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The penetration of moisture into soilsas affected by chemical
composition andphysical properties of irrigation waters
Item Type text; Thesis-Reproduction (electronic)
Authors Ayers, Alvin Dearing, 1909-
Publisher The University of Arizona.
Rights Copyright © is held by the author. Digital access to this
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Link to Item http://hdl.handle.net/10150/333156
http://hdl.handle.net/10150/333156
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TEE PENETRATION OF MOISTURE INTO OILS AS. AFFECTED BY
CHEMICAL COMPOSITION AND PHYSICAL PEOPERTIES OF
IRRIGATION WATERS
Approved:
by
Alvin D. Ayers
Submitted in p rtial fu1fiient of the
requirements for te degree of
Master of Sdience
in the Co1leg3 of Azriculture, of the
University of irjzoua
yW,4014.
iaior adviser10 I
-
E777/
6dAL
ACKNOWLEDGYENTS
The author takes this opportunity to acznowledge the
help and assistance given by the members of the Department .
of Agricultural Chemistry, and especially that of Dr. T. F.
Buehrer, with whom the work was done., for his help and con-
structive criticisms in the supervision of this research.
The author also wishes to thank Mr. Karl Harris for his
assi3tance in obtaining the samples of soil used in this
study.
9496G
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TABLE OF CONT-: S
PageI. Introduction 1-4
Importance of the problemPurpose of the inve stlgatiou
,,,eoretical aspects of the prob1e4Physical factors affecting
depth and rate of'-penetrationAssumptions-involved in the
application ofPoisouillets Law to water penetrationphenomena .
xII rvey of th lite.ature on water penetrationBriggs; Mechanics
of soil moistureMing: Flow of water thrauel-soils14aaughli.n;
Capillary movement of soil moistureecofieldt Uovement of water in
irrigated soilsHardy: Percolation -la colloidal
soilslicGeorge¡'Breazelle* vmd Burgess* Freezing up- of i13 - -
-reGiorge: Effect of fertilizerson water,
penetratioaKarraker; Effect of soluble sa ts on soilmoisture
IT0 Experimental work 1Physical and chemical soil factors '
vestIgated
Solis studiedDescriptionMechanical analysisMoisture equivalent
and saturation percentageChemical analysis of soli extractNature of
base excbange coat, x
'Irrigation waters studiedDescription of sourceChemical
tomPosition
Experiments on viscosityDescription of' vlsco-sime erPrecision
of measurementsCalibration of vesitels
Calculation of relative viscosity from flow dataComparisons of
results obtained with different
vesselsEalt solutions wed
ConcentrationsDensityViscosity measu ements
At various concentrationsAt various temperaturesAt various salt
mixturesAt various pff values
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Visotty determinations onextracts at various soilvw_r ratios
Irrigation watersSurface tension moasurclents
Pure solutionsSoil extracts at various soillwater rPt- sPure
solutions at dirferent pli values
no of water througla soil columnsOutline of methodEffect or
vary1-.ng flit i -_ content
V. Discussion of results 5
Vumaary 0C-.67
VII Bibliomtaphy S 70
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LIST OF TABLS
PageI. MECHANICAL ANALYSIS OF SOIL SAMPLES 42II. , MOISTURE
EQUIVALENT AND SATURATION PERCENTAGES
OF SOILS 23
III. SOLUBLE SALTS IN AIR-DRY SOIL 25IV. REPLACEABLE BASES IN
SOILS STUDIED 28
V. ANALYSIS OF IRRIGATION WATERS 30
RELATIVE VISCOSITIES OF SODIUM CHLORIDE AT
DIFFERENT TEMPERATURES AS -DETERMINED IN FIVE
DIFFERENT VISCOSIMETERS
VII. RELATIVE VISCOSITIES OF SINGLE SALT SOLUTIONS
AT VARIOUS TEMPERATURES AND CONCENTRATIONS 45
VIII. RELATIVE VISCOSITY OF SOLUTIONS OF MIXED SALTS 49
IX. SURFACE TENSION DATA FOR SALT SOLUTIONS AND
SOIL EXTRACTS 57
L.COMPOSITION OF ZEOLITIC COMPLEX 65
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LIST OF FIGURES
DESIGN OF VISCOSIMETERPage.53a
2. CALIBRATION CURVES FOR VISCOSIMETERS AT
DIFFERENT TEMPFAATORES 57a
a. RELATIVE VISCOSITY OF SODIUM CHLORIDE 45a
4. RELATIVE VISCOSITY OF SODIUM. SULPHATE 4Bb
5. RELATIVE VISCOSITY OF SODIU2 BICARBONATE 45c
6. RELATIVE VISCOSITY OF CALCIUM CHLORIDE 454
7". RELATIVE VISCOSITY OF CALCIUM SULPHATE 45e
8. AVERAGE RELATIVE VISCOSITIES OVER WERURE
RANGE OF 20° - 40° C. 45f
9. ABSOLUTE VISCOSITY AS A FOCTION OF TEMPERATURE 47a
10. RELATIVE VISCOSITY OF SOLUTIONS or SALT MIXTURES,
NaCI-Na2SO4 48a
11. RELATIVE VISCOSITY OF SOLUTIONS OF SALT MIXTURES
CaS0*-CaC12 s CaS044NaC1s NaCI-CaC12, NaC1 NaliCO3 48b
12. VISCOSITY OF SOIL EXTRACTS 54a
13. INITIAL MOISTURE CONTENT AS RELATED TO
PENETRATION 59a
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THE PENETRATION OF MOISTURE INTO 80 S AS AFFECTED BY
CHEMICAL COMPOSITION AND PHYSICAL PROPERTIES OF
IRRIGATION WATERS
,orw1040Am0.0.ow...m.
In =alas=
Every agri6ultural region as well as every arable soil
type._may be regarded as subject to some limiting factor.* -
which's by its insufficiency* limits orHinhibits other desir
able:factors which are necessary for. optimum growth or
yield
or crops, Usually such a limiting factor is attributed to
a single cause or condition in the soil* but it is more
likely to be the resultant of a number of different forces.
This . idea is embodied in a striking definition of a plant
by
3, F Breazeale* Biochemist of the Arizona Agricultural Ex
pertinent Station* when he says :. oThe plant is the vector
sum _of all of the influences to Which it has been.
subjected
during its era of adaptation°. In like manner* one might
define the soil as the vector sua of all of the forces*
chemical* physical biological climatic* or geological,.
which have at various times acted upon the parent rock to
bring the soil to Its preseat condition,
For this reason what appears to be a limiting factor
may in reality be the resultant of several forces* certain
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of -which predominate over the rest. The effect of such a
limiting factor is complicated by the action of the forces
mentioned above, and, because of the simultaneous action of
these forces almost any problem in soil research faces its
principal difficulty in singling out certain variables for
experimental measurement while at the same time keeping the
,'other. -r.2nditions constant.
The limiting factors in soils are probably as varied
le 'soils themselves. In one soil it may be the acidity
or ,alkalinity, in -another, salinity, temperature, nutrient
deficiencies, or soil moisture. In arid regions soil moist--
ure is considered to be the limiting factor tor profitable
agriculture. Where irrigation is practised the problem of
water penetration is an all-important one if losses by
evaporation are to be reduced to a minimum and the plant is
to receive the amount of 'moisture needed for its best
growth,
Irrigation practice has in recent years (1) concerned
itself primaril with the physical conditions of water appli-
cation, such as the head of water applied, the distribution
of the water as influenced by the slope of the land, fr
queny of irri ation, depth of application, and the downward
penetration of water and subsequent distribution. Such re
sults based upon sampling and moisture determinations upon
the soil at various 'intervals between p.Tiods of irri-ation
have yielded significant facts concerning the rate of water
movement in the soil.
-
should be noted, however, that in t,e highly saline
and gezeraUj alkaline soils of the desert, the accumulated
mi4eral .saltS rimy in time prove to be the limiting
condition.
This 1s particularly true if unwise irrigation,
practices:are
employed.. In many cases, to be sare,..the salinity or alka-
linity- are indigenous to the region and brave not
necessarily
resulted from Vad irrigation practices. There are instances
*here even with a bountiful supply of good water, reclama
tion:.of such areas is .either impossible or impractical .
It is perhaps more ,proper, therefore, to refer tø the
limiting condition of arid soils as a combination of the tac
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1,tor:or soil moisture on the one hand and an excessive
saline
or alkali. condition on the other. The high concentrations
.of. Oluble salts present in the water, as soon or shortly
after it is applied to the, soil, may very profoundly affect
the properties of water that are involved in water
penetra...
tion From the standpoint of the plant, the accumulation of,alts
in the feeding zone creates. a condition 'which in time
Tay avershadow, the soil moisture iactor. T11, nutritional.
'disorders. characteristic of. desert soilSi mentioned by
MCGedne and BreazeaIe. (2)0 are the resul,t tot only of
paired nutrition due to actual alkalinity tu t' also of
paireViaer intake. In ot4 r,Words, tho two factors of soil
moisture and salinity are int,r-de
the zazeexchange complex is an excellent eapIe of the effect
of alkali salts upon the penetration and distribution of
t. Th7a behavior of
-
moisture in the soi
oose A 4 es
The purpose of the present investigation was to study
certain paterrelationsblps of moisture penetration soil
alkalinity, and soil salinity. The factors studied re those
of sa lt composition, salt concentration temperature,
colloid content, and their effects upon those properties or
water wilich are ,closely linked up with water movement in
soil -,.. namely, viscosity and surfate teasion. These
studies
' were sup lamented by similar measurements upm xtracts from
three typical soils of the Salt River Valley, each of which
exhibited st.r1kin1y different yroperties with respect to
their composition and water penetration. A correlation was
made between their mechanical compositions chemical consti-
tution and water penetration. Certain studies were also
made on the flow of water through these soils under
controlled
conditions to observe, if possible, the e f et of varying
the
initial moisture content. From these various studies it has
been, possible to draw some ton:Ausions wtich may prove
helpful
in studying the probl _m of water penetration.
heo ca as " of te robler
The efficient us of water in agricultural practice may
depend as much upon the rate at 'which it penetrates into
the
soil as upon the depth to which it may penetrate under a
given
set of conditions. The time factor is it)portant since it is
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desirable to reduce evaporation losses to-a.minimum and
not to waterlog the soil for any pariod of i,..e. However,
the growing plant is the main ran for irrigation and also
the ultimate judge of the efficacy of the irrigation method
euployed. The soil moistur6 should move. at least as fast as
the plant withdraws it and it muat not be present in a4ounts
whichwill interfere with the respiration of the roots. In
the Lecì:a21is1 of water penetratic;:a or-mOvement ',Ile depth
to
which.it will penetrate is1 but slightly affected by
gravity;
.it depends primarily upon th. sua2face tension of the water
and4ndirectly upon the physical and ch.claical factors'that
kTeOt the surface tension. The rate of penetration, however#
depends chiefly upon the viscoaity of the water (salt solu
.tion
Thase two factors, surface
quite closely interrelated, one
teasioa and viscosity, are
being approximately a linear
fUn6tion. of the other for a given solution -Of varylnE
cancen
tratian but at constant teuperature. It does- not
110w-over, that these properties
with the temperature .
vlations appear as
affect the surface
and deviations are observe
will change at the .,:avie rate
In fact it is known that marked de-
the tepera
tendon arad
solutions changes.
It has long be
6
ure rises. Salts do not all
viscozlity in the same manner,
the cr,ncentration of the
n recognized that textural and structural
characteristics have much to da with the cap nary movement
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of water in soils. genorai, the finer the te ure., the.
slower the movement d the great retention os. : yiater
in the soil. . Various single-value .co Its have been pub-
lished in the soil literature to r present the physical
state
aggregation -of the soil particles, ofar as such state
m ay affect . the moisture relations. - . For examp e the
liporos.
it is a quantity often determ.ined in c-onnection with moist,ure
studies*. it is to be . sure-, of the greatest importance
a a measure Of the a.hi-iit of the soil to retain or hold
wate., but it is of less value in the matter of water move
meat in the latter ease, . the continuá,tY of the capillary
pores as well as their size is the principal determining
factor. ., . .
Al ough there. is an extensive literature on the subject
of water p.enetratio.n, . it appears that a relatively
limited
amount of work has been done to indicate and explain how th
chemical composition of the water applied to a soil affects
its penetrating properties. Of the various attempts to represent
the flow of water through soils based upon Poisseuillel s
Law it is tacitly assuMed that the viscosity the penetrating
soiution is the same as. that -ot pure wat or that it is
a constant irrespective of its content of di f erent salts
different concentrations. It will be hown m the results
of . this stu.dy that this assumption i ot tenable, but that
the '..effect of the dissolved salts and of d. .sersed
colloida,.
material upon the viscosity may be so great as to render the
-
flow equations invalid, or at least in serious error. This
is especially true as found from studie at different
&Mat
water ratios, that the viscosity rises rapidly as the soil:,
water ratio is increased.
aymtwn.e_it_tesza_tem...pintaio
. Before presenting the results of' the present investiga-
tion; it mill be of interest to review briefly the principal
research papers that have been published on this subject.
:The problem has been approached from various points of
view,
dealing on the one hand with the pure mechanics of soil
moisture movement, the capillary forces involved, the capil-
lary potential, and the effect of texture, al.V on the other
with
the chemical factors of character of the base exchange
complex,
effect of fertilizers, and the effect of alkali salts
naturally
present in soils which have been exten iv ly studied.
Briggs (3) has presented a general discussion of the fae .
tors which enter into the mechanics of ioil'moisture, Be In
cludes the effect of gravity sur4ace tension viscosity and
hygroscopic state of water upon the ret ntiah and movement
of
water in the soil.' The theory of surface tension of liquids
in relation to the formation and stability of the moisture
film on the soil particle is also discussed. Briggs points
out that the effect of the viscosity of water is to retard
the establishment of Moisture equilibrium and that
temperature
exerts a marked influence upan the flaw of water through
soils.
-
As .the effect of a t.s upon the viscosity was not mentioned
by this author appears that he did not consider this
variable of importance.
King ( 17) in his- studies of the of water through
-soils found variations due partly to temperature and partly
-.to dissolved salts-. The farce of surface tension is shown
to retard the action of gravity upon the cap.ill.ary-held
mouture in the soil. However, the movement of water by way
of afilm from one particle to another" depends upon three
factors:. the viscosity of th e water which reta..rdds the
rate
of such' adjustment a chau e In surface tension,. either allavi
.
i.ng the film to stretch, or causing it. to be ruptured, and
curvature of the film as determined by the size of particle.
Briggs also (3) shows from considerations pressure of a
water film resulting fr©m ts radiys of curvature, that move
meut of moisture iu the film should occur from particles of
smaller size to those of larger size. Quoting Briggs (p.
nif equal volumes of two soils are placed in coftt.act and
the
curvature of the surface is less in the first than in the :
seo.,
ond then water will move from the first to the second. if
the ecoud sail contains a greater number of capillary spaces
than the first it will contain more water -when equilibrium
is establ.ished. During this adjustment,. water will
actually
have moved from a soil contain ing a lower percentage of
water
to one having, a higher percentage. n It i the form of the
surface which determines the movement of the water.
-
The effect of the finer sizes of capillary in the finer .
textured soils is also treated. In a coarse sandy son the
interstitial spaces are relatively largeoperinitting the
water
to percolate and drain rapidly. As the texture becomes finer,.
.
the interstitial spaces become smaller, and the number- of
ac-
tual capillary spaces increases. Surface tension effects now
become pronounced, and the water tends to he held in the
capil
larie- since the extent of capillary rise varies inversely
With the radius of the ca,illary. At the same time the
viscos
ty effect increases to the point where movement is so slow
as
to be negligible. Increased watr-holdiag capacity in soils
must therefore of necessity be attended by greatly decreased
movement, or percolation. These obfservations suggest that
the
remedy for poor penetration is to found in a-condition which
will reduce the viscosity arid surface tension at the saxe
time,
so that this film pressure effect as pointed out by Briggs
be minimized sufficiently to allow movement,to occur.
McLaughlin (4) has made an extensive study of the effect
of capillarity with the purpose of explaining losses of
water
from irrigation systems, as well as the part it plays in the
distribution of irrigation water applied to the soil. xper
ments were carried out to determine the rate and extent of
capillary movement of moisture in columns of various types
of
soil under conditions such that ca illa ity was ass1stec7 by
gravity, where it. acted. against gravit- and where gravity
a factor was e iminated. The columns in which gravity was to
ay
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0
assist capillarity were inclined downwards at various angles
from the horizontal; those in which it acted against gravity
were inclined upwards at various angles from the horizontal;
and those columns in which gravity was entirely eliminated
were placed in an exactly horizontal position. Althou h the
factors of surface tension and viscosity, as affected by
pre-
sence of soluble gaits, were not 'involved in this
investigation,
it is of some interest to mention the general conclusions
reached- inasmuch as they do- indicate to what extent water
movement is influenced by the total,amount of moisture
present
in _the $oil at any given time. The author points out that
the
effect of soluble salts i not definitely known, and results
thus'far published are in many instanceS contradictory. He
also mentions the fact that while colloids influence the
move-
ment of capillary moisture in one way, the organic matter
exerts
an Influence in the opposite direction, and that it is not
de-
finitely known to what extent these factqrs may compensate
each
other, if at all.
When the results of capillary movement are plotted in terms
of inches rise against time in days, McLaughlin finds that
for
a wide variety of soils the curves are approximately
parabolic
indicating that the initial rise during he first few hours
is
very rapid the rate then slowing down markedly until about
the
fifth day when movement becomes quite Uniform. it was also
found that in the lighter soils the rate of movement is much
more rapid at the start and slows down much more quickly
than
-
in the heavier soils. The effect of Inclination with the
horizontal was found to be quite pronounced being greatest
for downward inclination and varying directly with the angle
of inclination. These findings are of importance to the
irrigation engineer in that they show clearly what distribu-
- tionof,moisture may be expected when irrigation water is
applied to sloping land. It is significant, however, that
in those soils which are known to contain higher quantities
of soluble . salts, the slowing up effect appeared to be
much
more pronounced than in, soils with a low salt content. This
might well have been the result of the gradually increasing
concentration of soluble salts in the water as the moisture
front progressed through the colum.
Scofield (5) 0 in an extended treatment entitled: "The
Movement of Water in. Irrigated Soilet has approached the
problem of water penetration from the point of view of the
effect exerted by the replaceable bases present in the ,Ase
.
exchange or ziolitic complex. of the soil. He measured the
of water penetration into soil columns, by compacting the
soil.
- (sifted through a -2-mm. sieve ) into glass tubes one-half
inrh
in diameter and 5 feet long with perforated stoppers at, the
bottom. The tubes were filled to a 4-ft. depth, clamped In.
a
, vertical position and distilled water added to a depth of
6
inches. From time to time additional portions of water were
added. The movement of the line of demarcation could be
readily followed, and readings were made in inches at the
end
-
of certain intervals of time. One of the tubes showed an
excellent rate of penetration - about 33 inches in 3 hours
while the other required 14 months to penetrate 48 inches,
the entire depth of the column. Both soils were classed as
sandy loams and resembled each other so clo ely as to be al
most indistinguishable. The difference is attributed to the
condition of the zeolitic fraction in the soils as a result
of which on of the soils was much more disper ed than the
other.
Scofield also points out that the amounts of alkali ta
soils exerts an important effect u;on the rate of pen_
ration.
For example in some of the experiments, the soils were sub-
jected to the action of certain alkali salts. lt was found
that the rate of penetration was six to eight times as fast
in the samples that had not been so trea ed. It is further-
morepointed out that when saline soils are leached, and as
a result the soil solution is greatly diluted, the soils
often
become in ermeable to water, which is the result of
defloccu*
lation of the clay colloids. Scofield does not hoAever at-
te:apt to show what the limiting concentration for
flocculation
of :ti clay colloid of the soil appears to be, and the
effect
of pH in this process was not considered. A
Hardy (6) investigated typical siliceous and lateritic
oil- of the West Indies, a teraining a 1 rge number of physi
Cal constants including sticky point, hygroscopic
coefficient
water absorption capacity, and volume expansion . The
mechanical
-
-13-
composition,. humus contenti calcium carbonate cant nt,:p
value, and the moisture content of the air-dry Soil were
also
determined. The so-called permeability constant, the volume-
of liquid that passes per second through a column of soil,
of
unit cross-section and unit lenth was also determined for -
horizontal flow for the two soil classes, using kerosene and
rater respectively as the liquids. Hardy found that the per
meability constants did not differ markedly- when kerosene
was
used-on the siliceous soils, but the lateritic soils gave
considerably lower values, probably due- to the naturally
finer subdivision of the soils. However, ,when water was
u ed, it was found that the lateritic soils are very re
dily-
permeable to water: soil from Barbados for example which
showed a clay plus silt fraction equal to 75%, and therefore
largely colloidal, had a permeability cOnstant of the same,
order of -agnitu,.4e of at average sandy or silty
non-colloidal
soil. The siliceous soils, on the other hand, were
practically
Impervious to. water When liie was added, the permeability
constant for water greatly increased. For example, the
sales.-
aus soil gave the following values for Pwx 104: Highly
calcar-
eous, .20; Calcareous, 1.81; Non-calcareous 0.37. At the
same time, the lateritic soils give pe m a i ity constants
to
ward water of 16.5 and 8.00 which are considerably higher.
These experiments give a hint as to the probable mechanism
of water movement in highly colloidal soils. The volume
expaa
sion (swelling) for the siliceous soils ranged from 60.8A to
66.9%. That of the lateritic soils was 112 and 23.3%.
cilific
-
14-
acid is a hydrophilic colloid, a gel, and it affects water
penetration in three possible ways: (1) the force of imbibi-
tion developed by the colloidal component when the soil is
moistened with water; (2) the conseauent swelling of the col
bid; (3) the extent to which water passes thrbugh the
colloid
phase. The process may be explained as follows: As soon as
the colloidal particle is wetted with water, imbibition of
water occurs and a tension or forae of imbibition is
developed
which is added to that due to capillarity ad which draws the
water from the wet to the dry portions of the soil. The ef
feet of this force may be lessened by the closing of the
pores
by swelling and to some extent by the c-,,alescence of the
par
ticles. We conceive, then, that the water moves _in part as
a
film over the surfaces of the soil particles, but also to
appreciable extent through the colloidal coating of the
parti-
iiei. It has not yet been definitely established whether the
soil Colloids behave as semi-permeable membranes* or whether
they act esseiltially like porous materials having
re1attve1y
large capillaries.
The above deductions wre made for siliceous and lateritic
sails here the soluble salt content was very low. The situa-
lOn. is quit different in ,ilkaline calcareous soils. The
flocculating action of the 'alkali salts upon the soil
colloid
s to some extent offset by the high p0 'which tends to
disperse
tLeni The soils investigated by -Hardy were neutral or acids
the siliceous soils having a pa of 7.5 to 7.1, and the
later-
itic soils 6.7 to 5.9. The soils foried tlie basis of
-
15-
the present stuty were actually alkaline, ranging tu pH from
8.3 to 9.7. The imbibition of water by theclay colloids in
alkaline soils is very closely coirelated with the
concentra'
tion of electrolyte and the pH, and the isoelectric point is
doubtless shifted as the concentration of electrolyte
decreases.
Then the factors of pit and soluble salt content are taken,
into
account one finds a fairly close correlation between the
sili
ceous soils of Barbados and the colloidal soils of Arizona.
Still another factor, however, enters into the pr.obie m of
permeability of alkaline soi12 as shown by McGeorge,
Breazeale
and Burgess (7). They established the fact that, on account.
of the free alkalinity in alkaline carcareous soils
appreciable
azo-unts of soluble aluminum exists in solution as sodium
alum-
inate. The presence of aluminates was established by
electro-
metric titration. Capillary experiT2ants were conducted on
columns of silica sand with which had been mix d certain.
amounts of calcium and sodium carbonates... The tubes
contain-
ing these mixtures were than placed in aluminum chloride
soIu
tions and the-rise of capillary -water noted in each case.
It
was shown that when the pH ranges betireen 7.6 and 11.0,
aluminaM
hydroxide precipitates out.and the movement of water through
the column stops. This same effect is shown to occur when
alum
or other similar soluble salts are added to soils as
amendments
to correct the alkaline condition.
It was also shown by Burgess and McGeorge (8) that the
process of zeolite formation occurs in alkaline soils by
means
-
6
of th'. reaction, between sodium aluminate and sodium siUcate
.
If the pH for any reason drops below 8.6 the aluminate
present
may precipitate ap gelatinous aluminum hydroxide in the soil
and 'freeze a it up, so that water penetration is extremely
slow if it is not entirely stopped. These authors ree=mend
as a reclamation procedure leaching of the sdil durinf., the
Sii141MST when the t-mperature of the soil is high, for
under
these conditions the aluminum hydroxide is.recipitated out
in the lesscolloidal form. Also alternate leaching and dry
in', tends to destroy the colloidal condition and render the
soil more permeable. The effect of alkali salts in this case
is largely indirect; however, the effect of alumirlates-on
the
.viscosity of water would be such as to greatly retard water
penetration,' even without the possibility of -aluminum
hYdrox
ide precipitation.
McGeorge (9) in a paper entitled: The Effect of Fertil-
izers upon the Physical Properties of Hawaiian Soilsa
studied
the effect of a large number of fertilizers upon such
proper-
ties as capillarity, percolation, flocculation, cohesion,
ap-
parent specific gravity, vapor pressure, and hygroscopic
moisture. The soils were typical Hawaiian soils: yellow
silty soil, manganiferous soil, red-clay soli, titaaiferous
so and 'dust a soil, He obtained some rather significant
results. For example, fertilizers considerably increase the
resistance to percolation, which by reason of the large appl
cations of fertilizer salts used, must have very materially
-
17
increased the viscosity of the water. He finds also that
flocculation Is increased by the addition of the salts. The
lowering of vapor pressure, as indicated by McGeorge, cannot
be explained from a consideration of the surface tension of
the added salts. A lowering of vapor pressure might, of
course, arise from the presence of the dissolved salts in
the
'i.ater film, but it might ,also arise from the fact that
the
smaller particles which have a smaller radius of curvature,
would have a less stable film, and therefore, a higher yapor
pressure. It would follow from this reasoning that the par
ticles must have increased in size, which is also
,consistent
with the observation that flocculation and cohesion often
increase the particle size.
Karraker (9) studied_the effect on soil moisture of changes
in the surface tension of the soil solution brought about by
the addition of soluble salts. The ob4eat was primarily to
ascertain a correlation between the moisture condition of
the
soil and the surface tension and viscosity of the solutions
added ae used sodium nitrate, ammonium sulf,;,te manure
extract
sodium chloride, potassium chloride, mono-calcium p-Losphate
sodium carbonate, and other. The solutions were made up by
dissolving 10 grams of each in i liter of water. The single
salts increased the surface tension but the effect was not
very
marked. The viscosity was also increased in all cases, but
no
cognizance was taken of the fact that the pH of some of
these
solutions were very markedly different. He then added these
solutions to different soils and determined the moisture con
-
tents after the lapse of a certain number of days- He con
eludes that the surface tension effect is too spril to ac..
count for the observed effects, attributing the effect of
the salts primarily to their effect upon th'structure of the
soil. There is some weakness in Karrakerts argument Jaow -
ever a the respect that he correlates the surface t-ns1on0
of the pure Solutioas with those of the resulting soil solu
tioas. This may-lead to decidedly erroneous results. By
reason of base exchange, éqssolution of calcium carbonate,
and other reactions occurring in the soil_ the concentration
of the soil solution might easily have been decidedly differ
.ent from that of the solution added. if he had mzasured'
the
sUrface tensions of the soil extracts t.emselves, he mould
have .secured a closer correlatiaa between the rate of moist
ure movement and the surface tension of the solution. The
viscosity would also probably have been in close correspon
dence.
-
19-
lalljauLsl_jamjImmkapntal Work on. Wate, Penetratl 11
In order to present the experidiental work of this !laves-
tigation in a systematic manner, we may first present a
general
outline of the determinations made and the points it was de
sired to investigate and establish. The factors affecting
penetration which were studied will be brie tir outlined as
followst
Physical and chemical soil factors inveStigatedSoils studied
Description_Mechanical analysisMoisture equivalent and sturation
percentageChemical analysis of soil extractNature of base exchange
complex
Irrigation waters studiedDescription of sourceChemical
comnositiam
Experiments on viscosityDescription of viscosimeter
Precision of measurementsCalibration of vessels
Calculation of .relative viscosity from flow data. Comparison of
.results obtained with different
vesselsSalt solutions used
ConcentrationDensityViscosity measurements
At various concentrationsAt various temperaturAt various salt
mixture,At various pH values
Viscosity determinations onSoil extracts at various soil:water
ratiosIrrigation waters
surface tension measurementsPure solutionsSoil extracts at
various soil :water ratios.Pure solutions at different pH
Nalues
Flow of water through soil columnsOutline of method.Effect of
varying initial moisture content
-
Since there are still various aspects of the penetration
process which are not definitely understood the emphasis in
this investigation was directed principally to gaining a
clearer
understanding of the effect of the-composition of the soil
moisture upon the various forces which play a part in the
movement of water, chief of wnich are the viscosity and
surface.
tension. In addition, it was planned to obtain, if possible,
some definite relationship between the nature of the soil
solution and the colloidal complex.
P______ ohe S2111-at110-ed
Three typical desert soils froT, the Salt River Valley
were selected for these experiments. The reason for their
eiectiôn was a pronounced difference in their water penetra-
tion characteristics.
No 1. Glassford Ranch is located west of Phoenix ia
T. 2 N.A. 2 E., N.W. 1/4 Sec... 32. This soil is classified
as a silty clay ,loam. It had been planted to 'whe-t and
alfalfa
and was being used for pature Samples were taken at depths
of 11 2, 31 and 4 feet,by means of .a soil tube. This Soil
gave a reaction with pheaolOhthalein showing that it wa s.
al-
kaline, yet it was known to give good water penetration.
No. 2 Befsnes Ranch, located south of Tempe in T. 1
È. 4_ E. N.W. 1/4 of LW. i Sec, 27. This souls cla si-
fled as a sandy clay loam, high in alkali and had been
leached some time previously to reclaim it. A test crop of
-
-21
Hegari had been grown on it. The saipies were taken where
the Hegari failed to m ke a stand, apparently a typical
slick spots'. It had a hard top crust, was very alkaline,
and was notably poor from the standpoint of penetration..
The first foot was extremely hard, the second fairly.soft;
at three and one half feet the soil tube stru. k. a hard pan
about _4 inches in thickness, thence to 4 feet it was again
quite soft.
.No. 3. State Land. This plot is located south of
Mesa and across the road from the Groehler ranch in T. I N.,
R. 5 E., S.E. 1/4. Sec. 34. This soil classif4ed as a
typical
clay, and was exceso vely hard throughout the four feet sam-
pled, it was alkaline in .reaction calc Galls, and shOwed
ex-
cessively poor penetration. There had. been no evident
attempt
to reclaim this land by leaching= The test crop of "agari
was apparently quite uniform, but on the whole rather poor.
.We fina in these zoiis, then, three markedly different .
conditions insofar as water penetration is concerned. In the
first we have a soil definitely alkaline and containing a.
high salt content. (Table III) and with. excellent water
penetra-
tion characteristics. In the second, we have another soil
with unusually high soluble alkali salt 'concentration but
much
more alkaline in react on and very poor in respect to
penetra-
'tion. In the last we have an almost pure clay, low in
alkali
salts, containing some free alkalinity, and excessively poor
in penetration.
-
ch n- alN o'
The textural compo .,tion of these soils was determined
by the hydrometer method of Bouyoucos (10) in which 50 grams
of soil are first dispersed with sodium bydroxide dlutidn
and ,sodium oxalate in a high speed ixing-lalachine for a
period
of .fifteen minutes. The dispersions are then placed in a
speciai cylinder' inverted several times, and hydrometer
readings taken at 40 seconds,'I5 m_nutes, and.one hdur. The
sands are calculated as having settled out _tn. 40 seconds.
The 1.5 minute rending represents the amount of colloidal
matter still in suspension, and also Includes the finer par-
tIdes of silt. The hour reading indicates the amdunt of
matter still remaining in suspension Dud is calculated as .
clay. By this method the textural composition was obtained
as shown in Table I.
TABLE I.
MECHANICAL ANALYSIS OF SOIL SAMPLES
Description1. Glassford Banch
1st foot2nd foot3rd foot4th foot
2. Refanes Ranch1st footknd foot3rd foot4th foot
7 4ate Land'1st foot2nd footZrd foot4th foot
% Sand % Silt % Clay
46.0 26.0 28.040.26 28.14 31.6039.64 t,O.W. 29.4049.53 25.11
25.36
' 49.8652.77
24.7027.43
A.5.3419.eo
50.42 24.1151.78 19.51 28.71
42.00 23.82 34.1843.14 20.69 36.1741.22 19.21 39.5740.07 11.99
47.94
-
The moisture relations were next determined. The moist-
ure equivalents were determined by the standard method of
Briggs and McLane (11). The saturation percentage was deter
mined by the method of Scofield WI as follows: 1,11, sample
or the air-dried soil, equivalent to 100 grams of moisture-
free soil i weighed into a soil can having a tight cover.
Distilled water,is added and the soil stirred with a spAtula
until a condition of saturation is reached. In its saturated
condition th soil mass should be plastic enough to flow
slightly when the container is tipped. The surface should
glisten it reflects light and the air should all be dis-
placed. Allow the sample to stand for several minutes, then
test again to make sure that the soil is still saturated.
-The can with its saturated soil is then weighed, and the
weight
of the contents in excess of 100 grams is recorded as the
saturation percentage.
- -Table II shows the results of the moisture
determinations.
TABLE II.
, MOISTURE EQUIVALENTS AND SATURATION PßRCNTAGES OF THE
&QILE3
Soil Moisture Equivalent% ir-dry basis
Saturation Percentage% water free basis
Glasford 21.12 35.3
Refsnes 19.28 35.2
State Land 25.44 42.9
The data in this table indicate that both moisture equi-
valents and saturation percentages are consistent with the
-
clay content of these soils, both of which are proportional
to the amount of moistuIP held by this fraction under differ
cat conditions: the ,oisture equ,.valent, the amount held
under 1000 times gravit- and the saturation percentage 1-,
ing
the total water holding capacity under ordinary conditions.
an e tratioI of the D_ .v!
T4._3 pg of these soils was dot2r2ined by mean* of the
hydrogen electrodt, using 10 gram: of soil shaken with 50
cc.
of.dtstiUed (CO2 free) water. The measurement was made in
each case with the zoii in contact with the 1:5 soil water
mixture.
The soluble salts present in these soils were determined
from the 1:5 COz free water extract. The ions 1, ermined
were
Ca, Mg SO4, Cl, CO3 and LIC03.- These were determined by
methods used in the Agricultural Chaaistry Laboratory,
Univer-
city of Arizona. The calcium and magnesium were determined
by soap titration, sulphates turbidmetricall, chlorides,
car-
bonates and bicarbonates by standard volumetric procedure
and
the sodium calculated by difference from the reaction values
of the ions. The analytical data are shown in Table III.
-
-25-
TABLE III.
SOLUBLE SALTS IN P.P.M. IN AIE DRY SOILS FO 1 SALT
RIVER VALLEY AS DETERIIINED FROM 1:5 WATEF EXTRACT
Description it ft. 2nd ft.Glassford
Total sol. salts 312 1240Calcium o oMagnesium 8 8Sodium 81
388Chlorides 40 240Sulphates trace 165Carbonates trace
traceBicarbonates 183 439
3rd ft. 4th ft.
2648 225860 12023 15
834 633850 920600 350trace trace281 220
pH* 8.33 8.85 8.42 8.31
e4snesTotal soluble salts 2121 3608 4738 3594Calcium 0 - - 0 0
0Magnesium 0 0 , 8 8Sodium 741 1314 1637 1302Chlorides 310 950 1370
1350Sulphates 75 350 700 375Carbonates 324 384 84 108Bicarbonates
671 610 939 451pli* . - 9.69 9.68 9.69 93$
State LandTotal soluble salts 796 793 770 898Calcium 0' 8 0
eMagnesium 8 8 0 8Sodium 240 234 237 456Chlorides 170 170 130
110Sulphates trace trace trace traceCarbonates trace trace trace
traceBicarbonates 378 366 403 52410* 8.39 8.39 8.26 8.64
*The pi' was determined by hydrogen electrode method on a
solution containing 10 grams of soil in equilibrium with 50
cc. of water.
-
-23-
The data show selmral remarkable relationship. In
the first place the soils are all very decidedly alkaline.
The Glassford soil had a relatively hizn amount of soluble
salts but was found to exhibit good water penetration
ilhereas the State Land, a clay soil with practically the
same pH and with a much lower total soluble salt content,
scarcely takes water at all. On the other hand, the Refsnes
soil which has an unusually high pH (0.69) and a high alkali
salt content is evidently in a dispersed condition in spite
of its high salt content as it takes water with great diffi-
culty
. It was also noticed that while the Glassford and Refsnes
soils increased in soluble salt content with the depth,
State Land soil showed practically the same percentage of
solli
ble salt throughout the four feet. In the foregoing two
soils,
there is evidence that irrigation is gradually carrytng the
salt to lower levels. In the Refsnes soil, it was noted that
there was a layer of hardpan between .3 and 3-1/2 feet which
-
was very difficult to penetrate. The table shows that at
three feet, the salt concentration is 4700 p.p.m. of the
air-
dry soil, whereas below and immediately above the level, it
is about 3G00 p.p.m. This disparity would indicate that the
soil moisture percolates down under gravity carrying the
alkali
salts with.it until it strikes the hardpan and can go no
fur-
ther. This results in an accumulation at that level. The
high
-
-27
concentration of ublack alkali' 1r the form of sodium carbon
ate and the almost total absence or calcium salts in the ex-
tract account for the high degree of di p rsion and
resulting
poor penetration.
Na .re of baEte-exchange coRr.nlex
The method of determining replaceable bases in calcareous
soils is somewhat different from that uzed in non- alcareous
soils because of presence of calcium carbonate in the solid
phase. Burgess and Breazeale (13) recognized this and made
corrections for this factor. The method used here is a modi-
fication of the method used by Magistad and Burgess 14) us-
ing alcoholic BaC12 as the replacing solution. The soils
were
first shaken with distilled water and filtered to remove all
the soluble salts. Fifty grams of the air-dry sample and 250
cubic centimeters of N/10 BaC12 in C8% ethyl alcohol was
added
and the mixture shaken on a shakIng machine for one hour.
The
solution was then filtered off and 200 cc more of the alco-
holic BaCl2 added and shaken for one hour. This solution was
filtered off. The soil was then all washed onto the filter
and several hundred cubic centimeters of the alcoholic
barium
chloride filtered 'through until the filtrate skiowed no
test
for calcium. The filtrates were then all added together and
evaporated to dryness on the sieam bath to drive off the
alco-
hol. The residue was taken up with water and diluted to 250
cc.
The replaceable calcium and magnesium were determined by
-
the soap method after first precipitatin out the barium
,r m the solution with odium chromat
Sodium was determined by the Uranyl-Zine-Ac tata Method
as used by the Division of Western irrigation. Agriculture
(15)
which was adapted from the method of Barber and Kolthoff
(16).
The results for the determination of exchangeable bases are
tabulated in Table IV.
TABLE IV
REPLACEABLE BASES IN THLEE TYPICAL SALT RIVER VALLEY SOILS
Soil M.E.*odium M.E. Calcium ILE. Magn, ium Na/Ca
Glasford 0.584 i336 0.28 0.06
Refsnes 4.26 .74 0.28 1.14
State Land 10.00 11.02 0.58 0.91
*M.E. Milligram equivalent or milliequivalents per 100
gramssoil.
The che4ical nature of the base exchange complex corre-
lates closely with the penetration characteristics of the'
'soils. The Glassford soil shows a predominance of cal(!ium
in
the complex and also shows good penetration. In the Refsnes
soil, the sodium exceeds the calcium .s14ht1y, but they are
both of about the same order of magnitude. In th. case of
the State Land, the calcium actually predominates slightly
11 M.E. of Ca per 100 gms. soll with 10 !I.E. of Na. Still,
the soil is so heavy in clay, that it is nearly
impenetrable.
The ratios of Na/Ca are very nearly equal for the Refsnes
and
State Land soil and both take water only with difficulty.
-
;it1ot? waters used
Four irrigation waters were used in this investigation.
The sampleS were taken March '"4 1934, at the following
pointSt
I. Arizona Canal at end of. Seventh Street north of the
City of Phoenix.
2. anal near Tempe along D. S. Righway No 80.
3. Head of Canal north side,of Sacaton dam, on the
Gila River.
.4. Canal south of Randolph carrying water fro a Picacho
Lake.
These waters were selected partly because of the differ-
ence in their sources and their resulting chemical composi-
tion. The first two waters spring from the Salt and Verde
Rivers, and represent the most widely used irrigation water
in the Salt River Valley. The Gila River water, sampled at
%,acaton is to be used on the new Indian irrigation project.
The water sampled south of Randolph comes from the Coolidge
Darn on the Oila River, being stored in Picacho Lake as an
intermediate reservoir, and is used on an extensive area now
under irrigation cultivation near Randolph, Coolidge, and.
Casa Grande.
The analyses of these waters are, shown in Table V.
-
TABLE V
ANALYIS OF IRRIGATION WATERS
Total soluble saltsCalcium (Ca)Magnesiu= Mg
' Sodium NaChlorides 'CIvulphates kS0Carbonates COBicarbonates
(HC0)
Arizona Canalp.p.m4
Tempe Sacatonp.p.mh p.p.m.
Picachop.p.m.
730 860 1143 117345 CO 83 12019 g,=z,,,, 30 23
173 205 274 253240 294 450 34870 80 150 1800 0 0 0
185 128 156 249
Experients on IrSCO3itl- of Solutions
As Stated in the Introduction, the vizposity factor_is
-important in water penetration in that it controls the rate
at which water flows throUgh the Soil capliTlarlea and thus
governs the rate at which moisture equilibrium_ is
established.
Numerous data on viscosity, covering a large number of com
pounds dissolved in different solvents, may be found in the
literature. Ratschek (18) in his book on rViscosity of
Liquidstf devotes considerable attention to the viscosities
of
solutions in relation to such physico-chemical properties as
conductivity of electrolytes.
The colloids of the soil classify in ceneral into inor-
ganic and organic. The inorganic colloids comprise chiefly
the silicates, alumino-silicates, certain oxides like those
of iron and aluminum, and certain inorganic salts which
readily
go into colloidal suspension. The organic colloids comprise
a
large class of compounds found in the intermediate
decomposi-
tion of organic matter in the soil. These different products
-
-31
have various isoelectric points and as a result one may find
some organic matter in a state of dispersion in the soil at
almost any pH. This condition contributes to the viscosity
of water as it penetrates into the soil, It is found, for
example, that while the suspensoids, that is the hydrophobic
colloids, do not'markedly affett the vistosity, the
emulsoids
of .hydrophilic colloids do greatly affect the viscosity. In
the case of the hydrophobic Colloids the viscosity varies in
some Measure with the concentration, but does not become ap-
preciable until higher concentrations are reached. The vis-
cosity is not greatly differeat from that of the solvent in
dilute solutions. However, in the case of the hydrophiles
such as the organic colloids, silica gel, and the alumino-
silicates, the effect of their dispersion upon t he viscosity
.
is far more pronounced4 -Small concentrations of agar, such
as
0.370, increase the viscosity of water up to 2.5 times that
of
pure water. This effect is partly due, to the swelling or
the
colloid as a result of which a certain amount of water In
the
bound form must be carried along by the particle as it moves
through the solution. There is still another aspect of the
behavior of hydrophilic colloids which is of intprest in
this
connection, that is the fact that the viscosity changes with
the time, increasing as the degree of dispersion and the
con-
centration of the dispersed phase builds up. This factor may
be important in explaining the characteristic slowing up of
the process after the first intervals of time. A certain
-
amount of gel-formation may also occur. If so, part of the
mechanism of penetration would then involve an endosmotic
pro
cess which is exceedingly slow. This process very probably
accounts for the extreme sIownes of penetration which is
sometimee observed on nslick spotsn of alkali soils.
Perhaps one of the most important factors affecting the
viscosity of these hydrophilic colloie is that of pH. It is
found, for example, that the hydrophiles have definite iso-
electric points at which tne viscosities are a minimum, and
above or below the, point the viscosity curve rises quite
, rapidly. If, Vierefore lthappenz that the soil has a pH
which corresponds with the isoelectric point of the
predomin-
- ating c011oid or group of colloids, one may expect the
optimum
penetration. FUrthermore if the soil should happen ta be
either more acidic or more alkaline than corresponds to the
isoelectric point, the. viscosity of the suspension should
be
expected to rise, and pcnetratiam slow up. This is exactly
the case In the siliceous soils of BarbadoS as found by
Hardy.
In the case of Hardyts results it was fdund that when clcium
carbonate was added to the acid ziliceoUs toils, the
penetra-
ion was increased about 5-fold, which is a simple corrobora-
tion of the above theory.
The isoelectric points of organic colloids are as a rule
found to be on the acid side of neutrality, usually between
pa of 35 or 6.8. How'ever, there is some evidence to show
that
the more complex zeolitic colloids have isoelectric points
at
-
neutrality or slightly on the alkaline side.
astiremel t on visccities of oiution s. and e: acts
of soils
In the experimental work on viscosity, measurements were
made on solutions of pure salts, ext acts of iis, irriga-
tion -waters, and colloidal suspeasions It s eered to be of
some interest to study solutions of pure salts, although it
is.to.be expected that the effect of the colloidal'fraction
upon the viscosity might overshadow that of the pure salts.
The principal reason for making these measurements, however,
wa that the data in the literature on the viscosities of
pure salt solutions are confined to a large extent to more
concentrated solutions, whereas in the soil we meet with re-
latively dilute sOlutions. It is evident that as the solu-
tions become more and more dilute,- the change in viscosity
becomes rather slight. and a more refined aad accurate tech-
nic of measurement must be developed. The viscosimeter used
will be first described.
The'viscosimeter designed and constructed in,this work
was a modification of the original Ostwald type, with dimen-
sions as shown in Figure 1.
-
-33a-
Fá urc /.
V/JcOs//:14e2zJrseo % . - =1em
-
The vessel was constructed of Pyrex Glass and incorpor-
ates several desirable features which add considerably to
the precision of measurement. In the first place, the reser
voir bulb was constructed in the form Of a large ellipsoid,
as suggested by ashburn so that the down..flow of solution
from the bulb abOve would not cause an appreciable back
pressure and thus reduce the rate of flow during the course
Of.a measurement.. The tubes immediately above and below the
deliVerybulb were made of tubing of sufficient diameter to
make accurate readings possible and at the same time to ob-
viate-the effect of capillarity. A small spherical bulb was
pladed between the stopcock and delivery bulb to serve as a
trap and also as a reservoir from which normal flow could be
set up before the .liquid passes the upper mark of the deli-
very bulb. It is more desirable to have such. normal flow
set
up-before observations are b gun than to start the flow from
rest .as it was found by experiment that such procedure
gives
more accurate and reproducible results. A cap was placed
over the open end of the funnel. tube to keep out foreign
matter.
The temperature of the thermostat was varied successively
over a range of 20 to 400 C. in five-degree intervals and
could
be easily regulated to 0.01° C. The thermometer employed had
been calibrated by the U. S. Bureau of Standards, and the
cor-
rections were applied at each temperature. The viscosimeter
and solution was kept at each temperature a sufficient
length
of time to allow thorough temperature equilibrium. Tests
were made as to the length of time required for the tempera-
-
ture of the solution in the vessel to come to the tempera-
ture of the thermostat. It was found that 25-30 minutes
were sufficient. Apparently the glass walls of the vessel
were thin enough to come to temperature equilitrium quickly.
The average dimensions of the various parts of the
vessel were as follows;
Vessel No. Vol. deliverybulb cc.
Vol. reservoirbulb, cc.
17 19917.5 178
3 17 20745
16.516
180201
The average bore of the capillary was about 0.75 ram. and
the average diameter of the reservoi.. bulb, 80 mm. It is
diff:l.cult to construa't the latter so that they will be
absolutely uniform; a tet was made, however, by using a
cathetometer and the increase in pressure head in the reser-
voirs of each of the above vessels was determined. The
readings, beginning with vessel No. 1, were as follows:
3.4 mm., 3.5, 2.9, 3.30 and 3.3 mm. These data show that
the magnitude of back pressure produced was practically the
same in all cases and could be considered as equal.
It was found also that the volume of solution placed
in the reservoir solution affected the rate of flow. An
experiment using different volumes of water was performed
with the following results:
-
Volume (cc.) Time (min.)
75 2.5603.00 2.630125 2.7$7150 2.870
A constant volume of 100 cc. wa chosen for all subsequent
measurements.
The time measurements were made with stop-watches which
had been checked against each other and found to be in sub-
stantial agreement. In the course of a given et of measure .
ments, observations were made on each visco ¡meter with each
watch. When these measurements were found to .heck , it was
concluded that the value so determined was very probably the
correct one. If there was lack of agreement, additional ob-
servations were made with the varticular watch which gave
the discordant result, and in most cases agreement with
other watches was obtained. Variations were attributed to
possible error in observing the in,,:tant when the meniscus
of
the solution crossed the mark on the viscosimeter, or to the
lack of temperature equilibrium. In some cases the first
observations were at variance with those subsequently ob
tained. This was particularly true in one vessel where the'
elliptical 'bulb had been made of somewhat thicker walled
glass. In cases where the observed tire S of flow never came
to a constant value, it was concluded that there must have
been a minute (invisible) obstruction in the capillary. When
the measuring bulb 'was filled by suction the particle may
-
l'Arf"'1,1"'"'
have loosened up and later, in the course of draining it
may have lodged in the capillary atad again affected the
rate of flow. When this difficulty diD manifest itself, the
.
vessel was removed and thoroughly cleaned. the visco imeters
were mounted on a frame made of strap brass Nelicn could
eas-
ily be clamped in place in the thermostat or removed when
desired, Care was taken to see that the vessel was mounted
vertically*
Calibration of the Ijimuir_rialt.52.
Since relative vi cosities were to be measured, it was
necessary to calibrate the vessels-under the same conditions
as described above,' with water as the refreence liquid. A
graph.how1ng the ty¡Acal calibration carves' is given in
Figure t.
. The vessels were calibrated at each of the tempraturesof
weaurement. Since the determinations were relative in
character, and there was no simple experimental means of de
termining the absolute accuracy of the determinations, an
analysis was made of the calibration data somewhat as fol
lows; it was assumed that the initial values of tifile of
flow
at 20° C. were most probably. correct. Using these figures
as
a basis, the percentage decrements were calculated for each
successive temperatùre interval. If the vessels all func-
tioned in a similar manner, and being similar in their
struc-
tural features, they should, the percentage decrement (or
-
21,A.L17X,7.:1IJ.7,.1orsiz,t
'All "003i11
.. ,.- ..-._ .. ... . . .. . - C....... .:.. . . ;, 1: u , ._.-
::.::..:. . OF : a .fi.E;; S7 ...i..:...:Pa9 .. .s : .... :.. . ...
.a. ...... . ...... CE Ers .. . . . . ,. . . : . : :: . . i , . . .
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-
-
-38
increment) ti the rate of flow should be the same for all
vessels through any given temperature interval. As an ex-
ample, the percentage decrements for the interval
were found for five vessels to be as follows:
O. 530,0.2760 0.273, 0.271 0.273.
The agreement is found to be satisfactory in all
o 350
ept the
firat vessel. The same lack of agreement for Vessel No. 1-
was also observed_ at the other teperatue intervals studied
and ttwas therefore concluded that some conditions possibly
lodgment of foreign matter In the capillary and not
necessar-
ily lac% of temperature equilibration, was reSponsible for
the discrepancy. When such disazreement was foUnd, the ves-.
sel as always recalibrated. mall .other ca.ses it was con-
sidered safe to conclude that the vessels had 'attained true
temperature equilibrium and were functioning normally in
every respect.
C 1 ula on vi
flow a., d de
a ; ttne _a es
' the solution,
The relative viscosity data as obtained by the foregoing
experimental procedure were computed from times of flow and
densities of the solutions by means of an equation derived
from Poinaeuillets Law:
4V =,
I, rt
where V = volume of liquid delivered in tie T.
P = difference in pressure under which the liquid flows
through the capillary.
-
'70
R = radius of the capillary.
L 22 actual vertical distance in capillary traversed
by the liquid during flaw, and maintaining pressure differ-
ence P.
= viscosity of the fluid.
The pressure difference under which flow of the 1iquid
through the capillary occurs may be expressed in terms of
the density of the solution and .the dtffereice In levels
between the marks above and below the delivery bulb, for a
given liquid of density d1;
PI b, di g
and for any other liquid who e viscosity relative-to it is
to be determined:
Pa h da g
The common form of Poiseuillets Equation is as follavs:
PR8V1
The relative viscosity becomes:
Pl R4 Tl
T
'1 =e V
p2 R4 Tx
8VlSubstituting for P1 and P2 in the foregoing equation, and
cancelling out constants and like terms, we obtain the final
form:
dl T1.
; d TA2 2
-
40
This equation was employed in calculating the relative vis-
cosities of the solutions used in this investigation. The
values of d2 and T refer to density and time of delivery of
pure water, and the terms with subscript 1, to the solution
being sltudied. As the solutions become more and more
dilute,
the density ratio obviously approaches unity, and can be
neglected as soon as the deviation from unity is found to
lie
within limits of experimental errore
obtained f
iven tion when measu ed simulta_ ou lv
a
different
vessels
It was considered of interest to measure the relative
viscosity of a given solution in five different vessels
under
identical experimental conditions to determine how closely
the results would agree. Such a test would also afford evi-
d.ence of the extent to which the precision of the values
ob-
tained was dependent upon the dimensional peculiarities of
the vessel. The solution chosen for this test was N/10 Noel
at two different temperatures, 30° and 35° C. The results
are shown in Table Vi.
-
-41
TABU VI.
Viscosit of N. 10 NaCl at Different Temperatures as
Determined in Five Different V , cos1rneters.
Vessel Temp.No.C. Rel.Viscosity1 30 1.01444 0 1.011D3 It 1.01154
a isolai5 v 1.0130
1 ,z-tap 1.0134,4,,
ft 1.01103 it - 1.01234 It 1.01335 II 1.0119
Ave.Viscosity
Deviationfrom Avg.
1.0129 0.00151.0129 0.00101.0129 0.00141.0129 0.00081.0129
0.0001
1.0124 0.0010 -1.0124 0.00141.0124 0.00011.0124 0.00091.0124
0.0005
The data show that none of the determinations varied
more. than 0.15A from the average, and the majority of them
showed much better agreement. We may assume, therefore,'
that If the experimental conditions, especially that of
attainment of true temperature equilibrium, are maintained
constant during the measurements, the viscosity measurements
will be reproducible to within 0.10 per cent. Table VI also
shows that the values of relative viscosity are
substantially
independent of the vessel S used in their measurement. How-
ever, in nearly every ease, the final values as given in
sub-
sequent tables, are averages of two or more determinations
made 6n the respective solutions with different vessels and
at different times.
-
-42-
Viscos t' Determinations on Salt Solutions
As stated in a previous section, it was considered of
Importance to investigate somewhat extensively the viscosity
relations of salt solution, particularly those which make
up in large part the soil solutim or closely approximate the
solution represented by the irrigation water after its
cation to the soil It is remarkable that the data on vis
cosities of salt solutions at high dilutions as recorded in
the International Critical Tables 19) and similar reference
works are rather limited in extent. They do not extend over
any appreciable range of concentrations below tenth-normal.
The choice of salts for this study was determined in a
large measure by the average composition of irrigation
waters
and soil extracts. The salts most commonly found in irriga-
tion waters are the sulfates, chlorides anc-vbicarbonates of
sodium, calcium and magnesium. The sodium salts usually
predominate, and the concentration of calciva salts is usu
ally about twice that of magnesium. Small amounts of carbon-
ates, nitrates, fluoridesi potassium and boron may also be
present in the water, but the concentrations are so small
that their physical or chemical effect upon the water may be
neglected. Of these latter salts, carbonates, if present in
any considerable quantity, give water an alkaline reaction
by
hydrolysis and affect water penetration through their dis-
parsing action on the soil colloids. The salts accordingly
-
chosen for this study were those mosteammonly present,
namely
sodium chloride, sodium sulfate, sodium bicarbonate, calcium
chloride and calcium sulfate.
The concentrations to be studied were also given careful
consideration' Irrigation waters may vary from 300 to MOO
p.p.m. of total dissolved salts. The latter figure is
tremely-tigh but cases are on record Where auch waters have
been succssfully ilsed in the production of alfalfa and
other
alkaliresistant crops. If such a water contained only one
saite the concentration would be less than 0.1 normal. How-
ever, the soil solution itself reaches a much higher concen-
tration. Waters are usually composed of several salts whoie
individual and total concentrations are less than 0.01
normal.
To cover all possible èasesi the concentration range chosen
was N/I, N/100 N/1000 N/1060, and N/104000, and the tempera-
ture range chosen was from 200 to 40° C. in five degree in-
tervals,
.The solutions were made up from the-crystalline salts
Of C.P. grade, which showed upon qualitative test that all
elements which might be present in appreciable quantity and
interfere with the determinations-were absent. The solutions
were made up with distilled water which WIIM tested showed
absence of chlorides, sulphates and ralcium. In. the cRse.of
sodium sulfate, a solution somewhat stronger than N/10 was
made up, analyzed, and the dilutions made accordingly. The
saturated solution of calcium sulfate was analysed and the
-
dilutions made up from this solutian.
Densities of the solutions were determined by means of
Sprengel density pipettes and with ordinary pyknometers
having capillary stoppers. These vessels were kept in the
thermostat at the desired temperature and filled with the
proper solution (also kept at the same temperature) before
weighing. The pyknometers had previously been calibrated
against wr,..ter at the several temperatures.
The viscosity measurements were made as previously
described 3.00 cc. of solution being placed in the viscosi-
meter and time being allowed for the establishment of tem-
perature equilibrium. To eliminate a possibility of error
in the time observation, sets of observations on the time
of Slow of each vessel were taken with four or five differ-.
ent stop-watches until substantial agreement was obtained.
From the density and time data, the relative viscosities o;
the solutions were calculated by the formula previously
described. The times of flow were found to be reproducible
to about 0.005 minute in a total time period of 2.5 to 6
minutes. This agreement is regarded as unusually satisfac-
tory in view of the fact that different watches were used,
. and different observers made part of the measurements. The
temperature in each case was held rigorously constant.
A summary of all relative viscosity data for the single
salt solutions is given in Table VIZ. These results have in
many cases been rechecked to confirm their accuracy.
-
TABLE VII.
Relative Viz,co.Aties of Lì 1e Salt Solutions a
Salt
Na01
Na2SO4
Normality p.p.m.
0.1 548500.01 - 5850.001 580.0001 5.8
0.1 701000..01 710
- 0.001 71
Temperature20$ 251 301 a5t 40,
1.0136 1.0140 1.0130 1.0125. 1.01681.0037 1.0036 1.0028 1.0028
1.00471.0022 1.0022 1.0022 1.0034 1.00221.0027 1.0017 1.0011 1.0022
1.0017
1.0267 1.0279 1.0266 1.0244 1,02451.0029 1.0029 1.0034 1.0030
1.00311.0027 1.0022 1.0009 1.0005 1.0010
0.0001 7.1 1.0010 1.0008 1.0010 1.0012 1.0012
NaHCO3 0.1 80400 1.0328 1.0318 1.0316 1.0319 1.02850.01 840
1.0020 1.0018 1.0014 1.0012 1.0013-0.001 84 1.0016 130012 1.0005
1.0017 1.00050.0001 8.4 1.0010 1.0000 1.0015 1.0017 1.0000
CaC12 0.1 « 5,550 1.0291 1.0322 1.0318 1.0320 1.02690.01 555
1.0019 1.0016 1.0025 1.0029 1.00360.001 55 1.0008 1.0016 1.0015
1.0002 1.00000.0001 . 5.5 1.0005 1.0016 1.0010 0.9937-1.0014
CaSO4 Saturated 2,080 '1,0114 1.0105 1.0114 1.0101 1.0090- 0.01
680 1.0026 1.0021 1.0020 1.0016 1.0029
,04001, 68 1.0011 1.0013 1.0016 1.0017 1.0011..0.0001 6.8 1.0011
0.9992-049997 1.0006 .1.0011
The data included in this table are plotted as shown
in Figures 3, 40 50 60 and 70 in which relative viscosity
is the Ordinate and the abscissae are represented as logar-
ithms of the reciprocal concentrations. This latter unit
of concentration was chosen so as-to_cive the widely varying
concentrations equal importance or significance in plotting.
Thus N/10 concentration corresponds to the value 10 N/100
represented by 2* N/1000 by 30 and so forth.
-
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