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Hydraulic design and engineeringaspects of combined sewersAyanangshu Dey PhD, CEng, MICE, MASCE, MIWAPartner, AND Engineers & Associates, Kolkata, India
Several cities of India were developed in the colonial era and provided with a combined system for sanitation and
disposal of storm run-off. Further extension of the sanitation infrastructure had to involve a combined system in order
to be consistent or address other constraints, generally congestion. For example, Kolkata receives . 1600 mm of
average yearly rainfall, mostly from July to September. Storm run-off from any catchment is estimated to be about 80
to 120 times the corresponding sewage flow. Hence, only a small portion of the conduit’s capacity is used during the
dry period constituting the majority of the time (nine months). This paper summarises the rationale behind the
general hydraulic design philosophy pertaining to the expansion of such a combined sewerage system. The approach
uses differential values of Manning’s coefficient (n) dependent on flow depth and restricts adoption of the qactual/Qfull
ratio to 1?0 to address potential surcharge condition. A reasonable and approximate procedure of hydraulic design
using a circular conduit is described thereafter utilising basic design charts and simple logic functions. Lastly, a set of
design evaluation parameters are suggested for comparison and optimisation of such hydraulic design. These
parameters, once calculated for similar designs, can be mutually compared and used as indicators to assess the level of
optimisation achieved in any particular design.
NotationD inside diameter of conduit (mm)
De equivalent diameter (mm)
Di diameter of the ith sewer
d depth of partial flow in conduit (mm)
de equivalent depth of flow (mm)
di depth of flow in ith sewer (mm)
fPU pipe utilisation factor
Ie equivalent invert level (m)
Iiav average of upstream and downstream
inverts of ith sewer
L total length of network (m)
Li length of the ith sewer (m)
n Manning’s coefficient
n9 total number of links in the network
nd Manning’s coefficient at d (depth of flow)
P ratio of total cost of supply and laying of
pipe to supply cost of pipe
Q discharge in conduit (m3/s)
Qf, Qfull full discharge in sewer conduit (m3/s)
qa, qactual partial or actual discharge in sewer conduit
(m3/s)
R hydraulic radius at partial or actual dis-
charge condition in sewer conduit
Rf hydraulic radius at full discharge condition
in sewer conduit
S slope or hydraulic gradient (given as 1 over
length, i.e. m/m)
Se equivalent slope
Si slope of the ith sewer
V velocity in conduit (m/s)
Vf, Vfull velocity at full discharge condition in sewer
conduit (m/s)
va, vactual velocity at partial or actual discharge
condition in sewer conduit (m/s).
1. Introduction
Hydraulic design of sewer systems is commonly based on the
application of Manning’s equation for open channel flow. This
equation is universally accepted and used routinely by
practising engineers all across the globe. Manning’s formulae
are used for their simplicity in design and generally satisfactory
prediction of velocity and flow at varying flow depths.
However, this application is based on the assumption of
steady-state, uniform flow conditions: a situation which is
rarely the case.
Basic expressions of Manning’s formulae for circular conduits
when flowing full are given as
1. V~1
n(3:968|10{3)D2=3S1=2
and
Municipal Engineer
Hydraulic design and engineering aspectsof combined sewersDey
Proceedings of the Institution of Civil Engineers
http://dx.doi.org/10.1680/muen.12.00055
Paper 1200055
Received 12/10/2012 Accepted 11/02/2013
Keywords: hydraulics & hydrodynamics/municipal & public
service engineering/sewers & drains
ice | proceedings ICE Publishing: All rights reserved
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2. Q~1
n(3:118|10{6)D8=3S1=2
where V is velocity (m/s), n is Manning’s coefficient of
roughness, D is the inside diameter of conduit (mm), S is
slope or hydraulic gradient (given as 1/length, i.e. m/m), and Q
is discharge (m3/s).
In the majority of cases, circular conduits are designed and
optimised for partial flow conditions. Attempts have been
made by past researchers to analyse the hydraulics of partially
filled conduits (Giroud et al., 2000; Wong and Zhou, 2003;
Zaghloul, 1998) and find out explicit solutions corresponding
to the depth of flow (Barr and Das, 1986; Esen, 1993; Giroud
et al., 2000; Saatci, 1990, 1992; Wheeler, 1992).
From the above formulae, it is observed that if the diameter
and slope (i.e. D and S) of any conduit are known, its discharge
capacity and velocity (i.e. Qfull and Vfull) under full flow
condition can be calculated immediately. However, when a
conduit has to be designed for a given flow, often referred to as
the actual flow or qactual (qa), the process of finding the exact
solution to calculate the hydraulic parameters of the conduit is
not as direct, particularly for any large combined system
collection network. Akgiray (2004) indicated that, provided the
diameter (D), slope (S), and discharge are known, iterative
calculations are required to find the hydraulic properties such
as the depth of flow (d) and corresponding velocity (v).
However, he also mentioned that, with the aid of modern
software, such iterative calculations could be completed
quickly and precisely. On finding this d/D ratio and after the
adoption of suitable values for the diameter and slope,
subsequent calculations are performed.
In all practical cases the design of any circular conduit over a
given length is required to be done to convey a previously
estimated flow, i.e. qactual. The conduit is required to be
designed and optimised to convey this flow and, hence, it is the
latter situation that any sewerage and drainage engineer has to
deal with most of the time. Furthermore, on many occasions
Manning’s formulae are applied but neglecting the variation of
Manning’s coefficient (n) with depth of flow (Benefield et al.,
1984; Metcalf & Eddy Inc., 1981). Previously, Saatci (1990,
1992) and Giroud et al. (2000) proposed solutions over the
range 0 # d # 0?938D, which removed the need to use the
iterative approach. However, their solutions did not take into
account the variation of Manning’s coefficient with the ratio of
d/D. As early as 1946, T R Camp (Camp, 1946) reported
changes in values of n with flow depth; in other words, it was
suggested that n was a function of the d/D ratio. This
phenomenon pertains to a number of factors commonly found
in sewers. These include: corrosion of the conduit above the
normal water surface, solids deposition at the bottom of sewers
during extended low flow conditions, erosion of the conduit
surface by solids contained in the flow. Recent studies by
Akgiray (2004, 2005) put forward explicit formulae for partial
flow in conduits over the entire range of flow depth, i.e.
0 # d # 1?0D taking into account both constant and variable
n values over depth of flow.
Furthermore, Escritt (1984) indicated that turbulent flow in
pipes flowing full appeared to be different from that in an open
channel, suggesting the application of Manning’s equation for
estimating the full flow capacity of a pipe was somewhat
flawed. This can be attributed to a number of differences
between a true open channel for which Manning’s variation on
Chezy’s equation is applicable and a full pipe. One specific
deviation is the availability of a free water surface which
provides for the dissipation of energy by water surface waves,
undulations and eddies. Escritt (1984) suggested that there is a
direct connection between the dissipation of energy by waves
and the water surface over which it occurs. Subsequently, he
attempted to refine the hydraulic radius of conduit flow as the
flow area over the sum of the wetted perimeter and half the
width of the air–water surface. However, Manning’s coefficient
was assumed to be constant over flow depth (d) in such
analysis. His proposed set of hydraulic properties of circular
conduits is given in Table 1 (set 3), which Escritt reported to
have been based on numerous tests on partially filled small and
large conduits. The other sets of hydraulic parameters (i.e. sets
1 and 2) for circular conduits are adopted from India’s Central
Public Health and Environmental Engineering Organisation
Manual (CPHEEO, 1993).
Instead of an iterative solution, it is preferable to have an exact
or theoretical solution which can only be solved by employing
established and commercially available software packages.
However, time and scope for such an elaborate and exhaustive
design for a combined sewer network can be limited for some
projects. Hence, an alternative yet sound engineering proce-
dure for hydraulic design needs to be devised and made
standard guidelines for designers. An approximate method
using basic hydraulic charts, tables, and design guidelines will
prove to be a reasonable alternative for use in such cases. One
such attempt using the logic function of the Microsoft Excel
software is described in subsequent sections. Certain assump-
tions are made in such an approach, making it an approximate
procedure.
2. Aspects of design philosophy
The basic philosophy of the hydraulic design of a combined
sewerage system is that it be a consistent approach which is
well-justified from a technical standpoint and at the same time
practical for adoption. The existing Manual of Sewerage and
Sewage Treatment (CPHEEO, 1993) contains the key guide-
lines to be followed by practising engineers all across India.
Municipal Engineer Hydraulic design andengineering aspects ofcombined sewersDey
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Other publications on recent trends in sewerage system and
sewage treatment continue to be published by the Ministry of
Urban Development, Government of India, pending a revised
edition of the sewerage manual. The requirement for a
comprehensive and exhaustive review of existing guidelines
and further recommendations is currently being felt by
engineers as well. The issues that need to be addressed urgently
by a newly revised document are, material selection for sewers,
methodology for advanced sewer installation, applicability of
material and methods under varied field conditions, sewer
appurtenant works, administrative framework for project
implementation, cost recovery, assessment of economic bene-
fits, and financial aspects.
A few of the critical design aspects are discussed here in view of the
limited available information on the subject. Recommendations
are put forward on these issues by analysing previous studies and
selecting the most applicable option. These issues are believed to
be among those playing a key role in design and optimisation of a
combined system.
2.1 qactual/Qfull ratio
In a combined sewerage system, there is always a chance that
the system might operate under flooded condition. This is a
result of it being designed for a specific storm event which
produces a design storm weather flow (SWF). However, for a
majority of the time, the sewer system handles primarily
domestic wastewater flow (i.e. dry weather flow or DWF). For
these systems, the SWF is sometimes significantly larger than
corresponding DWF and dominates the design. Flooding and
subsequent surcharging due to run-off events that are greater
than that used for design, do occur at times. Such combined
systems are also prone to siltation as it would be difficult (if not
hydraulically impossible) to maintain self-cleansing velocity in
sewers during minimum flow (DWF) condition. Their opera-
tion also becomes very much dependent on periodic and
regular de-silting.
From the hydraulics of a circular conduit, maximum flow
occurs over flow depth (d) of 0?83 and 1?0D (Table 1, including
all three sets of data). The three sets of conditions (Table 1)
refer to: (1) no variation in the value of n over depth of flow;
(2) including the variation in the value of n over depth of flow;
and (3) as evaluated by Escritt (1984) by his modified definition
of hydraulic radius mentioned earlier. Over this range of flow
depth, actual discharge was found to be more than the
discharge capacity (Qf) of the conduit (i.e. qactual/Qfull . 1?0)
while flowing full. It should be noted that adoption of a
constant value of n continues to be a common practice in
design.
Considering linear interpolation between points, namely the d/D
ratio from 0?8 to 0?9, for the first two data sets in Table 1, it can
be calculated that qactual becomes equal to Qfull at d/D ratios of
approximately 0?83 and 0?88, respectively. Escritt (1984)
referred to previous estimates that indicated that, at a d/D ratio
of 0?94, qactual discharge in the conduit would be about 1?0757
times its Qfull discharge. However, on analysing Escritt’s
equation, Akgiray (2004) concluded that the ratio of qactual/
Qfull was 1?022 at a d/D ratio of 0?9728. This was the reason why
Ratio of
d/D
Set (1): for constant
n value
Set (2): for n variable with depth
of flow (d)
Set (3): values as suggested
by Escritt (1984)
va/Vf qa/Qf n/nd va/Vf qa/Qf Aa/Af va/Vf qa/Qf
1?00 1?000 1?000 1?00 1?000 1?000 1?000 1?000 1?000
0?90 1?124 1?066 1?07 1?056 1?020 0?948 1?039 0?985
0?80 1?140 0?968 1?14 1?003 0?890 0?858 1?019 0?874
0?70 1?120 0?838 1?18 0?952 0?712 0?748 0?977 0?730
0?60 1?072 0?671 1?21 0?890 0?557 0?627 0?917 0?575
0?50 1?000 0?500 1?24 0?810 0?405 0?500 0?843 0?421
0?40 0?902 0?337 1?27 0?713 0?266 0?374 0?752 0?281
0?30 0?776 0?196 1?28 0?605 0?153 0?252 0?643 0?162
0?20 0?615 0?088 1?27 0?486 0?070 0?142 0?510 0?073
0?10 0?401 0?021 1?22 0?329 0?017 0?052 0?337 0?018
d, depth of flow; D, diameter of conduit; nd, value of n at depth of flow (d); va, actual velocity; Vf, velocity at full flow in conduit; qa,actual flow; Qf, full flow in conduit; Aa, actual area of flow; Af, area at full flow in conduit.
Table 1. Tabular representation of hydraulic properties of circular
conduits
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the same did not show up in the set 3 values of Table 1.
Adopting linear interpolation with Escritt’s values (set 3 in
Table 1), it was calculated that, at a d/D ratio of about 0?93,
qactual equals Qfull.
However, the formula for conduit flow as suggested by Escritt
does not contain any Manning’s coefficient and therefore also
ignores its variation with depth of flow. Akgiray (2004)
analysed the explicit solutions of partially flowing circular
conduits as proposed by him with three separate approaches:
constant value of n, alternative hydraulic radius suggested by
Escritt (1984), and variation of the value of n with depth of
flow (Camp, 1946). Akgiray concluded that these last two
approaches gave nearly the same results over the range
0 # d # 1?0D, giving Qfull values that were about 20–30%
less than that obtained with constant value of n and adopting
the conventional definition of hydraulic radius.
From a designer’s standpoint and incorporating some reason-
able level of approximation, it is suggested that the most
conservative approach to design of a combined sewer would be
to adopt a variable value of n (set 2 in Table 1) and at the same
time restrict qactual to Qfull ratio to 1?0; in other words putting a
ceiling of Qfull value on qactual. This argument for circular sewers
will also be applicable for ovoid sections. Bijankhan and
Kouchakzadeh (2011) showed that, for an ovoid sewer, the d
value at which qactual/Qfull 5 1?0 occurs was at 0?84D. Such a
point (qactual 5 Qfull) in the case of both circular and ovoid
sections also indicates that this point coincides with both R/Rf
(R and Rf are the hydraulic radii at flow depth d and full flow
conditions, respectively) and v/Vf (v and Vf are velocities at flow
depth d and full flow conditions, respectively) being maximum.
Such a criterion of basic sewer hydraulics might be extended for
other conduit sections; for example, elliptical, horse-shoe, and
semi-elliptical. In summary, there exists a range of flow depth in
the top portion of such conduit sections for which qactual exceeds
Qfull. Such flow estimation, apart from being relevant for new
design, is also applicable for re-sectioned circular and non-
circular conduits in sewer rehabilitation projects for conserva-
tive system planning.
Each link of sewer will then be designed to convey flows equal
to or less than their corresponding discharge capacity under
surcharge condition. This would infuse a conservative
approach to design and effective utilisation of sewers either
under flooded conditions or during maximum flow. In the
suggested procedure for hydraulic design of sewers presented
under section 3, the second set of values given in Table 1 have
been used.
2.2 Variable value of n
Literature provides only limited justification as to whether to
incorporate variation in the value of n with flow depth for
hydraulic design of a combined system under Indian condi-
tions. The current sewerage manual (CPHEEO, 1993), contains
relevant charts (Figure 1) and tables (set 1 and 2 in Table 1) for
using variations in the value of n but is silent on properly
encouraging its use and justification. As a result, it has become
a common and conventional practice to adopt a constant value
of n for design purposes and ignore the critical issue of
differential values over the range of flow depth, i.e.
0 # d # 1?0D.
For any combined system, consideration should be given to the
fact that, for the majority of the time (during dry weather),
sewage flow takes place over a small section of the combined
sewer. Actual capacity of these sewers only comes into play
during monsoon period when combined flow (DWF + SWF) is
conveyed. Hence, it would be reasonable to presume that there
would be a difference in n values of surfaces over which these
distinctively different quanta of flows occur. Hence, it is
considered logical and prudent to adopt differential values of
Manning’s coefficient for a conservative design instead of the
conventional approach of assuming constant n, all through the
conduit diameter.
2.3 Sewer transition
This is one very critical aspect to ensure proper hydraulics in
the collection network. For a specific reference, Kolkata’s
original underground combined sewerage network was devel-
oped over the years 1858 to 1875. As early as 1916, Goode
(2005) reported a serious defect in the system as sewer
transitions from smaller to larger diameters were made without
providing any drop. The branches and main sewers were built
by matching their inverts. Thus, full flow capacity of down-
stream sewers could not be fully utilised without causing a
1.00qa/Qf for constant n value
qa/Qf for variable n valueva/Vf for constant n value
va/Vf for variable n value
0.00
1.00
Hydraulic elements, va/Vf and qa/Qf
0.90
0.80
0.70
0.60
0.50
0.40
0.30
0.20
0.10
1.10
0.10
0.90
0.80
0.70
0.60
0.50
0.40
0.30
Rat
io o
f dep
th to
dia
met
er, d/D
0.20
Figure 1. Hydraulic-elements graph for circular sewers. (plotting
set 1 and 2 in Table 1)
Municipal Engineer Hydraulic design andengineering aspects ofcombined sewersDey
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certain amount of flooding on smaller diameter upstream
sewers.
In developing a new sewer system, transition from smaller to
larger diameters of the sewer needs to be done by matching the
top or soffits of corresponding sewers. For an extremely flat
terrain such as that in Kolkata, this practice will incur
additional invert depth as designers’ might prefer to restrict
the depth of the sewer invert up to a predetermined level to
facilitate installation. Invert matching may also arguably be
supported by prevailing soil condition, locations having acute
space constraints, or expected flooded condition causing full
flow in conduits. However, from a hydraulic standpoint it is
absolutely essential that the free-flowing water level of
branches and laterals are not restricted at junctions by the
maximum water level in main sewers, even if this calls for some
additional excavation depth.
Otherwise, when a long stretch of sewer is considered in a flat
terrain, it is pertinent to assume that its inverts would be less
over the initial stretches and gradually increase on the
downstream side. Hence, inverts of branch sewers culminating
in the main sewer over initial stretches might have to be
matched with its inverts in order to restrict the excavation
depth. However, over middle and terminal stretches, it may
very well be possible to match the soffits of sewer branches
meeting this sewer with its corresponding soffits so that
suitable hydraulic drops at these sewer junctions can be
provided (Figure 2).
Keeping such provision for incoming branches can eventually
reduce required depth of excavation and at the same time
facilitate better hydraulics at peak flow condition. Basically,
some level of physical drop at the junction of branches and the
main sewers should be kept in working out the hydraulic
design, and such design needs to be performed not by a generic
approach but by a more specific one in order to achieve
effective design.
2.4 Screening manhole
Expansion of a sewerage system into unsewered areas is usually
done in phases. Most of the time, it is observed that the
collector and interceptor sewers of any system are designed
and constructed ahead of branches, sub-laterals, and tertiary
level sewers which constitute the complete collection network.
It is likely that, when these facilities become ready for
commissioning, corresponding upstream components might
be under construction. Furthermore, in all probability,
existing surface drains, catering to drain the combined flow
from a catchment, will be connected to the newly constructed
underground sewer system to provide immediate relief to the
population from water logging. These surface drains will later
be dismantled once a permanent underground collection
network is completed.
Surface drains are mostly open over large stretches, and solid
waste is either indiscriminately dumped or street littering
eventually ends up in them. This chokes up the natural flow of
conduits during the dry season. It is clear that, if these drains
are connected to sewers without any arrangement for screen-
ing, it will inevitably clog these lines. This will disrupt natural
flow in sewers and cause severe deterioration in their carrying
capacity. This problem may become compounded over time if
this accumulated silt and waste are not regularly removed from
the sewers. In the majority of cases, a screening arrangement
cannot be provided at the outlets of the surface drains (opening
into these sewers) due to acute space constraints.
To safeguard these sewers from undesired solid waste
dumping, it is suggested that online screening be provided
inside some manholes at strategic locations. These will be
designated as ‘screening manholes’ and will house a detachable
manual screen fitted perpendicularly to the direction of flow,
an operating platform, preferably two access hatches, and
other facilities (Figure 3). The screen can be of stainless steel to
avoid corrosion under extended use. A screening manhole will
help in sewer maintenance by arresting the debris at some
specific locations, which would otherwise have been distributed
all over the length of the sewers, making its removal difficult.
The periodicity of cleaning of such manholes would depend on
the amount of debris accumulated over a stipulated time, field
conditions and might vary from one location to another.
Ground level
Access manhole
Manhole invert
Incoming sewers
Outgoing sewer
Figure 2. Typical detail of sewer transition
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2.5 De-silting work
The development of a combined sewerage network where there
is a very large difference between estimated DWF and SWF,
would perpetually have a siltation problem. If circular conduits
are used, their dimensions are primarily selected so these are able
to convey maximum flow. This in turn eliminates the possibility
of maintaining self-cleansing velocity at nominal DWF, causing
siltation all over the dry period. Although egg-shaped brick
sewers were used during the initial stages in the late nineteenth
century (Goode, 2005), oval-shaped sewers are neither readily
available in India nor preferred by the executing agencies
responsible for procurement and other contractual issues. As
such, their use is restricted to rehabilitation of old sewers and
not in the design of new ones. Regular and adequate de-silting
becomes quite a challenge and remains the only option for
keeping the sewers in adequate serviceable conditions. This is a
continuous process and should be made exhaustive and
continued all over the year to offset the siltation problem.
3. Method statement for hydrauliccalculations
A description of the method of performing hydraulic calculations
of a gravity sewerage network is presented here. As earlier
justified, this approach uses set 2 design data (Table 1) of
hydraulic properties of circular conduits. Linear interpolation of
intermediate values given in the above table is performed to work
out ratios corresponding to intermediate values of qa/Qf and v/Vf.
A representative layout of a combined sewerage system is
shown in Figure 4. This constitutes a reasonably long and
continuous stretch of lateral or secondary sewer, a branch or
tertiary sewer converging with it, and its ultimate culmination
into a trunk (primary) sewer. This network is used to
Ground level
Access manholes
Bar screen Operating platform
Outgoing sewerIncoming sewerhf
Figure 3. Arrangement of screening manhole. hf is the total head
loss for full flow condition, provided as the drop between incoming
and outgoing manhole inverts
8
67
5
Trun
k Se
wer
4Lateral Sewer
32
1
Sub-
late
ral
Figure 4. Sample layout of a combined sewerage network
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demonstrate sample hydraulic calculations of a gravity sewer
system ignoring other laterals and branches. The node numbers
are indicated as appropriate and referred to in the design. The
lateral sewer originates at node 1 and connects to trunk sewer
at node 7, and a branch sewer starts from node 8 and joins with
this lateral at node 4. Only a few of the strategic manholes are
shown on this layout. Intermediate manholes are omitted for
clarity; however, these are considered in the design to make it
as exhaustive as possible.
A sewer connecting an upstream manhole to a downstream one
is referred to as a link, and a sewer line comprises a collection
of several such links. The estimated flow in each link
contributed by their respective catchments were ascertained
as given. Hydraulic design of this network needs to be
performed keeping the maximum depth of sewer invert to
4?0 m due to acute space constraints, soil and groundwater
conditions, and safety of adjoining structures. Furthermore, all
individual links will be designed with a design philosophy of
qactual # Qfull, as mentioned and justified earlier.
At first for any link, diameter and slope are selected and the
resulting full discharge capacity (Qfull) and velocity (Vfull) for
that link are calculated. This is matched against the estimated
flow (qactual) that the particular link will be required to carry.
The ratio of qactual/Qfull is then calculated. From Table 1, the
corresponding values of vactual/Vfull and d/D ratios are
calculated by linear interpolation for intermediate values.
Multiplying this vactual/Vfull ratio by Vfull gives the value of
vactual. If required, the diameter is suitably selected against the
slope provided. After selecting the diameter, the slope of the
link is meticulously adjusted to meet the stipulated criterion of
qactual/Qfull # 1?0 to optimise the slope as much as possible.
Once the slope of the link has been ascertained, sewer inverts,
depths of inverts and excavation depths can be calculated.
These values and some other parameters are checked against
their permissible corresponding values (e.g. minimum clear
cover, maximum invert depth). If these are found to be
satisfactory and met certain stipulations, the design of this
particular link becomes final. However, the design can always
be reviewed later to suit either any additional requirement or
overall optimisation of the network or both. This process is
repeated for each of these links. Some decisions are also
dependent on any incoming sewer invert, its diameter, and
several other factors.
A snapshot of the proposed design output using MS Excel
(Microsoft Corporation, Redmond, WA, USA) is given in
Figure 8 (see appendix) and a step-by-step numerical sample
calculation is given in Table 3 (see appendix). Turbulence and
hydraulic losses are expected at locations where incoming flow
will be mixing with the flow in laterals, and at appurtenant
structures. However, such losses are considered to be minor
without having any significant impact on the overall hydraulics
of sewers; hence they are neglected in the design. In this
hydraulic analysis, the diameters of the sewers are defined as
the internal diameter of the RCC (reinforced cement concrete)
pipe barrel.
4. Hydraulic design of a combined systemThe design of a combined sewerage system is usually aimed at
striking the most effective balance between the diameters of the
conduits used and the depths of the sewer inverts. Direct
construction cost and indirect social cost associated with the
laying of sewers at large depths in the congested urban areas
normally found in Kolkata (or any other congested Indian
cities) are high enough to offset the material cost of the sewer
conduit. As an estimate, say ratio P depicts the ratio of total cost
of supply and laying of RCC (class NP3) pipe to the supply cost
of pipe under Kolkata conditions. Then it is calculated that, at
present, the value of ratio P can vary from 3?3 to 2?4, which
means that the complete installation cost of 300 to 1200 mm
diameter RCC sewers installed between a 1?5 and 4?5 m sewer
invert can be as high as 3?3 to 2?4 times the pipe supply cost
(Figure 5), respectively. Accordingly, in finalising any sewerage
and drainage design in congested urban areas, the diameters of
sewers are weighed against their inverts to satisfy both space
requirements for laying such sizes of sewers and also the
feasibility of construction at corresponding depths.
In handling large and complicated sewerage networks, it is
always preferable to have a link-by-link analysis for better
design control rather than have a generic approach of stipulating
certain parameters applicable to all links in the network. The
detailed hydraulic design of each link of the combined flow
network is absolutely essential as opposed to a design adopting
longer stretches (i.e. stretches with two or more links). Not only
3.0
2.0 60
40
20
0
80
100
Rat
io P
1.0
0.0
Per
cent
age
mat
eria
l cos
t
300
900
Ratio P
Sewer diamater, mm
% Material cost
800
700
600
500
400
1000
1200
1100
Figure 5. Variation of material cost and total pipe installation cost.
It is assumed that sewers #600 mm are laid within 2?5 m invert
depth and those #1200 mm within 4?5 m invert depth
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does such a design approach determine the hydraulic properties
of all pipes and related pertinent structures, but more
importantly the entire sewerage system can be better optimised
by individual calculations for each such link.
There remains the possibility that the combined system would be
required to operate under flooded conditions. For large
differences between SWF and DWF (as in the case of
Kolkata), the combined system will primarily behave as a
drainage system. As for the hydraulics of a circular sewer,
maximum discharge occurs between 0?83D and 1?0D depth of
flow. Over this range, the actual discharge capacity is found to
be more than the discharge capacity of the same sewer under
flooded condition (i.e. qactual/Qfull 5 1?0 or qactual . Qfull),
regardless of diameter. For conservative hydraulic design,
efforts should be made during hydraulic analysis of combined
sewers to keep the qactual/Qfull ratio equal or below 1?0 for all
stretches. Hence, sewers are dimensioned to convey flows equal
to or less than their corresponding discharge capacity under full
flow condition. The difference between depth of flow and
conduit diameter provides a minor amount of ‘safety’ margin
and some amount of sewer ventilation. This would ensure
effective utilisation of sewers under a flooded condition
conveying the maximum flow.
In developing this design, minimum clear cover over pipe barrels
is kept at 1?0 m as stipulated by the sewerage manual
(CPHEEO, 1993) and suitable protection needs to be provided
if this becomes less. The invert of starting manhole at node 1 has
to be adequately low to ensure proper draining of its catchment.
Furthermore, the maximum depth of the invert is restricted to
4?0 m in view of space constraints and to safeguard existing
buildings in close proximity to the alignment. Each link is a
separate hydraulic element and designed to convey its estimated
flow against these stipulated hydraulic criteria. Minor losses at
junctions and drops are assumed to be negligible.
This layout thus represents a small portion of a large network, yet
the same design procedure is applicable following a part-to-whole
design approach. For this lateral, at first tentative but fair
estimates of diameters and slopes in various stretches are made.
The resulting minimum cover and depth of inverts are checked
against the stipulated values. Then, fine tuning of the design is
carried out by meticulously adjusting the slope of every link to
make it just enough to match the qactual/Qfull ratio of #1?0 as much
as possible and practicable while adhering to other conditions.
Later, the same approach is repeated to design the branch sewer.
Hydraulic design of any sewerage network can be optimised
following this procedure. This applies to smaller and even large
and more complicated networks as well. The single longest
stretch of main sewer is designed first and its hydraulics is
worked out. Subsequently, all its laterals and branches can be
taken up one by one to work out their design in reverse as the
inverts of these branches (at their connecting points on the
main sewer) become available as soon as the inverts of the
main sewer are calculated. Hence, the hydraulics of the laterals
and branches can effectively be calculated backwards. Fine-
tuning and minor adjustments to suit the site conditions and
any specific design requirements can always be done later
taking one particular stretch at a time.
5. Hydraulic design evaluation parameters
Hydraulic design of a gravity sewer system fundamentally
attempts to optimise the diameters of conduits and their invert
depths. The basic factor dictating such optimisation is the fact
that the material cost of the conduit is found to be nominal in
comparison with its installation cost at the design invert depth.
Several other factors also play critical roles in developing the
design philosophy: for example, defining the correct flow,
maximum depth of invert, groundwater table, space con-
straints, attainment of self-cleansing velocity, sewer ventila-
tion, possible flooding condition, environmental aspects, and
social issues.
Once the hydraulic design of any gravity system has been
finalised, it is necessary to ascertain not only whether all design
considerations were duly satisfied but also to what extent they
were met. This would eventually lead to comparative analysis
of that design with some stipulated parameters or if required
with some other similar designs. A set of such evaluation
parameters have been worked out; in the following subsections
they are proposed and elaborated for such an assessment.
5.1 Equivalent diameter
Different diameters adopted in various stretches of the network
have been reduced to a parameter referred to as the equivalent
diameter (De). It is the summation of individual diameters of
stretches with their corresponding lengths over total length of
network and is expressed by
3. De~1
L
Xn
i~1
DiLi
where De is the equivalent diameter (mm), L is the total length
of the network (m), n is the total number of links in the
network, Di and Li are the diameter and length of the ith sewer,
respectively.
The equivalent diameter can be regarded as a measure of
diameter optimisation for any network design. In any given
network, for two separate hydraulic designs (done as per
minimum and maximum depth of invert criteria) two
corresponding values of De can be calculated. A lower value
of De would indicate that particular design is better optimised
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from the standpoint of using lower conduit diameters under
the same design criteria.
5.2 Pipe utilisation factor
The pipe utilisation factor (fPU) is the ratio of the equivalent
depth of flow (de) and the equivalent diameter (De), given by
the following expression
4. fPU~de
De
with De and de measured in millimetres. The equivalent depth
of flow (de), like De, is the summation of the depth of flows in
individual stretches multiplied by their corresponding lengths
divided by the total length of the network and is given by
5. de~1
L
Xn
i~1
diLi
where di is depth of flow (mm) in the ith sewer. The various
depths of flow in different sewers are thus condensed to a single
depth of flow (de).
When the sewer diameters and their flow depths are reduced to
single values of De and de, then based on the previously presented
justification, the pipe utilisation factor, fPU, should be adjusted to
approach 0?88 (see Table 1, set 2, at d/D 5 0?88, qactual 5 Qfull
for variable n value) but never allowed to cross this value for
conservative design. Furthermore, in evaluating the hydraulic
design of the system, the depth of flow in each hydraulic element
or sewer is meticulously adjusted by altering its slope to bring it
as close as possible to this value, namely d/D 5 0?88. The
closeness of this parameter to that value will indicate both the
level of design optimisation and also its conservativeness from
the standpoint of possible surcharge in the system.
5.3 Equivalent slope
The slope provided in the sewers is given in 1/length format, for
example, 1/100 or 0?01 or 1%. The different slopes provided in
stretches of any network are reduced to an equivalent slope
(Se) that is expressed as
6. Se~1
L
Xn
i~1
SiLi
Evaluation parameter Design 1 Design 2 Remarks
Equivalent diameter, De: mm 945 850 Higher value indicates high equivalent
diameter of sewer used in design signifying
higher cost of pipe procurement. In this
case, design 2, having lower De value, is
concluded to have used less pipe diameter
than design 1.
Pipe utilisation factor, fPU 0?76 0?87 Proximity of this value to 0?88 would
indicate how efficiently proposed pipe
diameters are utilised. Here, design 2,
having approached this value more,
becomes a preferred design over 1.
Equivalent slope of invert, Se 1 in 962 (0?00104) 1 in 614 (0?00163) Higher value of Se is an indication of
increased excavation and pipe laying cost.
Higher value for design 2 also alludes to
higher Ie as calculated below.
Equivalent depth of invert, Ie: m 2?389 2?761 This value needs to be weighed against the
first parameter value. A lower value of this
parameter will indicate less excavation cost.
Stipulated maximum depth of invert was
4?0 m. Marginal increase in Ie (for design 1)
will result in significant savings in pipe
material cost, hence to be selected.
Table 2. Comparison of hydraulic designs
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where Si and Li are the slope and length of the ith sewer,
respectively.
A lesser equivalent slope of two similar hydraulic designs
would signify a reduced depth of invert for the corresponding
one. Understandably though, this parameter will be inversely
proportional to equivalent diameter (De) and directly propor-
tional to the next parameter, equivalent invert (Ie).
5.4 Equivalent invert depth
Similar to the above parameter, equivalent invert level (Ie) can
be calculated as
7. Ie~1
L
Xn
i~1
LiIavi
where Ie is the equivalent depth of the sewer invert (m), Li is the
length of the ith sewer, and Iavi is the average of the upstream
and downstream inverts of the ith sewer.
This is also a comparison parameter and the greater the value,
the steeper is the equivalent slope of the network, signifying
higher excavation. This parameter will be inversely propor-
tional to the equivalent diameter (De) and directly proportional
to the previous parameter, equivalent slope (Se), as mentioned
earlier.
Separate designs of the same network can be evaluated by
comparing these parameters. A single design can be adjusted to
make these parameters converge to stipulated values for
optimisation. This process can be extended to compare the
design of two separate networks which are similar with regard to
existing terrain, development pattern, design philosophy, soil
conditions, and so on. An example showing the usefulness of
these parameters for comparative analysis is given in Table 2.
Here, two separate designs of a single network are now compared
in the light of suggested evaluation parameters. The network is
about 7 km in length comprising main sewers, laterals and
branches, with given flows in every link. The network is a
reasonably representative sample for such a comparative analysis.
The terrain is generally flat with ground levels varying within 1?5
to 2?0 m across 1 km. Minimum clear cover (1?0 m) and
maximum invert depth (4?0 m) criteria are same for this design,
which forms the basis of comparison. Evaluation parameters are
given in Table 2 and compared, and adoption of a better design
option is justified in terms of these parameter values.
6. Conclusions
A meaningful and relevant hydraulic design philosophy to be
adopted for a combined sewerage network is discussed above.
This directly relates to and takes cognisance of previous studies
done in analysing the hydraulics of partially flowing circular
conduits. Furthermore, the theoretical and practical design
considerations proposed here can very well be applicable for
designing sewerage and drainage infrastructure for cities with
similar physical and historic settings in India and inter-
nationally, and can also be extended to sewer rehabilitation
works. The following critical issues for hydraulic design of a
combined sewerage network were identified.
& Variation of Manning’s coefficient with flow depth needs to
be considered specifically for combined flow as it would be
justified to consider variable n value in conduits conveying
two very different quanta of flows over corresponding
periods of their occurrence. Use of applicable hydraulic
charts should be made mandatory for a conservative design
approach.
& Regardless of diameter, hydraulic design of a gravity sewer
system should be done restricting qactual/Qfull ratio to equal
or be below 1?0 for all sewers under consideration.
Hydraulic calculations are required to be performed
adopting charts for an n value varying with flow depth and
over a range of d/D ratio from 0?1 to 0?88. This ceiling in
adoption of flow depth will provide sewer ventilation and
more importantly a minor amount of ‘safety’ on account of
actual flow deviations from estimated figures, possible
siltation in the sewer, and actual construction slope. This
will also ensure effective utilisation of sewers under flooded
conditions during maximum flow. Such a stipulation is also
applicable for non-circular sewer hydraulics and finds its
relevance when century-old non-circular brick sewer reha-
bilitation works are undertaken in colonial cities with
combined drainage systems (Figure 6).
& Sewer transition by matching the soffit levels of corre-
sponding sewers (and definitely not inverts) and the
introduction of online screening manholes at strategic
locations will prove to be useful to ensure better system
hydraulics and facilitate future maintenance of the system,
respectively.
& A set of evaluation parameters have been suggested to
compare similar hydraulic designs of combined sewers with
an aim to standardising such designs, for example,
equivalent diameter (De), pipe utilisation factor (fPU), and
equivalent invert depth (Ie) being the most important ones.
These parameters can very well assess the efficiency of a
hydraulic design produced by comparing these with pre-
determined values or corresponding parameter values of
similar and comparable designs. Such an optimisation
approach is pertinent for any gravity sewer network system.
A reasonably practical and complete procedure for hydraulic
design of a combined sewerage system has been described.
Such calculations are based on design philosophy as described
above. Although approximate, the assumptions are rational
and based on standard hydraulic charts and guidelines. This
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can prove to be useful for designing and detailing either
combined or separate gravity sewer networks.
Faulty, inconsistent and ad hoc design concepts and con-
siderations can potentially jeopardise the philosophy and basic
engineering of sewer hydraulics and subsequent operation of
such an extremely important infrastructure facility especially
under the Indian scenario. This can potentially give rise to
optimistic and under-designed drainage system leading to
flooding of streets (Figure 7). Sewerage and drainage infra-
structure development needs to be carried out following a
standard set of design parameters and specially stipulated
guidelines. Procedures and parameters should be available to
assess the efficacy of design against some standard preset
values. This will eventually ensure consistency in design and
response of various systems under operation. This current
paper is an attempt towards that direction.
AcknowledgementThe author would like to extend his sincere appreciation to
Professor Dr Omer Akgiray (Department Head, Department
of Environmental Engineering, Marmara University, Istanbul,
Turkey), Professor Dr Dennis D. Truax (Department Head,
Department of Civil and Environmental Engineering,
Mississippi State University, USA), Nilangshu Bhusan Basu
(Principal Chief Engineer, Department of Planning and
Development, Kolkata Municipal Corporation, India) and
Parthajit Patra (Consultant, Asian Development Bank) for
their encouragement and support. The contribution of the
author’s past colleagues in development of the hydraulic design
model for sewers in MS Excel is gratefully acknowledged.
Appendix 1
Sample calculations with numerical example
A combined sewer system is designed to carry the combined
flow of SWF and peak DWF. In this hydraulic analysis,
diameters of sewers have been adopted as internal diameter of
the barrel of the RCC pipe, with an n value of 0?013. Columns
in Figure 8 are numbered serially and values given in these
columns for the highlighted row were worked out as a
numerical sample calculation. Table 3 shows sample hydraulic
calculations for a combined sewerage network.
Figure 6. Brick sewer rehabilitation by glass-reinforced plastic
lining. Photograph: courtesy of the Department of Planning and
Development, Kolkata Municipal Corporation
Figure 7. Typical flooding of manhole in urban area. Photograph:
courtesy of the Department of Planning and Development, Kolkata
Municipal Corporation
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Des
ign
flow
, m
3 /s
Upstream
Downstream
Sewage
Storm Run-off
Upstream
Downstream
"qactual"
Upstream
Downstream
Upstream
Downstream
(1)
(2)
(3)
(4)
(5)
(6)
(7)
(8)
(9)
(10)
(11)
(12)
(13)
(14)
(15)
(16)
(17)
(18)
(19)
(20)
(21)
(22)
(23)
(24)
11
1/1
0.1
386.
35.
265
5.38
00.
390
700
550
180.
395
1.03
0.98
81.
070.
8861
33.
500
3.46
71.
765
1.91
32.
050
0.98
01/
11/
11/
20.
138
4.4
5.38
05.
573
0.38
870
055
019
0.39
51.
030.
983
1.07
0.87
610
3.46
73.
433
1.91
32.
140
2.19
81.
128
1/2
1/2
1/3
0.2
391.
65.
573
5.61
20.
396
700
530
110.
402
1.05
0.98
31.
090.
8761
03.
433
3.41
22.
140
2.20
02.
425
1.35
51/
31/
31/
40.
238
9.5
5.61
25.
955
0.39
470
053
021
0.40
21.
050.
978
1.09
0.87
607
3.41
23.
372
2.20
02.
583
2.48
51.
415
1/4
1/4
1/5
0.4
398.
95.
955
6.18
90.
403
700
510
110.
410
1.07
0.98
31.
110.
8761
03.
372
3.35
12.
583
2.83
82.
868
1.79
81/
51/
51/
60.
942
9.8
6.18
96.
310
0.43
570
045
016
0.43
71.
130.
996
1.19
0.88
617
3.35
13.
315
2.83
82.
995
3.12
32.
053
1/6
1/6
1/7
0.9
428.
66.
310
6.11
20.
434
700
450
120.
437
1.13
0.99
31.
190.
8861
63.
315
3.28
92.
995
2.82
33.
280
2.21
01/
71/
72
1.3
449.
16.
112
6.38
30.
455
700
400
130.
463
1.20
0.98
21.
250.
8761
03.
289
3.25
62.
823
3.12
73.
108
2.03
82
22/
11.
344
7.2
6.38
36.
028
0.45
380
082
017
0.46
20.
920.
981
0.96
0.87
696
3.15
63.
135
3.22
72.
893
3.52
22.
332
2/1
2/1
2/2
1.8
475.
06.
028
6.16
50.
482
800
740
210.
486
0.97
0.99
01.
010.
8870
23.
135
3.10
72.
893
3.05
83.
188
1.99
82/
22/
22/
32.
048
1.9
6.16
55.
898
0.48
980
072
013
0.49
30.
980.
991
1.02
0.88
702
3.10
73.
089
3.05
82.
809
3.35
32.
163
2/3
2/3
2/4
2.3
502.
65.
898
6.07
70.
510
800
650
180.
519
1.03
0.98
31.
070.
8769
73.
089
3.06
12.
809
3.01
63.
104
1.91
42/
42/
42/
52.
350
0.1
6.07
75.
435
0.50
880
066
021
0.51
51.
020.
986
1.07
0.87
699
3.06
13.
029
3.01
62.
406
3.31
12.
121
2/5
2/5
2/6
3.3
554.
45.
435
5.38
70.
563
800
540
140.
569
1.13
0.99
01.
180.
8870
13.
029
3.00
32.
406
2.38
42.
701
1.51
12/
62/
62/
73.
656
5.1
5.38
75.
287
0.57
480
052
016
0.58
01.
150.
990
1.20
0.88
702
3.00
32.
973
2.38
42.
314
2.67
91.
489
2/7
2/7
33.
757
1.5
5.28
75.
332
0.58
180
051
018
0.58
61.
160.
992
1.22
0.88
703
2.97
32.
937
2.31
42.
395
2.60
91.
419
33
3/1
3.8
575.
15.
332
5.63
70.
585
900
950
210.
588
0.92
0.99
50.
970.
8879
32.
837
2.81
52.
495
2.82
22.
795
1.49
53/
13/
13/
23.
857
2.4
5.63
75.
660
0.58
290
095
021
0.58
80.
920.
991
0.96
0.88
790
2.81
52.
793
2.82
22.
867
3.12
21.
822
3/2
3/2
3/3
4.4
599.
85.
660
5.90
60.
610
900
860
330.
618
0.97
0.98
81.
010.
8878
82.
793
2.75
52.
867
3.15
13.
167
1.86
73/
33/
33/
44.
459
6.9
5.90
65.
265
0.60
790
086
022
0.61
80.
970.
983
1.01
0.87
785
2.75
52.
729
3.15
12.
536
3.45
12.
151
3/4
3/4
3/5
4.6
603.
85.
265
5.06
90.
614
900
860
210.
618
0.97
0.99
51.
010.
8879
32.
729
2.70
52.
536
2.36
42.
836
1.53
63/
53/
53/
64.
660
1.4
5.06
95.
218
0.61
290
086
018
0.61
80.
970.
991
1.01
0.88
790
2.70
52.
684
2.36
42.
534
2.66
41.
364
3/6
3/6
45.
765
8.1
5.21
85.
169
0.66
490
071
016
0.68
01.
070.
977
1.11
0.87
780
2.68
42.
661
2.53
42.
508
2.83
41.
534
2.96
14
44/
19.
887
8.6
5.16
94.
597
0.89
710
0070
026
0.90
71.
150.
990
1.20
0.88
877
2.56
12.
524
2.60
82.
073
2.92
31.
493
4/1
4/1
4/2
9.9
878.
14.
597
5.27
30.
897
1000
700
270.
907
1.15
0.98
91.
200.
8887
62.
524
2.48
62.
073
2.78
72.
388
0.95
84/
24/
24/
39.
987
7.7
5.27
35.
178
0.89
710
0070
026
0.90
71.
150.
989
1.20
0.88
876
2.48
62.
448
2.78
72.
730
3.10
21.
672
4/3
4/3
4/4
10.1
881.
95.
178
5.29
90.
901
1000
700
290.
907
1.15
0.99
41.
210.
8888
02.
448
2.40
72.
730
2.89
23.
045
1.61
54/
44/
44/
510
.489
1.3
5.29
95.
334
0.91
110
0068
017
0.92
01.
170.
990
1.22
0.88
877
2.40
72.
382
2.89
22.
952
3.20
71.
777
4/5
4/5
4/6
11.1
924.
75.
334
5.16
20.
945
1000
640
340.
948
1.21
0.99
71.
260.
8888
22.
382
2.32
92.
952
2.83
33.
267
1.83
74/
64/
64/
711
.493
3.9
5.16
25.
410
0.95
510
0062
025
0.96
31.
230.
991
1.28
0.88
878
2.32
92.
289
2.83
33.
121
3.14
81.
718
4/7
4/7
4/8
11.6
942.
45.
410
5.41
50.
964
1000
610
250.
971
1.24
0.99
21.
290.
8887
92.
289
2.24
83.
121
3.16
73.
436
2.00
6
Depth of Flow, mm
Clear cover above Pipeline, m
Incoming Invert, m
Depth of Excavation, m
Dep
th o
f Inv
ert,
m
Qfull "Q" in m3/s
Vfull (m/sec) "V"
Sew
er In
vert
Le
vel,
m
Ratio of qactual/Qfull
Vactual (m/sec) "v"
Link
Man
hole
Gro
und
Leve
l, m
Diameter, mm
Slope 1 in
Length, m
Estim
ated
Flo
w,
lps
Ratio of "d/D"
Fig
ure
8.
Snapsh
ot
of
the
pro
pose
ddesi
gn
outp
ut
usi
ng
MS
Exc
el
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Column
no. Information/calculations
(1) 3/6 the no. of the link
(2) 3/6 is upstream manhole/node no.
(3) 4 is downstream manhole/node no.
(4) estimated peak sewage flow for this link is 5?7 l/s
(5) estimated storm water run off for this link is 658?1 l/s
(6) 5?218 m is existing ground level at manhole 3/6
(7) 5?169 m is existing ground level at manhole 4
(8) design flow for this link is calculated by adding columns (4) and (5) 5 5?7 + 658?1 5 663?8 l/s < 0?664 m3/s
(9) diameter of sewer (D) adopted is 900 mm
(10) slope of sewer is taken as 1 in 710
(11) length of this link is 16 m
(12) full capacity of sewer is calculated as Qfull 5 (1/0?013)(3?118 6 1026)(9008/3)(1/710)1/2 5 679?6 l/s < 0?680 m3/s
(13) velocity at full flow is calculated as Vfull 5 (1/0?013)(3?968 6 1023)(9002/3)(1/710)1/2 5 1?068 m/s < 1?07 m/s
(14) ratio of qactual and Qfull is calculated as qactual/Qfull 5 0?664/0?680 5 0?977
(15) from Table 1, ratio of Vactual/Vfull, corresponding to the calculated value of qactual/Qfull (i.e. 0?985), is worked out as
follows considering linear interpolation between terminal values, Vactual/Vfull 5 [1?056 2 (1?020 2 0?977)
{(1?056 2 1?003)/(1?020 2 0?890)}] 5 1?038; this ratio is then multiplied by the value of Vfull in column (13) to obtain
Vactual 5 1?038 6 1?068 5 1?112 m/s < 1?11 m/s
(16) from Table 1, ratio of d/D, corresponding to the calculated value of qactual/Qfull (i.e. 0?985), is worked out as follows
considering linear interpolation between terminal values, d/D 5 [0?90 2 (1?020 2 0?977){(0?90 2 0?80)/
(1?020 2 0?890)}] 5 0?867 < 0?87
(17) depth of flow (d) is calculated by multiplying this value with sewer diameter in column (9)
d 5 0?867 6 900 5 780 mm
(18) upstream sewer invert is calculated similarly in previous row as 2?684 m
(19) downstream sewer invert is calculated by deducting the drop between two terminal manholes of this link from
upstream invert as in column (18) 5 2?684 2 (16/710) 5 2?661 m
(20) depth of upstream invert is worked out by deducting value in column (18) from existing ground elevation in column (6)
5 5?218 2 2?684 5 2?534 m
(21) depth of downstream invert is worked out by deducting value in column (19) from existing ground elevation in column
(7) 5 5?169 2 2?661 5 2?508 m
(22) depth of excavation for upstream manhole is calculated by adding pipe thickness (100 mm), thickness of PCC cradle
below pipe barrel (125 mm), and depth of brick flat soling (75 mm) to depth of invert as found in column (20)
5 2?534 + 0?100 + 0?125 + 0?075 5 2?834 m
(23) clear cover over pipe barrel is calculated by deducting pipe diameter in column (9) and pipe thickness (100 mm) from
depth of upstream sewer invert as in column (18)
5 2?534 2 0?900 2 0?100 5 1?534 m
(24) invert level of incoming sewer converging to this manhole 4 is 2?961 m
Table 3. Step-by-step numerical sample calculation
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