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WE NOW HAVE OUR OFFICIAL
PATENT!

IN SITU TREATMENT OF STORM
WATER
Presented at the Central States
Water Environment Annual Meeting - Rochester, Minnesota
May 20, 1999 - Nonpoint / Watershed Session
Harry Jebens*, PE, PhD, DEE and Lyle Clemenson**
INTRODUCTION
The treatment of
storm water and snow melt runoff has been attempted by different
classes of systems: storm water retention ponds, end of pipe
systems, and inlet treatment devices. Each system has its own
inherent advantages and applications. The patented Raynfiltr®
developed by Environmental Filtration, Inc. of Brooklyn Park,
Minnesota is an inlet treatment device. The system was developed
as an outgrowth of a need recognized in 1993 by Lyle Clemenson,
president of Environmental Filtration, who was serving as Chair
of a Blue Ribbon Task Force on Storm Water / Land Use. The Task
Force was appointed by the then Mayor of Brooklyn Park, Jesse
Ventura.
THE Raynfiltr®
The Raynfiltr®
utilizes a canister that is 20 inches in diameter and 36 inches
in height that is placed in inlet basins to remove pollutants
from storm water and snowmelt runoff. The canisters have a removable
cone shaped inlet screen to remove large particulates. The lower
portion of the inlet screen has a porous material that removes
fine particulates. The canisters also have a similar exit cone
that prevent blockage of the canister by fines or precipitates.
Figure 1 shows the components of a Raynfiltr® in a
catch basin.

Figure 1 Raynfiltr®
Canister
The Raynfiltr®
Media is a peat derivative. The process to produce the media
begins with mixing raw peat with a sulfonating agent - this enhances
the natural ion exchange capacity of peat to remove heavy metals.
The next step in the process is to dewater the mixture - initially
by gravity and then utilizing a press. Next a binder is mixed
with the sulfonated peat. The mixture is then extruded to form
pellets. The pellets then flow through a rotary kiln at very
high temperatures and in the absence of oxygen - this gives the
media the additional characteristics of Activated Carbon. Figure
2 is the process schematic for producing Raynfiltr® Media.

Figure 2 Process to Produce
Raynfiltr® Media
INSTALLATION
The canisters can
be easily installed in existing catch basins where surface runoff
represents an environmental hazard - upstream of lakes, ponds,
and groundwater recharge basins. Maintenance is easy - simply
remove the inlet grate and remove the inlet cone. The solids
removed by the inlet prefilter and cone can be disposed of via
landfill with municipal refuge - they are not a disposal problem.
HYDRAULIC CAPACITY
The Raynfiltr®inlet
cone has a porous fabric that acts as a prefilter to remove fines,
The prefilter occupies the lower portion of the inlet cone. The
large size of the media allows high flow rates through the system.
The hydraulic capacity of the units using graded media is 0.8
cfs ~ 350 gpm (22 l/sec), When runoff flows exceed this amount
the excess flows out of the canister through the High Flow Orifices
(36 2" Diameter Orifices surrounding the canister). Even
at inlet flows up to 3.0 cfs the runoff will pass through the
Inlet Screen. Most storm water inlets are over designed. Inlets
with curb openings allow larger particulates to enter the systems
(kids balls and beverage containers). When inlets appear to back
up the cause can usually be traced to downstream water levels
not inlet grate capacity.
PROCESS OF CONTAMINANT
REMOVAL
Contaminants are
removed by physical, chemical, and biological means. The physical
removal of particulates begins in the canister inlet cone. A
prefilter of high porosity fiber in the lower 8" of the
inlet cone serves to filter out fine particulates. When the capacity
of the prefilter is exceeded, the excess runoff passes through
the upper 2" of the inlet cone and gross particulates are
filtered out. In passing through the Raynfiltr®, further
removal of particulates takes place.
Chemical removal
of contaminants in solution takes place due to the unique nature
of the Raynfiltr® media. Removal mechanisms are: adsorption,
absorption, chemical fixation, and biological conversion. Due
to the high surface area of the Raynfiltr® media rapid
removal of contaminants in solution is due to adsorption. Heavy
metals in solution are removed via transfer to exchange sites
within the media pores and fixation via ion exchange - the exchange
ion is Hydrogen. Unlike conventional ion exchange resins, peat
based medias are not effected by calcium, magnesium, and sodium
in the stream of water being treated. Organics in solution are
likewise removed by adsorption onto the surface of the media
and absorption into the media. Biological conversion of organics
takes place for organics removed onto the media surface and to
organics that become trapped within the biological film that
develops on the media. Phosphates are removed via chemical fixation
with metals retained and removed by the media.. Figure 3 is an
attempt to depict the mechanisms for the removal of contaminants
by Raynfiltr® media.

Figure 3: Mechanisms of Removal
of Contaminants
Raynfiltr® EFFECTIVENESS
Laboratory testing
and initial demonstration field testing in Brooklyn Park, Minnesota
have yielded promising results. Laboratory testing of pond water
resulted in the removal of: Cu from 9.91 to 0.03 mg/l, Cr from
0.06 to 0.02 mg/l, and Pb from 1.69 to 0.02 mg/. Laboratory test
on five different hydrocarbons resulted in removals of 74.1 to
88.9%. Field tests on phosphorous removals where initial concentrations
ranged for 0.48 to 1.30 mg/l resulted in concentrations of 0.06
to 0.30 mg/l after passing through the Raynfiltr® for
removal efficiencies of 70.5 to 87.5%.
SYSTEM COSTS
Cost are $500 per
unit which includes media. Media replacement should be performed
in the fall and more often in more suspected contaminated locations
- inlets where high concentrations of pollutants are expected.
Replacement media costs $195 / canister. The Inlet Screens should
be inspected periodically visually and cleaned when necessary
- typically once in the spring and once in the summer. Environmental
Filtration disposes of the spent media.The spent media is graded
into three categories: Saturated - this media is crushed,
bioactivated and refined into commodity-grade, natural phosphorous
based fertilizer and soil conditioner, Recyclable - this
media is hydro and pyro-thermally reactivated for use in industrial
treatment applications, and Contaminated this media is
disposed of by industrial recyclers.
FURTHER STUDIES
Additional work
to verify and demonstrate the efficiencies for the removal of
contaminants, capacity of the Raynfiltr® media under
field conditions is in progress. Research sponsored by Environmental
Filtration at Bemidji State University is underway to characterize
the media and the mechanism for phosphorous removal. The Beltrami
Soil and Water Conservation District has recently applied for
a Conservation Partners Grant to the Minnesota DNR - "Enhancement
of Aquatic Habitat Through Stormwater Treatment". the University
of Minnesota has developed a research proposal to characterize
and test our media and are seeking funding from regulatory agencies.
In addition Environmental
Filtration, Inc. is in the process of entering a program of verification
testing through EPA's partner NSF International.
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