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1Gord Geoffrey
Contact: loewend@ae.ca
1Associated Engineering, Calgary, Alberta
ABSTRACT
The analysis and implementation of drainage improvements in a built-up
area should be based on a comprehensive understanding of the behaviour
of the existing drainage system. This understanding is only available
through interpretation and analysis of all available information. Information
that must be considered includes system record information, flooding and
insurance claim information, computer modelling results and public consultation.
KEYWORDS
stormwater management, modelling, public consultation
INTRODUCTION
The City of Regina has been subjected to a number of intense rainfall
events which could not be accommodated by the existing storm drainage
system. As a result, flooding has occurred in the basements and yards
of residential and commercial properties. Street flooding, ponding in
low areas and excessive overload runoff have also occurred during these
periods. The City has instituted a long range master plan process to review
performance of drainage and storm sewer systems throughout the City for
the purpose of upgrade and retrofit. The process was developed because
of the high number of intense rainfall events which could not be accommodated
by the existing storm drainage system.
The main objectives of the long range master plan studies are as follows:
- to investigate the extent of flooding;
- to determine the standards for acceptable service levels;
- to identify areas with substandard drainage;
- to develop upgrading options;
- to undertake a benefit/cost analysis; and
- to recommend upgrading works and work schedule.
Collection and analysis of all available data is regarded as key to successful
implementation of these long range master plans.
Background
Master Plan Drainage Area #10 comprises an approximate area of 348 hectares
located near City Centre. The area is bounded at the following locations:
- on the west by Albert Street;
- on the south by Wascana Creek;
- on the north by the Canadian Pacific Railway; and
- on the east by Winnipeg Street.
There is a wide range of development within the study area. The northern
part is mainly commercial development which contains the downtown core.
The commercial area contains older one and two storey buildings with or
without basements, high rise office towers and the Cornwall Centre. The
central portion is made up of older residential homes and apartment complexes.
The southern section is a combination of residential housing, apartments
and Wascana Park which includes the Saskatchewan Science Centre and the
University of Reginas College Avenue campus.
INFORMATION
COLLECTION

Area Discretization
The drainage areas were broken into four separate drainage
areas selected based on the exit point from the study area.
The four drainage zones are described as follows:
- Zone 100 - This area is roughly described as the entire area south
of College Avenue. The storm sewer in this area discharges to Wascana
Creek. Zone 100 is a stand alone area and is not impacted by the rest
of the study area.
- Zone 200 - This area is the largest drainage zone within the study
area and is located within the area approximately bounded by College
Avenue to the south, Victoria Avenue to the north, Albert Street to
the west and Toronto Street to the east. The storm sewer in this area
discharges into Wascana Creek.
- Zone 500 - This zone basically covers the east portion of the study
area and most of the north area also. The approximate boundaries of
the area are Winnipeg Street to the east, College Avenue to the south,
the railway to the north and a line running north on Toronto Street
from College Avenue to Victoria Avenue then west along Victoria Avenue
to Broad Street then north on Broad Street to South Railway Avenue.
There is a large pocket of land in the Scarth, Hamilton, Rose Street
area north of 12 Avenue that is also part of this zone. This area drains
to the 7 Avenue Trunk Storm Sewer west of Winnipeg Street.
- Zone 700 - This zone covers the northwest corner of the study area.
The approximate boundaries are Albert Street to the west, Victoria Avenue
to the south, Scarth Street to the east and Saskatchewan Drive to the
north. This area drains to the 7 Avenue Trunk Storm Sewer at Albert
Street.

The discretization was performed based on the storm sewer system and
the area contributory to the catch basins. The area contributory to the
catch basins was derived from City record plans showing surface grading
and the field surveys conducted by Associated Engineering as part of this
study. The major system drainage scheme was derived from the surface grading
elevations. Air photos were utilized to determine the impervious ratios
for the individual sub-catchments. The plans of the minor system created
from the Citys as-built drawings compared closely with the Citys
digital drawing of their trunk storm sewer system.
Surface Depression
To accurately define the topography, a Surface Depression Storage Plan,
or more simply, a contour plan of the area was required. The construction
of this plan relied heavily upon available information from the City of
Regina using as-built drawings containing geodetic elevations on approximately
80% of all catch basin and storm manhole rims, as well as some nearby
gutter elevations.
A field survey was conducted to complete those areas lacking sufficient
survey information. The survey focused on any catch basin or manhole rims
and street or parking lot gutter elevations. This information was added
to the base plan to produce a complete contour map of the area.
Table 1. Surface Depression Statistics
|
Item
|
Qty. in Study Area
|
Qty. in Depression Areas
|
% in Depression Areas
|
| Catch Basins |
660
|
181
|
27.4
|
| Storm Manholes |
536
|
84
|
15.7
|
| Sanitary Manholes |
322
|
58
|
18.0
|
Storm Sewer System Inspections
As part of the overall system condition assessment an inspection of a
portion of the existing storm system was undertaken during the course
of the study.
The City of Regina Public Works supplied inspection records from 1991
and 1992 which included information documented in the storm system for
one hundred and ten manholes and catch basins within the study area. From
these reports, six catch basins and twenty-four manholes were identified
to have problems in the past and warranted further inspection.
Thirty manholes and relevant sewers were inspected. These inspections
did not note any problems which would affect the hydraulic performance
of the sewer system.
Sanitary Sewer Monitoring
A sanitary monitoring program was undertaken during the course of the
study to assist in quantifying the degree of infiltration and extraneous
flows which enter the sanitary sewer.
For this study infiltration and extraneous flows are described as follows.
Infiltration occurs due to the presence of ground water which is able
to enter pipes or manholes through structural defects. Extraneous flows
are derived from the following three main sources:
- stormwater flows through manhole lids;
- direct cross-connections from storm mains to sanitary mains; and
- service connections on private property via roof leaders and weeping
tile connected to storm mains.
Two locations were identified for installation of the monitoring equipment
and were based on the hydraulic behaviour of the site and the relative
importance of the sanitary main as well as the flooding history of the
area.
Public Consultation
A comprehensive public consultation program was initiated to gather information
on the existing study area, as well as to inform the public of the study
intent.
The consultation program was conducted jointly by The City of Reginas
Municipal Engineering Department and Associated Engineering Ltd.
Associated Engineering undertook the initial task of preparing a questionnaire
for property owners within the study area. The questionnaire was designed
based on samples from previous studies of this nature. It sought to acquire
general information about individual properties such as; the extent of
flooding, cost of repairs, physical characteristics, etc. Due to the fact
the study area houses both residential homes and businesses, two separate
forms were designed. A key aspect in this public questionnaire process
was the decision that all returned questionnaires would be entered into
a draw to win a $100.00 gift certificate for the Cornwall Centre. The
information package was distributed to 60% of the study area, which was
approximately 1,940 homes and businesses.
The response rate to the questionnaire was over 28%, consisting of 136
commercial and 419 residential for a total of 555 responses.
The residential statistics indicated several trends:
- Almost 50% of respondents experienced past basement flooding from
all sources.
- Very little yard and lane flooding but a larger portion of street
ponding was mentioned.
- Half of the respondents have sump pumps in their homes. 68% of the
sump pumps discharge to the sanitary sewer systems.
- Weeping tile is present in nearly half of the homes.
- Approximately one-quarter of roof drains discharge into the sewer
systems. The remainder discharge into the yards.
- Nearly 40% of homes have yards which slope towards the foundation.
- 25% of the roof leaders discharge onto the ground adjacent to the
foundation.
The Commercial questionnaire yielded the following conclusions:
- A large majority of business have basements. About half have experienced
past basement flooding.
- 60% of the respondents own sump pumps. 83% discharge to the sanitary
sewer systems.
- 60% of roof drains were connected to the storm or sanitary sewers.
However, 34% of the respondents to this question were not sure where
their roof drain discharges and only 7% of the roof drains discharge
to the yard.
- 56% of the respondents indicated they have roof control drains.
Flood Damage Record Analysis. Essentially two sources of information
were available to identify and compile flood damage information.
The first source was a summary of flood damage claims for the 1983 storm
event which surpassed a 1:100 year storm event. This data was assumed
to be related mostly to damaged belongings and property as a result of
direct basement flooding.
A second source of flood damage information was obtained through the
public questionnaire where property owners were asked to give damage estimates
from basement flooding.
From the data comparison of the minor system (see Table 2), it is evident
that the occurrence of flooding associated with minor subsystem Zone 700
and 200 is quite low.
Zone 500 had 22% of the lots report past basement flooding. Zone 100
was slightly higher at 27%. Zone 3 has the highest reported number of
basements being flooded and represents 62% of all reported basement flooding
in the overall study area.
Table 2. Minor System Flooding Statistics
|
Zone |
Description |
Total
Lots |
Flooded
Lots |
% of
Flooded Lots |
% of Total
Flooded Lots |
|
700 |
Northwest |
339 |
17 |
5 |
3 |
|
200 |
West Central |
1438 |
158 |
11 |
25 |
|
500 |
Eastern |
1740 |
385 |
22 |
62 |
|
100 |
Southeastern |
215 |
59 |
27 |
10 |
|
Total |
3732 |
619 |
17 |
100 |
A similar analysis can be made on lot flooding in relation to major
system subareas.
Table 3. Major System Flooding Statistics
|
Zone |
Description |
Total
Lots |
Flooded
Lots |
% of
Flooded
Lots |
% of Total
Flooded
Lots |
|
700,200 |
Northwest |
1450 |
102 |
7 |
16 |
|
500 |
Eastern |
1641 |
374 |
23 |
60 |
|
100 |
Southern |
641 |
148 |
23 |
24 |
|
Total |
3732 |
624 |
17 |
100
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Zones 500 and 100 reported 23% of the lots experienced past surface flooding.
However, 60% of the flooded lots in the overall study area are located
in Zone 500.
The questionnaire issued to property owners proved to be a valuable resource
to identify locations which have experienced past flooding. In addition,
the questionnaires also provided physical data which showed a number of
factors which may have contributed to flooding and related damages.
Servicing Policies
The City of Reginas servicing policies for commercial and residential
developments have undergone several changes over the years to represent
the construction standards in place at the time. The majority of the changes
have been concentrated on the discharge location of roof leaders and weeping
tile drains.

Table 4. Servicing Policy
|
Policy |
Effective Date |
System Type |
Sewers to House |
Roof Leader Discharge |
Weeping Tile Discharge |
| Combined |
1883 - 1910 |
Combined |
1 Combined |
1 Combined |
N/A |
| 1 |
1910 - 1945 |
Separate storm/sanitary |
1 Sanitary |
To sanitary |
N/A |
| 2 |
1945 - 1965 |
Separate storm/sanitary |
1 Storm
1 Sanitary |
To storm |
To storm |
| 3 |
1965 - Present |
Separate storm/sanitary |
1 Sanitary |
To surface |
to Sanitary*
Sump Pump to Lawn |
* Currently in use but discouraged by the City.
The combined area is the oldest part of the study area. It was originally
constructed with one sewer which collected both sanitary sewage and roof
leader runoff from the lots. Subsequent to the original construction,
a separate storm sewer was constructed through the area and is generally
located in the back alleys. The storm sewer is isolated from the sanitary
sewer and collects stormwater runoff from the streets and lots. The original
combined sewer now functions as a sanitary sewer except for any roof leaders
which remain connected to the system.
Development in Policy Area 1 includes separate storm and sanitary sewers
which were typically installed at the same time. However, in most cases
combined manholes were installed and cross flow can occur if either sewer
becomes sufficiently surcharged.
In addition the City has used different methods to calculate stormwater
runoff. Up to 1955 the City used the Rational Method, from 1955 to 1978
the City used an "Improved" Rational Method and since 1978 has
switched back to the standard Rational Method as was used prior to 1955.
The "Improved" Rational Method was based on average time of
concentrations depending on area drained. This had the result of over-sizing
the upstream end of a system and under-sizing the downstream end.
Computer Modelling
Computer modelling of the stormwater drainage system was undertaken in
order to determine the effects on the system of stormwater runoff and
to allow determination of possible remedial works which could lessen the
impact of future rainfall events on residents in the area. The modelling
was also used to analyse the capacity of the surface drainage system to
determine possible improvements.
Computer Model. The OTTSWMM computer model was used during this
project as required by the City of Regina. The OTTSWMM model
is an adaptation of the US-EPA Stormwater Management Model
(SWMM) RUNOFF block.
General Comments on Drainage System. There are a number of storage
facilities in place on the minor system. The majority of these storage
facilities are superpipes. Superpipes are pipes in a system
which are oversized in relation to the downstream system. These superpipes
provide in line storage of flow to reduce the impact on the downstream
pipes. Superpipes invariably cause surcharging in the minor system upstream
of their location. In general superpipes are only effective for high frequency
rainfall and runoff events.
Review of data provided by the City with respect to the 7th Avenue Trunk
indicates that this trunk has very low capacity and surcharges under very
frequent runoff events. The behaviour of this trunk effects Zone 700 and
Zone 500. City staff have remarked that this trunk sewer has a capacity
to handle runoff from less than a 1:2 year event. This, in general, means
that any drainage system connected to the 7th Avenue Trunk has a true
capacity of less than 1:2 years because of the restriction caused by the
trunk. This occurs even if the local drainage system has a capacity significantly
higher than the capacity of the trunk.
Review of surface grading in the study area indicates no major drainage
system is in place or even possible without very significant road reconstruction.
The surface grading also indicates very flat lots. The implication is
that precipitation, once on the ground, takes a relatively long time to
reach the major drainage system, and once in the major drainage system
has no where to go if there is no spare capacity in the minor system.
Considering the individual lots the lack of slope is significant. Flow
takes place across ground if there is sufficient slope for the flow to
occur by gravity or there is sufficient hydraulic head to push the flow
across the lot surface. In the case of this study area a major component
of the driving force for lot drainage is hydraulic head or depth of water.
The offshoot of this is two fold: the depth of water on the lot can cause
flooding of the building by entering through windows, doors or cracks
in the foundation, and; the depth of water increases the quantity of the
water which is absorbed into the ground thereby increasing the load on
the weeping tiles and from there on the sewer system. The increased amount
of water absorbed into the ground also increases the amount available
to enter the sewer system through defects in pipes and manholes.
The lack of a major drainage system also has significant effects on the
potential for flooding. Each non-continuous portion of the major drainage
system becomes its own ponding area. The depth of the ponding is dependent
on how much runoff reaches the area, the geometry of the ponding area,
how much can physically be captured by the catch basins and how much can
be conveyed in the minor drainage system. The higher the ponding in the
major system the higher the depth of flow on the lots must be to force
the runoff from the lots to the major system.
As ponding in the major system increases, the potential for increased
inflow and infiltration into the domestic system also increases because
the domestic system is usually located under the major drainage system.
The increased water absorbed into the ground also impacts the domestic
system through the weeping tiles, if connected and through infiltration
into the house service connection. House service connections are rarely
water tight and in some municipalities are a major source of extraneous
flows into the domestic system.
System Storage. Existing system storage is in place in Zones 200,
500 and 700. The purpose of these storage facilities is to store flows
in excess of the downstream sewers ability to convey. The storage
system used consists of superpipes. This storage totals 3,233 m3
which is equivalent to just over 1 mm of runoff from the entire drainage
area.
Results. The modelling indicates that the existing subsystems
have overall stand-alone design return periods of:
|
Zone |
Return Period |
|
100 |
1:5 year |
|
200 |
<1:5 year & 1:2 year |
|
500 |
<1:2 year |
|
700 |
1:5 year |
Within each subsystem, individual sections may have greater or lesser
capacity than the design return period assigned to the overall subsystem.
Zones 500 and 700 drain into the 7th Avenue system which currently has
a design return period of less than 1:2 years.
The design return periods as determined in the model are realistic based
on the layout and catchment area of each subsystem.
SUMMARY
Analysis of all the information gathered throughout the course
of the study allowed a comprehensive understanding of the drainage network.
Based on the minor system statistics, the major system statistics and
the modelling results the zone of concern is Zone 500, the Eastern area.
This area had 22 % of the lots report flooding from the sewer systems,
23 % of the lots report major system flooding and a storm sewer minor
system with a capacity less than 1:2 years.
The information allowed relief scenarios to be tailored for each drainage
zone.
Relief Scenarios - West Side Area Zones 200 & 700
This area has the lowest incidence of basement flooding in the study area.
The storm sewer system was constructed after the original combined system
which now functions as a sanitary sewer. The minor system was determined
to have a capacity greater than a 1:2 year storm and less than a 1:5 year
storm.
- disconnect catch basins from sanitary system, reconnect to storm
- separate cross connections
- place inserts in all sanitary manhole covers located in depression
areas
Relief Scenarios - South Area Zone 100
This area has good topographical relief towards Wascana Lake and only
minimal surface ponding occurs. The minor system was determined to have
a 1:5 year level of service.
This area has the highest percentage of flooded basements in the study
area. This is also Policy Area 2 which has separate storm and sanitary
services to each lot. The results of the questionnaire indicate that sanitary
sewer backup into the basements is not a problem. Typically the basement
flooding was minor and was caused by seepage through cracks in the basement
walls, inflow from the tile drains or backup of the storm sewer.
The problems in this area can basically be solved by undertaking improvements
to private property including:
- disconnecting roof leaders from the storm sewer and directing flows
into the yards away from the house foundation.
- installing a sump pump which discharges water from the weeping tile
to the yard.
- capping the storm sewer service.
- regrading the lots to ensure rainwater flows away from the foundation.
- installing a sanitary sewer back flow prevention valve.
Relief Scenarios - Eastern Area Zone 500
It was concluded that the northeastern portion of the study area has the
highest incidence of both basement and surface flooding. The minor system
has less than a 1:2 year design capacity. This area has the largest depressional
storage, has a high number of combined manholes, and connects to the overloaded
7th Avenue Trunk Sewer. All of the above factors are the main contributors
to the flooding problem.
A number of potential relief scenarios are available for this area. These
scenarios require additional investigation to determine the best relief
scenario for this area. The scenarios consist of:
- installation of a gravity storm trunk sewer to Wascana Lake from the
centre of Zone 500
- installation of surface detention
- installation of underground detention
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