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Performance requirements for traps in drainage systems

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NATIONAL RESEARCH COUNCIL OF CANADA D I V I S I O N OF BUILDING RESEARCH

PERFORMANCE REQUIREMENT5 FOR TRAPS I N DRAINAGE SYSTEMS by

R.K.

B e a c h

DBR P a p e r N o . 6 7 0

O t t a w a M a r c h 1976

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PERFORMANCE REQUIREMENTS FOR TRAPS IN

DRAINAGE SYSTEMS

by

R.K.

Beach

ABSTRACT

Current plumbing code requirements,

behaviour of trap seals and related

research are reviewed and revisions to

plumbing code requirements suggested.

LES EXIGENCES FONCTIONNELLES DES SIPHONS

DANS LES SYSTEMES DE DRAINAGE

par

R. K. Beach

RESUME

Les auteurs passent en revue les

exigences actuelles des codes de plomberie,

le comportement des garde-eaux ainsi que

les recherches connexes, et proposent des

modifications aux exigences des codes de

plomberie.

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PERFORMANCE REQUIREMENTS FOR TRAPS IN DRAINAGE SYSTEMS

R.K. Beach

A

sanitary building drainage system is required to carry

waste from plumbing fixtures to the public sewer or a private sewage

disposal system without permitting foul air to escape into the building,

This is achieved by means of water seal traps, which are either integral

with the fixtures or installed as close as is practical to the outlet from

the fixtures. At one time traps were also installed on the sanitary

building drain to prevent sewer air from entering the drainage system, but

most plumbing codes now prohibit or advise against them because they create

undesirable positive pressure conditions in the system and add to its cost.

Several factors affect the performance of traps in drainage

systems, principally self-siphonage, induced siphonage and evaporation.

As the first two depend on the air pressure in the drainage system, the

venting system must be considered in conjunction with traps, and vice

versa.

CONSEQUENCES

OF A TRAP SEAL FAILURE

A

factor that ought to be considered is the quality of the air

in the drainage system. Is it a health hazard or just an unpleasant

nuisance? When the water-borne system of handling night soil was

introduced in the late 18001s,

it was believed that sewer gas was harmful

to health. Although accidental deaths may still occur, such as the recent

asphyxiation of a man and a boy while cleaning a septic tank, some men, of

necessity, are required to work indefinitely in areas where there is a

concentration of sewer gas. They do so without apparent ill effect.

In the early 19501s,

when research work was being carried out

on the performance of traps, this subject was investigated (1,

2).

The

same conclusion was reached in both cases: that sewer gas does not

transmit disease and that its composition differs little from that of

outside air. Consequently, accidental discharge of air from a drainage

system into a building is not likely to cause anything more than the

annoyance of a temporary odour problem. There is no need to provide as

large a factor of safety in the system design as there would be if the

air in a drainage system presented a serious hazard to health.

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TERMINOLOGY

AND

TYPES OF TRAP

It is well known that the configuration of a trap has an effect

on its performance or operating characteristics. The three principal

configurations are illustrated in Figure.1,

which includes a diagrammatic

presentation of the terminology used in this paper. In particular, it

should be noted that the term, trap seal depth, always refers to the

vertical distance between the trap dip and the trap weir. It is clear that

each of the three types of trap will experience a different trap seal loss

or have a different trap seal retention if subjected to the same suction

pressure. Except for water closets, the most common type of trap is the

tubular trap, which has the same diameter throughout. Most research to

date has made use of this type because it simplifies investigations

considerably. The present paper also uses the tubular trap as the basis

for discussion, but the recommendations are applicable to all types of

trap.

Depending upon its location in the drainage system, a trap will

usually be subjected to either predominantly positive pressures or

predominantly negative pressures, but not to both. The effect on its

water seal will be different for the two cases because of the presence of

the trap weir on the downstream leg.

EFFECT OF POSITIVE PRESSURES

Consider the trap shown in Figure 2(a).

It is located in a

positive pressure zone and has a seal depth of

Z

in. The air pressure on

each side of it is equal to the atmospheric pressure, pa. When the air

pressure in the trap arm rises to pa

+

Ap owing to discharge of fixtures

elsewhere in the system, the water rises in the fixture side of the trap

until the water column, h, just balances the increase in pressure Ap

(Figure 2(b)).

As the trap has a uniform cross-section, the trap seal

depression in the downstream leg is equal to the rise of water in the

upstream leg. The change in water level in each leg, h/2, is therefore

equal to Ap/2. (This simple U tube relation really does not hold true if

one water level is near the trap weir or trap dip where the horizontal

cross-sectional area changes slightly. The difference is small, however,

and for practical purposes it can be ignored.)

When Ap and h increase to the point where they are equal to 22,

(i.e., h/2

=

Z)

a tubular trap has reached its limit of protection

against positive pressure. (This statement does not hold true for the

other types of trap shown in Figure 1; there are significant differences

in the size and volume of their upstream and downstream legs.) A slight

overpressure is required to form air bubbles and to force them past the

trap dip; if this happens a trap seal failure is deemed to have occurred.

When the pressure in the drainage system returns to atmospheric,

the water will drain back into the trap and tend to return to the original

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seal height Z.

A

small quantity of water, however, will adhere to the

sides of the trap and the fixture outlet pipe and will eventually

evaporate. There is the further possibility that if the positive pressure

is suddenly reduced to zero or to a negative value the momentum of the

falling water in the trap will be sufficient to carry some of it over the

trap weir. In practice, the amount of water lost by these occurrences

will be very small and will not normally cause a problem.

EFFECT OF NEGATIVE PRESSURES

The effect of negative (suction) pressure on a tubular trap is

shown in Figure 3. If a full trap (Figure 3(a))

is subjected to a steady

suction pressure Apl, the water level in the upstream leg is depressed by

atmospheric pressure pa and water is forced over the trap weir and lost

down the drainage system. This will continue until the difference in the

water level, hl, just balances the suction pressure Apl (Figure 3(b)).

When the pressure in the drainage system returns to atmospheric pressure,

the trap will be found to have suffered a trap seal loss

!tl

equal to

h1/2 (Figure 3(c)).

From this it may be seen that a tubular trap will

prevent room air from bubbling into the drainage system as long as the

steady suction pressure is less than the trap seal depth t, or twice the

height of the trap seal retention

Z, whichever is less.

If the trap

in

Figure 3(d) is then subjected to a steady

suction pressure Ap2 larger than t, water will be lost over the trap

weir and air will bubble past the trap dip. This air replaces water in

the downstream leg and this also is lost over the trap weir. The total

amount of water 22 that can be lost in this manner is indicated in

Figure 3(e), but it is highly variable, depending on the diameter of the

trap, its trap seal retention at the start, the magnitude of the suction

pressure and its steadiness and length of application.

PERFORMANCE CHARACTERISTICS OF TRAPS

The performance characteristics of traps in drainage systems

have been studied in Denmark (3) and Belgium (4) and are currently under

study at the Division of Building Research, National Research Council of

Canada. Because of the characteristics of the traps, test methods, and

pressures used in Europe, however, the information gained there can only

be related to North American practice in a general way.

One European test consists of suddenly applying a negative

pressure to the downstream side of the trap and measuring the trap seal

loss after suction pressure has been removed. The test is repeated

without refilling the trap and the results are plotted as shown in

Figure 4. Curve I11 is of particular interest. It shows the sudden

increase in trap seal loss that occurs once bubbling has started. With

a test pressure of -1.68 in. (-420 ~ / m ~ )

water column the test had to

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would have been required if the differential test pressure had been

smaller and fewer if the pressure had been larger. It is important to

note that the suction pressure used in the tests was ap lied suddenly and

Y

that it was considerably higher than the 1-in.

(250

N/m

)

negative

pressure that could be expected in a North American system. It can be

deduced that any trap that has a performance curve with a very small

decrease in trap seal after the first one or two tests will probably

perform satisfactorily; and that the performance of a trap in a drainage

system can be determined by repeating the test only two or three times.

The latter is an important practical consideration.

DRAINAGE SYSTEM CHARACTERISTICS

The entry of air into a drainage system is not a problem except

for the noise that may be caused by bubbling. Once bubbling into the

system has occurred, the trap will have a reduced capacity to provide

protection from positive pressure since it will have lost a significant

amount of seal. Fortunately, the characteristics of flow in a stack are

such that a negative pressure tends to exist throughout the stack,

except near the bottom. Here, as a result of change in the direction of

flow, from vertical to horizontal, a positive pressure usually exists.

The pressure gradient in a stack is fairly smooth, with a large increase

in negative pressure occurring immediately below the fitting where waste

enters the stack.

A

typical stack pressure gradient for a British single-stack

system is shown in Figure 5 (5). It is similar to that found in North

American systems. The point where the pressure in a stack changes from

negative to positive is indefinite, but it is always close to the base of

the stack. The important thing is that although the pressure at a

particular point in the stack will vary with flow, it will not normally

change from a negative to a positive value, or vice versa, except near

the point where the pressure is close to atmospheric. Thus a trap

subjected to a large negative pressure may experience a large seal loss,

but it is very unlikely that it will subsequently be subjected to a large

positive pressure that could cause trap seal failure.

BEHAVIOUR

OF

TRAPS

The behaviour of individual traps with either full seal or

reduced seal must be considered. It is known that positive pressure in

a drainage system will not normally cause loss of seal, but that negative

pressure and evaporation will. If the negative pressure acting on

a

trap

is caused by discharge from the trap itself, it is called self-siphonage;

if caused by the discharge of other fixtures, it is called induced

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Se

1

f

-

Siphonage

The phenomenon of self-siphonage can be explained by reference

to Figure 6. Discharge from a fixture such as a lavatory consists of

air and water; the two pass through the trap into the trap arm in such a

way that slugs of water, or water and air, often fill the entire cross-

section of the trap arm at points along its length (Figure 6(a))

;

that is,

full-bore flow occurs intermittently in the trap arm. If such a slug is

present in the trap arm near the end of the discharge period (Figure 6(b)),

it produces a suction behind itself as it moves towards the stack. This

suction may draw air through the trap and water out of it, as with

induced siphonage.

As the last slug of water moves towards the stack, water

sloughs off both ends of the slug. Some from the trailing end flows back

towards the trap (Figure 6(c)).

Water remaining in the trap aids this

refill by applying a negative pressure equal to the difference in height

of water in the two legs of the trap. If the slug is close to the trap,

the backflow of water may be sufficient to refill it. If the slug is

too far down the trap arm, however, the backflow will not reach the trap

and the result will be a trap that is only partially filled (Figure 6(d)).

Slug action depends primarily on the length and slope of the

trap arm.

A

trap arm set at a low slope tends to produce maximum

refilling of the trap. The S trap, which is usually not permitted

because it is highly susceptible to self-siphonage, shows the effect of

a trap arm that can be considered to have either zero length or an

infinite (vertical) slope. Increasing the diameter of the trap arm has

the effect of reducing the chance of self-siphonage, but this is variable

and depends on where the enlargement occurs. It has the further

advantage of increasing the permissible length of the trap arm.

Another significant source of water for refilling a trap is

the trail discharge from the fixture. Its size depends primarily on the

area and slope of the bottom of the fixture; the hydraulic characteristics

of the fixture outlet, strainer, and fixture outlet pipe have a secondary

effect. Whether a trap is susceptible to self-siphonage in a particular

installation, therefore, depends on the characteristics of the fixture

and the actual arrangement of the piping.

Induced Sinhonaee

Induced siphonagc is the mechanism whereby the operation of a

fixture or fixtures elsewhere in a system creates a negative pressure

that reduces the water seal in idle traps. Because of minor variations

in manufacture or installation the effect of the same induced siphonage

will vary slightly from trap to trap. In a particular installation one

trap will tend to be more susceptible to failure than others, and when

it does fail it will tend to protect the remaining traps by relieving

the negative pressure in the system.

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EVAPORATION

If a trap remains idle it becomes more susceptible to induced

siphonage as it slowly loses its seal by evaporation, the total loss

depending on the rate of evaporation and the period of idleness. Both

are highly variable, but only the rate of evaporation lends itself to

investigation. A study carried out at the Building Research Station (1)

in England reports an evaporation rate of 0.15 in. per week for a

1-114-in. diameter trap with both legs exposed to room air whose

temperature varied between 55 and 70.'~.

This corresponds to a rate of

about 0.08 in. per week where only one leg of the trap is exposed to

room conditions. In the USA, the Housing and Home Finance Agency carried

out

a similar program that produced essentially the same results

(2).

The American publication includes a method of estimating

evaporation rate based on trap size, length of fixture outlet pipe, air

temperature, and relative humidity. Vertical tubes and open traps were

used so that, as for the British study, the test installations did not

simulate actual installations very closely. Reference is made to the

very low rates of evaporation reported by other workers and a comment is

included that the actual evaporation rate may be less than that determined

by the U.S. method. A lower rate can be readily attributed to the

presence of strainers and mechanical wastes, which tend to restrict room

air movement over the exposed water surface.

In the UK an evaporation rate of 0.1 in. per week is presumed,

and this seems to incorporate a safety factor of about 1.25. As the rate

of evaporation is highly variable, the same rate of evaporation, 0.1 in.

per week, is tentatively recommended for use in North America. Where

fixtures are expected to be subjected to long periods of idleness, either

deep-seal traps or anti-siphon type traps can be used to provide added

protection from loss by evaporation.

TESTING

OF TRAPS

After the performance requirements for traps have been fixed

there remains the matter of testing. It may be classified according to

its purpose as follows:

-

laboratory tests to establish the characteristics of a trap and

determine whether it meets the requirements of the appropriate product

standard

,

and

-

site tests to prove out

(i) the complete

DWV (drain, waste, vent) system with regard to

control of pneumatic pressure variations within the system, and

(ii) the installed trap and its related piping with respect to

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It is relatively easy to establish suitable test methods, but

it is not so easy to determine the number of times the test must be

repeated to determine trap performance. As has been mentioned, only

three repeated tests are needed to establish the performance of a trap

subjected to the laboratory test procedure, and this would normally form

part of the product standard. It is not so easy to establish whether

three repeated tests are sufficient to establish the performance

characteristics of a trap installed in a drainage system. In this case

the suction test load is produced by discharging fixtures in the system.

The number to be discharged should be determined on the same basis as

that for establishing the sizing tables used in designing the system and

contained in present plumbing codes. Owing to slight variations in

fixtures and traps caused by the manufacturing process and the difficulty

of repeating practical tests exactly, some variation in the individual

test loads and results can be anticipated, but it should not be

sufficient to obscure the difference between acceptable and unacceptable

performance.

Another factor with a significant effect on the results of a

test is the location of the fixtures that are discharged. It is common

practice to select for testing fixtures that will apply the severest

load on the system, generally those furthest upstream. Although a

system must be able to withstand one application of a load of this nature,

for it to withstand repeated applications without trap refill is a very

severe requirement. The probability that specific fixtures will be found

in operation together is considerably less than the probability that an

equal number of any of the fixtures will be found in operation. It is

suggested, therefore, that repeating the test three times without trap

refill, using fixtures that apply the severest load, will establish

whether the performance of the traps in a drainage system is adequate.

CURRENT REQUIREMENTS FOR TRAPS

The Canadian Plumbing Code 1975 (6) requires that traps have a

minimum trap seal depth of 1-1/2 in. Most traps used in Canada, however,

are manufactured to conform to the standards of the Canadian Standards

Association and these generally require a trap seal depth of at least

2

in. The trap seal depth generally varies with the size, radius of

curvature of the flow path, and the manufacturing process. In North

America, traps for small fixtures are usually found to have a trap seal

depth of between 2 and

3

in.

Current plumbing codes in Great Britain call for a minimum

trap seal depth of

2

in., but the British Standard Code of Practice (7)

states that traps

2

in. or less in diameter should have a trap seal depth

of at least

3

in. This difference originated many years ago when the

British changed from the two-pipe system of separate soil and waste

stacks to the one-pipe system, so named because it uses the same pipe for

both soil and waste (as in North America).

Both the two-pipe and one-pipe

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d i s p e n s e s w i t h t h e i n d i v i d u a l d r y v e n t and v e n t s t a c k g e n e r a l l y used i n North America and uses t h e s o i l - o r - w a s t e s t a c k t o f u l f i l b o t h d r a i n a g e and v e n t i n g f u n c t i o n s .

The o l d B r i t i s h two-pipe system used t r a p s w i t h 1 - 1 / 2 - i n . t r a p s e a l depths i n t h e waste system and w a t e r c l o s e t s w i t h 2 - i n . t r a p s e a l d e p t h s i n t h e s o i l system. The B r i t i s h were r e l u c t a n t t o permit t r a p s w i t h a 1-1/2-in. t r a p s e a l depth i n t h e new one-pipe system and i t was s u g g e s t e d t h a t t h e minimum t r a p s e a l depth should be 3 i n . The c o s t o f r e d e s i g n i n g water c l o s e t s was c o n s i d e r e d t o b e s o g r e a t , however, t h a t t h e y agreed t o r e q u i r e o n l y t h e s m a l l - d i a m e t e r t r a p s used i n o n e - p i p e . systems t o have a 3 - i n . t r a p s e a l d e p t h . When t h e s i n g l e - s t a c k system was i n t r o d u c e d t h e t r a p s e a l requirements o f t h e one-pipe system were r e t a i n e d .

Model plumbing codes i n t h e USA follow t h e recommendations o f t h e Subcommittee on Plumbing of t h e B u i l d i n g Code Committee (8) t h a t 'IEvery f i x t u r e t r a p s h a l l have a w a t e r s e a l o f n o t l e s s t h a n 2 i n . and n o t more t h a t 4 i n . " T h i s i s r e l a t e d t o recommendations t h a t s e l f - s i p h o n a g e and induced siphonage b e l i m i t e d t o a l o s s o f 1 i n . and t h e maximum

p e r m i t t e d p r e s s u r e v a r i a t i o n i n t h e system t o +1 i n . o f w a t e r column. I t was c o n s i d e r e d t h a t a t r a p which l o s t 1 i n . o f s e a l by s e l f - s i p h o n a g e c o u l d s t i l l w i t h s t a n d an a p p l i e d p r e s s u r e of +2 i n . o f w a t e r column and hence had a s a f e t y f a c t o r o f 2. For a t r a p t o be s u b j e c t e d t o such a p r e s s u r e , however, t h e v e n t i n g system must have f a i l e d t o l i m i t t h e p r e s s u r e t o w i t h i n t h e + l - i n . r a n g e . The wording of t h e r e q u i r e m e n t s have changed i n t h e USA o v e r t h e y e a r s and i t i s now o f t e n e x p r e s s e d a s ' T r a p s e a l r e t e n t i o n s h a l l b e a t l e a s t 1 i n . o r one h a l f o f t h e t r a p s e a l d e p t h , whichever i s g r e a t e r " . Although t h i s c o v e r s t h e u s e o f t r a p s w i t h t r a p s e a l d e p t h s g r e a t e r t h a n 2 i n . , i t i s i n c o n s i s t e n t w i t h t h e

requirement t h a t t h e v e n t i n g system l i m i t t h e p r e s s u r e t o a r a n g e o f

+1 i n . o f w a t e r column.

PERFORMANCE REQUIREMENTS OF VENTING SYSTEMS

The performance requirements of t r a p s and v e n t p i p e s i n a s a n i t a r y d r a i n a g e system a r e dependent on each o t h e r , t h e common f a c t o r b e i n g t h e v a r i a t i o n i n pneumatic p r e s s u r e t h a t o c c u r s i n t h e d r a i n a g e p i p i n g . I n g e n e r a l terms, t r a p s a r e r e q u i r e d t o p r e v e n t t h e p a s s a g e o f a i r from t h e d r a i n a g e system i n t o t h e b u i l d i n g when t h e p r e s s u r e i n t h e system i s w i t h i n t h e d e s i g n range; t h e v e n t i n g system i s r e q u i r e d t o

l i m i t t h e p r e s s u r e v a r i a t i o n i n t h e d r a i n a g e system t o t h a t a l l o w a b l e

r a n g e .

C u r r e n t plumbing codes a r e i n v a r i a b l y o f t h e s p e c i f i c a t i o n t y p e , a l t h o u g h t h e y a r e o f t e n c o n s i d e r e d t o be d e s i g n manuals. A s has been p o i n t e d o u t by Hunter ( s e e Ref. 8, p. 142) "with any r u l e s t h a t may be a p p l i e d g e n e r a l l y with s a f e t y , many p l a c e s w i l l b e found where we could go beyond t h e limits s t a t e d i n t h e r u l e s w i t h p e r f e c t s a f e t y were t h e r e a competent a u t h o r i t y t o p r e s c r i b e t h e limits f o r t h e c o n d i t i o n encountered." The e x p e r i e n c e o f t h e p a s t 40 y e a r s h a s p l a c e d t h o s e

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i n v o l v e d i n a b e t t e r p o s i t i o n t o a s s e s s c o n d i t i o n s under which r i g i d r u l e s can be r e l a x e d s a f e l y . This i s r e f l e c t e d i n t h e changes t h a t have been made i n c u r r e n t plumbing codes and t h e d e s i r e t o move d e s i g n

d e t a i l s o u t o f codes i n t o supplementary d e s i g n manuals, t h e d e t a i l e d requirements t o be r e p l a c e d by performance requirements.

Without b e i n g i d e n t i f i e d a s s u c h , s e l f - s i p h o n a g e and induced siphonagc a r e u s u a l l y covered i n c u r r e n t plumbing codes i n t h e s e c t i o n on v e n t i n g . The requirements governing s e l f - s i p h o n a g e and induced siphonage a r e based on o r i g i n a l r e s e a r c h by Hunter and by o t h e r s a t t h e National Bureau o f S t a n d a r d s ( 8 ) . I n making h i s recommendations concern- i n g s e l f - s i p h o n a g e Hunter c o n s i d e r e d many f a c t o r s , i n c l u d i n g p o s s i b l e f o u l i n g o f t h e p i p i n g , t h e shape o f t h e bottom o f t h e f i x t u r e , and t h e f a c t t h a t t h e Subcommittee had agreed t h a t t h e l o s s of s e a l from a t r a p with a s e a l d e p t h o f 2 i n . should n o t exceed 1 i n . I n g e n e r a l , H u n t e r ' s o r i g i n a l recommendation was t h a t t h e maximum l e n g t h o f a t r a p arm

s h o u l d b e 6 f t , e x c e p t f o r washbasins and s i m i l a r l y shaped f i x t u r e s where i t s h o u l d b e 4 f t . The U.S. Department o f Commerce Subcommittee on Plumbing s u b s e q u e n t l y a g r e e d on a maximum l e n g t h o f 5 f t f o r a l l t r a p arms.

F u r t h e r r e s e a r c h i n t o s e l f - s i p h o n a g e c a r r i e d o u t a t t h e N a t i o n a l Bureau o f S t a n d a r d s (9) h a s provided a n e n g i n e e r i n g b a s i s f o r

d e t e r m i n i n g t h e maximum t r a p arm l e n g t h . The C o o r d i n a t i n g Committee r e s p o n s i b l e f o r t h e p r e p a r a t i o n o f t h e American Standard N a t i o n a l Plumbing Code, ASA-A40.8, c o n s i d e r e d t h e r e p o r t b u t a p p a r e n t l y d i d n o t f i n d t h e e n g i n e e r i n g approach s u i t a b l e f o r i n c l u s i o n i n t h e code. I n s t e a d a simple t a b l e was adopted o f l e n g t h v e r s u s f i x t u r e d r a i n d i a m e t e r t h a t would be s a f e f o r a l l i n s t a l l a t i o n s . T h i s t a b l e , which may be found i n most American model plumbing codes, i s more r e s t r i c t i v e t h a n t h e p r e s e n t Canadian requirement f o r f i x t u r e d r a i n s w i t h s m a l l

d i a m e t e r s b u t l e s s r e s t r i c t i v e f o r t h o s e w i t h l a r g e d i a m e t e r s . A c t u a l l y , b o t h t e n d t o be o v e r l y r e s t r i c t i v e and d e a l w i t h o n l y one of s e v e r a l

e q u a l l y i m p o r t a n t f a c t o r s t h a t a f f e c t t r a p s e a l l o s s due t o s e l f - s i p h o n a g e . More work i s r e q u i r e d i n t h i s a r e a , i n p a r t i c u l a r i n developing a

p r a c t i c a l d e s i g n method based on t h e f i n d i n g s of BMS 126 ( 9 ) , and t h e recommendations c o n t a i n e d i n t h i s p a p e r a r e a s t e p i n t h a t d i r e c t i o n . The p r o p o s a l s p r o v i d e a n e a s i n g o f t h e dimensional requirement w h i l e m a i n t a i n i n g t h e s a f e t y of t h e system. T h i s , f o r t h e owner, means g r e a t e r

freedom i n t h e l a y o u t of f i x t u r e s and reduced c o n s t r u c t i o n c o s t s .

Induced siphonage, which r e l a t e s t o t h e n e g a t i v e p r e s s u r e t h a t niay o c c u r i n a d r a i n a g e system, i s covered i n most plumbing codes by s p e c i f i c a t i o n o f where v e n t p i p e s a r e r e q u i r e d and p r o v i s i o n o f t a b l e s t h a t g i v e t h e maximum a l l o w a b l e l e n g t h of v e n t p i p e , depending on s i z e , h y d r a u l i c l o a d s e r v e d , and s i z e o f s o i l - o r - w a s t e s t a c k . A l i m i t e d amount o f wet v e n t i n g i s provided f o r by i n c l u d i n g c l a u s e s t h a t a r e , i n e f f e c t , c x c c p t i o n s t o t h e b a s i c requirement o f t h e North American system t h a t a l l f i x t u r e s must be i n d i v i d u a l l y v e n t e d .

(14)

The tables are based on Hunter's work

(8,

p. 114) in which he

assumed that "no positive or back pressure greater than 1 in. or no

negative pressure or partial vacuum less than 1 in. of water, measured

from atmospheric pressure as the zero, is to be developed in any branch

drain connecting to the stack above the house drain." He continued with.

the very important statement: "It should be kept in mind that pressure

variations in the stack which cannot possibly be transmitted to a

fixture trap have no bearing on the problem. We are only concerned with

the pressure effects in the branches, whether vented or unvented."

The presence of the +l-in. requirement in a plumbing code has

little effect, however, since the venting systems must be designed in

accordance with the vent sizing tables contained in the code. There is

ample evidence that in many cases these tables result in the oversizing

of vent pipes and venting systems. As traps with trap seal depths

greater than

2

in. are readily available, a requirement that the pressure

in a drainage system be limited to +1 in. of water column is also overly

restrictive. It is therefore proposed that the basic requirement of a

venting system should be to limit the pneumatic pressure variation that

can act on a trap to a maximum design value that is consistent with the

capabilities of the traps used in the system.

The present vent sizing tables are applicable in cases where

the design pressure variation is 21 in. of water column and the traps

being used have a trap seal depth of

2

in. Although this will be the

most common situation, tieing the pressure limitation to the trap seal

'

depth of the traps being used eases the restrictions on properly

designed systems. Such a change will not increase the possibility of a

trap seal failure nor reduce the safety of the system.

DETERMINATION OF TRAP PERFORMANCE REQUIREMENTS

The performance requirements of a trap must be expressed in

terms of induced siphonage, self-siphonage, evaporation and the maximum

permitted variation from atmospheric pressure that may occur in the

system. These represent loads that may be applied to the trap in any

sequence, so that performance requirements must be based on the worst

possible sequence of events. That sequence of loads is as follows:

induced siphonage or self-siphonage, evaporation and, finally,

application of the maximum deviation from atmospheric pressure that the

venting system may permit. These may be expressed by the following

equations

(15)

B1

=

trap seal loss caused by induced siphonage resulting from the

effect of D, the maximum deviation from atmospheric pressure that

may occur in the system in accordance with the performance

requirements of the venting system,

B2

=

trap seal loss caused by self-siphonage,

B3

=

minimum depth of seal required to prevent the passage of air

through the trap under the effect of D, the maximum deviation from

atmospheric pressure that may occur in the system in accordance

with performance requirements of the venting system,

C

=

minimum allowance for evaporation.

The relations af these variables for tubular traps are shown in Figure 7.

When the level of water in a tubular trap is in mid-range, the

trap will behave like a simple

U tube: if pressure is applied to the

water in one leg, the surface will be depressed and the same volume of

water will flow into the other leg to raise the surface by the same

amount. Thus, the depression of the first surface is equal to the

elevation of the second, and both changes in elevation are equal to half

the applied pressure in inches of water. If either or both surfaces

approach the trap dip or trap weir, this relation will change slightly

because the horizontal cross-section of the trap will increase as it

changes shape from round to oval; and in order to keep the displaced

volume the same there will be a change in height. For tubular traps

with small radii of curvature the deviation from a simple

U tube is

small. As may be seen in Figure 7, the radius of curvature of the trap

will cause

B1 and B3 to be slightly smaller than D/2. The result is

that both errors add additional depth of seal to the evaporation

allowance

C.

Although assuming that

Bi

=

B3

= D/2

causes some

difference between calculated and actual values, it simplifies

calculations considerably. As the error involved is small and not

critical, it will be assumed for tubular traps that

(16)

and equation

(2) becomes

Equation (4) applies to all traps in a system and covers any

combination of occurrences of evaporation and induced siphonage. Those

traps in the system that are susceptible to self-siphonage must also

comply with equation (5).

The loss of seal from induced siphonage and

self-siphonage is not cumulative. A trap that loses some seal by

self-siphonage will not lose any seal by induced siphonage unless it is

exposed to suction pressure with a value greater than twice that of the

seal already lost. Conversely, a trap that provides protection from

induced siphonage pressures equal to

D/2

will provide the same protection

from self-siphonage. Setting minimum values for C and

D

in

equation

(4) automatically sets the minimum value of B2 in equation (5)

at

D/2

for traps whose trap seal depth,

A,

equals C plus

D.

Both equations (4) and

(5) are useful in showing the benefits

that can be obtained by having traps available with varying trap seal

depths. These benefits may be gained at the design stage or at the

installation stage, but the greatest benefit accumulates at the design

stage. The designer has freedom to use larger values for B2, C and

D

in the design of the system as long as he specifies that the traps have

a trap seal depth

A equal to or greater than that determined by

equations (4) and

(5).

The value of

D

will apply over the whole system,

but values for B2 and C can be varied to suit particular situations.

It is anticipated that most designers will not take advantage of this

opportunity, but present plumbing codes specifically prohibit the

minority from taking any advantage of special traps and traps with large

trap seal depths.

The owner enjoys additional benefits when trap seal depths

greater than that required by both the plumbing code and the designer's

requirements are installed. The excess depth is available as increased

protection from any load that may occur in the system; that is, all safety

factors have been increased. The user also gains a similar benefit when

the maximum individual load represented by C and B2 or

D

is lower

than the minimum design level required by the plumbing code or the

designer. The "unused" safety factor is available as added protection

from other loads. Because of this fortuitous arrangement the individual

values specified in the plumbing code for Br, C, and

D

need not include

a large factor of safety. Setting minimum values for B2 and

C

and a

maximum value for

D

in the code ensures that the designer and owner will

be able to use special traps such as deep seal traps and anti-siphon traps

to their best advantage while still ensuring that the system is safe.

(17)

A f u r t h e r use f o r e q u a t i o n s

(4)

aad (5)

is

t o phrve t h e s a f e t y and a c c e p t a b i l i t y o f a c t u a l i n s t a l l a t i o n s . The p r e s e n t dimensional l i m i t a t i o n i n codes p l a c e d on t r a p arms t o p r e v e n t s e l f - s i p h o n a g e i s

s t i l l v a l i d i n t h a t any i n s t a l l a t i o n t h a t conforms w i l l comply w i t h e q u a t i o n s (4) and ( 5 ) . An i n s t a l l a t i o n t h a t does n o t conform t o t h e p r e s e n t dimensional l i m i t a t i o n s w i l l probably r e q u i r e t e s t i n g t o e n s u r e t h a t it complies w i t h e q u a t i o n s (4) and ( 5 ) .

The t e s t involved i s very simple: f i l l t h e f i x t u r e and t h e n d i s c h a r g e i t . T h i s s h o u l d be r e p e a t e d s e v e r a l times and t h e maximum v a l u e o f t r a p s e a l l o s s used t o determine compliance w i t h t h e requirement f o r s e l f - s i p h o n a g e . Much o f t h i s t e s t i n g was c a r r i e d o u t and r e p o r t e d by t h e National Bureau o f S t a n d a r d s i n BMS 126 (9), b u t i t needs t o b e

brought up t o d a t e by addiTiona1 l a b o r a t o r y and o n - s i t e t e s t s . I f t h i s

i s done a t a b l e o f p i p i n g arrangements "deemed t o s a t i s f y " e q u a t i o n s (4) and (5) can e a s i l y be developed.

RECOMMENDATIONS

P r e s e n t plumbing code p r a c t i c e i s t o s p e c i f y a minimum v a l u e f o r A. Equation (4) c l e a r l y shows t h a t i t

i s

p r e f e r a b l e t o s p e c i f y minimum v a l u e s f o r C and D . I n Canadian plumbing codes where t h e minimum v a l u e f o r A i s 1-1/2 i n . t h e corresponding v a l u e s t o b e

s u b s t i t u t e d would be 1/2 i n . f o r C , t h e evaporationallowance,and 1 i n . f o r D , t h e maximum pneumatic p r e s s u r e v a r i a t i o n l i m i t e d by t h e v e n t i n g system. D / 2 s e t s t h e a b s o l u t e minimum v a l u e f o r B2, t h e l o s s o f s e a l by s e l f - s i p h o n a g e , s o t h a t t h e minimum v a l u e recommended f o r B2, C and D/2 i s i n each c a s e 1 / 2 i n . A s Canadian plumbing codes r e q u i r e t h a t t r a p s conform t o recognized product s t a n d a r d s and t h e s e g e n e r a l l y r e q u i r e t h a t t r a p s have a minimum t r a p s e a l depth o f 2 i n . , t h e same a s t h e p r e s e n t minimum v a l u e f o r "A" i n American plumbing codes, t h e a d d i t i o n a l 1 / 2 i n . o f t r a p s e a l depth c ~ n s t i t u t e s an added margin of s a f e t y o v e r and above t h a t provided by i n d i v i d u a l f a c t o r s .

CONC LUS I ON

These recommendations do n o t reduce t h e i n h e r e n t s a f e t y o f d r a i n a g e and v e n t i n g systems. They i n c o r p o r a t e t h e same minimum s a f e t y f a c t o r s , b u t t h e f a c t o r s a r e e x p r e s s e d i n a way t h a t shows t h e r e l a t i o n between them. There i s no need t o p r o v i d e l a r g e i n d i v i d u a l s a f e t y

f a c t o r s because t h e s e combine t o make up t h e f u l l depth o f w a t e r s e a l t h a t r e a c t s t o t h e i n d i v i d u a l l o a d .

There a r e many b e n e f i t s t o b e gained from i n c l u d i n g t h e s e

recommendations i n plumbing codes. R e s t r i c t i o n s on system d e s i g n w i l l be eased, w h i l e s t i l l r e t a i n i n g t h e i n h e r e n t s a f e t y o f p r e s e n t r e q u i r e m e n t s . T h i s w i l l allow g r e a t e r freedom i n f i x t u r e l a y o u t and p i p i n g arrangements and w i l l i n many c a s e s r e s u l t i n lower i n s t a l l a t i o n c o s t s . The

recommendations a l s o e s t a b l i s h a b a s i s f o r t e s t i n g new and e x i s t i n g systems t o determine whether, i n f a c t , t h e y a r e s a f e .

(18)

REFERENCES I

1. Wise, A.F.E. Design factors for one pipe drainage. Royal Sanitary

Institute Journal, Vol. 74, No. 4, April 1954, p. 231 - 241.

2. Housing and Home Finance Agency, U.S.A., Performance of plumbing fixtures and drainage stacks. Housing Research Paper 31, March 1954. 3. Christiansen, J. Characteristics of traps. Proceedings of

Symposium - Drainage Services in Buildings, Stockholm, CIB Working Commission W62, September 1973.

4. Centre Scientifique et Technique de la Construction, Belgium. Les coupe-air; i5tude de leur indi5samorqabilitG. Note d'information technique 81, aoGt 1970.

5. Building Research Station, Great Britain. Soil and waste pipe systems for office buildings, Digest 115, March 1970.

6. Canadian Plumbing Code 1975. Associate Committee on the National

Building Code, National Research Council of Canada, NRCC 13983, 1975. 7. British Standards Institution. British standard code of practice,

CP 304:1968, sanitary pipework above ground, 1968.

8. National Bureau of Standards, Washington. Recommended minimum

requirements for plumbing, Report of Subcommittee on Plumbing of the Building Code Committee, BH 13, Revised May 1931.

9. French, J.L. and H.N. Eaton. Self-siphonage of fixture traps. National Bureau of Standards, Washington, BMS 126, October 1951.

BIBLIOGRAPHY

Babbitt, H.E. Tests on the hydraulics and pneumatics of house plumbing. University of Illinois, Engineering Experimental Station, Bulletin No. 143, July 1924.

Babbitt, H.E. Tests on the hydraulics and pneumatics of house plumbing, Part 11. University of Illinois Bulletin, Vol 25, No. 46, July 1928.

rlawson, F.M. and

A.A.

Kalinske. Report on l~ydraulics and pneumatics of

the plumbi.ng drainagc system. National Association of Master Plumbers of thc United States, Incorporated, Technical Bulletin No. 2, 1939.

Wisc, A.l:.Ii. One-pipe plumbing: some rcccnt

experimental

hydraulics at

the Building Rcsearcli Station. Journal of the Institutc of Sanitary Iingineers, Vol 51, Part 1, 1952, p. 20-49.

Wise, A.F.E. The design of simple one-pipe plumbing. Plumbing Trade Journal, March 1952.

(19)

Wise, A . F . E . , and J . C r o f t . I n v e s t i g a t i o n o f s i n g l e - s t a c k drainage f o r m u l t i - s t o r e y f l a t s . J o u r n a l , Royal S a n i t a r y I n s t i t u t e , Vol 74, September 1954, p. 797.

Wise, A . F . E . Self-siphonage i n b u i l d i n g drainage systems. I n s t i t u t e of C i v i l Engineers, Proceedings, P a r t 111, 3 ( 3 ) , 1954, p . 789-808.

French, J . L . S t a c k v e n t i n g o f plumbing f i x t u r e s . National Bureau o f S t a n d a r d s , Washington, BMS 118, January 1959.

French, J . L . , H.N. Eaton and R.S. Wyly. Wet v e n t i n g o f plumbing f i x t u r e s , National Bureau o f Standards, Washington,

BMS

119, December 1959.

Ministry o f Housing and Local Government, Great B r i t a i n . S e r v i c e c o r e s i n

I high f l a t s . Design B u l l e t i n 3, 1962.

Wise, A.F.E., and M.S .T. L i l l y w h i t e . Towards a general method f o r t h e d e s i g n

I

of drainage systems i n l a r g e b u i l d i n g s

.

Building Research S t a t i o n , CP27/69 August 1969.

National Bureau o f Standards, U.S .A. I n v e s t i g a t i o n o f performance c h a r a c t e r i s t i c s f o r s a n i t a r y plumbing f i x t u r e s . Building Science S e r i e s 22, January 1970.

National A s s o c i a t i o n o f Home B u i l d e r s , U.S.A. Performance o f reduced-size v e n t i n g i n r e s i d e n t i a l DWV systems. LR-210-17 June 1970.

I

Drainage s e r v i c e s i n b u i l d i n g s . Presented

a t

t h e Symposium o f Working Commission W62, o f CIB, Stockholm, September 1973.

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1 R A P

F I G U R E 2

1 0 1 WATER CLOSE1 1 1 , ) TUBULAR l c l A N T I S I P H O N OR INTERCEPTOR TRAP S E A L DEPTH SEAL LOSS SEAL ( R E T E N T I O N ) ATMOSPHERIC PRESSURE ( d l TERMINOLOGY F I G U R E 1 B A S I C T R A P T Y P E S A N D T E R M I N O L O G Y B R 5 2 6 6 - I

(21)

( 0 1

E

&

L O S S

.

Z 2 - L a

f

~

F I G U R E 3

(22)

N o . O F R E P E T l T l O N S F I G U R E 4 C U M U L A T I V E T R A P S E A L L O S S A T V A R I O U S S U C T I O N P R E S S U R E S ( 3 ) T Y P I C A L A I R PRESSURE D I S T R I B U T I O N I N S T A C K W I T H 2 B R A N C H E S D I S C H A R G I N G F I G U R E 5 P R E S S U R E V A R I A T I O N S I N A S T A C K ( 5 )

(23)

FI'GURE 6

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