CHAPTER X

_SEWAGE DISPOSAL_

The subject of sewage disposal for a single house in the country does

not at all present the elaborate problem that is suggested when the

disposal of sewage of a city is under discussion. In the first place,

the amount of sewage to be dealt with is moderate in quantity; and in

the second place the area available on which the sewage may be treated

is in almost all cases more than ample for the purpose. Nor is there the

complication that arises with city sewage, due to the admixture of

manufacturing wastes. The material to be handled is entirely domestic

sewage and varies only according to the amount of water used in the

house, making the sewage of greater or less strength according as less

or more water is used. Sewage from a single house differs only in one

respect disadvantageously from city sewage, namely, in the fact that the

sewage, not having to pass through a long length of pipe, comes to the

place of disposal in what is known as a fresh condition; that is, no

organic changes have taken place in the material of which the sewage is

composed.

_Definition of sewage._

The great bulk of sewage is water, and, in quantity, the amount of

sewage to be cared for is about equal to the amount of water consumed

in the household, although this will depend somewhat on the habits of

the family. If, for example, part of the water-supply is used for an

ornamental fountain in the front yard, or if in the summer time a large

amount of water is used for sprinkling the lawns, that water is not

converted into sewage, and the amount of the latter is thereby

diminished; but, ordinarily, it is safe to say that the quantity of

water supplied to the house and the quantity of sewage taken away from

the house is identical, and since it is much easier to measure the

water-supply than the sewage flow, the former is taken as the quantity

of sewage to be treated.

In the course of its passage through the house, however, the water has

added to it a certain amount of polluting substances, largely derived

from the kitchen sink, where dirt from vegetables and particles of

vegetable material, together with more or less soap, are carried by the

waste water from the sink into the drain. In the bath-room, also, some

small amount of organic matter is added to the water, but the proportion

of such matter to the total volume of water used is very small, probably

not exceeding one tenth of one per cent. This small proportion is

nevertheless sufficient to become very objectionable if allowed to

decompose, and the problem of sewage disposal for a single house is to

drain away the water, leaving behind the solids so disposed that they

shall not subsequently cause offense by their putrefaction.

The process of decay is normal for all organic matter and is due to the

agency of certain bacteria whose duty it is, providentially, to

eliminate from the surface of the earth organic matter which otherwise

would remain useless, if not destructive, to man. It is impossible to

leave any vegetable or animal matter exposed to the air without this

process of decay at once setting in. Apples left in the orchard at the

end of the season inevitably are reduced and disappear in a short time.

Dead animals, whether large or small, in the same way succumb to the

same process of nature, and it has been pointed out that, unless this

provision did exist, the accumulation of such organic wastes since the

settlement of this country would be so great as to make the country

uninhabitable. Fortunately, however, this inevitable process breaks down

the structure of all organic material, partly converting fiber and pulp

into gas, partly liquefying the material and converting the remainder

into inorganic matter which is of vast importance as food for plant

life. A cycle is thus formed which may be best illustrated in the case

of cows which feed on the herbage of a meadow, the manure from the cows

furnishing food for the grass which otherwise would soon exhaust the

nutriment of the soil.

_Stream pollution._

The first fundamental principle of sewage disposal, therefore, is to

distribute the organic matter in the sewage so that these beneficent

bacteria may most rapidly and thoroughly accomplish their purpose.

During the last fifty years, a great deal of study has been expended on

this problem, and while it has not as yet been entirely solved, certain

essential features have been well established.

The most important factor promoting the activity of these agents of

decay is the presence of air, since in many ways it has been proved that

without air their action is impossible. Thus it has been shown that

discharging sewage into a stream, whether the stream be a slow and

sluggish one or whether it be a mountain stream churned into foam by

repeated waterfalls, has little other power to act on organic matter

than to hold it for transportation down stream, or to allow it to settle

in slower reaches until mud banks have been accumulated which will be

washed out again at the first freshet. Experiments have shown that the

agencies to which certain diseases are attributed, commonly known as

pathogenic bacteria, are frequently, if not always, found in sewage, and

that when these bacteria are discharged into streams they may be carried

with the stream hundreds of miles and retain all their power for evil,

in case the water is used for drinking purposes. No right-minded person

to-day will so abuse the rights of his fellow-citizens as deliberately

to pour into a stream such unmistakable poison as sewage has proved

itself to be. The fact is so well known that it is not worth while

pointing out examples. It is enough to say that some of the worst

epidemics of typhoid fever which this country has known have been traced

to the agency of drinking water, polluted miles away by a relatively

small amount of sewage.

In a number of states, laws have been passed which expressly prohibit

the discharge of sewage, even from a single house, into a stream of any

sort, even though the stream is on the land of the man thus discharging

sewage and where it would appear as if he alone might control the uses

of that stream. Unfortunately, the machinery of the law does not always

operate to detect and punish the breakers of the law, but any law which,

as in this case, has so positive a reason for its existence, and

violation of which is so certain to bring disaster on persons drinking

the water of the stream below the point where the sewage is discharged,

any law which appeals for its enforcement so directly to the common

sense and right feeling of all intelligent people, seems hardly to need

legal machinery for its enforcement. It must depend, as indeed all laws

must depend, upon the intelligent support of the community, and surely

no law would commend itself more urgently than this one forbidding the

pollution of drinking water.

In spite of the fact that the lack of air in the water will prevent

bacterial action, there are, nevertheless, many cases where the

discharge of sewage into a stream may be permitted as being the best

solution of the disposal problem, provided always that the stream is not

used and is not likely to be used for drinking water. Such cases occur

where the stream is relatively large and where the level of the stream

is fairly regular, so that there is no likelihood of the deposit of

organic matter on the banks during the falling of the stream level.

Examples of this sort might be cited in the vicinity of the Mohawk or

Hudson River, or in the vicinity of any of the larger rivers of any

populous state, since although the water of the Mohawk is used by the

city of Albany for drinking purposes, yet the amount of organic matter

which inevitably finds its way into such rivers precludes its use for

drinking without filtration. Into the Hudson below Albany there can

hardly be any question of the propriety of discharging sewage from a

single house.

Again, houses in the vicinity of large bodies of still water may without

question be allowed to discharge into those lakes. For example, houses

in the vicinity of Lake Ontario or Lake Michigan, or even of much

smaller lakes, should not contribute any offensive pollution to the

waters of the lake. In New York State, some of the smaller lakes are

used as water-supplies for cities, as, for example, Owasco Lake for the

city of Auburn and Skaneateles Lake for the city of Syracuse, and,

acting under the statutes, special laws have been passed by the State

Department of Health, forbidding any discharge of any kind of household

wastes into these lakes. The same is done in other states. Here, again,

it is a question of the drinking supply which is being considered, and

not a question of the possibility of any nuisance being committed.

_Treatment of sewage on land._

If no stream suitable for the reception of sewage is available, then the

sewage must in some way be treated on land before it passes into the

nearest watercourse. For the second fundamental principle about the

treatment of sewage is that of all places the action of putrefactive

bacteria is most energetic in the surface soil and that it is there that

the organic matter of sewage can be most rapidly accomplished.

Experiments already referred to have shown not only this, but also that

their activity is most noticeable in the surface layers of the soil and

that their action continues for scarcely two feet downward, and it is

customary to assume that the largest amount of work done is accomplished

in the top twelve inches. Further than this, it has been established

that in order to persuade the bacteria involved to do their work as

promptly as possible, the application of sewage to any particular

locality should be made intermittent; that is, that a resting period

should be given to the bacteria between successive applications of

sewage.

For example, one can recall without difficulty the conditions on the

ground at the back of the house where the kitchen sink-drain commonly

discharges. At the beginning of summer perhaps a rank growth of grass

starts up vigorously in the vicinity, and the path of the surface drain

can be traced by the heavy vegetation along the line of the drain. If

the slope of the surface away from the house is considerable, no other

effect may be noticed through the season, since the surface slope

carries away the sewage, spreading it out over the ground so that the

soil really has a chance to breathe between successive doses. But if the

ground is flat, it will be remembered that before many weeks the sewage

ceases to sink into it; the ground becomes "sewage-sick," as they say in

England, and a thick, dark-colored pool of sewage gradually forms, which

smells abominably. If a piece of hose a dozen feet long had been

attached to the end of the drain and each day shifted in position so

that no particular spot received the infiltration two days in

succession, it is probable that no such pondage of sewage would occur,

but that the mere intermittency of the application thereby secured would

permit the successful disposal of this sink waste throughout the season.

The same effect is to be noted in some cesspools where, because of the

great depth to which they are dug and because no overflow into the

surface layers of the soil is provided, the pores of the ground around

the cesspool become clogged and choked, and the cesspool becomes filled

with a thick, viscous, dark-colored, objectionable-looking, and

evil-smelling liquid.

The three principles which will avoid these conditions are, as already

stated, plenty of air, presence of bacteria normally found in the

surface layers of the soil, and intermittency of application.

In order to secure the operation of these three principles in the

application of sewage onto land, the sewage must be made to pass either

over the surface of the land in its natural condition in such a way that

the sewage may sink into the soil and be absorbed and at the same time

give up its manurial elements to whatever vegetation the soil produces;

or, as a modification of this principle, the sewage may be required to

pass through an artificial bed of coarse material by which the rate of

treatment may be considerably increased. In the latter case, although

probably the greater part of the action of the bacteria takes place in

the top twelve inches, it is customary to make the beds about three feet

thick, chiefly in order to prevent uneven discharge of the sewage

through the bed. Finally, wherever, for aesthetic reasons, it is

desirable that the sewage should not be in evidence, either before

passing through the natural soil or exposed in an artificial bed, the

practice may be resorted to of distributing the sewage through

agricultural tile drain laid about twelve inches below the surface. In

this way, the sewage is scattered through the top soil, where bacteria

are most active, without being apparent, and a front lawn thus treated

would not give any indication of its use.

Taking up now in order these three methods of treatment, we may consider

some of the details of construction. In spreading the sewage over the

lawn or in distributing it on the surface, due regard must be paid to

the kind of soil. Clay soils and peaty soils are useless for the

purpose of sewage disposal unless as the result of continuous

cultivation a few inches of top soil may have accumulated on the clay.

This top soil is adapted to sewage purification, provided the quantity

applied is not excessive.

_Surface application on land._

Two methods of operation may be pointed out. The sewage (and this is the

simplest method of disposal possible) may be brought to the upper edge

of a small piece of ground, usually sowed to grass, and allowed merely

to run out over the surface of the ground. There should be, however,

some method of alternating plots of ground, one with another, so that

the sewage is turned from one to the other every day. Each plot will

then have one day's application of sewage and one day's rest, and this

would complete the disposal, were it not for the interference of rain

and cold. The winter season practically puts a stop to this method of

treatment, and rainy weather reduces the power of the soil to absorb

sewage. For these two reasons, it is desirable to have one plot in

reserve, or three in all, and the area of each plot should be based on

the amount of sewage contributed. For a family of ten persons using

twenty-five gallons of water per day the total area provided should be

one tenth of one acre, or an area seventy feet square divided into three

plots. Figure 67 shows six beds arranged to care for the sewage of a

public institution in Massachusetts. As a guide to the amount of land

needed, it will be safe to provide at the rate of one acre for each

forty persons where the soil is a well-worked loam but underlaid with

clay. The effect of this irrigation on the grass will be to induce a

heavy, rank growth which must be kept down by repeated cutting or by

constant grazing. Both methods are practiced in England, and it may be

said in passing that no injury to stock from the feeding of such

sewage-grown grass has been recorded. The grass cut from such areas (and

the cutting is done every two weeks through the whole summer) is packed

into silos and fed to cattle through the winter with advantage. Or, if

grazing is resorted to to keep the grass down, the herd is alternated

with the sewage from one field to the other, so that the bed which has

received sewage one week is used for pasture the next week, and the

number of head which can thus be fed is astonishing. In order to secure

an even flow of sewage over such grass land as is here contemplated,

there must be a gentle slope to the field, and the ditch or drain

bringing the sewage to the field should run along its upper side.

Openings from the drain, controlled by simple stop planks, are provided

at intervals of about ten feet, and no attention is needed further than

the opening and closing of these admission gates.

[Illustration: FIG. 67.--Sewage beds.]

Another method of applying sewage to the surface of the ground is to

lead it in channels between narrow beds on which vegetables have grown.

These beds are made about eight feet wide with two rows of root crops,

such as turnips or beets, set back about two feet from the edge. The

beds are made by properly plowing, the channels between the beds being

back-furrowed. Here, again, the principle of intermittent application is

essential, and the area to be provided is the same as already given for

the surface irrigation. Three beds should be provided, as before; but,

in general, no provision need be made for carrying off the sewage at the

lower end of the beds, since it may be safely assumed that all of the

sewage will be absorbed by the soil. Of course, a sandy soil will

absorb more water than a clay soil, and if the soil is entirely clay, it

is not suitable for such treatment. Sewage passed over the surface of

clay soil, however, will, in the course of a few months, so modify the

clay as to convert it into a loam, and in this way increase its

absorptive power.

When possible, it is desirable to have a plot of plowed ground over

which the sewage may pass before reaching the beds, so that the grosser

impurities may be left behind and harrowed in or plowed under. If proper

regard is paid to intermittent application, no danger from odors need be

feared, and the repeated plowing in will increase immensely the

fertility of the soil. Nor need one be afraid that all of the manurial

elements will be left behind on this plowed ground. About two thirds of

the organic matter in sewage is in solution, and this will be carried

onto the beds just as if passage over the plowed ground had not

occurred.

_Artificial sewage beds._

In order to secure a higher rate of discharge of sewage through the soil

it is best to arrange an artificial bed which shall be made of coarse,

sandy material which will allow a rate of at least 10 times that already

given. The best material out of which to make such an artificial bed is

a coarse sand; that is, a sand whose particles will not pass through a

sieve which has 60 meshes to the inch and which would pass through a

sieve of 10 meshes to the inch. Such an ideal sand will purify sewage at

the rate of 50,000 gallons per acre per day, or an acre will take care

of the sewage of at least 1000 persons. This means that it is necessary

to provide about 50 square feet for each person in the family, or a

family of 10 persons could have all the sewage taken care of on an area

25 feet square. The same principle of intermittency of application,

however, must be observed by dividing the bed into three parts, so that

the sewage may be alternated from one bed to another. Practice has

indicated that it is better to shift from bed to bed about once a week

and to deliver the sewage onto each bed intermittently; that is, to

discharge a bucketful at a time with short intervals between, rather

than to allow a small stream to flow continuously onto a bed. Such a bed

should be about 3 feet deep, as already stated, and preferably should

have light concrete side walls and bottom, as shown in the sketch (Fig.

68). Ordinarily, the surface of the sand will be level, and the dose of

sewage applied to the bed will cover it a fraction of an inch deep, and

in the course of an hour or so will disappear into the sand and reappear

in the underdrains as clear water.

[Illustration: FIG. 68.--Sewage beds.]

In cold weather a thin sheet of sewage spread out over the surface of

the sand would freeze before penetrating the bed; therefore, in the

winter time, it is usual to furrow the beds; that is, dig furrows across

the beds 2 or 3 inches wide at the bottom and about 10 inches deep, so

that in the bottom of these furrows the sewage may be, partly at least,

protected against frost. It has been found that, if sewage is discharged

intermittently,--that is, in bucketfuls into such furrows,--the beds

open and allow the filtration of the sewage. To be sure, the

purification effected in cold weather is not quite that accomplished in

warm weather, but the results are sufficiently satisfactory, and no

nuisance ensues.

_Subsurface tile disposal._

The other method of distributing sewage over land is by means of

draintile placed in shallow trenches, so that the sewage may leach out

into the soil through the open joints of the pipe. These draintiles

receive the sewage intermittently, and by the constant rush of water are

presumably filled throughout their length. The sewage then gradually

works out of the joints into the surrounding soil, and the pipes are

empty and ready to receive another dose when next delivered.

Two essential points must be considered in the successful operation of

such a plant: the grade of the tile and the length of the tile.

The grade of the tile must be properly adjusted to the porosity of the

soil; that is, in open, porous, and gravelly soils a grade must be

steeper than in loamy and dense soils. The reason is manifest. In a

gravel soil, the sewage is at first rapidly absorbed, so that as the

sewage goes down the pipe line the first joints take up the water and

deliver it to the soil, where it disappears, and probably no flow

reaches the end of the line at all. This means that the soil surrounding

the first joints does the work which the entire pipe line was intended

to do and thus becomes overworked. When overworked, the soil always

refuses to do anything, so that when the succeeding joints take up the

sewage and in their turn become overworked, the line is useless. If, on

the other hand, the grade had been steep enough to carry the sewage down

the pipe line gradually so as to secure a uniform distribution, then the

same or approximately the same amount of sewage would be taken out of

the pipe at each joint, securing a long life for the system. In loamy

soil, on the contrary, there is not the same absorption at the joints,

and so on a steep grade there is the tendency for all the sewage to

follow down the pipe line to the lower end and there escape to clog the

soil and thus spoil the system. As a general average, it may be said

that the proper grade for such a subsurface distribution pipe line in a

fairly good sandy loam should be 5 inches in 100 feet; less than this as

the loam becomes clay and more as the loam becomes gravel.

The other essential point for the successful operation of this method

of distribution is to provide a proper length of pipe for the number of

persons contributing sewage. The soil itself will absorb about the same

amount as when the sewage is spread over the surface, so that a family

of ten persons would require, as before, an area about 70 feet square.

The pipe lines may be laid in different sections, provided the different

lines of pipe are not nearer together than 10 feet. On an area 70 feet

square there would be, therefore, 7 lines of pipe each 70 feet long, or

490 lineal feet of pipe in all, or 49 feet per person. The writer

generally allows 40 feet in well-cultivated soil as a reasonable length

of pipe for each person in the family. If the soil is sandy, this may be

reduced one half, but need not be increased under any conditions, since

a soil requiring a greater length of pipe than 40 feet per person would

be so dense as to be unfit for use. To properly arrange the lines of

pipe on a sloping ground requires careful study of the inclination of

the ground and of the relation of direction of lines of pipe to slope.

Usually the slope of the ground is greater than the 5 inches per 100

feet just referred to, but by laying out the lines of pipe across the

slope instead of with it any grade desired may be obtained. Nor is it

necessary that these lines of draintile be run in straight lines; they

may very properly follow the curving slope, the proper grade being

always carefully maintained.

[Illustration: FIG. 69.--Plan of subsurface irrigation field.]

Common agricultural tiles three inches in diameter and costing about two

cents per running foot are suitable material for these distribution

lines. The sewage enters these distribution lines from a larger pipe,

usually six inches in diameter, and a difficult adjustment is presented

that each branch tile line shall receive its own proportionate share of

the sewage. If only one line of tile is provided, say 200 feet long for

5 members in the family, then all the sewage goes into that line with no

question of distribution arising, but if a number of short parallel

lines must be used, as shown in the sketch (Fig. 69), the difficulty of

subdividing the sewage properly among the different branch lines becomes

very great. For that reason the writer prefers to use not more than two

lines, with the possibility of delivering the sewage alternately in the

one and the other. In this way, the bed not receiving sewage is resting,

while the other bed is acting, and also the outlet for the sewage is

always definitely known. And particularly in the case of these

subsurface tile, the necessity for the intermittent dosing is apparent,

since with small, constant trickling discharges the difficulty of

distribution through the long length of tile is gradually increased, and

usually saturation of the soil occurs from joint to joint, as already

described. Therefore it becomes most necessary, in this case, for the

best results on the soil not merely to alternate the beds receiving

sewage, but also to effect the intermittent discharge onto the beds or

through the pipes although the sewage itself may flow very uniformly in

volume.

_Automatic syphon._

This intermittent discharge is accomplished by constructing on the pipe

line from the house and before it reaches the beds an "automatic

syphon," as it is called, the operation of which may be described as

follows: As the sewage enters the tank containing the syphon and rises

outside the syphon-bell, air is compressed between the water surface

inside the bell and the water left inside the syphon-leg. With greater

and greater height of water outside, this compression inside becomes

greater and forces the water in the syphon-leg lower and lower. Finally,

the water sinks so low as to allow the compressed air to escape suddenly

around this bend, instantly relieving the compression, and the water

outside rushing in to fill up the space occupied by the air starts the

syphon (see Fig. 70).

[Illustration: FIG. 70.--Section of "Miller" syphon.]

This syphon, in size suitable for a single house, costs about $12

delivered, and will always be available to secure an intermittent dosing

of the bed or pipe line. Usually the chamber in which this syphon is

placed holds about one hour's flow, so that it may be estimated that

this syphon will discharge on the bed every sixty minutes. The exact

interval of time is not essential nor, perhaps, important, although it

may be noted that the coarser the material,--that is, the nearer uniform

all the sand particles are to the largest size passing the ten-mesh

size,--the smaller must be the dose applied, but the more frequently

must the application be made. This has been very thoroughly studied in

Massachusetts, and the views of experts on this subject may be found in

the report of that Board.

Such an intermittent discharge may be made and often is made by a hand

valve leading out from this chamber in institutions or in private houses

where some one constantly is available for the purpose. Thus it becomes

the duty of the man in charge every hour or perhaps three times a day to

pull the valve and allow the sewage to discharge (see Fig. 71). An

overflow pipe should always be provided, so that if he forgets to pull

the valve, the sewage will still find its way into the system rather

than out on the ground.

[Illustration: FIG. 71.--Plan and section of a septic tank with valve.]

_Sedimentation._

As a matter of economy of operation, it has been found desirable to take

out from the sewage before the treatment already described as much of

the solid matter as may be reasonably done, and for this purpose

sedimentation is made use of. Most of the solids in sewage are slightly

heavier than water, so that if they be allowed to stand in the water for

a short length of time, they will settle to the bottom of the tank and

allow the liquid above to pass on, considerably clarified. It has been

found worth while to do this, since all three processes described are

interfered with if the solids taken out by sedimentation are allowed to

be deposited either upon the surface of the ground, giving rise to odors

as well as to objectionable appearances, or onto the surface of the sand

beds, which they clog up, or in the three-inch tile drain, which may be

filled in a short time.

It has been further found by experience that if these sedimentation

tanks are made large, really larger than necessary for sedimentation, in

some way a large proportion of the matter accumulating in the tank will

disappear, so that the amount of sediment to be taken out of the tank is

not as large as might be expected. In fact it is usual for such tanks to

run one or two years without cleaning, although the amount of solids

shown by chemical analysis to have been removed from the sewage would

fill the tank twice over.

It has been found that a tank, in order to do successful work in

separating solids and in eliminating as much as possible of the

sediment, needs to be of a capacity to equal about one day's flow of the

sewage, and this is a good basis for computation. Here, again, the fact

that the sewage from a single house is considerably fresher than the

sewage from a city must be remembered, since, while many cities build

tanks holding only one third or one fourth of their daily flow with good

results, in the case of a single house this is not possible, and the

tanks, if built at all, ought to hold at least the full day's flow. Ten

persons, at 25 gallons each, furnish 250 gallons per day or 33 cubic

feet. The tank, then, must be large enough to hold this volume, and

suitable proportions generally require that the tank be at least 5 times

as long as wide. A certain allowance must always be made for deposit in

the bottom and for the accumulation of scum on the top, so that an extra

foot or more of depth is desirable. The tank, then, to furnish the

required 33 feet, might be made 3 feet wide, 3 feet deep, and 5 feet

long, and probably in no case would a tank much smaller than this be

used.

[Illustration: FIG 72.--Section of a septic tank with syphon chamber.]

There are two or three details of tank construction which may be

suggested, although almost any kind of tank will answer the purpose. It

is desirable in order that the surface scum may not be disturbed, and in

order that the inflowing sewage may distribute itself as uniformly as

possible across the tank, to attach an elbow to the entering pipe so

that the sewage enters about halfway between the top and bottom of the

tank (see Fig. 72). Similarly, at the outlet or weir an elbow should be

provided because it is not desirable to allow the floating matter of the

surface to be carried onto the bed, and a pipe taking off liquid, open

halfway between top and bottom, will carry away but little of either the

surface scum or bottom sediment. Such a tank must be built of concrete

or masonry or timber, although the latter is not to be recommended

because of its short life. The walls of an ordinary tank may be built 6

inches thick at the top and 12 inches to 18 inches thick at the bottom,

the latter being necessary if the depth is over 8 feet. The tank should

have 6 inches of concrete on the bottom, and the roof may be made of

flagstone or of concrete slabs in which some wire mesh has been buried.

It is not necessary to ventilate this tank, although it is desirable to

have perhaps a foot of air-space between the water level and the roof of

the tank. During the first few months of its operation such a tank is

very likely to smell badly, and, if ventilators are provided, the

presence of the tank will be well known by the odors sent off. After the

tank has been in operation two or three months these odors gradually

disappear, due presumably to the fact that the surface of the water in

the tank has become coated with a thick blanket through which odors

cannot penetrate. On the other hand, there have been a few cases

recorded where the production of gas in a septic tank was so great that

an explosion occurred, tearing off the roof and otherwise doing

considerable damage.

The full plant, therefore, will consist of the settling tank, receiving

the raw sewage from the house and discharging it into a small tank

holding about one hour's flow and containing the automatic syphon

apparatus for intermittent discharge. This dosing tank must provide for

one hour's flow at the maximum rate of flow, and should hold about one

fourth of the total daily flow. Then the ground area, either natural or

artificial, which receives the intermittent discharge from the dosing

tank, completes the installation (see Fig. 73).

[Illustration: FIG. 73.--Plan of sewage disposal for single house with

details of receiving tank.]

_Underdrains._

The question of installing underdrains will arise only in cases where

the ground water, always to be found below the surface somewhere, comes

up so high as to affect the disposal of sewage. Usually no underdrains

will be needed unless the ground water gets up to within three feet of

the surface, and, in a number of cases, underdrains have been laid under

a sewage filter at considerable expense, only to find when the filter

was in operation that they were never in use. In clay soils the

underdrain is not necessary. In fact, it may be noticed that the

underdrain is not for the purpose of taking care of the sewage, but

rather of draining off the soil-water and preventing its interference

with the action of soil on sewage. This principle will indicate where

underdrains are necessary and where not.

When used, underdrains should be laid from three to four feet below the

surface in parallel lines about fifteen feet apart and on grades of not

less than one foot in one hundred. It is always better to have the

underdrains too large than too small, and drains less than three inches

in diameter should not be used, and they should increase in size to four

inches and then to six inches as the separate drains are brought

together. The writer has seen a six-inch underdrain running full of

ground water collected within a distance of a hundred feet, but this was

in gravel soil through which the water passed very freely. No exact

rules can be given for the size of the underdrains, but it will be

noticed that, since water passes through clay soil slowly and through

gravel soil rapidly, larger pipes must be used where the soil is

coarse.

Rural Hygiene · 第 10 / 21 章