Newsletter and Technical Publications
<Sourcebook
of Alternative Technologies for Freshwater Augumentation in East and
Central Europe>
1.4 Collection And Reuse Of Stormwater
Technical Description
In developing urban areas, stormwater can be gathered in separate
stormwater sewers and reused after simple treatment for washing streets,
cooling, watering of gardens, and other purposes requiring nonpotable
water. In addition to providing this reuse potential, this technology
makes possible the treatment of urban runoff before it enters waterbodies.
The simplest form of stormwater treatment consists of open or closed
sedimentation basins, retention ponds, or storm sewer, in-line separation
chambers for capturing oil products. Stormwater management technologies
include provision of grit chambers and swirl separators within sewer
mains, and skimmers which capture floatable solids and oil products from
the water surface of basins. Infiltration ditches also can be used for
filtration of oil products.
Extent of Use
As a rule, in the central and oldest parts of Central European cities,
stormwater is conveyed in combined sewer systems to municipal treatment
plants, and discharged, following treatment, to receiving waterbodies. In
a few newer urban districts, separated sewer systems have been constructed
which allow for stormwater reuse. However, this technology is not very
popular and not widely used.
Operation and Maintenance
Regular inspections during rainy weather should be conducted to minimise
the occurrence of blockages within the collection system. If basins are
used, mowing of the grass within the basins, periodic removal of
sediments, and cleaning of the outlet pipe are also required. Litter,
soil, and leaf removal is required from in-line separators.
Level of Involvement
This technology is best implemented at the municipal government level.
Costs
Costs are different according to local conditions, possibilities for
stormwater usage, and existing infrastructure. Because dual collection
systems are required for stormwater and wastewater conveyance, the costs
may be higher than for combined systems (which may require larger diameter
pipe networks to convey the higher volumes of wet weather flows).
Effectiveness of the Technology
The efficiency of this technology when combined with simple pond-based
treatment facilities is high, with approximately 80% of oil products and
suspended solids being removed from the stormwater. Depending on the area
drained by the system, a large volume of water can be saved if stormwater
is reused for purposes requiring low quality source waters.
Suitability
Reuse of stormwater can be a favourable option for municipalities with
scarce water resources and an high demand for low quality, nonpotable
water. The desirability of stormwater reuse is strongly dependent on
general environmental quality and pollution within the rainwater catchment
area, and may vary depending on the intensity and duration of storms and
the length of the period between storms. Stormwater quality also varies
within individual storms, with water quality at the beginning of a storm
pollution being poor (known as the "first flush" effect). Also,
the quantity of stormwater is variable, with periodic high flows during
storms and low or no flows between storms. Hence, detention ponds, using
biological treatment, are often used as such ponds are most flexible with
regard to volume. Nevertheless, it is important that such ponds are of
adequate volume to detain between a 2 and 100 year recurrence interval
design storm, so that the runoff is not discharged into waterbodies
without sufficient treatment. Because water quality of the runoff
generally improves during the course of a storm, the degree of impairment
at the end of the storm is rather low and this water can be reused after
simple treatment or discharged into waterbodies without a significant
pollution risk. Investigations of the stormwater flows show that long
rains of low intensity create greatest pollution loads to surface waters.
Table 2 presents a summary of the principle chemical characteristic of
stormwater based on pollutant concentrations reported in the literature.
The Table clearly shows that pollutant concentrations are such that
treatment should be provided prior to discharging the runoff to natural
water courses.
TABLE 2. Typical Pollutant Concentrations in Stormwater in Eastern
Europe.
Pollutant concentration
(mg/l) |
Rainwater |
Snowmelt |
Street wash water |
| Suspended solids |
50-16 000 |
570-6 580 |
30-8 300 |
| COD |
24-260 |
33- 250 |
35-280 |
| BOD 5 |
10-285 |
5-270 |
6-225 |
| Chlorides |
10-35 |
35-1 600 |
11-37 |
| Oil products |
2-24 |
35-72 |
2-72 |
Advantages
Using low quality water for nonpotable needs, instead of potable
freshwater resources, augments the available supplies of the latter.
Providing treatment of stormwater runoff from urban areas also provides an
opportunity to upgrade degraded natural waters that have previously
received untreated stormwater discharges.
Disadvantages
Because limited treatment methods of purifying stormwater are used,
effluents may remain contaminated with persistent pollutants like heavy
metals, and, in consequence, should not be used for gardening purposes if
the produce is intended for human consumption. Use of contaminated
stormwater may lead to contaminant accumulation in the soil.
Cultural Acceptability
This technology is culturally acceptable. Its use is largely outside of
the public eye, and, hence, is mainly of concern to administration staff
and workers.
Further Development of the Technology
Better schemes of the assessment of environmental impacts connected with
stormwater use for various purposes need to be developed. Given that
treatment is often needed, improved methods of purifying stormwater, that
are inexpensive and simple to install and operate, should be developed.
Information Sources
Rolands Bebris, Ministry of Environmental Protection and
Regional Development, 25 Peldu Street, 1494 Riga, Latvia, Tel. (371-7)
227145, fax: (371-7) 820442, e-mail: BEBRI@VARAM.GOV.LV.
Anna Egle, V/U "Meliorprojects", 11 Novembra
Bulvaris 31, LV-1494 Riga, Latvia, Tel. (371- 7) 228734.
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