biological and chemical contaminants are often
    released on the land surface as part of human
    existence (fuels, pesticides)
  • Theory travel time from any influence lt time
    needed to dilute or degrade a potential
    contaminant

30
Example Pesticides
  • Degradation in soil and water occurs because
    chemicals are unstable broken down by microbes
  • Degradation often represented as an exponential
    decay function
  • Risks posed by pesticides are characterized by
    solubility, partitioning in soils (esp. organic
    matter), toxicity, half-life

31
Concept of half-life
  • Definition typical length of time needed for
    one half of the total mass of a pesticide to
    break-down to a non-toxic substance

32
Example Oxamyl
  • Carbamate pesticide
  • Highly soluble in water (2000 mg/l)
  • Half-life 1 day
  • If we had water with a maximum concentration of
    2000 ppm and we waited for 1 day, we should find
    that the total mass of toxic material has
    decreased to 1000 mg (1000 ppm).

33
Estimating fractional loss from half-life
  • We want to know how long it would take for 99.99
    of Oxamyl dissolved in water to be degraded
  • Half life 1 day
  • C1 C0 ek(1)
  • C1/ C0 0.5 ek(1)
  • ln(C1/ C0) k(1) -.6931

34
  • (C1/ C0) ? .0001
  • .0001 ? e-.6931(t)
  • -9.2103 ? -.6931 (t)
  • 13 days ? t
  • Conclusion we should see 99.99 reduction in
    concentrations (mass/volume) after approximately
    13 days.
  • Significance compare time needed for
    degradation to groundwater transport velocities
    to assess likelihood of contamination.

35
Identifying zones of influence
  • Conceptual application of representations of
    groundwater flow (extended to 2-3 dimensions)
  • Use available information about formation
    characteristics, location and amount of
    discharge, general directions of groundwater flow

36
Simple approach
  • Fixed radius
  • Requires minimal information about formation
    characteristics
  • May or may not provide reasonable protection

37
Parabolic capture zones
  • Account for general directions of groundwater
    flow
  • Require some information about piezometric
    surface elevations

38
Analytic solutions
  • Require more information about piezometric
    surface and formation characteristics
  • Represent solutions to groundwater flow equations
  • Based on computer simulations

39
Summary
  • Darcys law is a fundamental tool for analysis of
    groundwater flow
  • Can be applied to estimate flow quantities and
    travel times
  • Wellhead protection zones are based on
    multi-dimensional applications of groundwater
    flow models
  • Wellhead protection assumes that dilution and
    chemical degradation occur before surface and
    subsurface sources influence water quality
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