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RFI - Attachment F - Engineering Report
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4
Technical Papers
Spearman Rank Order correlation test, phosphorus, but are ineffective at aluminium oxide powder is mixed with
positive correlations (P<0.05) were removing soluble phosphorus. The clay to form a slurry, which is coated and
determined between influent and effluent absorptive filtration properties of the then baked onto the perlite media. In
EMCs for Ortho-P and NH3+. Based activated alumina media provides further operational conditions at low cartridge
on the use of the Mann-Whitney Rank removal mechanisms of total phosphorus flow rates, the RCFS also has the ability
Sum test, the difference in the median in stormwater through the synergistic to physically remove clay particles in
values between the influent and effluent effects of precipitation, adsorption and addition to the clay found within the
EMCs is greater than would be expected filtration (Ma, 2009). media from the manufacturing process.
by chance. Therefore, a statistically Substitution of silica by aluminum in
These results not only demonstrate
significant difference (P<0.05) was soil clay particles causes clays to have
that the system was able to provide
observed for TSS, SSC (<2000µm), SSC a negative charge (Cornell University,
substantial and consistent removal,
(<500µm), TP, PP, TKN, TN, and ON. 2007). Because of this negative charge
given the high solubility of phosphorus
at sites on or within the media structure,
Suspended Solids and at low mean influent concentration
we expect that the media would provide
Parameters for the study of 0.22mg/L, but was
some sorptive capacity and affinity for
Under Australian conditions Walker and able to attenuate TP captured by the
ammonium. The characteristics of the
Wong (1999) found that most suspended system over the entire course of the
media would also result in an increase in
solids in stormwater runoff is smaller than study. The soluble fraction appears to
pH. This increase in pH would cause the
500µm. In this study the closest parameter be higher than found by Vaze and Chew
ammonium to convert to ammonia and
was SSC<500µm. Influent EMCs for SSC (2004) under Australian conditions;
then volatilise into the atmosphere.
<500µm ranged from 9mg/L to 393mg/L they estimated that 20 to 30% of the
with a median of 29mg/L and a mean of phosphorus is soluble. It would be Fletcher et al. (2004) measured
66mg/L. Corresponding effluent EMCs expected, given the primary removal nitrogen concentrations of at least 2mg/L
ranged from 2mg/L to 10mg/L with a mechanism of the RCFS is physical for most urban land uses within Australia,
median of 3mg/L and a mean of 4mg/L, filtration, that a higher particulate while Duncan (1999) determined
resulting in an ER of 93% and a SOL fraction of phosphorus would yield median concentrations for roads and
efficiency of 94%. a similar result. urban catchments of 2.2 to 2.5mg/L.
In Melbourne, Taylor et al. found that,
This result needs to be explained Fletcher et al. (2004) measured mean
for TN in stormwater, 49% consisted of
in context with lower than expected TP concentrations of between 0.25
dissolved inorganic nitrogen (NH3+ and
influent concentrations. High pollutant and 0.50mg/L for most land uses while
NOx), which compares well with the 44%
concentrations lead to high percentage the BMP Database (2010) suggests
dissolved inorganic nitrogen load from
reductions and tend to over-estimate a typical TP range 0.11 to 0.38mg/L,
the RCFS study. The soluble component
the removal efficiency of pollutants from across a variety of land uses. Clearly
of nitrogen in stormwater found by
stormwater treatment systems (CSIRO, the mean influent TP concentration of
Wicks et al. (2011) and Miguntanna et al.
2010). A literature review by Duncan 0.22mg/L for this study correlates well
(2010) from roadways and commercial
(1999) showed that the median influent with the published data from Australia.
areas in Queensland was 50 to 60%. Vaze
concentration for total suspended In addition, the removal processes of
and Chew (2004), also under Australian
solids ranged from the lowest 41mg/L physical straining and adsorption are
conditions, found that the soluble portion
for roofs to 232mg/L for urban roads. independent of location and solely a
of nitrogen in stormwater can be up to
Fletcher (2004) found that mean influent function of water chemistry, filtration
50%. In the RCFS study, soluble organic
concentrations for roofs to roadways media and associated hydraulic
nitrogen was not measured; however,
ranged from 20mg/L to 270mg/L. conductivity. Hence our results should
assuming a modest allowance for soluble
apply to Australian stormwater.
Phosphorus Parameters organic nitrogen the soluble component
Nitrogen Parameters of nitrogen in stormwater for the RCFS
Given that the phosphorus removal
Given that the nitrogen removal target in study would be expected to be similar to
target in the Australian context is based
the Australian context is based solely on results from Australian studies.
solely on TP load removal efficiency, the
review of additional data was required TN load removal efficiency, the review of Conclusions
to further demonstrate the significance additional data was required to further
Between April 2011 and June 2012, 13
of the RCFS TP removal efficiencies demonstrate the significance of the
storm events were monitored and were
obtained. In an effort to isolate RCFS TN removal efficiencies obtained in
determined to meet the relevant USA
phosphorus removal efficiency based on this study. In an effort to further isolate
storm data collection requirements.
solubility of TP, dissolved phosphorus nitrogen removal efficiency NH3+ was
Significant reductions in sediment and
was also measured. Removal efficiencies also measured. Removal efficiencies
nutrient pollutant concentrations were
for TP and dissolved P were 86% and based on NH3+, led to overall removal
measured between influent and effluent
74%, respectively, using the ER method efficiency of 63% based on the ER and
sampling locations using the Efficiency
cf 87% and 67%, using the SOL efficiency 60% using the SOL efficiency calculation
Ratio (ER) calculation method (TSS 90%,
calculation method. method.
TP 86%, and TN 56%) and Summation
The removal of dissolved phosphorus There are several pathways in which of Load (SOL) efficiency calculation
is unsurprising but warrants further ammonium reduction may be occurring method (TSS 91%, TP 87%, and TN 50%).
discussion. Traditional forms of treatment in the RCFS system that require further These results demonstrate that the
such as settling and inert filtration discussion. During the manufacturing radial cartridge filter system was able
are able to remove particulate bound process of the activated alumina media, to successfully meet the current load-
water SEPTEMBER 2014
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