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Design Overview:
The concept of this project was to create a stormwater
wetland out of an existing detention basin, creating a water
quality treatment facility.
The existing
stormwater detention basin was originally designed to reduce
the increased peak flows caused by the construction of the
university campus. As shown below, runoff enters the basin
through sheet flow from a large parking lot (left), and
through two major pipes (48” and 36”) entering the site
(lower left corner of Figure 1.) There is also a steady
baseflow entering the site. Originally the site had a 12”
underdrain that kept the basin dry except during storm
events. In the past the university had kept the basin mowed.

Figure 1: Original stormwater detention basin.
Water quality considerations
were not part of the original design. The baseflow entering
the basin represents the very headwaters of a small first
order stream that eventually drains to the Schuylkill River.
While the basin remained mostly dry, there was always some
flow through the underdrain, even during a severe drought
during the summer of 1999. This observation supported the
concept that the site was ideal for the creation of a
stormwater wetland.
The design focus required for
water quality is very different then that used traditionally
to create a peak flow detention basin. The first part of the
rain event or the “first flush” is critical. Traditionally
the "first flush" is defined as the first inch of runoff.
What is not usually understood is that designing for this
volume includes the majority of the annual rainfall for this
region. As per Pennsylvania’s BMP manual (PACD 1998) the 75%
rainfall event by volume is 1.25 inches. Assuming .25” is
lost due to depression storage and infiltration, designing
for 1 inch of runoff captures 75% of the rainfall volume
falling on the site in an average year. This fact along with
the theory that the first inch is the most polluted makes
this initial small volume the focus for water quality
design.
The site is designed to control
both water quality low flows and extreme event peak flows.
The sediment forebay and berm were placed to insure all
runoff from the parking lot and piping went through the
forebay. The forebay is placed to the side for maintenance
access and to prevent the sediment in the forebay from being
washed out during larger storm events. A series of small
berms and meanders were created and the underdrain was
removed. Lastly the outlet structure was modified to hold
back low flows, maintain the water quality wetland, and
still control the 2 – 100 year storms.
Energy
Gradient: The most important design component of
the project was to insure that the energy gradient of the
system enables a slow meandering path for smaller storms as
shown below in Figure 2. This dictated the elevation of the
outlet weirs and that of the sediment forebay. The devices
were originally designed so the difference in elevation
between the outlet weir and that of the sediment forebay was
only 0.5 feet. The outlet weir was also designed to be
adjustable and and control the water surface elevation and
energy gradient in the wetland.
Sediment Forebay: The sediment forebay was
originally designed to hold .1 inches of rain over the
entire watershed. In the original design, this resulted in a
40’ x 50’ structure 4.5’ deep. This was reduced to 40’ by
40’ and 4’ deep by assuming that the gradually sloping
approach could also be included in the volume. To construct
the forebay, the site was excavated leaving the underdrain
intact to avoid flooding. Next, a 5” reinforced concrete pad
was poured. The purpose of the concrete pad was to support
maintenance of the site. After the pad was in place, gabions
were placed along the lower side, using geotextiles and an
earthen berm to make it impervious. The gabions merged with
the earthen berm extending across the basin. All materials
used were from the excavation of the forebay, so as not to
change the available storage.

Figure 2: Concrete pad under the sediment forebay.
The forebay
outlet weir was created from the gabions, with a low weir
passing the 2-year storm with a larger step passing the 10+
year storms. The contractor added a design element by
placing small riprap around the edges. This change enhanced
safety, allowing someone to walk out of the basin in case
they fell in. The permanent pool of the sediment forebay has
remained stable and is three feet deep.

Figure 3: Completed sediment forebay.
Outlet Structure: The
design focus for the outlet was to maintain the existing
flood control functionality and still sustain the wetland by
restricting low flows. First the area in front of the outlet
structure was excavated, removing the old underdrain. Next a
series of gabions were placed in front of the existing
structure, with the top at a level above the previous
underground 12” orifice but below the first weir in the
outlet structure. The gabions were wrapped in geotextiles to
make them impervious and reinforced with an earthen berm.
Then an adjustable wooden weir designed for the two year
storm was placed between the concrete structure and the
gabions. Flow during smaller events goes along and around
the outside of the gabions, then over the weir through the
original 12” orifice. Larger storms have unimpeded access to
the original T-shaped weir designed to control flood events.

Figure 4: Modified outlet structure during a storm event.
Meander Design: The
design of the meanders was simply to construct earthen berms
and sculpt out a series of turns extending the flow path
with as flat a bottom as possible. See Figure 5. The grading
was intentionally rough, to allow for multiple
micro-habitats. The chief concern was to insure the energy
gradient was as flat as possible to force a meander pattern
and to minimize high velocities and channelization.

Figure 5: Meander Detail.
The planting
scheme was designed by Chuck Leeds, the chief horticulturist
of Villanova, and is detailed in Figures 6 and 7. Plants
were selected based upon their ability to thrive at
different inundation levels, and for diversity. It is
understood that natural competition may change this mix
rapidly. Before planting, the side was sprayed with a
herbicide to kill off the phragmites that had previously
dominated the site. The University Arboretum is providing
maintenance for the site.

Figure 6: Planting Scheme.
|
Key |
Quantity |
Description |
|
ACCA: |
500 |
ACORUS CALAMUS (SWEET FLAG) |
|
ASIN: |
500 |
ASCLEPIAS INCARNATA (SWAMP MILKWEED) |
|
ASNO: |
250 |
ASTER NOVAE-ANGLIA (NEW ENGLAND ASTER) |
|
CACA: |
500 |
CALAMAGROSTIS CANADENSIS (BLUE-JOINT GRASS) |
|
CACR: |
500 |
CAREX CRINATA (FRINGED SEDGE) |
|
CALU: |
500 |
CAREX LURIDA (LURID SEDGE) |
|
CAST: |
500 |
CAREX STRICTA (TUSSOCK SEDGE) |
|
IRVE: |
### |
IRIS VERSICOLOR (BLUE FLAG IRIS) |
|
LOCA: |
250 |
LOBELIA CARDINALIS (CARDINAL FLOWER) |
|
LOSIl |
### |
LOBELIA SIPHILITICA (BLUE LOPELIA) |
|
PEVI: |
### |
PELTANDRA VIRGINICA (ARROW ARUM) |
|
POCO: |
### |
PONDETERIA CORDATA (PICKERELWEED) |
|
SACE: |
### |
SAURURUS CERNUS (LIZARDS TAIL) |
|
VENO: |
250 |
VERNONIA NOVEBORACENCIS (NEW YORK IRONWEED) |
|
ALSE: |
10 |
ARNUS SERRULATA (SMOOTH ALDER) |
|
ARAR: |
20 |
ARONIA ARBUTIFOLIA (RED CHOKEBERRY) |
|
CPOC: |
20 |
CEPHALANTHUS OCCIDENTALIS (BUTTONBUSH) |
|
CLAL: |
20 |
CLETHRA ALNIFOLIA (SWEET PEPPERBUSH) |
|
COAM: |
10 |
CORNUS AMOMUM (SILKY DOGWOOD) |
|
VAAN: |
25 |
VACCINIUM ANGUSTIFOLIUM (LOWBUSH BLUEBERRY) |
Figure 7: Planting List. |