=123. Summary of Data.=—If a solution of a soluble sulfate, chloride or

nitrate of an alkali or an alkaline-earth metal be placed in contact

with a soil, the result is that the soil takes up a part of the base but

none of the acid. This absorption of base is attended with the

liberation of some other base from the soil which combines with the acid

of the solution. Any alkali or alkaline earth base has the power of

replacing any other such base. However, if soluble phosphates and

silicates of these bases be placed in contact with the soil both the

base and the acid are removed from the solution.

Peters[82] has shown that the amount of absorption depends upon the

concentration of the solution, the relation between the quantity of

solution and the soil and the kind of salt used. He treated 100 grams of

earth with 250 cubic centimeters of solutions of different potash salts

with the following results:

Strength of solution. ⅒ Normal. ¹⁄₂₀ Normal.

Grams Grams

Salt Used K₂O absorbed. K₂O absorbed.

KCl 0.3124 0.1990

K₂SO₄ 0.3362 0.2098

K₂CO₃ 0.5747 0.3154

Biedermann[83] proves that, for phosphoric acid at least, the absorption

increases with the temperature.

It has also been found that the amount of absorption depends upon the

time of contact between the soil and solution. Way found that the

absorption of ammonia was complete in half an hour, while Henneberg and

Stohmann[84] noticed that the phosphoric acid continued to be fixed

after the expiration of twenty-four hours.

It is a very important fact that the absorption of a base is never

complete; no matter how dilute the solution it will still carry a small

portion of the base with it. Peters states that it requires about 28,000

parts of water to remove one part of absorbed potash and Stohmann found

that it required about 10,000 parts of water to remove one part of

absorbed ammonia. With phosphoric acid, the resulting compound seems to

be much more insoluble.

According to Tuxen[85] the presence of salts of soda and potash in

solution decreases the power of a soil to absorb ammonia compounds and

the presence of sodium salts decreases the power of a soil to absorb

potash. On the other hand the presence of potassium compounds

considerably increases the absorption of phosphoric acid. He further

affirms that the compounds of potash, phosphoric acid, etc., formed in

the soil, are decidedly more soluble in sodium salts than in pure water.

=124. Cause of Absorption.=—The withdrawing and fixing of phosphoric

acid from solutions by the soil is not very difficult to understand as

this acid forms insoluble compounds of iron, lime, and magnesium, some

or all of which are present in all soils. As to the absorption of the

alkalies, the explanation is far more difficult as nearly all of their

ordinary compounds are readily soluble in water.

As lime is usually found combined with the acid part of an alkali salt,

from which the base has been absorbed by the soil, it might naturally be

supposed that the absorptive power of the soil would depend upon the

amount of lime present. Way found, however, that the addition of chalk

in no way influenced the absorption of ammonia by a soil which contained

but a small amount of lime. This fact was also confirmed by Knop[86] who

found that chalk exerted no influence on the absorption of ammonia

salts. These facts would seem to point to the conclusion that lime was

present in sufficient quantity in these experiments, or that it is not

essential to the phenomena of absorption. However, as any alkali or

alkaline-earth base can replace any other such base, the presence of

lime in the filtrate is probably more of an accidental occurrence, owing

to the comparatively large amount of that substance in most soils, than

a necessary condition, as any other base would doubtless answer in the

absence of lime.

=125. Warington=[87] has shown that hydrated oxides of iron and

aluminum, and especially the former, are capable of absorbing potash and

ammonia, and as more or less of these hydrates exist in nearly all

soils, a part, at least, of absorptive phenomena is to be ascribed to

them.

=126. Way= tried to determine which of the constituents of a soil

exercised chiefly the absorptive power. He passed a solution of ammonia

through tubes containing pure sand and found that it came through

apparently unaltered from the first, while a soil treated in the same

way removed the ammonia for a considerable time. He concluded from this

that the absorptive power does not exist in the sand. He next oxidized

the organic matter in a soil with nitric acid and then treated it with

ammonia in the same way. The first portions of the filtrate showed no

ammonia in any form, hence he concluded that organic matter is not

essential to the act of absorption. He further showed that clay alone is

capable of causing absorption phenomena, by treating powdered clay

tobacco pipes with ammonia.

Having shown that clay was the main constituent in a soil which caused

the absorption of alkalies, he tried next to trace out the particular

compound which caused the absorption. Having tried various natural

silicates he at last succeeded in producing a hydrated silicate of

aluminum and soda which exhibited displacement and absorptive properties

very similar to those shown by the soil.

As Way had succeeded in producing an artificial hydrated silicate

possessing absorptive properties, Eichorn[88] thought of trying natural

hydrated silicates or zeolites and found that they exhibited the same

power as Way’s artificial preparation. It has also been shown by

Biedermann,[89] Rautlenberg,[90] and Heiden[91] that the absorptive

power bears a close relation to the amount of soluble silicates present.

In view of these facts it is now generally accepted that the absorption

of salts of the alkalies, accompanied by the change of base, is due

chiefly to the presence of decomposed zeolite minerals in the soil.

Besides the purely chemical absorption of salts by the soil, we have a

physical absorption of various substances similar to the action of

charcoal when used as a filter.

=127. Conclusions of Armsby.=—The data connected with the absorption of

bases by a soil have also been reviewed by Armsby.[92] He shows that the

absorption is accompanied by a chemical reaction between the salt whose

base is absorbed and some constituent of the soil, and this change seems

to be due particularly to certain zeolitic silicates, although Liebig

and others were disposed to credit this absorption largely to physical

causes.

Knop advances the idea that the soil has the power of disintegrating

salts in the presence of some substances like calcium carbonate which

can unite with the acid. In experiments made with hydrous silicates it

was shown that the absorption resembled in all cases like phenomena in

the soil; hence the supposition already advanced in regard to the

influence of such silicates is doubtless true.

In respect of absorption in general, the following conclusions were

reached:

1. The absorption of combined bases by the soil consists in an exchange

of bases between the salt and the hydrous silicates of the soil.

2. This exchange, which is primarily chemical, is only partial, its

extent varying

(a) with the concentration of the solution, and

(b) with the ratio between the volume of the solution and the quality of

soil used.

3. The cause of these variations is probably the action of mass or the

tendency of resulting compounds to re-form the original bodies, the

absorption actually found in any case marking the point where the two

forces are in equilibrium.

=128. Selective Absorption of Potash.=—As a rule more potash is absorbed

from the sulfate than from the chlorid. This fact would seem to point to

the advisability of using sulfate as a fertilizer in preference to

chlorid. However, as with the exception of nitrates, the absorptive

power of a soil, for the salts used as fertilizers, is many times

greater than it is ever called upon to exert in fixing applied

fertilizers, we need not trouble ourselves in regard to the absorption

of phosphoric acid, potash or ammonia, in so far as the practical side

of the matter is concerned. For example, an acre of soil to the depth of

nine inches weighs about 900 tons. Now it has been found by Huston,[93]

that 100 parts of a soil experimented upon absorbed over 0.25 part of

P₂O₅, hence 900 parts would absorb over 2.25 parts of P₂O₅; or an acre

of this soil to the depth of nine inches would absorb over two and

one-fourth tons of phosphoric acid. 500 pounds per acre is a large

dressing of a phosphatic fertilizer for field crops and 500 pounds of a

high grade fertilizer would contain about 100 pounds of P₂O₅; hence the

power of such a soil to absorb phosphoric acid is more than forty-five

times as great as it is ever likely to be called upon to exert in fixing

the phosphoric acid added to it as a fertilizer.

Huston has further shown that an acre of soil nine inches deep will

absorb more than 2.7 tons of potash (K₂O) from potassium chlorid from

which salt less potash is absorbed than from the sulfate. Now one-tenth

ton of potassium chlorid per acre would be a large dressing of potash,

hence this soil possesses the power of absorbing more than twenty-seven

times as much potash as is ever likely to be applied as a fertilizer.

In like manner it may be shown that the power of an acre of soil nine

inches deep to absorb ammonia from ammonium sulfate is more than

thirty-two times as great as it would be called upon to exert in fixing

the ammonia from a dressing of one-quarter ton of ammonium sulfate per

acre.

With sodium nitrate, however, there is no absorption; hence great care

is necessary in the application of nitrogen as a nitrate, for, if it be

put on in large quantities, at a season when the plant is not prepared

to assimilate it, or during a period of heavy rains, there must

unavoidably result loss from drainage. The best time to apply a nitrate

is evidently during the active growing season.

=129. Whitney=[94] places great emphasis on the surface area of soil

particles in respect to their power to absorb solutions of salts. The

approximate surface area of a cubic foot of each of the different

typical soils of Maryland is as follows:

Pine barrens 23,940 square feet.

Truck lands 74,130 „ „

Tobacco lands 84,850 „ „

Wheat lands 94,540 „ „

River terrace 106,260 „ „

Limestone subsoil 202,600 „ „

It will be seen that there are about 24,000 square feet of surface area

in a cubic foot of the subsoil of the pine barrens, no less then 100,000

square feet or two and three-tenths acres of surface area in a cubic

foot of the subsoil of the river terrace, and 200,000 square feet of

surface area in a cubic foot of the limestone subsoil.

These figures seem vast, but they are probably below rather than above

the true values, on account of the wide range of the diameters of the

clay group. This great extent of surface and of surface attraction,

which has been described as potential, gives the soil great power to

absorb moisture from the air, and to absorb and hold back mineral

matters from solution. A smooth surface of glass will attract and hold,

by this surface attraction, an appreciable amount of moisture from the

surrounding air. A cubic foot of soil, having 100,000 square feet of

surface, should be able to attract and hold a considerably larger amount

of moisture.

It might have been added that if the potential of the surface,

separating the solution from the soil, be greater than the potential in

the interior of the liquid mass, there will be a tendency to concentrate

the liquid on this surface of separation. It has been shown that certain

fluids have greater density on a surface separating the fluid from a

solid. On the other hand, if the potential were low there might be no

tendency for this concentration, and even the reverse conditions would

prevail and the soluble substance could be readily washed out of the

soil.

=130. Removal of Organic Matters.=—It is probably largely due to this

straining power that organic matters are removed from solutions in

percolating through the soil. Whitney[95] has observed that the organic

matter may be coagulated and precipitated from solution by the soil

constituents, and held in the soil in loose flocculent masses, while the

liquid passes through nearly free of organic matter.

=131. Importance of Soil Absorption.=—The importance of the absorptive

power of the soil can hardly be overestimated. By means of this power

those mineral ingredients of plant food, of which most soils contain but

little, are held too closely to allow of rapid loss by drainage, and

still sufficiently available to answer the needs of vegetation, provided

the store is large enough. The only important plant food liable to be

deficient in the soil which does not come under the influence of

absorption is nitrogen in the form of salts of nitric acid, and nature

has made a wide provision for this element by binding it in the form of

organic bodies which nitrify but slowly, and by supplying each year a

small quantity from the atmosphere.

By means of the absorptive power of soils the farmer, if he puts on an

excess of potash or phosphoric acid as a fertilizer, does not lose it

but is able to reap some benefits from it in the next and even in

succeeding crops. If it were not for this power the best method for

applying fertilizers would be a much more complicated problem than it is

at present; and it would be necessary to apply them at just the proper

season and in nicely regulated amounts to insure against loss.

=132. Method of Determining Absorption of Chemical Salts.=—The soil

which is to be used for this experiment should be treated as has been

indicated and passed through a sieve the meshes of which do not exceed

half a millimeter in size. From twenty-five to fifty grams of the fine

earth may be used for each experiment.

The fine earth should be placed in a flask with 100 to 200 cubic

centimeters of the one-tenth to one-hundredth normal solution of the

substance to be absorbed. The flask should be well shaken and allowed to

stand with frequent shaking twenty-four to forty-eight hours at ordinary

temperatures. The whole is then to be thrown upon a folded filter and an

aliquot part of the filtrate taken for the estimation. The methods of

determining the quantities of the substances used will be found in other

parts of this manual. It is recommended to conduct a blank experiment

with water under the same conditions in order to determine the amount of

the material under consideration abstracted from the soil by the water

alone. The difference in the strength of the solution as filtered from

the soil, corrected by the amount indicated by the blank experiment, and

the original solution will give the absorptive power of the soil for the

particular substance under consideration.

If it should be desired to determine the absorptive power of the soil

for all the ordinary chemical fertilizing materials at the same time, a

larger quantity of the sample should be taken corresponding to the

increased amount of the standard solutions used. About 500 cubic

centimeters of the mixed salt solution should be shaken with 125 grams

of the earth and the process carried on in general as indicated above.

The absorption coefficient of an earth for any given salt according to

Fesca,[96] is the quantity of the absorbed material expressed in

milligrams calculated to a unit of 100 grams of the soil.

=133. Method of Pillitz and Zalomanoff.=—It is recommended by Pillitz

and Zalomanoff[25] to reject the old method, _viz._, shaking the soil

with the solution in a flask, and substitute the filtration method both

because it gives a more natural process and because the results are more

constant. The apparatus is shown in Fig. 15.

[Illustration:

FIGURE 15.

ZALOMANOFF’S APPARATUS FOR DETERMINING ABSORPTION OF SALTS BY SOILS.

]

Two cylinders are placed vertically, one over the other. The lower

cylinder is graduated in cubic centimeters, the upper cylinder is closed

at each end by perforated rubber stoppers A and B through the openings

of which the glass tubes _c_ and _d_ pass. Within the cylinder A the

opening of the small tube _d_ is closed with a disk of Swedish filter

paper. The lower part of the small tube is _d_ connected by means of a

rubber tube carrying a pinch-cock C, with another small tube _e_ which

passes through the stopper _f_. In carrying out the process the weighed

quantity of soil is placed in the upper cylinder and afterwards the

measured quantity of the solution, the whole thoroughly mixed and the

cylinder closed. The valve C is then opened, a given quantity of the

solution, but not all, is made to drop into the lower cylinder and the

valve C is then closed. The liquid which has passed into the lower

cylinder as well as that which remains in the upper cylinder, is

thoroughly stirred and the quantity of the material remaining in both

liquids determined and the absorbing power of the soil estimated from

their difference. It does not appear that this method of estimation of

the absorption power possesses any special advantages over the old and

far simpler method of shaking in a flask.

[Illustration:

FIGURE 16.

MÜLLER’S APPARATUS TO SHOW ABSORPTION OF SALTS BY SOILS.

]

=134. Method of Müller.=—The method of Müller[97] for illustrating

absorption is carried out by means of the apparatus shown in Fig. 16. A

glass cylinder A about 750 centimeters long and four to five centimeters

wide is closed at each end with rubber stoppers with a single

perforation. The cylinder A is for the reception of the soil with which

the experiment is to be made. Before using, the lower part of it is

filled with glass pearls or broken glass and above this a layer of glass

wool is placed about one centimeter thick. The object of this is to

prevent the soil from passing into the small tube below. As soon as the

soil has all been placed in the cylinder A the upper part of the tube is

also filled with glass wool. The cylinder A is connected with the

pressure bottle B by means of a rubber tube and the small glass bulb

tube shown in the figure. The bottle B should have a content of about

two liters. It is filled with the standard solution of the material of

which the absorption coefficient is to be determined. At _c_ the rubber

tube is connected with a glass T one arm of which is provided with a

piece of rubber tubing which can be closed by means of a pinch-cock. At

_c_ a screw pinch-cock is placed which can be used to regulate the flow

of the solution from B to A. By opening the pinch-cock at _e_ on the

short arm of the T piece, a sample of the original liquid can be taken

and this can be compared with the part which runs to _b_. If it is

desired for instance, to show that potassium carbonate has been absorbed

by the soil the two bulbs shown on the small glass tubes connecting with

A can be filled with red litmus paper. This paper will at once be turned

blue in the lower bulb while in the upper one it will retain its

original color because the liquid in passing through the soil will have

lost its alkaline reaction. The solutions used should be very dilute.

The apparatus is designed for lecture experiments and not for

quantitative determinations.

=135. Method of Knop.=—For rapid determination of the absorption

coefficient of the soil Knop’s method may be used.[98]

The fine earth which is employed is that which passes a sieve with

meshes of half a millimeter. From 50 to 100 grams of this soil are mixed

with from five to ten grams of powdered chalk and with about twice the

weight of ammonium chlorid solution of known strength, _viz._, from 100

to 200 cubic centimeters. The ammonia solution should be of such a

concentration that the ammonia by its decomposition for each cubic

centimeter of the liquid evolves exactly one cubic centimeter of

nitrogen. This solution is prepared by dissolving in 208 cubic

centimeters of water one gram of ammonium chlorid. With frequent shaking

the solution is allowed to stand in contact with the soil for

forty-eight hours. The whole is now allowed to settle and the

supernatant clear liquid is poured through a dry filter. From the

filtrate twenty to forty cubic centimeters are removed by a pipette, and

evaporated to dryness in a small porcelain dish, with the addition of a

drop of pure hydrochloric acid. The ammonium chlorid remaining in the

porcelain dish is washed with ten cubic centimeters of water into one of

the compartments of the evolution flask of the Knop-Wagner azotometer.

It is decomposed with fifty cubic centimeters of bromin lye and the

nitrogen estimated volumetrically. The difference between the amount of

nitrogen in this material and that of the original material will give

the amount of absorption exercised by the fine earth. This number,

without any further calculation, can be taken as the coefficient of

absorption.

=136. Method of Huston.=—The salt solutions recommended by Huston[99]

are sodium phosphate (Na₂HPO₄), potassium chlorid, potassium sulfate,

ammonium sulfate and sodium nitrate.

The solutions should be approximately tenth normal, the actual strength

in each case being determined by analysis. The phosphorus is determined

as magnesium pyrophosphate in the usual way, the potash as potassium

platinochlorid, the ammonia by collecting the distillate from soda in

half normal hydrochloric acid and titrating with standard alkali, and

the nitrate by Warington’s modification of Schlösing’s method for gas

analysis. The details of these methods of determination will be given

later. One hundred grams of the sifted, air-dried soil are placed in a

rubber stopped bottle and treated with 250 cubic centimeters of the

solution to be tested. The digestion is continued for forty-eight hours

in each case, the bottles being thoroughly shaken at the end of

twenty-four hours. At the end of the treatment the solutions are

filtered and the salts determined in aliquot portions. The details of

this method are essentially those already described.

=137. Statement of Results.=—Duplicate analyses should be made and the

tabulation of the data is illustrated in the following analyses by

Huston:

Na₂HPO₄ cubic Weight of Weight of P₂O₅ Salt

centimeters Mg₂P₂O₇ in Mg₂P₂O₇ in absorbed removed

filtrate taken. twenty-five filtrate. by 100 per

cubic grams cent.

centimeters of soil.

the solution.

(a) 25 0.1368 gram 0.0962 gram

(b) 25 0.0963 „ 0.2589 29.6

gram

——————

Mean 0.0963 „

KCl cubic Weight of Weight of K₂O Salt

centimeters K₂PtCl₆ in K₂PtCl₆. absorbed removed

filtrate taken. twenty-five by 100 per

cubic grams cent.

centimeters of soil.

solution.

(a) 25 0.6154 gram 0.4505 gram

(b) 25 0.4540 „ 0.3161 26.5

gram

——————

Mean 0.4523 „

K₂SO₄ cubic Weight of Weight of K₂O Salt

centimeters K₂PtCl₆ in K₂PtCl₆. absorbed removed

filtrate taken. twenty-five by 100 per

cubic grams cent.

centimeters of soil.

solution.

(a) 25 0.6113 gram 0.4426 gram

(b) 25 0.4371 „ 0.3324 28.0

gram

——————

Mean 0.4399 „

(NH₄)₂SO₄ cubic Number cubic Half normal acid N absorbed Salt

centimeters centimeters neutralized. by 100 absorbed

filtrate taken. one-half normal grams per

acid neutralized soil. cent.

by fifty cubic

centimeters of

solution.

(a) 50 10.00 7.25 grams

(b) 50 7.25 „ 0.0964 27.5

gram

————

Mean 7.25 „

NaNO₃ cubic Number cubic Cubic centimeter N absorbed Salt

centimeters centimeters N₂O₂ N₂O₂ at 0° and by 100 absorbed

filtrate taken. afforded by ten 1000 grams per

cubic millimeters. soil. cent.

centimeters of

solution at 0°

and 1000

millimeters

pressure.

(a) 10 16.63 16.77 grams

(b) 10 16.70 „ none 00.00

—————

Mean 16.73 „

Upon comparing the figures it will be found that the absorption, passing

from the greatest to the least, is as follows: phosphoric acid (P₂O₆),

potassium sulfate, ammonium sulfate, potassium chlorid and sodium

nitrate.

Principles and practice of agricultural analysis. Volume 1 (of 3), Soils · 第 11 / 54 段