Vadose
Zone Hydraulic Process- Infiltration and Percolation- and
Their Function in Hazardous Materials Transport
Alton Day Stone, Alton Stone Engineering, Sterling, MA
Evaluation
of NAPL Migration Resulting from Big Dig Activities
Frank Ricciardi, Weston & Sampson Engineers, Inc.,
Peabody, MA
DNAPL
Dissolution- Evaluating Natural Depletion Over Time
Jeffrey A. Johnson, The RETEC Group, Inc., Houston,
TX
Vadose
Zone Hydraulic Processes – Infiltration and Percolation
– and their Function in
Hazardous
Materials Transport
Alton Day Stone, PE, LSP, Alton Engineering, 10
Rugg Road, Sterling, MA 01564, Tel: 978-422-8014, Fax:
978-422-8014, Email: adaystone@verizon.net
James C. O'Shaughnessy, Ph.D., PE, Civil Engineering Department, Worcester Polytechnic
Institute, 100 Institute Road, Worcester, MA 01609, Tel:
508-831-5309, Fax: 508-831-5808, Email: jco@wpi.edu
The release of most hazardous materials occurs through
spillage or other deposition on the ground (soil) surface,
either in the liquid-phase - e.g. gasoline or solvent
spill, or solid-phase - e.g. lead paint chips, and
deposition of atmospheric particulates. The transport of surface deposited hazardous materials to an
underlying water supply aquifer is of great concern, and
necessitates liquid and dissolved-phase transport through
the vados or unsaturated zone.
Vadose zone flow is very complex, being a function
of several interdependent (and dependent) variables, that
is not easily described or modeled and commonly is not
well understood by environmental professionals.
The importance of unsaturated flow cannot be
ignored; risk characterization models and associated
substances-specific risk levels, involve vadose zone
transport modeling at some level.
Understanding of vadose zone processes permits
adaptation of site-specific data to the general transport
models. This
paper describes the basic mechanisms of vadose zone flow,
in particular infiltration and percolation,
and their relationship to hazardous materials transport.
Infiltration is the movement of water through the
soil surface into the underlying soil column.
Percolation is the subsequent movement of water,
usually downward, through the subsurface soil. Both mechanisms involve two hydraulic phenomenon – gravity
drainage through macorpores and capillary flow through
micropore - that are highly dependent on soil type and
structure. This
paper focuses on one-dimensional downward vertical flow
(∂v/∂z) as described by the Buckingham-Darcy
and Richards Equations.
One-dimensional flow is adequate for practical
description of most common engineering applications.
The results of bench scale experiments using soils
common to New England, including outwash sands, marine
clay and till, are used to illustrate transport
mechanisms.
Evaluation
of NAPL Migration Resulting from Big Dig Activities
Frank
Ricciardi, P.E., Project Manager, Kelley Race, P.G.,
LSP, Associate, Ken Bisceglio, CHMM Project Manager,
Weston & Sampson Engineers, Inc., 5 Centennial Drive
Peabody, MA 01960, Tel: 978-532-1900
The Big Dig required numerous complex
construction projects to complete arguably one of the
biggest civil engineering projects of mankind. One of
these projects involved the installation of an access road
to service the numerous construction vehicles through a
dense, highly populated area of South Boston. This road
was installed adjacent to a bus maintenance facility that
contained several feet of light non-aqueous phase liquid (LNAPL
- Diesel#1 and gasoline) over a 2.5-acre area. LNAPL
migration from this site was influenced by a myriad of
complex urban subsurface conditions including:
-
Numerous
active and abandoned utility ducts and conduits
-
An
MBTA red-line tunnel
-
An
active aboveground rail line and bus maintenance facility
-
A
regional stormwater pump station
-
Underdrain
system to control groundwater for the newly installed Big
Dig access road and
-
Complex,
heterogeneous urban stratigraphy including urban fill and
interbedded clay lenses
This paper will evaluate and discuss the fate and
transport/hydrogeologic characteristics of the site and
how these characteristics influenced LNAPL migration
toward the underdrain system of the access road. Also, we
will discuss how these data were used to design the
multi-million dollar, multiphase extraction system
including measures to intercept LNAPL prior to reaching
the stormwater pump station. The remediation system
contains the following processes LNAPL separation,
groundwater and soil vapor treatment via carbon
adsorption, metals precipitation, and bioremediation
complex.
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