Bioretention gardens for improved nutrient removal
Mark T. Randall and Andrea Bradford
ABSTRACT
Bioretention gardens are stormwater management practices capable of providing numerous water
quantity and quality benefits. However, previous studies have reported inconsistent removal of
nitrogen and phosphorus in these systems. This study used ten, vegetated, mesoscale (0.20 m
3
),
bioretention cells in a field setting to provide a comparison of the nutrient removal capabilities of five,
alternative bioretention designs. Applying a synthetic stormwater to the bioretention cells
demonstrated that a sandy soil mix can provide a 75.5 and 53.4% reduction in concentrations of total
phosphorus and total nitrogen, respectively. Phosphorus removal was found to be only slightly
enhanced in bioretention cells where soil was amended with alum-based drinking water treatment
residuals, a commercially available oxide-coated media, or a commercially available lanthanum-
modified bentonite product. However, improvements in phosphorus removal were observed in some
cells when elevated phosphorus loads were applied to evaluate longer term performance. In cells
incorporating a permanently saturated zone containing shredded newspaper to promote
denitrification, effluent concentrations of nitrate were reduced by >99%, however total nitrogen
concentrations increased.
Mark T. Randall (corresponding author)
Computational Hydraulics International,
Guelph,
Ontario, N1H 4E9,
Canada
E-mail: mark@chiwater.com
Andrea Bradford
School of Engineering,
University of Guelph,
Guelph,
Ontario, N1G 2W1,
Canada
Key words | anoxic, bioretention, low impact development, nitrogen, phosphorus, stormwater
INTRODUCTION
The bioretention garden is a low impact development (LID)
stormwater management practice capable of mitigating
runoff volumes, reducing peak flows, transforming and
sequestering pollutants and providing aesthetic appeal in
urban areas. Numerous studies have been conducted showing
high removal efficiencies of pollutants including: nutrients,
metals, oil and grease, and pathogens (Davis et al. ;
Hsieh & Davis ; Davis ; Hsieh et al. a; Hath-
away et al. ; Hunt et al. ). However, other studies
have indicated leaching of phosphorus and/or nitrogen
from bioretention systems (Dietz & Clausen ; Hunt
et al. ; Toronto & Region Conservation Authority ;
Denich ). Identifying bioretention designs which can
reliably remove a high percentage of nutrients from storm-
water is a necessity as eutrophication of surface waters
remains a high priority water quality challenge.
Hunt & Lord () specified a bioretention soil mix
consisting of 85–88% sand, 8–12% fines (i.e. clay and silt)
and 3–5% organics intended to provide adequate drainage,
reduce pollutant levels and support plant growth. This soil
specification is recommended in bioretention design guide-
lines including those published by the Toronto and Region
Conservation Authority and Credit Valley Conservation
Authority () and has become commonly used in
Southern Ontario. The low percentage of organic matter
(OM) in this mix relative to previous mixes reduces the
potential of nutrient leaching, however there is minimal
data published on potential nutrient removal achieved in
bioretention gardens using this mix.
In addition to testing alternative bioretention mixes,
some studies have investigated bioretention soil amend-
ments capable of improving phosphorus retention. Some
of the materials tested include: steel wool (Erickson et al.
), fly ash (Zhang et al. ) and alum-based drinking
water treatment residuals (Al-WTRs) (Lucas & Greenway
). Bachand & Heyvaert () suggested that Phoslock,
372 © IWA Publishing 2013 Water Quality Research Journal of Canada | 48.4 | 2013
doi: 10.2166/wqrjc.2013.016
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