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Methods for the Estimation of Mine Infiltration

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Title: Methods for the Estimation of Mine Infiltration


1
Methods for the Estimation of Mine Infiltration
Bruce Leavitt PE PG, Consulting Hydrogeologist
Washington, Pennsylvania
2
  • Mine Infiltration
  • has been used to
  • Estimate inflow during mining
  • Calculate the rate of mine flooding
  • Estimate post closure mine discharge and
  • Inform permitting decisions.

3
New Applications of Mine Infiltration
  • Project mine discharge from underground mines for
    mine water utilization under varying amounts of
    annual precipitation.
  • Project groundwater discharge from surface mine
    backfills in support of stream mitigation.

4
Mine Infiltration Methods
  • Rule of Thumb
  • 0.50 gpm / acre
  • Possibly based on diPretoro 1986
  • 56 surface mines principally on the Waynesburg
    (14) and the Upper Freeport (31) coals.
    Pittsburgh seam excluded.
  • Flow, one time site visit lt10 gpm bucket and
    stop watch gt10 gpm visual estimate 10 gpm.
  • Data range, 0.02 to 4.35 gpm / acre

5
Mine Infiltration Methods
  • Rule of Thumb
  • Leavitt (1997)
  • Pittsburgh seam underground mines
  • gpm/acre 1.117e-0.0045H where H average of
    the Maximum and minimum overburden thickness.
  • Based on pump curves and hour meter data from
    active mines.
  • Forced to 0.50 gpm / acre at 200 ft overburden
  • Includes longwall and full extraction room and
    pillar.

6
Mine Infiltration Methods
  • Rule of Thumb
  • Leavitt (1997)
  • McCoy (2002)
  • Primarily flooded Pittsburgh Seam underground
    mines.
  • Removed gaining and loosing barrier pillar
    leakage.
  • Based on the percent of the mine deeper than 150
    meters (492 ft).
  • Places a lower limit on infiltration of about
    0.003 meters per year which equals 0.006 gpm /
    acre.

7
McCoy 2002
8
Mine Infiltration Methods
9
New Applications of Mine InfiltrationMine Water
Utilization - Underground mines
  • Large quantities of water are discharged annually
    from flooded mines in the Pittsburgh Basin.
  • The bulk of this water is untreated.
  • Water quality has improved over time.
  • The flooded mines of the Pittsburgh Basin
    represent the second largest aquifer in the
    region.
  • Utilization of this water could benefit
    industrial water users, and reduce the
    environmental mining legacy.

10
Power Plant Cooling
  • Power plant cooling requires large amounts of
    water and cool water improves the efficiency of
    plant operation.
  • The power plants need for water must be satisfied
    in both wet and dry years, or a second water
    source will be required.
  • Existing mine infiltration methods do not provide
    for variations in precipitation.

11
Project WV 232
12
Hydrograph JB-1
13
Recharge Based on Precipitation
  • Recharge inches
  • (? Precipitation (October May) 6.68 inches)
    0.27
  • Based on
  • Average Killing Frost October 1
  • End of Recharge May 31

14
New Applications of Mine InfiltrationMine Water
Utilization - Surface mines
  • Surface mining operations are being required to
    provide mitigation for stream values that are
    lost due to the mining operation.
  • One mitigation option is to create a constructed
    stream segment to replace the lost stream.
  • Discharge from mine spoils, either back stack or
    valley fill, can be used as a water source for
    the mitigation.
  • An estimate of discharge from mine spoils is
    needed to project the flow and duration of flow
    from these designs.
  • The Rule of Thumb method is not appropriate in
    this application.

15
USGS Studies
  • Ballard Fork and two of its tributaries were
    monitored for two years November 1999 to November
    2001.
  • Spring Branch, unmined, 339.2 acres
  • Unnamed tributary, mined, 121.6 acres
  • Ballard fork, mixed, 1,401.6 acres
  • Four rain gauges, two mountain top, and two at
    valley locations.
  • Based on this work two reports have been
    published - Messinger, 2003 and Messinger and
    Paybins, 2003 focused on storm response, and
    precipitation effect on mean flows.

16
USGS Studies continued
  • Precipitation data obtained from Messinger and
    Paybins, 2003
  • Daily stream flow data downloaded from USGS Web
    site.

17
Stream Flow Hydrographs
18
Base Flow Averaging
  • Minimum 0.5 inches of rain in a 2 day period.
  • Base flow proportionally increased from pre rain
    level to the post rain level either 3, 4, or 6
    days following the rain event.

19
Comparison of Discharge
20
Monthly Precipitation Vs. Mine Discharge
21
Estimation of Mine Discharge
  • Three Outliers two were months of normal
    precipitation preceded by a month of abnormally
    high precipitation.
  • The outliers skew the regression to a higher flow
    rate.
  • Equation with outliers removed
  • Q 0.405e0.130P
  • Where Q is gpm per acre and P is monthly
    precipitation.

22
Summary
  • The Rule of Thumb is quick and easy, but is only
    appropriate for surface mines and even then may
    be significantly in error.
  • The Leavitt 1996 method is based on Pittsburgh
    seam unflooded underground mines and is not
    appropriate at less than 200 feet of overburden.
  • The McCoy method is appropriate to flooded
    Pittsburgh seam mines, but places a lower limit
    on the infiltration rate despite overburden
    thickness.

23
Summary Continued
  • Surface mine hydrographs show significant
    response to precipitation, while the hydrographs
    from underground mines do not.
  • Surface mine recharge can occur any time there is
    sufficient precipitation.
  • Recharge to underground mines is negligible
    during the growing season and can be delayed
    until the soil has been resaturated.
  • Estimation of the amount of groundwater available
    from surface and underground mines based on
    precipitation is possible.

24
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