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Drainage Systems · Hydraulic Sizing and Gradient Design

How to Size the Slope of a Stainless Steel Linear Drain: Back-Calculating Minimum Gradient from Self-Cleansing Velocity

Open almost any landscape or industrial yard drainage drawing and you will find the same line: channel invert slope i = 0.5 percent, falling towards the catch pit. The number has been copied for years, and it is very rarely calculated. The result is a familiar kind of rework: the channel is built to 0.5 percent, one rainy season leaves a layer of silt on the invert, and from then on the grates have to be lifted and the channel cleaned by hand every year.

The problem is not that 0.5 percent is too small or too large. It is that 0.5 percent is a standalone number that has never been tied to the cross-section, the water depth or the inflow. The same gradient is generous in a 300 mm wide channel and can be insufficient in a 100 mm one. It works on a trunk run with a large catchment and fails on a short branch that only collects a few metres of pavement.

This article does one thing: it turns gradient back into a quantity you can compute. The only tools required are the Manning equation and one criterion, the self-cleansing velocity. Along the way it produces a counter-intuitive result: in a linear drainage channel the place that silts up first is the inlet end, not the outlet. Every number here can be checked by hand; all formulas and parameter tables are given.

Basis and assumptions: head loss is computed with the Manning equation v = (1/n) times R to the power two thirds times the square root of i, valid for uniform open-channel flow. Stainless steel channel body in clean new condition is taken at n = 0.011; once silt, biofilm or grease has built up, n = 0.013 to 0.015 is used, and the sensitivity analysis in this article spans that range. The silting criterion is a minimum velocity of 0.60 m per second, the order of magnitude given in GB 50014, the Chinese standard for outdoor wastewater engineering, for minimum design velocity in sewers (0.75 m per second is used for storm sewers checked at full flow); this article consistently uses the stricter 0.60 m per second. Design flow follows the rational method Q = psi times q times F, where the runoff coefficient and the rainfall intensity must be taken from the local rainfall intensity formula for the project location; q = 300 litres per second per hectare is used here purely as an illustrative value. Channel geometry is treated as a rectangular open channel: flow area A = B times h, wetted perimeter chi = B + 2h, hydraulic radius R = A / chi, where B is the clear internal width and h the water depth. A linear drain receives lateral inflow along its length and is therefore strictly a gradually varied flow; this article uses the standard step-wise uniform flow approximation (normal depth computed section by section). That approximation is common practice for gentle slopes and moderate inflow, and it is appropriate for establishing trends and orders of magnitude, not as a substitute for the final construction-stage hydraulic check.

1. The threshold that matters: where self-cleansing velocity comes from

A channel moves sediment because the water is fast enough, not because there is a lot of it. Below the threshold, particles settle on the invert; above it, they are repeatedly lifted and carried along. That critical speed is the self-cleansing velocity.

The Chinese code states it plainly: GB 50014 sets a minimum design velocity of 0.60 m per second for sewers, rising to 0.75 m per second when storm sewers are checked at full flow. A linear drain is an open channel and normally runs part full, so adopting the stricter 0.60 m per second is the safe choice.

One clarification matters a great deal later: the criterion applies to the velocity at design flow, not at storm peak. A channel may well hit 1.5 m per second during a cloudburst, but that happens a few times a year. What actually decides whether the invert silts up is the high-frequency small-flow condition: light rain, routine wash-down, road dust. That point becomes decisive in the inlet reach analysis below.

2. Turning an empirical gradient into a computed one: inverting Manning

Uniform open-channel flow is described by the Manning equation:

v = (1/n) · R^(2/3) · i^(1/2)

where v is the mean cross-sectional velocity in metres per second, n is the roughness coefficient, R is the hydraulic radius in metres, and i is the invert gradient, dimensionless. The usual direction is to take a gradient and compute the velocity. We want the reverse: given a velocity that must be achieved, find the gradient required. Rearranging:

i_min = [ v_min · n / R^(2/3) ]²

There is a relationship hidden in this expression that is easy to miss: gradient and velocity are linked by a square. Halve the gradient and the velocity falls only to 1 divided by the square root of 2, about 70.7 percent of its former value. Double the velocity you want and the gradient has to go up fourfold. This is why the site instinct that nudging a slope from 0.3 to 0.4 percent should be enough so often fails when the numbers are actually run.

The geometry of a rectangular channel is simple:

A = B · h  chi = B + 2h  R = A / chi = B·h / (B + 2h)

Note that R is not monotonic in depth alone: it depends on both B and h. What is certain is that at a given flow area, a narrow deep section has a smaller hydraulic radius than a wide shallow one, and conversely, in shallow conditions where h is small, R collapses and the required gradient rises steeply. The next table makes that non-linearity explicit.

3. Worked example one: minimum gradient by section and depth

Taking a clean stainless channel at n = 0.011 and the criterion v_min = 0.60 m per second, here is i_min for several common sections:

Clear width B (mm) Design depth h (mm) Flow area A (m²) Wetted perimeter chi (m) Hydraulic radius R (m) Minimum gradient i_min
300 150 0.04500 0.600 0.07500 0.138 percent (1.38 per mille)
200 100 0.02000 0.400 0.05000 0.236 percent (2.36 per mille)
150 75 0.01125 0.300 0.03750 0.347 percent (3.47 per mille)
200 50 0.01000 0.300 0.03333 0.406 percent (4.06 per mille)
100 50 0.00500 0.200 0.02500 0.596 percent (5.96 per mille)

Three conclusions that can be taken straight to site:

4. The counter-intuitive result: silting happens at the inlet, not the outlet

Everything above assumes the channel is already carrying that much water. But flow in a linear drain accumulates along its length: at the inlet it is essentially zero, and it grows downstream. Writing the lateral inflow rate as q₀, in litres per second per metre of channel, the flow at distance x from the start is:

Q(x) = q₀ · x

Substituting Q(x) into Manning section by section to recover the normal depth h(x) gives the depth and velocity profile along the run. Take a typical case: clear width B = 200 mm, gradient i = 0.35 percent, inflow rate q₀ = 0.5 litres per second per metre, n = 0.011.

Distance from inlet x (m) Flow Q (L/s) Normal depth h (mm) Mean velocity v (m/s) Above self-cleansing?
0.5 0.25 6.8 0.184 No (31 percent of criterion)
1.0 0.50 10.4 0.240 No (40 percent)
2.0 1.00 16.1 0.310 No (52 percent)
5.0 2.50 29.1 0.429 No (72 percent)
10.0 5.00 46.4 0.539 No (90 percent)
14.3 7.15 59.5 0.601 Threshold reached
20.0 10.00 75.7 0.661 Yes
30.0 15.00 102.1 0.735 Yes
40.0 20.00 127.1 0.787 Yes (check depth ratio)

The conclusion is direct: in this channel the first 14.3 m from the inlet never reaches self-cleansing velocity, so that reach will accumulate silt. At 30 to 40 m the velocity is 0.74 to 0.79 m per second, comfortably above what is needed.

This explains a long-standing misreading on site. During cleaning, the reach nearest the inlet always has the most silt, and the usual explanation is that sediment carried in from upstream settles out first. In reality most of that material settled exactly where it is found, because the velocity there never reached the threshold.

4.1 The compliance distance x*: how far before the channel can scour itself

Generalising the table above, define the compliance distance x* as the run length needed from the inlet before the velocity reaches 0.60 m per second. Smaller is better, since it means most of the channel self-cleanses. It depends on both gradient and inflow:

Invert gradient i q₀ = 0.3 L/(s·m) q₀ = 0.5 L/(s·m) q₀ = 0.8 L/(s·m)
0.20 percent 52.4 m 31.4 m 19.6 m
0.35 percent 23.8 m 14.3 m 8.9 m
0.50 percent 16.0 m 9.6 m 6.0 m
1.00 percent 8.2 m 4.9 m 3.1 m

Read this table in the right direction: the higher the inflow rate, the shorter the compliance distance, so a channel that receives more water is less likely to silt. The high-risk objects are therefore branch channels with a small catchment, not trunk runs. That is the opposite of what most people assume.

The engineering response follows directly. If a channel's x* approaches or exceeds its own length, no part of that channel can scour itself and it will always need manual cleaning, unless the design changes: steepen the inlet reach, shorten the run, or start the channel at a catch pit so the inlet reach carries little or no flow.

5. Where the inflow rate q₀ comes from

So far q₀ has been treated as given. It is set by the catchment and the design rainfall, through the rational method:

Q = psi · q · F  q₀ = Q / L

where psi is the runoff coefficient, q the design rainfall intensity in litres per second per hectare, F the catchment area in hectares, and L the channel length in metres.

An example: a channel of length L = 30 m with a pavement catchment width of 12 m gives F = 30 times 12 = 360 m² = 0.036 hectares; asphalt or concrete paving takes psi = 0.90; assume a local design rainfall intensity q = 300 litres per second per hectare (illustrative only; the real value must come from the local rainfall intensity formula).

Referring back to the previous table: at i = 0.35 percent and q₀ = 0.3, the compliance distance is 23.8 m. This channel is 30 m long, so roughly 80 percent of its length sits below self-cleansing velocity. That is exactly how a drawing can be code-compliant while the channel still silts up.

Typical runoff coefficients for estimating purposes (final values should follow the local planning or design institute practice):

Surface type Runoff coefficient psi Note
Roofs, asphalt or concrete paving 0.90 ~ 0.95 Hard surface, essentially impermeable
Setts, jointed paved plazas 0.60 ~ 0.80 Higher value where joints are sand-filled
Unpaved earth surfaces 0.30 ~ 0.40 Common during construction
Lawns and planted areas 0.15 ~ 0.20 Sunken green space needs sponge-city reduction

6. The other end: gradient is not free, and available fall sets the maximum run

If a steeper gradient helps, why not build the whole line at 1 percent? Because gradient consumes vertical level, and the level a site can give is usually fixed. The downstream end has to connect to a catch pit or a municipal manhole; the upstream end is constrained by the pavement level. The difference between the two is the available fall, and it caps the run length outright:

L_max = available fall / i
Available fall Maximum run at i = 0.35 percent Maximum run at i = 0.50 percent
50 mm 14.3 m 10.0 m
100 mm 28.6 m 20.0 m
150 mm 42.9 m 30.0 m
300 mm 85.7 m 60.0 m

Choosing a gradient is therefore a three-way trade. Steeper: better self-cleansing, but shorter runs, more catch pits, higher cost. Flatter: longer runs, but a silting inlet reach. The design task is not to pick a standard value but to balance i against L within the fall that the site can actually give.

Three standard ways out when the required run exceeds L_max:

  1. Intermediate drop manholes. Split the long run into two, each consuming its own share of the fall, with energy dissipation at the drop. The most common solution.
  2. Stepped gradient. Make the inlet reach steep, say 1.5 percent over the first 5 m, which drives x* down sharply, then ease back to 0.35 percent downstream. This targets inlet silting directly and works best, but it demands manufacturing precision, which is the subject of section 8.
  3. Reduce the channel width. For a given flow, a narrower channel raises both depth and hydraulic radius, but the depth ratio and the grate intake capacity must be rechecked, and narrow channels are less tolerant of construction tolerance.

7. Section shape: why a V-bottom performs better at low flow

Collecting the same 0.5 litres per second on the same 0.35 percent gradient gives quite different results depending on the shape of the invert. Compare a 90-degree V-bottom (a triangular section with zero base width) against a 200 mm flat-bottomed rectangle:

Section Flow Q (L/s) Depth h (mm) Flow area A (m²) Mean velocity v (m/s)
Flat rectangle, B = 200 mm 0.50 10.4 0.00208 0.240
V-bottom, 90-degree 0.50 39.9 0.00159 0.314

At the same small flow the V-bottom lifts the velocity from 0.240 to 0.314 m per second, about 31 percent more. The reason is that at low flow a flat channel spreads the water very thin, 10 mm here, and the hydraulic radius is dragged down by the shallow depth; the V-bottom concentrates the same water at the channel centreline, giving greater depth and a relatively smaller wetted perimeter, hence a better hydraulic radius.

That advantage is not free, and two costs must be stated with it:

That is why the common arrangement is V or U bottoms on branches and flat bottoms on trunk runs, rather than one section throughout.

8. Roughness degrades: the smooth stainless advantage is not permanent

Stainless channels are often sold on a smooth inner wall that resists fouling, which is true when new: clean stainless can be taken at n = 0.011, clearly better than concrete at 0.013 to 0.014. But that advantage degrades in service, as silt, biofilm and grease build up a rough layer on the wall.

For B = 200 mm, h = 100 mm, i = 0.50 percent, here is what roughness does to capacity:

Roughness n Velocity v (m/s) Capacity Q (L/s) Relative to clean Condition
0.010 0.960 19.2 110 percent New, very clean
0.011 0.872 17.4 100 percent Clean new stainless (design value)
0.013 0.738 14.8 85 percent Light fouling
0.015 0.640 12.8 74 percent Heavy fouling, close to the criterion

The last row is the dangerous one: at n = 0.015 the velocity of 0.640 m per second is close to the 0.60 m per second criterion. A channel that was only just adequate when calculated in the clean condition can, after two or three years of service, fall below self-cleansing velocity altogether and enter a positive feedback loop where more silt means more roughness and more roughness means more silt. This is why a margin is essential at design stage: we normally recommend checking against the in-service roughness of 0.013 rather than the new-wall value of 0.011, which raises the required gradient by roughly 40 percent.

The maintenance implication is equally concrete. Periodic high-pressure washing is not cosmetic; it is what restores the roughness to the design value. Washing n back from 0.015 to 0.013 recovers about 15 percent of the channel's capacity, which is an argument that can be made to a client in numbers.

9. Manufacturing and installation: how the gradient actually gets built

A computed gradient still has to survive contact with the channel body and the bedding. Three stages routinely destroy the design intent.

9.1 A stepped gradient must be prefabricated, not found on site

The steep-inlet, flat-downstream arrangement from section 6, if left to an in-situ screed, usually comes out as a discontinuous wavy invert: each unit is levelled independently and the joints end up as adverse slopes that pond water upstream. An adverse slope is worse than an insufficient one, because it creates a permanently standing length.

The workable approach is to build the gradient into the channel itself. Design the run in segments and prefabricate each segment to its own gradient in the factory, so the invert is a plane and the difference in level between the two ends is that segment's fall; site work then only has to install the segments in numbered order. Stainless has a clear advantage here: folding and welding are done under factory control and the fall can be held to millimetres, whereas an in-situ screed rarely achieves it.

9.2 Tolerance on joint step

Level differences at joints between adjacent units break hydraulic continuity. The practical control is a step of no more than 1 mm in the direction of flow, and no reverse step at all, since a downstream unit sitting higher than its upstream neighbour becomes a small dam. Levelling must be referenced to the invert, not to the top of the grate, because grate thickness tolerance will mask the true invert difference.

9.3 Catch pits and silt capture

Since inlet-reach silting is mathematically unavoidable, give it somewhere to go. On long runs, provide a catch pit with a silt bucket at the inlet end or every 20 to 30 m, so the sediment that must settle has a place to settle, and cleaning means lifting the bucket rather than lifting the whole run of grates. Size the bucket on the expected silt volume, generally not less than 0.05 cubic metres, and fit a basket that can be lifted out complete.

10. Checklist you can use on site

Stage Check Criterion
Design flow Q = psi·q·F, convert to q₀ = Q/L q from the local rainfall intensity formula, never an imported value
Minimum gradient i_min = [v_min·n / R^(2/3)]², checked at in-service roughness v_min = 0.60 m/s; use n = 0.013 in service, not 0.011 new
Inlet reach Back-calculate x* and compare with run length x* should be one fifth of the run or less; otherwise steepen or shorten
Maximum run L_max = available fall / i Beyond it, add a drop manhole or step the gradient
Depth ratio Check downstream depth against channel depth Keep below 0.75 in open reaches; check storm flow separately
Invert geometry Survey invert levels segment by segment, plot the long section No adverse slope; step in flow direction 1 mm or less
Silt facilities Silt bucket volume and lift-out access At least 0.05 cubic metres per bucket, liftable complete
Maintenance access Wash-down points, grate removal Provide a wash point every 20 to 30 m on long runs

In one sentence: gradient is not a copied 0.5 percent, it is i_min = [v_min·n / R^(2/3)]² computed from the section, and because flow accumulates along the channel as Q(x) = q₀·x the inlet reach never reaches self-cleansing velocity, so a linear drain silts at the start rather than the end, while the available fall caps the run at L_max = fall over slope. Design against the in-service roughness of 0.013 rather than the new-wall 0.011, or the whole channel drops into the silt-and-roughness feedback loop within a few years.

Frequently asked questions

What gradient should a linear drainage channel have?

There is no universal value; it must be back-calculated from the section and the actual water depth. Inverting Manning gives i_min = [v_min·n / R^(2/3)]². With a self-cleansing velocity of 0.60 m per second and an in-service stainless roughness of n = 0.013, a 200 mm clear width at 100 mm depth needs about 0.33 percent (0.236 percent if calculated at the new-wall value of 0.011, but the in-service margin is advisable), and the same width at only 50 mm depth needs about 0.57 percent. The familiar 0.5 percent holds only for medium sections at medium depth and is clearly insufficient below 150 mm width or in low-flow conditions.

Why does the channel silt up at the inlet rather than the outlet?

Because flow accumulates along the length of a linear drain, so the flow at the inlet is close to zero. With a lateral inflow of q₀ litres per second per metre, the flow at distance x is Q(x) = q₀·x, and substituting that into Manning section by section gives a velocity that rises monotonically with x. For a 200 mm clear width at i = 0.35 percent and q₀ = 0.5 litres per second per metre: at x = 1 m the depth is only 10.4 mm and the velocity 0.240 m per second, and the velocity does not reach 0.601 m per second until 14.3 m. Everything in the first 14.3 m is below self-cleansing velocity, so sediment settles there. Branch channels with small catchments, where q₀ is small, have a longer compliance distance and are at higher risk than trunk runs.

Stainless is smooth inside, so is silting still a concern?

Yes, and this is a common misconception. Clean new stainless can be taken at n = 0.011, better than concrete at 0.013 to 0.014, but silt, biofilm and grease in service push the roughness to 0.015. For a 200 mm channel at 100 mm depth and i = 0.50 percent: at n = 0.011 the velocity is 0.872 m per second carrying 17.4 litres per second, while at n = 0.015 it is 0.640 m per second carrying 12.8 litres per second, close to the 0.60 m per second criterion. Check against the in-service roughness at design stage, and treat periodic high-pressure washing as roughness restoration, since returning n from 0.015 back to 0.013 recovers roughly 15 percent of capacity.

Want your channel run calculated?

Send us the clear width, channel depth, run length, available fall, catchment area and local rainfall intensity, and we will return the minimum gradient i_min, the compliance distance x*, the maximum run L_max, and a segment-by-segment fabrication table for a stepped-gradient channel.

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