One of the side tubulures carries a burette, B, containing five per cent

sulfuric acid, the other one filled with a hyposulfite solution of known

strength. The middle tubule serves to introduce a glass tube through

which carbon dioxid or illuminating gas passes for the purpose of

driving out the air from the solution and the flask. If carbon dioxid be

used it should be generated by the action of sulfuric acid on marble.

The cork holding this is furnished with a slot or valve to permit the

exit of the air and the excess of the gas.

Before inserting the middle stopper, a few cubic centimeters of

potassium iodid solution and a few drops of thin starch paste are added,

the potassium salt being always used in excess of the nitrite supposed

to be present.

[Illustration:

FIGURE 89. METHOD OF CHABRIER.

]

After the air has all been expelled from the flask the analytical

process is commenced, the carbon dioxid current being slowly continued.

At first, a few drops of the dilute sulfuric acid are allowed to flow

into the flask. As soon as the liquid is colored blue a sufficient

quantity of the thiosulfate solution is added to discharge the color.

The successive addition of acid and thiosulfate is continued until

another portion of the acid fails to develop the blue color, thus

indicating that all the nitrite has been decomposed. From the volume of

thiosulfate used the quantity of nitrite is calculated.

_The Thiosulfate Solution._—The thiosulfate solution is conveniently

prepared, when a large number of analyses is to be made, by dissolving

twenty-five grams of pure crystallized sodium thiosulfate in 100 cubic

centimeters of water and diluting any convenient part thereof to 100 or

1,000 cubic centimeters, according to the supposed strength of nitrite

solution under examination.

For fixing the strength of the solution dissolve 3 348 grams of pure

iodin in a solution of potassium iodid and make the volume up to one

liter. Each cubic centimeter of this solution corresponds to one

milligram of nitrous acid. A given volume of the iodin solution is

titrated against the thiosulfate, but it is best not to add the starch

paste until the greater part of the iodin has been removed. The starch

paste is then added and the titration continued until the blue color has

been discharged. Ten cubic centimeters of the iodin solution is a

convenient quantity for the titration and the thiosulfate should be

diluted by adding to ten cubic centimeters of the solution mentioned

above, 990 cubic centimeters of water. Each liter of this dilute

solution contains two and a half grams of the sodium thiosulphate.

_Example._—Let us suppose that it has required 21.3 cubic centimeters of

thiosulfate to absorb ten cubic centimeters of the iodin solution;

further that ten liters of water have been evaporated and titrated as

described above, and that the volume of thiosulfate employed was 13.8

cubic centimeters. From this is derived the following formula: (13.8 ×

10)/(21.3) = 6.48 milligrams of nitrous acid; or 0.648 milligram per

liter.

=508. Estimation of Nitrous Acid By Coloration of Solution of Ferrous

Salt.=—This method, due to Picini is based on the production of the

well-known brown color formed by the action of nitric oxid on a ferrous

salt.[339] The nitrite is decomposed by heating with acetic acid while

nitrates thus treated do not develop the reaction. The tint produced is

imitated as above by testing against a standard solution of nitrite.

Ferrous chlorid is to be preferred to other ferrous salts for the above

purpose. The process should be carried on in solutions free of air.

=509. Estimation of Nitrous Acid By Decomposition with Potassium

Ferrocyanid.=—The method of Schaeffer was first described in 1851, but

little attention has been paid to it since. The method has lately been

brought into notice again by Deventer.[340]

The reaction depends upon the decomposition of nitrous acid by potassium

ferrocyanid in the presence of acetic acid with the formation of

potassium ferricyanid and acetate, and nitric oxid. The reaction is

expressed by the following equation:

2K₄FeCy₆ + 2HNO₂ + 2C₂H₄O₂

= K₆Fe₂Cy₁₂ + 2KC₂H₃O₂ + 2NO + 2H₂O.

[Illustration:

FIGURE 90.

SCHAEFFER’S NITROUS ACID METHOD.

]

A eudiometer with a glass stop-cock is arranged as shown in Fig. 90. The

lower part of the eudiometer is closed with a rubber stopper carrying a

glass tube which ends in the pan _f_ as shown at _e_. The eudiometer is

filled to the stop-cock with a solution of potassium ferrocyanid of

about fourteen per cent strength. The dish _f_ is also filled up to the

height indicated in the figure with the same solution. The solution of

nitrite is used in such quantities that the nitric oxid evolved will

occupy a space of about twenty cubic centimeters. The whole eudiometer

should contain about fifty-seven cubic centimeters. The nitrite solution

is added to the eudiometer by means of a funnel, _a_. The vessel

containing it is washed out with a little water and then with acetic

acid and finally with a few cubic centimeters of strong potassium

ferrocyanid solution. The last fluid flows through the solution of

nitrite and acetic acid and thus mixes it with the solution already in

the eudiometer. The liquids reacting on each other float together on the

strong ferrocyanid solution and each one of them is at once pressed

downward by the gases which are evolved. When the evolution of gas

becomes slower the apparatus should be shaken for about twenty minutes,

moving it back and forth without taking the bottom of it out of the

dish. When there is no longer any evolution of gas, water is added

through a slowly, until the heavy potassium ferrocyanid solution is

almost completely driven out of the eudiometer. The opening of the tube

at _e_ is then closed with the thumb, the apparatus is taken out of the

dish, shaken for some time in a vertical direction and again placed in

the dish. Water of any required temperature is now allowed to flow

through the jacket, _g_, _h_, until the temperature is constant, when

the volume of nitric oxid is read. The whole experiment can be performed

in less than an hour. Operating in this way, at the end there is in the

eudiometer a liquid which is not very different from water and one whose

coefficient of solubility for nitric oxid is practically the same as

that of water. The gas volume read is to be corrected for temperature,

pressure, tension of the aqueous vapor, height of the water column in

the eudiometer, and, after the end of the calculation, five per cent of

the volume of water remaining in the eudiometer is to be added to the

volume of gas obtained. This is to compensate for the volume of the gas

absorbed by the water. The method gives good quantitive results.

=510. Method of Collecting Samples of Rain Water for

Analysis.=—Warington collects rain water in a large leaden gauge having

an area of 0.001 of an acre.[341] Of the daily collection of rain, dew,

and snow water, an aliquot part amounting to a gallon for each inch of

precipitation is placed in a carboy; at the end of each month the

contents of the carboy are mixed, and a sample taken for analysis. In

the carboy receiving the rain for nitric acid estimation a little

mercuric chlorid is placed each month with the view of preventing any

change of ammonia into nitric acid. It may be doubted, however, if this

precaution is necessary, as the rain water thus collected always

contains a very appreciable amount of lead; and experiments have shown

that on the whole, rain water more frequently gains than loses ammonia

by keeping.

_Preparation of the Sample._—The method first employed by Warington was

to concentrate ten pounds of the rain water in a retort, a little

magnesia being used to decompose any ammonium nitrite or nitrate

present. Concentration by evaporation in the open air, and especially

over gas, results in a distinct addition to nitrites present. When

concentrated to a small bulk, the water is filtered and evaporated to

dryness in a very small beaker. The nitrogen as nitrates and nitrites is

then determined by means of the methods already described.

DETERMINATION OF FREE AND ALBUMINOID AMMONIA IN RAIN AND DRAINAGE WATERS

AND SOIL EXTRACTS.

=511. Nessler Process.=—The quantities of free ammonia in rain and most

drainage waters are minute, but may reach considerable magnitude in some

sewages. By reason of these minute proportions, gravi- and volumetric

methods are not suitable for its quantitive determination. Recourse is

therefore had to the delicate colorimetric reaction first proposed by

Nessler. This reaction is based on the yellowish-brown coloration

produced by ammonia in a solution of mercuric iodid in potassium iodid.

The coloration is due to the formation of oxydimercuric ammonium iodid,

NH₂Hg₂OI, and takes place between the molecule of free ammonia and the

mercuric iodid dissolved in the alkaline potassium iodid as represented

by the following equation:

Hg—O—Hg—I Hg

/ / \

O + 2H₂N = 2O NH₂I + H₂O

\ \ /

Hg—O—Hg—I HG

_Nessler Reagent._—Dissolve thirty-five grams of potassium iodid in 100

cubic centimeters of water. Add to this solution gradually a solution of

seventeen grams of mercuric chlorid in 300 cubic centimeters of water

until a permanent precipitate of mercuric iodid is formed. Add now

enough of a twenty per cent solution of sodium hydroxid to make 1000

cubic centimeters.

The mixed solutions, at room temperature, are treated with additional

mercuric chlorid until the precipitate formed, after thorough stirring,

remains undissolved. This precipitate is then allowed to subside, and

when the supernatant liquid is perfectly clear, it is decanted or

filtered through asbestos and kept in a well-stoppered bottle in a dark

place. The part in use should be transferred to a smaller bottle as

required. The solution should be made for a few days before using, since

its delicacy is increased by keeping. The nessler reagent should show a

faint yellow tint. If colorless it is not delicate, and shows the

addition of an insufficient quantity of mercuric chlorid. When properly

prepared, two cubic centimeters of the reagent poured into fifty cubic

centimeters of water containing 0.05 milligram of ammonia will at once

develop a yellowish-brown tint.

_Preparation of Ammonia-Free Water._—To pure distilled water add pure,

recently-ignited sodium carbonate, from one to two grams per one liter,

and distill. When one-fourth of the whole has passed over, the

distillate may be regarded as free from ammonia; fifty cubic centimeters

of the following distillate should give no reaction with the nessler

reagent. The distillation should be continued until the residual volume

in the retort is about one-fourth of the original, and the distillate

free of ammonia is carefully preserved in close glass-stoppered bottles

previously washed with ammonia-free water. Pure water, free of ammonia

may also be obtained by distilling with sulfuric acid.

_Comparative Solution of Ammonium Chlorid containing 0.00001 gram

Ammonia in one cubic centimeter._—Dissolve 3.15 grams H₄NCl in

ammonia-free water and make the volume up to one liter. Take ten cubic

centimeters of the above solution and dilute to 1000 with water, free

from ammonia.

_Solution containing 0.00001 gram Nitrogen in one cubic

centimeter._—Dissolve 3.82 grams H₄NCl in water, free from ammonia and

dilute with same to 1000 cubic centimeters. Dilute ten cubic centimeters

of the above solution to 1000.

_The Distillation._—Any kind of suitable retort or flask connected with

a good condenser may be used. The capacity of the retort should be from

700 to 1,000 cubic centimeters. The retort and condenser preferred by

Leffmann and Beam are shown in Fig. 91. Any good lamp may be used in

which the flame is under complete control. The gauze burner shown in the

figure is easily controlled and distributes the heat evenly over the

surface of the retort thus diminishing the danger of fracture. The

apparatus having been previously rinsed with distilled water receives

500 cubic centimeters of the liquid to be tested for ammonia, together

with a few pieces of recently ignited pumice stone to prevent bumping

and five cubic centimeters of the twenty percent sodium carbonate

solution to render its contents alkaline. The water is raised to the

boiling-point and with gentle ebullition fifty cubic centimeters of

distillate collected. The distillate is conveniently collected in a

color-comparison cylinder of thin white glass and flat bottom, about two

and a half centimeters in diameter, and marked at fifty and one hundred

cubic centimeters. Two cubic centimeters of the nessler reagent are

added and if ammonia be present a yellowish-brown color will be

developed, the intensity of which is matched by taking portions of the

ammonium chlorid solution, diluting to fifty cubic centimeters with pure

water and treating with the same quantity of the nessler reagent. The

process is repeated until a distillate is obtained which gives no

reaction for ammonia. The sum of the quantities obtained in the several

distillates gives the total amount of ammonia in the 500 cubic

centimeters of the water taken. In most cases practically all the

ammonia is obtained in three or four portions of the distillate.

[Illustration:

FIGURE 91. RETORT FOR DISTILLING AMMONIA.

]

_Albuminoid Ammonia._—The residue from the process just described is

employed for the purpose of determining the albuminoid ammonia. Two

hundred grams of potassium hydroxid and eight grams of potassium

permanganate are dissolved in 1,000 parts of distilled water. Fifty

cubic centimeters of the solution are placed in a porcelain dish with

100 cubic centimeters of distilled water and evaporated to fifty cubic

centimeters. This liquid is placed in the retort and the distillation

resumed and continued until an ammonia-free distillate is obtained. The

total albuminoid ammonia is determined by taking the sum of the

quantities in the several distillates.

=512. Nessler Reagent of Ilosvay.=—To secure greater delicacy in

nesslerizing, Ilosvay uses a reagent prepared as follows:[342]

Dissolve two grams of potassium iodid in five cubic centimeters of

water, heat the solution gently, and add three grams of mercuric iodid.

After the solution is cooled, add an additional portion of three grams

of the mercury salt, and then twenty cubic centimeters of water, and

wait until the precipitation is complete. After filtering, there are

added to the filtrate from twenty to thirty cubic centimeters of a

twenty per cent solution of potassium hydroxid. Only the limpid

supernatant liquid is used in the analytical work. With this reagent,

Ilosvay has been able to detect 0.02 milligram of ammonia in 110 cubic

centimeters of water.

AUTHORITIES CITED IN PART SEVENTH.

Footnote 274:

Comptes rendus, Tome 84, pp. 301, et seq. Journal of the Chemical

Society, (Transactions), 1878, p. 44; 1879, p. 429; 1884, p. 637.

American Chemical Journal, Vol. 4, p. 452. Proceedings of the American

Association for the Advancement of Science, Vol. 41, p. 105. Annales

de l’Institut Pasteur, Tome 4, pp. 218, 257, 760; Tome 5, p. 92.

Footnote 275:

Comptes rendus, Tome 118, p. 604.

Footnote 276:

Bulletin de la Academie royale de Belgique, [3], Tome 25, p. 727.

Journal of the Chemical Society, (Abstracts), June, 1894, p. 248.

Footnote 277:

Chemical News, Oct. 13, 1893, p. 176.

Footnote 278:

Comptes rendus, Tome 109, p. 883.

Footnote 279:

Op. cit. supra, Tome 89, pp. 891, et seq.

Footnote 280:

Journal of the Chemical Society, (Transactions), Vol. 45, pp. 645, et

seq.

Footnote 281:

Jahresbericht der Agricultur Chemie, 1881, S. 43.

Footnote 282:

Annual Report of the British Board of Health, 1883.

Footnote 283:

Annales de l’Institut Pasteur, 1891, S. 93.

Footnote 284:

Philosophical Transactions of the Royal Society of London, Vol. 181,

(1890).

Footnote 285:

Zeitschrift für Biologie, Band 9, S. 172.

Footnote 286:

Archives de Science Biologique à St. Petersbourgh, Tome 1, p. 1331.

Footnote 287:

Annales de l’Institut Pasteur, 1891, pp. 581, et seq.

Footnote 288:

Op. cit. supra, 1891, Plate 18, Fig. 2.

Footnote 289:

Op. cit. supra, 1891, pp. 595, et seq.

Footnote 290:

Op. cit. supra, 1891, Plate 18, Fig. 1.

Footnote 291:

Journal of the Chemical Society, (Transactions), 1891, pp. 498, et

seq.

Footnote 292:

Annales de l’Institut Pasteur, 1891, pp. 605, et seq.

Footnote 293:

Journal of the Chemical Society, (Transactions), 1882, p. 357.

Footnote 294:

Annales de Chimie et de Physique, 1854, Tome 40, p. 479. Zeitschrift

für analytische Chemie, 1870, S. 24; 1877, S. 291. Die

Landwirtschaftlichen Versuchs-Stationen, Band 12, S. 164. Journal of

the Chemical Society, (Transactions), 1880, p. 468; 1882, p. 345;

1889, p. 537.

Footnote 295:

Encyclopedie Chimique, Tome 4, p. 151.

Footnote 296:

Annales de la Science Agronomique, 1891, pp. 263, et seq.

Footnote 297:

Berichte der deutschen chemischen Gesellschaft, Band 23, S. 1361.

Footnote 298:

Zeitschrift für analytische Chemie, Band 9, S. 24, 401. Die

Landwirtschaftlichen Versuchs-Stationen, Band 9, S. 9. Berichte der

deutschen chemischen Gesellschaft, Band 6, S. 1038.

Footnote 299:

Zeitschrift für analytische Chemie, Band 33, S. 200.

Footnote 300:

Apotheker Zeitung, 1891, Band 5, S. 287.

Footnote 301:

Sutton’s Volumetric Analysis, 3d edition, p. 316. Warington, Journal

of the Chemical Society, (Transactions), 1879, p. 376.

Footnote 302:

Report of the National Board of Health, 1882, p. 281.

Footnote 303:

Berichte der deutschen chemischen Gesellschaft, Band 11, S. 432.

Footnote 304:

Bulletin de la Société Chimique, [3], Tomes 11–12, p. 625.

Footnote 305:

Encyclopedie Chimique, Tome 4, p. 154.

Footnote 306:

Zeitschrift für analytische Chemie, Band 7, S. 412. Fresenius,

Quantitative Analysis, Grove’s translation, special part, p. 118.

Footnote 307:

Journal of the Chemical Society, (Transactions), 1879, pp. 578, et

seq.

Footnote 308:

Bulletin 38, Department of Agriculture, Division of Chemistry, p. 204.

Footnote 309:

Die Landwirtschaftlichen Versuchs-Stationen, Band 41, S. 165.

Footnote 310:

Chemiker Zeitung, 1892, Band 16, S. 1952.

Footnote 311:

Zeitschrift für angewandte Chemie, 1893, S. 161.

Footnote 312:

Chemiker Zeitung, 1889, No. 15.

Footnote 313:

Vid. op. cit. 38, 1890, S. 695.

Footnote 314:

Archives de la Société Physique de Genève, Tome 31, p. 352.

Footnote 315:

Chemiker Zeitung, 1890, S. 1410.

Footnote 316:

Chemisches Centralblatt, 1890, Band 2, S. 926.

Footnote 317:

Vid. op. cit. 38, 1891, S. 241.

Footnote 318:

Vid. op. cit. 34, 1889, p. 538.

Footnote 319:

Op. cit. supra, 1881, p. 100.

Footnote 320:

Op. cit. supra, Vol. 57, p. 811.

Footnote 321:

Op. cit. supra, 1891, pp. 530, et seq.

Footnote 322:

Op. cit. supra, 1874, p. 630, and 1885, p. 86.

Footnote 323:

Sutton’s Volumetric Analysis, 4th edition, p. 103.

Footnote 324:

American Journal of Science, Vol. 44, p. 117.

Footnote 325:

American Chemical Journal, Vol. 11, p. 249.

Footnote 326:

Journal of the Franklin Institute, Vol. 127, p. 61.

Footnote 327:

Zeitschrift für Hygiene, Band 2, S. 163.

Footnote 328:

Chemical News, 1889, Nov. 29, 261.

Footnote 329:

Vid. op. cit. supra, p. 51.

Footnote 330:

Examination of Water for Sanitary and Technical Purposes, p. 28.

Footnote 331:

Chemical News, 1890, Jan. 10, p. 15.

Footnote 332:

Zeitschrift für angewandte Chemie, 1894, Heft 12, S. 347.

Footnote 333:

Journal of the Chemical Society, (Abstracts), 1891, p. 489.

Footnote 334:

Zeitschrift für analytische Chemie, Band 18, S. 597. Zeitschrift für

angewandte Chemie, 1889, S. 666. Bulletin de la Société Chimique, [3],

Tome 2, p. 347.

Footnote 335:

Op. cit. 57, p. 30.

Footnote 336:

Zeitschrift für angewandte Chemie, 1894, S. 349.

Footnote 337:

Bulletin de la Société Chimique, [3], Tomes 11–12, p. 218.

Footnote 338:

Encyclopedie Chimique, Tome 4, p. 262.

Footnote 339:

Peligot, Traité de Chimie Analytique appliqueè à Agriculture, p. 261.

Footnote 340:

Berichte der deutschen chemischen Gesellschaft, 1893, S. 589.

Footnote 341:

Journal of the Chemical Society, 1889, p. 537.

Footnote 342:

Op. cit. 64, p. 216.

NOTE.—On page 158, paragraph 172, third line, insert, “and determining

matters dissolved therein,” after “flow.”

PART EIGHTH.

SPECIAL EXAMINATION OF WATERS, VEGETABLE SOILS, AND UNUSUAL SOIL

CONSTITUENTS.

=513. Further Examination of Waters.=—Having described in the preceding

part the approved methods of determining the oxidized nitrogen in waters

and soil extracts there remains to be considered the examination of

waters for other substances of importance to agriculture. Rain waters

add practically nothing to the soil but nitric acid and ammonia, and,

therefore, demand no further discussion here. In drainage and sewage

waters, in addition to the oxidized nitrogen, there may be sufficient

quantities of phosphoric acid and potash to make their further analysis

of interest. But by far the most practical point to be considered is in

the case of waters used for irrigation purposes where the continued

addition to the soil of mineral matters may eventually convert fertile

fields into barren wastes. In irrigated lands there is practically no

drainage and the whole of the water is removed by superficial

evaporation. It is easily seen how these mineral matters tend to

accumulate in that part of the soil in which the rootlets of plants seek

their nourishment.

=514. Estimation of Total Solid Matter.=—The total solid contents of a

sample of water are determined by evaporating a known volume or weight

to dryness and weighing the residue. For comparative purposes a given

volume of water may be taken if the solid contents do not exceed four

grams in a United States gallon. The water should be measured at a

temperature of about 15°.5. Where the content of mineral matter is

greater it is best to weigh the water and calculate the solid contents

to parts per one hundred thousand. For practical purposes in the United

States it is customary to state the content of solid matter in grains

per gallon. Since, however, the gallon has so many different values it

is always necessary to indicate what particular measure is meant.

In ordinary spring and well waters the volume to be used is conveniently

taken at 100 cubic centimeters. To avoid calculation a volume in cubic

centimeters corresponding to some decimal part of a gallon in grains may

be taken and the weight in milligrams will then be equivalent to the

grains per gallon. Thus in the imperial gallon which contains 70,000

grains of distilled water at 15°.5, seventy cubic centimeters may be

taken. If the residue weigh twenty-five milligrams the water contains

twenty-five grains of solid matter per gallon. The United States gallon

at 15°.5 contains 58,304 grains of distilled water. In this case 58.3

cubic centimeters should be used, or double this amount and the weight

in milligrams be divided by two.

The evaporation may be made in a platinum, porcelain, or aluminum dish,

preferably with a flat bottom; The dish does not need to hold the whole

volume at once, but the water may be added from time to time as the

evaporation continues. The dish, however, should, as a rule, hold not

less than 100 cubic centimeters. The evaporation is best conducted over

a steam-bath, and after the complete disappearance of the liquid the

heating should be continued until the residue is perfectly dry.

In the case of mineral waters highly impregnated with inorganic salts, a

smaller volume or weight may be taken, and greater care must be

exercised in drying the residue. For the purpose of qualitively

determining the percentage of special ingredients, quantities of the

water should be taken inversely corresponding to the content of the

ingredient desired. In general, it will not be necessary to evaporate

the sample to complete dryness, but only to concentrate it to a volume

convenient for the application of the analytical process. Where a

complete quantitive analysis of the solid residue is desired, a

sufficient quantity of the water is evaporated to give a weighable

amount of the least abundant ingredient. The total solid content of the

water having been previously determined, the actual weight or volume of

the water taken to obtain the above residue is of no importance.

Principles and practice of agricultural analysis. Volume 1 (of 3), Soils · 第 51 / 54 段