A CORRE’LAHON STUDY :3; :Nmmmou, PERMEABKUTY, AND was 5:25 msmaunon Thai: for m Degree of M. S. mcmcm 57m cause: Howard Albert Voiibrachf 1954 fir-1:53.73} L. WW 1 “Wiles 00796 3592 ,V _‘.__ __.—.—. g This is to certify that the thesis entitled v'- *9 ur- l :r‘ : S. A Correlation Study of Infiltration,- Penlo-‘agiugz.’ and .v '0' ‘- P9re Size mamfifitw 2:121: ._ ,d ‘d‘ "IJ presented by Howard A. Vollbrecht has been accepted towards fulfillment of the requirements for Master of Science degree inmnco green—E Major professor Date ML 0-169 — ' CWfCWpflI'J-DJ PLACE IN RETURN BOX to remove this checkout from your record. TO AVOID FINES return on or before date due. I DATE DUE DATE DUE DATE DUE raw: “ “ D; .:| I: |l____]| f MSU Is An Affirmative Action/Equal Opportunity Institution enema-annea- ,4 7 777 i "7 ~7-<..--.—_______—4- A CORRELATION STUDY OF INFILTRATIJN, PERMHABILITY, AND FORE SIZE DISTRIBUTION by Howard Albert Vollbrecht A THESIS submitted to the School of Graduate Studies of Michigan State College of Agriculture and Applied Science in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE Department of Soil Science l95h a. .3. ".1 n a ' “A 9v :1.— m THESIS AC KNONLEDG EMENT The investigator expresses his sincere thanks to Dr. Earl Erickson, under whose supervision and guidance this study was undertaken. 331297 I INTRODUCT ION . II REVIEW OF THE LITERATURE III EXPERIMEITAL PROCEDURE. Field Procedures Laboratory Procedures Statistical Procedures IV RESULTS AND DISCUSSION . Variability Analysis Surface Soil Correlations subsoil Correlations Regression Line Predictions. V CONCLUSst . . BIBLICBRAPHY . APPENDIX . . Tables . . Figures . . TABLE CF CONT L‘INTS Basic Field and Laboratory Data. Page 10 10 12 15 17 17 '18 26 33 3h 35 38 39 76 INTRODUCTION The disposition of rainfall and irrigation water has posed a problem to many workers in certain fields of science and engineering. The question is asked, ”How fast and at what sustained rate will a soil infiltrate water before surface run-off occurs?" Estimations of infiltration rates have been made by hydrologic engineers from the analysis of rainfall intensity curves and surface run-off data. The information gained in this manner is satisfactory for certain controlled watershed areas where rainfall intensities and surface runpoff measurements can be made. However, a solution to the problem of surface run-off is quite extensive in scope and cannot be easily solved by the soil conservationist or the highway engineer.far removed from.an area wheretiata is collected and assembled in a hydrograph. A large volume of data have been obtained from soil core permeability studies. However, the predictions of infiltration rates for a given soil from these data have been subject to question. Therefore, data concerning correlations between infiltration and permeability rates, and pore size distributions would be valuable in planning for irrigation, flood control, drainage, erosion control, and in the construction of highways. The purpose of this paper is to show what correlation existed between observed infiltration rates, core permeability, and pore size distribution. 80113 at twentyasix different sites, including seventeen different soil types found in the lower peninsula of Michigan, were included in this study. REVIE'J CF LITERATURE The investigation of the processes involved in the infiltration of water into the soil is not new. The investigation of infiltration started as early as 1911 when Green and Ampt (12) made a study on the effect of capillary pull on the downward advance of a moisture front in a column of soil. Investigations of soil-water relationships goes back even farther to the work of King (16) who in 1898 made comprehensive studies on the flow of air and water through a column of soil. It has been stated that rainfall can enter the soil only as fast as the escape or displacement of an equal volume of soil air (16). If this is the case, the relationship between infiltration and the dispos- ition of soil air becomes quite important. Many investigations have been made of the effect of trapped air on the rate of infiltration. Free and Palmer (11) were interested in determining the importance of air movement in the soil during the infiltration process. They attempted to correlate the interrelationships between air movement, pore size, and infiltration so the results could be applied to field soil under natural rainfall. When they maintained a constant head of water on sands of different I texture, they found that in open columns infiltration decreased with depth and time. Infiltration proceeded slowly in the closed columns at first and only increased when entrapped air had sufficient pressure to lift a layer of saturated sand and escape through the top of the column. This was observed to be true only for the columns which contained the finer sand sizes. Free and Palmer felt that retarded infiltration was due 3. to the small capillaries which were blocked by compressed air and a saturated layer at the top of the soil column'which resisted nonnal air passage. No definite conclusions were drawn but tendencies were noted. Further conclusions were drawn by Free and Palmervwhen they stated that in undisturbed soils, infiltration was dependent upon the independent interaction of cracks, worm and root holes, degree of aggregation, degree of shrinkage, swelling, number of pores, size and distribution of pores and other factors found in a normal soil. Musgrave (23), in making infiltration capacity determinations of soils in the field, employed single unbuffered steel rings long enough to reach the ”B” or impervious horizon as an infiltrometer, and one thousand cubic centimeter'burettes for the.maintenance of water heads. 'With similar apparatus Zwerman (33) found that on.Duffield silt loam in four’stages of erosion (slight, moderate, severe, and a virgin soil) in- filtration rates were unexpectedly high for the moderately eroded soil 'with lower infiltration rates for’the virgin soil next in order. Zwerman reasoned that this unexpected order was due to the impedence of water flow by entrapped air. The aieras said to be trapped between particles 2mm and less. An aggregate analysis of the moderately eroded and virgin soils showed that particles greater than 2mm in size were about the same for both. However, at a depth of sixteen inches the moderately eroded soil showed a 38% non-capillary porosity value while the virgin soil showed only 26%. Since the infiltration cylinders‘were Jacked down to the . "B" horizon and the moderately eroded soil had more favorable conditions for air permeability as well as water permeability, it showed a much higher infiltration capacity over a seven and one-half hour run. Zwerman felt th 2 2154.“: 179 form 1: 3n: ‘ non-ca:-l. ‘. ‘. . “DIES, an; Wire an l‘ . bm'lgn 8: “mus k: soil, 58 b. that Musgrave's method gave much higher infiltration values than would be found in natural and artificial rainmaker type infiltrometers. Lewis and Powers (20) mentioned porosity, chiefly non—capillary, as a factor to be considered in soil infiltration capacity. In addition to non-capillary porosity, the porosity factor is increased by cracks, worm holes, animal burrows, shrinkage, and root channels. In addition, texture and structure were mentioned. They stated that infiltration through soils of a given texture and structure is influenced by colloid content, character of the colloid as to exchangeable bases, pH, SiOZ/A1203 ratio, character of moisture, wetting and drying effects, swelling of col- loids, duration of wetting, and other related effects on organic colloidal material. Lewis and Powers also discussed the moisture pressure gradients of various kinds that were found to affect the infiltration capacity of a soil. is a unit volume of water entered the soil, conditioned by its physical properties, it became subject to the forces of capillary pull or particle field forces. They stated that to a large extent the pull of capillarity would be determined by the moisture content of the soil hori— zons at the time of water entry. Among the effects to be considered would be the state of hydration of the soil colloids, the depth of the soil, the permeability of the subsoil or of the soil horizon which is the least permeable. In addition, these investigators mentioned the factors of soil temperature, water temperature and its viscosity, and their influence upon infiltration capacity. In 'his study of the surface factors affecting the rate of intake of water by soils, Duley (6) found cultivated and bare soils had a high rate of water run-off and soil erosion. This was especially true when soils S. were left smooth by cultivating implements. Making tests on soils rang- ing from sandy loams to clay loams, Duley used photomicrographic studies of treated soil cross-sections and found that in all cases increased run- off was due to the beating effect of rain drops which formed a thin com- pact layer of soil. This compact layer was formed by the assortment of small particle sizes from structural disturbances which fitted around larger particles forming a relatively impervious seal. Workers in the field of soil conservation have contributed to the study of infiltration by indirect methods. By making studies of soil structure and its corresponding permeability characteristics, Uhland and O'Neal (32) have attempted to relate infiltration to soil structure. Although, while not actually performing infiltration tests, these workers have described drainage and irrigation problems mainly in the light of the permeability of the horizons and their interaction for any given soil of known texture, structure, degree of aggregate overlap, and other ob- servable soil characteristics of subsurface horizons. They admitted that the occurrence of natural water passageways were important factors in soil permeability and also agreed that infiltration of water into the surface of the soil was important. However, due to the affect of manage- ment and cropping practices, variability in infiltration and permeability of the surface seven inches prohibited significant permeability deter- minations. Musgrave (23) used a single unbuffered ring type infiltrometer to conduct a study for determining the infiltration capacity of soils in the field. He attempted to relate infiltration capacity to soil structure insofar as its capacity is related to the structure of the horizon which permits its lowest normal infiltration. While lusgrave’s results compared favorably wi‘ lysiretrez-s, . the variatil Nelson . on liscansi: m lusgra're into soil (:3 “31'. The} Stones and ,- decided that apparatus .15 by Rem-9v ‘I shall" deem hrt’lt‘x tmmiSSia Sing b‘i ta: rate:- ‘as n true beta; 6. favorably with other methods of infiltration measurement, i.e. erosion lysimeters, and Horton's (lb) rainfall-runoff curves, it was noted that the variability of the infiltration curve was quite large. Nelson and Muckenhirn (25) in determining field percolation rates on Wisconsin soils obtained data which agreed with those cited by Zwerman and Iusgrave. They found large variations in the amount of water taken into soil columns enclosed by the long steel cylinder type of infiltrom- eter. They felt this was due to the disturbance of the soil caused by stones and roots being driven down into the soil by the cylinder. They decided that this method was unsatisfactory and settled on the type of apparatus used by Katchinsky (15) and Kohnke (17) as initially designed by Nestrov which consisted of two concentric steel squares, driven to a shallow depth in the surface soil. Horton (11;) stated that infiltration capacity was usually less than transmission capacity because of the related effects of packing and plug- ging by rainfall on the surface of a soil mass. Transmission of soil water was much more rapid within the soil mass. He believed this to be true because in the process of infiltration soil air must escape from the soil surface as fast as water enters, while percolation is only dependent upon saturated soil. Horton cites the work of King (16) who made calcula- tions of air flow through different grades of sand. King found that air flow was 26.5 times greater than water flow through the same material. Horton did not feel, however, that air would flow as fast when water was flowing into a soil in the opposite direction. He also felt that the de— termination of infiltration capacities in some instances was actually estimation of transmission capacities. Relative to transmission capaci- ties Horton cited the work of Green and Ampt (12) who were attempting to reasrre he thick. was s nation H 531mm an: '1! the at” Y eater (; distrihu. 7. measure the downward advance of a moisture front in a column of soil which was saturated above a moisture front. Horton felt that this deter- mination was a transmission and not an infiltration capacity study. Bodman and Colman (2) with air dry soils maintained a head of water on a soil column for a twenty hour period and found by moisture potential studies that only the surface one to two centimeters of the soil column ever reached the state of pore space saturation. Probably the most important physical characteristic of the soil profile yet to be considered in a study of infiltration on various soils is the effect of permeability and pore size distribution. Lutz and Learner (21) studied the relationship between permeability and pore size distribution in three North Carolina subsoils (Iredell, Cecil, and Davidson) each having about the same texture. They found that permea- bility increased exponentially with particle size and pore size. In addition, they found that permeability increased greatly with the per- cent increase of pores larger than 0.1mm and suggested a direct relation- ship might exist between percent increase of pores greater than .05mm but less than 0.1mm. The clay content of these soils was also thought to have some effect upon the decrease in permeability. In order of greatest to least clay content the soils were in order Davidson, Cecil, and Iredell, while in permeability rate their order was reversed. They found that an inverse relationship existed between clay swelling and permea- bility. The greater the swelling, the lower the permeability. They attributed this to the clogging of smaller pores with swelling water. They also found that in the coarser fractions permeability was found to increase exponentially with an inerease in particle size. N915): . - 0 “fly- "Alp 0A rat 9 . 3:16“.- oe 17..--..(1 ' . a given 531* ficult to 3 istic pert: arates, it the can-es; 3 decmase Cohtion TE size of p,, EaVer Boil pef'flea ”it'd an t; ImiI‘QCt. 3;. 8Pace, M181 1 imgatign '5‘" 34931 x 3011 has 3:141 Pregip I“ 'K- ‘ af’rq‘r‘a FA slur 4“ a mi. 8. Nelson and Baver (26) showed similar data in regard to the relation- ship of pore systems and permeability. They found that the disposition of infiltrated water is governed by the nature of the pore space in a given soil profile. These investigators also made a study of percolation rates through cores and found that constant percolation rates were dif- ficult to obtain. They did, however, find a tendency toward character- istic percolation rates and particle size. ‘When'working'with sand sep- arates, it was noted that as the average size of the particle decreased, the corresponding percolation rate decreased. This is coincident with a decrease in percent non-capillary porosity. It was found that the pare colation rate varied directly with volume of pores and inversely with the size of pores. Baver (1) has stated that the best known direct methods of evaluating soil permeability involve the determination of the infiltration rate in situ and the measuring of percolation rates of cores in the laboratory. Indirect methods must be used to determine the character of soil pore space. Much work has been done in determining the infiltration capacity of soils primarily from the standpoint of the soil conservationist and the irrigation engineer. Their interest lies in the answer to the question, "How'much rain or sprinkler irrigation can be applied to a given area or soil type and for how long a period before the soil becomes saturated and precipitation or irrigation rates exceed infiltration capacities?" The apparatus generally-used by these investigators has?been the F or IFA infiltrometer, of the rainmaker type. This equipment is expensive, has a high operating cost, and is cumbersome. Reviewi: cusses pessi‘: deaided to u. posed by See that allele“: did mt all: “19!! they a “Want or infiltratio: mospheric '33 for t}; '1‘ Steel 51“ r 9. Reviewing other methods of infiltration study, Kohnke (l7) dis-~ cusses possible sources of error. In conducting his own study, Kohnke decided to use the concentric square buffer type infiltrometer as pro- posed by Nestrov, and used later by Katchinsky. He wanted an apparatus that allowed vertical.flow, unimpeded lateral flow, and at the same time did not allow air pressures in the soil column to build up to a point ‘where they exceeded natural conditions. Kohnke further explained his viewpoint on trapped soil air during infiltration.and pointed out that infiltration rates were much reduced when air pressures greater than atmospheric conditions caused impeded flow of water.into the soil. It 'was for-this reason, in addition to others, that he used the concentric steel square principle of Nestrov. The concentric ring infiltrometer used in this study is essentially of the same type used by Lewis (19), Musgrave (23), Katohinsky (IS), and Kohnke (l7) and has the advantage over the rainmaker type because it is inexpensive, easily set up, and is easily transported. 10. EXPERIMENTAL PROCED [IRES Field Procedures Infiltration characteristics in situ. The field laboratory for the measurement of infiltration rates was enclosed in a large tent. (Figure 2 and 3.) The concentric rings were temporarily placed in zoosition in a block I'H" (Figure h) pattern to assure adequate and con- ssistent spacing. After the design and spacing patterns were determined ‘tihe vegetation was removed with a minimum of soil disturbance. If the soil was thought to have a subsurface horizon impervious enough to im- pede water flow, a trench as shown in Figure 1; was dug to the surface of the impervious horizon. Rings were placed on these prepared sur- :ffaaces and driven into the soil to a depth of one to two inches depend— ing upon the micro-topography of the site . This was accomplished by unesans of a heavy sliding weight on a.rod welded perpendicular to a Erizeel plate so designed to hold the rings in place while being driven. A total of fifteen sets of concentric rings was set up at each £3c>il site. Ten ring sets were used for surface determinations and five ring sets were located on the subsurface for infiltration determina- tions. After the rings were in place, a small buffer plate was placed in ‘the>inner ring and burettes essentially of the same type used by Stauffer (31) were placed directly over the inner ring. The set up of the burettes, infiltrometer rings, and water cans is shown in Figures 2 and h. Prior 1: tmttes wen the desirei 1 and car. are; 311;; flairtai the Stcpcge, on the 331:; Peadi; fifteen min mainir “Ch Site, in the 3.3:: we take} Plic ed L”. 11. Prior to zero time, the two and one-half gallon cans and the burettes were filled with water. The head of water was maintained at the desired depth (two inches) by adjusting the height of the burette and can above the soil surface. Air displacement of water automatic- ally maintained the head of water at the two inch depth. At zero time the stopcock on each burette was opened and the water cans were inverted on the outer, larger rings. Readings were taken every ten minutes for the first hour, every fifteen minutes for the next three hours, and every half hour for the remaining three hours in the seven hour run. Two runs were made on each site. The initial or dry run was made the first day with the soil in the moisture condition that it was found. Ck: the second day a wet man was made. A minimum of twelve hours was allowed to elapse between runs. Just prior to the time the initial run was started, moisture samples were taken of each of the horizons in the profile. The samples were Placed in standard type moisture cans. Lids were taped on with masking tape. In addition, air and soil tanperatures, temperature of the water, and evaporation readings were recorded at the beginning and at the end 01‘ each seven hour run. At each site the profile was studied carefully. The texture, structure, and color of each horizon was observed and recorded. Core Samples of each horizon were taken, using the methods of Uhland and 0'Neal (32) and care was taken to have the soil at approximately field capacity before sampling. The numbered cores were placed in pint con- tainers and transferred to the laboratory. 12. Definition 32 terms. Various investigators (1h), (33) have re- ported that some confusion exists in the use and definition of the term infiltration capacity. In order to meet on common ground in this matter, this thesis will follow the concepts of Horton (In) and his definition of this term. Horton states that infiltration capacity is the maximum rate at which a given soil in a given condition can absorb rain as it falls. Horton further states that infiltration capacity varies with time and as a soil continues to absorb moisture, each soil reaches a minimum infiltration capacity. The term, initial c_l_r_y infiltration, will apply to the maximum in- filtration capacity of a soil at the start of the dry run. The term, initial wet infiltration, will apply to the maximum in- filtration capacity of a soil at the start of the wet run. Measurements for these two values were taken as the average rate 01‘ flow, in inches of water, during the first hour of a seven hour run. The term, minimum infiltration capacity, is used to describe the rate of flow of water through the soil profile after a dry seven hour run was made on the soil, followed twelve to eighteen hours later by a Wet run. The measurement was taken as the flow of water in inches per hour based upon the average rate of flow from the fifth to the seventh hour of 'the wet run. At that time a constant rate of flow had been eBtablished. Laboratory Procedures Upon arrival in the laboratory the core samples were trimmed and fitted with a filter paper and cheesecloth base to prevent soil loss or mil 5 lass seas: tension ta ables '9; mm ten cabinet 1r' I tens “he h. fez“ 13. during laboratory manipulations. Approximate field moisture determina- tions were made by weighing the prepared cores. The cores were then placed in deep pans of distilled water for a period of one to two days, or until saturated. They were then weighed. Pore size distribution determinations were obtained from weight loss measurements which were made after equilibrium was established on tension tables similar to those used by Learner and Shaw (18). The tables were set at 0.01, 0.02, 0.03, 0.01;, and 0.06 atmospheres of water tension. The tension tables were contained in an upright steel cabinet which reduced evaporation losses from the cores. The cores were taken from the 0.06 atmosphere tension table and placed on porous ceramic plates in pressure cookers of thetype des- cribed by Richards (28). In the apparatus the cores were subjected to tensions of one-third, one-half, and one atmosphere, respectively. Permeability determinations were made by the method described by Uhland and O'Neal (32). A one inch aluminum ring was taped to the core cynnder with masking tape. The surface of the soil core was protected fIron: excessive turbulence by means of a small filter paper. The cores were then resaturated and water was added in 100 milliliter increments. Permeability was determined from the amount of water percolating through the core in a two hour period and was reported as inches of water per hour. When permeability determinations were completed, the cores of soil were oven dried at 110 degrees Centigrade for thirty-six hours and weighed. Volume weight and moisture content at the various tensions on an oven dry weight basis were calculated. W" ..‘ ‘ 139 ad ,, in far: in the Art! Laboratary 3a: 5 11;. The data obtained from these procedures are contained in tabular form in the Appendix under the section headed, "Basic Field and Laboratory Data." 15 . Statistical Procedures The procedures followed for all statistical determinations in this thesis were described by Dixon and Massey (5). Data contained in Tables III and IV are the correlation coefficients between the factors thought to influence infiltration and permeability in soils. Dixon and Massey (5) stated that in a sampling of any population believed to be normal and involving two variables, a test of the inde- pendence of corresponding values may be ascertained. This is to say, if these variables as points in a plane have little or no relation to each other, the correlation coefficients will approach or be equal to zero. If the variables are in some manner related, certain minimal values, based on N—2 degrees of freedom and percentiles of significance, will show the probability percentiles for the minimum chance of inde- pendence in this population. Correlation coefficients which exceed the minimal values in any particular case show a probability of signifi- cance toward dependence, or correlation. However, in a sampling of some populations involving two variables which are independent, it is Possible to find a series of points, if the data'are plotted in two di- men sions, which show a significance of correlation at various percentage leVels. The test of the validity of the correlation, or an indication 01‘ significance, is to show that the correlation coefficient is greater that: three standard deviations of the correlation coefficient obtained. Calculations were made to determine the validity of extreme values i'Cnmd in raw permeability and infiltration data for each soil site. An Opinion on the statistical significance of these extreme values was ob- tained and it was decided that values which exceeded three times the 16 . standard deviation from the mean value, positively, or negatively, would be discarded. It was noted that only the extremely high values could be discarded on this basis. This was not true for the very low values since three Standard deviations from the mean in almost every case allowed zero rates of flow. In addition, it was felt that the range of values ob- tained in this manner was not too wide when the variability of soil is considered in the light of past investigation and when wide coefficients of variation found in this study are noted. 17. RESULTS AND DISCUSSION Variability Analysis It has been noted by some investigators (10), (26) that constant rates of flow in core permeability studies are difficult to obtain. Replicate infiltrometers have also been found to give a range of rates which are mainly due to soil variability in addition to other variables. Lewis and Powers (20) mention several factors which may limit constant infiltration measurements. They are (l) the pressure effect of different hydraulic heads, (2) depth of moisture penetra- tion, and (3) textural differences in a soil column. As infiltration of water proceeds, differential swelling of the colloids probably due Partially to the initial soil variability tends to increase the var- ia‘bility between replicates . A statistical analysis of individual variability was made of core Permeabilities and infiltration rates on a sampling group taken from the twanty-six sites. The sampling group contains three soil types, Fox sandy loam, Hillsdale sandy loam, and Miami silt loam. The Fox sandy loam was replicated to see if there were trends toward constant relationships between the same soil type located in different areas of the state. The data reported in Tables I and II show that wide variations were commonplace. However, certain trends were found to exist for the Sampling group. For instance, as shown in Table I, the average readings :P 1: its! D, i’nNrdlh. m ruli‘: \EQEIPQ‘: .. .. New... n“ J. _ . HuihH 18. of minimum infiltration showed the highest range of variability. It was felt that whatever the cause for wide variability in minimum infil- tration flow rates, the same processes affected the permeability of saturated cores. The initial wet infiltration variations were usually less variable than were the measurenents for the initial dry infiltration rates. This is not strange since certain variable factors present in a dry soil ap- proach equilibrium in a saturated soil. The permeability data show wide variation also which, from past investigations (26), was not surprising. However, variations in the measurements for minimum infiltration capacity were also wide and of the same order. &rrf ace Soil Correlations Certain of the physical properties of soils seem to be related to the moisture characteristics which a soil may exhibit. The factors of Pore size, pore size distribution, continuity of pores, and moisture content of the soil, may have some effect upon the rate of infiltration and permeability. Several of those factors which might be related to each other were selected and tested for a correlation study. Their cor- I‘elations will be considered individually in the discussion to follow. Minimum infiltration capacity 3.112 permeability. There is a very high significance of correlation for minimum infiltration capacity and permeability. The correlation coefficient is 0.88 .t. 0.01:7. The reason for this high correlation may be explained by stating that both methods of water flow measurement are of the same type, that is, measuring rates of water flow through soils in a saturated or very wet state. It is be- l9. lieved that the saturation of cores prior to permeability determinations was approximated by long periods of water flow through a soil profile undergoing an infiltration study. Under these conditions of inf iltra- tion, most of the variable properties in a soil body would have reached a state of equilibrium and would give readings related to core perm- eability. Figure 5 gives the regression line which appears as a solid line, where Y =- 0.82 X +0.90. Examination of this line for the two variables, shows three soils far out of line. The data related to these points were discarded for pertinent reasons. Sites 7 and 8, Nappanee and Paulding soil series respectively, were very fine textured soils. Due to the dryness of’the soils, core sampling was difficult. This probably altered the structure in the soil cores to allow an excessively high permeability rate. Values for Site 3, a Sprinks sandy loam, were disregarded for the reason that infiltration rates were obtained on the Spinks soil While the core samples were in- advertently taken from a Hillsdale sandy loam. An important point to be made at this time is that even though the regression line for the total twenty-six sites is distorted by the poor .results from the three previously mentioned soils, the correlation is 3t I‘ong enough to hold the regression line well within significance at the one percent level (r - 0.59 1 0.133). In addition, if the high cor- relation of these two variables is considered in the light of the wide Variability in the rates of flow for both methods, it must be assumed that the magnitude and direction of the variations are of the same order. The correlation between these two variables has proven to be strong and Very highly significant. The correlation is also very close to a straight 20. line relationship. On the 13271:: of these results it is concluded that if cores of the surface horizon of a given soil are carefully taken at approximately field capacity, the approximate minimum infiltration capacity of a soil can be estimated in the laboratory by saturated permeability determinations Minimum infiltration capacity and lowest permeable horizon in p rofile. The correlation coefficient is 0.20 3 0.196 and is not sig- nii'icant. horizon which is less permeable than the horizon above it, with flow This also shows a This is probably due to lateral flow taking place over a mOVZ’Lng laterally through the more permeable horizon. 8hortcoming in the concentric ring infiltrometer for the measurement of infiltration characteristics of the total soil profile. In defense of the infiltrometer, the buffer compartment prevents lateral flow of Water from the inner ring down to the horizon which is impervious. H Owever at this point lateral flow is unimpeded and correlated data for this point are not obtainable. Minimum infiltration capacity and. volume weight. coefficient is a negative 0.53 3 0.11:7 (see Figure 6 for the regression The correlation line) and is significant. This is to be expected since as volume weight i“creases, porosity should decrease, with a corresponding decrease in De meability . Minimum infiltration and percent pores drained at various tensions. The significant correlations in this group are shown in Table III. Their COrresponding regression lines are presented in Figure 7, 8, 9, and 10. The correlations at the 0.01 atmosphere and 0.03 atmosphere tensions were not significant but at higher tensions the correlations improved. 21. This apparently was where pores were becoming continuous. There was an additional improvement in the correlation when pore sizes 100 and 18 microns in diameter at 0.60 and one-third atmosphere of tension were added to the total volume of pores drained. The addition of pores drained at one atmosphere of tension did not seem to further improve the correlation. The increase and steady correlation, starting at the 0.h0 atmosphere tension and continuing through the one atmosphere tension level seems to indicate that the smaller pores influenced the minimum infiltration capacity runs. Scth (29) working with large pond type inf-'1 ltrometers, has stated that infiltration rates are directly pro- Portional to the combined depth of the surface water head and the hydro- static head existing in the soil. The depth of the hydrostatic head is dependait upon the nature of the soil and will not always be constant for a given depth of surface head. Edlefsen and Anderson ( 8 ) have ataimed that hydrostatic pressures in soils are nearly proportional to the depth of water in the soil column. Considering the added depth of the hydrostatic heads that might exist in a soil and the corresponding 1":v’ntribute to an estimate of the initial moisture content of the soil Pore systen. However, such pores do not contribute to infiltration because of their discontinuity. Therefore, flow rates would be dis- Proportionate again due to non-functioning large pores. Initial 15y infiltration capacity and permeability. The correla- tion coefficient is 0.81 _+_- 0.095. (See Figure 31 for the regression 1”?! 1! i. . .. E i: “i with. 3‘"! Vi . .tr «I. 31. line.) There is a high significance of correlation. Permeability in this case again is probably dependent upon the ability of the smaller continuous pores in the soil to act as transmission channels through a relatively impervious soil. This is consistent with previous discussions. Initial 1'23: infiltration papacipy and permeability. The correlation coefficient is 0.85 i 0.077. (See Figure 32 for the regression line.) There is a very high significance of correlation. The situation for this correlation is the same as previously discussed for initial wet in- filtration capacity and permeability in surface soils. The degree and extent to which factors influencing infiltration and permeability have acted upon the soil body with its pores and cracks, determines its re- sponse to further tests of relative rates of water flow. In the case of subsurface soils, if the pore’ volume of the smaller pores is reduced by swelling then as is indicated by the high correlation, the infiltration and permeability rates are proportionately reduced. Summary of Subsoil Correlations It should be noted that while the number of significant correla- tions for the surface soil were many, significant correlations for the Shbsoil were not so frequent. It was noted that this loss of correla- tion was primarily due to the relatively moderate loss of total pore 8pace with a corresponding increase in'volume weight, while permeability and infiltration rates did not decrease proportionately. Most of these cases can be explained by noting that in infiltration and permeability, the continuity of small pore sizes did not always. produce a significant correlation. Therefore, some of the distortion of the correlation was due to the flow of water through channels other than the pores. This 32. flow may have been through cracks and checks associated with soil structure. The lack of correlation between permeability and volume weight illustrates this point. It was noted that a high correlation existed between minimum in- filtration and subsoil permeability. The high correlation between these two variables as opposed to the lack of correlation between permeability, minimum infiltration, and their corresponding volume Weights, was thought to arise from the fact that approximately the same type of disturbance of soil structural cracks and pores occurs Widen preparing cores for permeability determinations and the prepara- tion of subsoil trenches in infiltration studies. Initial dry and initial wet infiltration, as compared with perm- eability, had a very high significance of correlation. This close association was probably due to the fact that as in minimum infiltra- tion and permeability correlations, the soils are not too far from a 8aturated state. Thus flow rates in the subsoil for initial dry, initial wet and minimum infiltration, approximate each other with re- sI>ect to permeability rates of flow. Evidence is shown of the fact that when comparisons were made between infiltration, permeability and their corresponding pore size distribution, the relatively high corre- lations involved a wider range of pore sizes which included the very 8mall sizes. Such a close relationship indicates that while the total Dore space in the subsoil was less, the continuity of the pores was much increased over the pore systems in the surface soils. 33. Regression Line Predictions It was felt that since certain of the correlations in this study were very high, regression lines with the necessary conversion factors could be employed to predict such quantities as the minimum inf iltra- tion capacity of a soil from given information on core permeability determinations, or other data which might result in the valuable saving of time. The regression lines and associated data were submitted to a statistical test to determine the coefficients of the regression lines With regard to predicting the above mentioned quantities. In many cases, the distribution of points about the regression line is wide, thus leading to a high standard error of estimate or a wide margin for predicting purposes. However, certain correlations were found that Showed a narrow distribution of points about the regression line. The best of these correlations was selected to test its value in prediction d eterminations . The coefficient of the regression line for the best correlation Was calculated in order to find the band of normality for predicting Purposes. The best correlation coefficient in this study existed between the two variables, minimum infiltration and permeability of the Ap horizon where r - 0.88 i 0.01:7. In a comparison of these two Variables, Figure 5 shows the limits of the band of normality into Which sixty-eight percent of all estimates will fall. The equation for the expression of this association is Y - 0.82]! + 0.902532 .1, showing that for any given permeability the corresponding unknown minimum in- filtration capacity can be estimated to within 2.1 inches per hour of its actual flow rate. 311. C OK- CLUS I ONS The relation between infiltration, permeability, and pore size distribution has been presented in this thesis by means of correlation studies. An attempt was made to make the correlation study complete Within the limits of time allowed for a study of only those essential and related variables thought to pertain to soil infiltration rates and permeability determinations. The results of this study seem to point toward certain relationships, listed below, which may be of value as an aid to further research in projects similar to this study. 1. There is a significant relationship between minimum infiltra- tion capacity and permeability rates for a given soil horizon. 2. If cores are taken at the proper moisture content and care- fully treated, it is possible to predict, within certain limits, the Tuinimum infiltration capacity of a soil. 3. Permeability and infiltration are directly affected by the e3Ct.ent of continuity and total percent of pores in the soil body. ’4. Pores in the size range, 600 to 200 microns in diameter, are More often than not, discontinuous. 5. The infiltrometer, as used in this study, will not supply infiltration data beyond the least permeable horizon in the profile. (1) (2) (3) (h) (S) (6) (7) (8) (9) ' (10) § (11) 35. BIBLIOGRAPHY Baver, L. D. 1938 Soil permeability in relation to non- capillary porosity. Soil Sci. Soc. Amer. Proc. 3: 52-56 Bodman, G. B. and Colman E. A. 19h3 Downward entry of water into soils. Soil Sci. Soc. Amer. Proc. 8:116-122 Bradfield, R. and Jamison, V. C. 1938 Soil structure - attempts at its quantitative characterization. Soil Sci. Soc. Amer. Proc. 3:70-76 Browning, G. M. 1939 Volume change of soils in relation to their infiltration rates. Soil Sci. Soc. Amer. Proc. hz23-27 , Dixon, W. J. and Massey, F. J. 1951 Introduction to statistical analysis. McGraw Hill Book Company pp. let-165 Duley, F. L. 1939 Surface factors affecting the rate of intake of water by soils. Soil Sci. Soc. Amer. Proc. h:60-6h and Domingo, C. E. 19h3 The effect of water temperature on rate of infiltration. Soil Sci. Soc. Amer. Proc. 8:129-131 Edlefsen, N. E. and Bodman, G. B. 19hl Field measure- ments of'water’movement through a silt loam soil. Jour. Amer. Soc. Agron. 33:713-731 and Anderson, A. B. C. 19143 Thermodynamics of soil moisture. Hilgardia, 15:20h-210 Edminister, T. W., Turner Jr., W. L., Lillard, J. H., and Steele, F. ‘1951 Test of small core samplers for permeability determinations. Soil Sci. Soc. Amer. Proc. 15: h17-h20 Free, G. R. and Palmer, V. J. 19h0 The interrelation- ship of infiltratiOn, air movement, and pore size in graded silica sand. Soil Sci. Soc. Amer. Proc. 5:390-398 (12) (13) (1h) (15) (l6) (17) (18) (19) (20) (21) (22) (23) (2h) 36. Green, W. H. and Ampt, G. A. 1911 Studies in soil physics. Journ. Agron. Sci. hzl—Zh Haines, W. B. 1927 Studies on the physical properties of soils. IV A further contribution to the theory of capillary phenomena in soil. Jounn. Agr. Sci. 17:26h-29O Horton, Robert E. 19h0 An approach toward a physical interpretation of infiltration capacity. Soil Sci. Soc. Amer. Proc. 5:399-h17 Katchinsky, N. A. 193k Methodes Pour Determiner la Permeabilite du sol a'leau envue d'une Irrigation. Trans. of the Internet. Soc. of Soil Sci. A 2:79-99 King, F. H. 1898 Principles and conditions of movements of ground water. 19th Annual Report, Part II, U. 3. Geological Survey, pp lS-29h Kohnke, H. 1938 A method for studying infiltration. Soil Sci. Soc. Amer. Proc. 3:296-303 Leamer; RW‘W. and Shaw, R. l9h1 A simple apparatus for measuring non-capillary porosity on an extensive scale. Jour. Amer. Soc. Agron. 33:1003-1008 Lewis, M. R. 1937 The rate of infiltration of water in irrigation practice. Trans. Amer. Geophysical Union. Part II:361—368 and Powers, W. L. 1938 A study of factors affecting infiltration. Soil Sci. Soc. Amer. Proc. :60—6 Lutz, J. F. and Leamer, R. W. 1939 Pore size distri- bution as related to the permeability of soils. Soil Sci. Soc. Amer. Proc. h:28-3l Moore, R. E. 19h0 The relation of soil temperature to soil moisture: pressure potential, retention, and infiltration rate. Soil Sci. Soc. Amer. Proc. 5:61-61: Musgrave, G. W. 1935 The infiltration capacity of soils in relation to the control of surface runoff and erosion. Jour. Amer. Soc. Agron. 27:336-3h5 and Free, G. R. 1936 Some factors which madify the amount of infiltration of field soils. Jour. Amer. Soc. Agron. 28:727-739 (26) (27) (28) (29) (30) (31) (32) (33) 37. Nelson, L. R. and Muckenhirn, R. J. 19bl Field percolation rates of four Wisconsin soils having different drainage characteristics. Jour. Amer. Soc. Agron. 33:713-731 and Baver, L. D. l9h0 Movement of water through soils in relation to the nature of the pores. Soil Sci. Soc. Amer. Proc. 5:69-76 Peels, T. C. l9h9 Relation of percolation rates through saturated soil cores to volume of cores drained in fifteen and thirty minutes under sixty cm of tension. Soil Sci. Soc. Amer. Proc. lb:359-361 Richards, L. A. l9h8 Porous plate apparatus for measuring moisture retention and transmission in soils. Soil Sci. Soc. Amer. Proc. 66:105-110 Schiff, L. 1953 The effect of surface head on infiltrap tion rates based on the performance of ring infiltromp eters and ponds. Trans. of Amer. Geophysical Union 3hz257-266 ' and Dreibelbis, F. R. 19h9 Preliminary studies on soil permeability and its application. Trans. of Amer. Geophysical Union 30:759-766 Stauffer, R. S. 1938 Infiltration capacity of some Illinois soils. Jour. Amer. Soc. Agron. 30:h93—500 U'hland, R. E. and O'Neal, A. M. 1951 Soil permeability determinations for use in soil and water conservation Mimeograph material U.S.D.A. SCS-TP 101:1-36 Zwerman, Paul J. 1938 The relation of sheet erosion to the structure of Duffield silt loam. Soil Sci. Soc. Amer . Proc . 66 :105-110 rail-lax. ill; 4.“. . . \ APPENDIX 39. TAB LE I STATISTICAL ANALYSIS OF INFILTRATION DATA as Site Soil Type Infiltration Av. Stazdard Coefficient b!c>. In. hr. . . 0 __g / Dev1atlon Variation 5? Fox Sandy Loam Surface Initial Dry 6.3 .78 12.3h Initial Wet 3.9 .33 8.38 Minimum 2.? 2.56 93.81 subsurface Initia1.Dry 6.6 2.25 3h.09 Initial Net 3.6 .56 15 .246 Minimum 1.8 .96 53.21 JUO Fox Sandy Loam Surface Initial Dry 9.0 2.8h 31.55 Initial Wet 6.0 1.88 31.33 Minimum 3.7 1.89 51.08 Subsurface Initial Dry 9.0 3.55 39.hh Initial Net 5.0 .52 10 .hh Minimum 1.9 .96 50.h7 3L5 Fox Sandy Loam Surface Initial Dry 111.2 3.68 25.91 Initial Wet 71; 2 .32 31.35 Mfinimwm 8.8 3.65 bl.h7 Subsurface Initial Dry 7.3 1.83 25.06 Initial Wet 3.7 .50‘ 13.37 Minimum 2.0 .58 28.90 17 Miami Silt. Loam Surface Initial Dry lh.1 6.1M h3.5h Initial Wet h.7 1.60 311.01; Minimum , 3.6 1.27 35.27 Subsurface Initial Dry 3.0 .29 9.6 Initial Wet 1.11 .29 20.57 Minimtml 03 015 so .66 23 Hillsdale Sandy Loam Surface Initial Dry' 8.6 1.92 22.32 Initial Net 6 .h 1 .77 27 .65 Minimum 8.1 h.l6 51.32 Subsurface Initial Dry 3.5 .37 10.h8 Initial Wet 2.3 .21 9.21 Minimum .h .lh 35.25 \ y‘ A * in inches per hour ** in percent L0. TABLE II STATISTICAL ANALYSIS OF PEifl-JIMABILITY DATA A M. a «m A # I— -‘ -‘ A w W ‘-‘-r-HW ESjsbe Soil Type Average Average Stahdard Coefficient P‘<’- ml/mln- In-/hr° Deviation of Variation 5? Fox Sandy Loam Ap 3 .50 l .79 1 .55 1111 .15 Bl*** 2.00 1u02 1.19 59.50 B2 b.60 2.30 1.77 38.h7 B3 15.60 7.90 8.b7 5h.22 10 Fox Sandy Loam Ap 2.60 1.33 .87 33.57 Bl 1 055 079 057 1‘9 e20 82*":31’ 1‘ 039 2 023 1 093 1‘3 096 B3 30.00 15.30 8.22 27.39 15 Fox Sandy Loam AP 7 .79 3 .97 2 .110 30 .80 12 1.00 2.01 0.71 18.50 A3 2.52 1.28 1.18 h5.23 3L7 Miami Silt Loam Ap 3.8h 1.95 1.28 33.68 1.2 1 .30 .66 .57 M .88 A3 .ho .20 .28 71.89 B21” 077 039 037 ’89 .79 B22 .28 01h .10 36 036 B3 .29 .15 .07 217.82 2 3 Hillsdale Sandy Loam AP 5.50 2.80 1.52 27.62 Ap 1.60 .81 .82 51.31 12 .32 .16 .11 3h .37 B21“ 026 013 013 he 0&6 822 .17 .86 .05 28.23 B3 .25 .151 .101 39 .60 B3 036 0181 0131 36 091‘ c .20 .101 .07 32.75 \ A 44—. * in milliliters per minute 11* in percent m subsoil infiltration capacities were made on this horizon I"'F '- mfljhchwj- TABLE III SURF. CE CORRELATION DATA :- 1 ‘-—‘—-._ :—__ 'Ffiigure Variables r arr 5 Minimum Infiltration and Permeability .88* I: .0h7 Minimum Infiltration and Lowest Permeable Horizon in Profile .20 I .196 6 Minimum Infiltration and Volume Weight 53* 1 .1117 Minimum Infiltration and Percent Pores Drained at 0.01 Atms. Tension .25 I .191 0.03 Atms. Tension .117 I .159 7 0.0L Atms. Tension .50* f; .153 8 0.06 Atms. Tension .5819 i .1118 9 0.33 Atms. Tension .58* I .135 10 1.00 Atms. Tension .55* I .1112 11 Minimum Infiltration and Percent Total Pore Space .60Kb I .131 12 Permeability and Percent Total Pore Space .72* i .098 Permeability and Percent Pores Drained at 13 0.01 Atms. Tension .53* I .1117 111 0.03 Atms. Tension .67* i .112 15 0.0h Atms. Tension .62* 31 .125 16 0.06 Atms. Tension .57* I: .138 0.33 Atms. Tension .38 j: .175 01.00 Atms. Tension .33 .C .182 17 Permeability and Volume Weight .7531 j; .089 18 Initial Dry Infiltration and Permeability .63* I; .123 Initial'Wet Infiltration and Permeability .1.3 3: .166 19 Initial Dry Infiltration and Initial Air Space .72* I .105 «- Significant of the 1% level bl. TABLE IV SUBSURFACE CORRELATION DATA W “m Figure Variables r r r 20 Minimum Infiltration and Permeability .811!- 1’. .093 Minimum Infiltration and Lowest Permeable Horizon in Profile .32 I; .2h9 Minimum Infiltration and Volume Weight -.17 I .269 Minimum Infiltration and Percent Pores Drained at 0.01 Atms. Tension .09 L: .275 0.03 Atms. Tension .h3 5: .226 21 0.014 Atms. Tension .81* i .095 22 0.06 Atms. Tension .86* j; .072 23 0.33 Atms. Tension .77*' Q: .113 2b 1.00 Atms. Tension .78*- j: .108 Minimum Infiltration and Percent Total Pore Space .29 I .2511 25 Permeability and Percent Total Pore Space .66* J: .156 Permeability and Percent Pores Drained at 0.01 Atms. Tension .22 .1 .26h 26 0.03 0.03 Atms. Tension .67* 1'. .1119 27 0.011 Atms. Tension .8h* I .082 28 0.06 Atms. Tension .81* ;t .095 29 0.33 Atms. Tension .76* Li .117 30 1.00 Atms. Tension .79* I .1011 Permeability and Volume'Weight -.23 .1 .263 Initial Dry Infiltration and Initial Air Space -.08 i .271 .31 Initia1.Dry Infiltration and Permeability .81* 2‘. .095 .32 Initial Wet Infiltration and Permeability .85* I. .077 \ M2. * Significant at the 1% level m .g ant...“ ‘- w TAB LE V AVERAGE VALUES FOR BASIC FIELD AND LI‘ABOIDATOR‘Ir DATA Surface Initial Air Space (%) Initial Dry Infiltration (in./hr.) Initial Wet Infiltration (in./hr.) Minimum Wet Infiltration (in./hr.) Permeability Volume Weight (gms/cc) Total Pore Space (1) Percent Pores Drained at 0.01 Atms. 0.03 Atms.) 0.0h Atms. 0.06 Atms. 0.33 Atms. 1.00 Atms. subsoil Initial Air space (5) Initial Dry Infiltration (in./hr.) Initial Wet Infiltration (in./hr.) Minimum Wet Infiltration (in./hr.) Permeability Volume Weight (gms/cc) Total Pore Space (1) Percent Pores Drained at 0.01 Atms. 0.03 Atms. 0.0h Atms. 0.06 Atms. 0.33 Atms. 1.00 Atms. Minimum Permeability of Profile (in./hr.) Peg??? 888888 NH h3. .k Hen-Ia“ ‘ 3““? . to: .-'“ - .- 4.1““ .1—____—-———-I 47. mm at.“ #1 IHfi-‘a—— an MD oscaoA Aicom mscou. OGEMAIV Iosco "‘ escrow an: rum!” MENAC u. in)?“ MY Figure 1 , wmrco MfcasrA mum mouwo - ruscou 3.4mm Numbers Indicate Location of 3011 Sites . non/tram suitor «own new . r1 sense: ““5“ am in mm cumow 3mm. "cum 19 mum fut—— mu um: ”mm! mmcsr‘u 16 17 1 2 3 23 115 mum. cums JAtKJOIl msumuw mm 11 10 suosmv Mam pursuit-unite: manor 3!! 15 9 78 r—A_ I" ~. 0 ‘7 C" o . u 0‘ 0’. l.._—-—- a ’_ .— 2. Photograph showing infiltrometer apparatus set up and in operation on a soil site in Southern Michigan. .. ‘ \ ‘Q I a a" " )1 ' Q I}. t{- ' ".;. 'yl‘K‘h ' . ‘s s . _ ~ ‘ - "‘. ‘ ‘ . . " a... ‘ L. “’ r "8 ' - :" . .' ' I 4 . ‘1 p ‘ . u- ‘ ._ 4 . , - - I ' 'a . ‘v' "‘73:“ .o .‘ .' - . . ' ' ' ' - ’ t . , _- ' 7.. . . ,, '- - 7- .' ,5 -- W , . ‘ ‘ . ' g .' s y o' ‘ o . .‘ ' O Figure 3. Typical set up of apparatus and tut. ‘_ b7. 1 W e W. WW / /’\ ,‘ . K\“// \£;;;Z) :\\W”Ej SURFACE GROUP 3 T. l *-_--———————-_~ SUBSOIL GROUP IN TRENCH a. Arrangement of individual infiltrometers, using 5 and 9 inch rings. j l 1 Trench F F Impervious horizon b. Cross section of the subsoil group. Figure A. The arrangement used for the infiltrometers, (a.) showing general set up, (b.) a cross section showing the infiltrometer on an impervious horizon. ll. _1I(.Iai.|'4|1| .l filiall‘i, ,IE 1...? nhfl? 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BASIC FIELD AND MBOFJ‘xTOitY DATA _-—-—-— ‘W ——~—- —— _§oil Type Berrien Granby Hillsdale Miami Loamy Loamy Sandy Sandy ___ Sand ‘_ Sand Loamy Loam Site Number 1 2 3 h Sample Number 1 6 ll 18 Horizon Ap Ap Ap Ap Initial Air Space, :5 .. .. .. - Infiltration Initial Dry 2h.1 11.3 18.6 u.s Initial Wet 13.2 6.6 23.5 3.3 Minimum Wet 13.2 5.0 13.2, 1.1 Permeability 13.h 6.9 3.h 2.8 Volume Weight (gms/cc) 1.3 1.1 1.3 l.b Total Pore Space, % Sh S2 h8 h2 Percent Pores Drained at 0.01 Atms. h l h 6 0.03 Atms. 11 6 8 10 0.01; Atms. 13 9 10 11 0.06 Atms. 20 1h 13 1h 0.33 Atms. 27 20 17 19 1.00 Atms. 30 22 21 22 Sample Number 2 8 13 21 Initial Air Space, 5% - - .. .. Infiltration Initial Dry - _ - - Initial Wet - - - - Minimum wet - - - _ Permeability - - - - Volume Weight (gms/cc) - - .. - Total Pore Space, 1 - - - - Per Cent Pores Drained at 0.01 Atms. - - III «- 0.03 Atms. - _ - _ 0.0h Atms. — - - _ 0.06 Atms. - - _ - 0.33 Atms. — - - _ 10m Amso -' ‘- - .- Lowest Permeability of Profile .92 2.10 .13 .1h Rota: Infiltration and permeability values are given in inches per hour. '77. BASIC FIEID AND LABORATORY DATA L. Wang ‘nr‘b 1.5.;- Soil Type —§rookston Sims Nappanee Hoytville Sandy Clay‘ Silt Clay A ‘Qoam Loam Loam Loam Site Number 5 6 7 8 Sample Number 2h 30 35 LO Horizon Ap Ap Ap Ap Initial Air Space, 1 - 55 117 1111 Infiltration Initial Dry 17.1 h5.8 1h.9 26.? Initial Wet 17.9 27.0 5.5 20.1 Permeability h.0 15.1 20.1 27.6 Volume Weight (gms/cc) 1.h .9 1.1 .9 Total Pore Space, % 113 611 55 58 Per Cent Pores Drained at 0.01 Atms. 3 10 11 7 0.03 Atms. 6 17 15 13 0.0h Atms. 8 19 16 1h 0.06 Atms. 10 21 17 16 0.33 Atms. 15 23 17 17 1.00 Ath. 17 25 18 18 Horizon Bgl Blg Beg 62b Sample Number 25 31 37 h2 Initial Air Space, % -- 2h 20 32 Infiltration Initial Dry 10.6 7.5 2.7 6.h Initial Wet 2.5 5.3 1.5 2.1 Minimum Net 2.1 1.2 .1 0.14 Permeability 2.2 2.0 3.1 1.7 Volume Weight, (gms/cc) 1.6 1.1; 1.5 1.14 Total Pore Space, % ‘ 36 h? hl ’45 Per Cent Pores Drained at 0.01 Ath. 2 6 h 3 0.03 Atms. 7 10 6 5 0.0h Atms. 8 ll 6 5 0.06 Atms. 11 13 6 6 0.33 Atms. 17 13 10 9 1.00 Atms. 18 1h 11' 10 Lowest Permeability of Profile .10 2.00 3.10 1.70 Note: Infiltration and permeability values are given in inches per hour. 78. BASIC FlELD.AND LABORATORY DATA Soil Type Fox Fox Warsaw Spinks Sandy Sandy Silt Sandy Loam Loam Loam Loam Site number 9 10 ll 12 Sample Number h3 h8 5h 60 Horizon Ap Ap Ap Ap Initial Air Space, % 15 20 22 25 Infiltration Initial Dry 11.11 6.1 8.1 20.0 Initial Wet 3.9 hit 6.5 19.8 Minimum Wet 1.h 1.7 2.8 11.3 Permeability 1.5 l.h 2.9 7.5 Volume Weight (gms/cc) 1.6 1.5 1.2 1.5 Total Pore Space, % 33 37 149 39 Per Cent Pores Drained at 0.01 Atms. 1 h 5 2 0.03 Atms. h 7 9 6 0.0h Atms. 7 7 11 9 0.06 Atms. 10 9 13 20 0.33 Atms. 15 10 11 29 1.00 Atms. 17 10 11 29 Horizon . B3 82 B]. B]. Sample Number h6 50 - - Initial Air Space, % 27 22 - - Infiltration Initial Dry h.6 6.3 - ‘ Initial wet 2.1 3.1 - - Minimum‘Wet 1.0 1.3 - - Permeability h.0 2.0 - - Volume Weight (gms/cc) 1.5 1.6 - - Total Pore Space, % 35 37 - - Per Cent Pores Drained at 0.01 Atms. 3 h - - 0.03 Ath. ll 7 .. _ 0.0h Atms. 12 8 - - 0.06 Atms. 1h 9 - - 0.33 Atms. 23 9 - - 1.00 Atms. 2h 10 - - Lowest Permeability of Profile .78 .67 .hh 5.00 Note: Infiltration and permeability values are given in inches per hour. “ n , Fixbiil . rt! PF- . BASIC FIELD AND LABORATORI DATA '79- Soil Type Berrien 'Warsaw Fox Conover Sandy Silt Sandy Silt Loam Loam Loam Loam Site Number 13 1h 15 16 Sample Number 6h 68 73 82 Horizon Ap Ap Ap Ap Initial Air Space, % 3h lb 18 18 Infiltration Initial Dry 11.8 11.14 15.14 11.5 Initial Net 7.6 3.9 12.3 7.5 Minimum Wet 6.1 1.7 5.3 1.7 Permeability 9.7 1.0 3.8 h.3 Volume Weight (gms/cc) 1.h 1.5 l.h 1.3 Total Pore Space, % hO 39 h0 h7 Per Cent Pores Drained at 0.01 Atms. h 3 6 6 0.03 Ath. 8 h 11 8 0.0h Atms. 10 5 12 9 0.06 Atms. 12 6 1h 10 0.33 Atms. 17 9 16 1h 1.00 Ath. 19 11 17 16 Horizon —— 822 B2 32g Sample Number -- 7O 76 85 Initial Air Space, % - 17 11 23 Infiltration Initial Dry .— 10.6 7.2 3.3 Initial Wet -- S .5 3.6 2.3 Minimum Wet - 1.9 1.0 0.2 Permeability' - .9 1.2 0.8 Volume Weight (gms/cc) - 1.6 1.7 1.5 Total Pore Space, % - 32 37 hl Per Cent Pores Drained at 0.01 Atms. - 00 3 h 0.03 Atms. - 2 6 6 0.011 Atms. -- 6 6 7 0.06 Atms. - 8 7 9 0.33 Atms. - 10 ll 15 1.00 Atms. -— 11 12 17 ILowest Permeability of Profile h.00 .76 1.00 .12 Note: Infiltration and permeability values are given in inches per hour. BASIC FIELD AND LABORATORY DATA 80- W ___ Soil Type Miami Newton Saugatuck Conover Silt Loamy Loamy Silt Loam Sand Sand Loam Site Number 17 18 19 20 Sample Number 87 9h 99 10h Horizon Ap Ap Ap Ap Initial Air Space, % 20 27 38 18 Infiltration Initial Dry 111.1 8.1: 28.2 1h.5 Initial Net 5.8 h.6 23.1 14.9 Minimum Net 2.1 2.h 10.h 2.2 Permeability 1 .7 h .2 8 .1; 1 .6 Volume Weight (gms/cc) 1.5 l.h 1.3 l.h Total Pore Space, % 10 hh L? h} Per Cent Pores Drained at 0.01 Atms. h 1 2 h 0.03 Atms. h h 7 5 0.0b Atms. 5 l2 l7 6 0.06 Atms. 6 15 20 7 0.33 Atms. 8 22 33 12 1.00 Atms. 10 26 36 15 Sample Number 90 - 100 106 Initial Air Space, % 22 - - 11 Infiltration Initial Wet 2.0 - 19.2 2.5 Minimum Wet 0.2 - 8.2 0.3 Permeability 0.3 - 10.8 0.5 Volume Weight (gms/cc) 1.6 - 1.2 1.6 Total Pore Space, % 38 - N9 39 Per Cent Pores Drained at 0033 Ame. 6 " 28 11 1400 Atms. 9 - 31 1h Lowest Permeability of Profile 12 66 7.50 .18 INote: Infiltration and permeability values are given in inches per hour. ‘ 81. BASIC FIEID AND LABORATOHR DATA Soil Type Granby Berrien Hillsdale Ubly Sandy Loamy' Sandy Silt Loam Sand Loam Loam Site Number 21 22 23 2h Sample Number 109 11h 121 127 Horizon Ap Ap Ap Ap Initial Air Space, % 39 27 27 32 Infiltration Initial Dry 20.1 15.2 10 3 h.l Initial Net 13 .3 13 .6 8 h 14.8 Minimum Wet 9.9 6.0 h 0 1.6 Permeability 10.7 h.l 1 8 1.0 Volume Weight (gms/cc) 1.2 1.5 1.5 1.5 Total Pore Space, % 52 39 39 DD Per Cent Pores Drained at : 0.01 Atms. 8 l 5 h 0.03 Atms. 16 3 9 5 0.01. Atms. 19 6 10 6 0.06 Atms. 18 8 11 8 0.33 Ath. 27 22 16 11 1.00 Atms. 30 25 18 13 Horizon ' BE B2 B21 82 Sample Number 11 - 121 128 . Initial Air Space, % 20 - 13 19 Infiltration Initial Dry 5.9 - 3.5 11.2 Initial wet 5.2 - 2.3 2.5 Minimum Wet 3.6 - 0.2 0.3 Permeability 0.5 - 0.1 0.3 Volume Weight (gms/cc) 1.7 - 1.8 1.7 Total Pere Space, % 30 - 31 35 Per Cent Pores Drained at 0.01 Atms. h - 1 l 0.03 Atms. 6 - 2 h 0.01. Atms. 10 - 3 6 0.33 Atms. 20 - 5 7 1.00 Atms. 20 g - 7 9 .Lowest Permeability of Profile .51 2.80 .06 .31 '1 O '7 i-J n—ei‘J'n-v‘zsn‘ . Note: Infiltration and permeability values are given in inches per hour. BASIC FIELD AND LABOEG‘iTOh’Y DATA WJ'32‘33'2—‘33—3‘3-‘3‘S‘33‘r m Soil Type A! Kalkaska Mancelona Loamy Loamy _ _- . -_,_____§aad_i Sand w Site Number 25 27 Sample Number 130 1&1 Horizon Ap AP Initial Air Space, % 28 28 Infiltration Initial Dry 11 .1. 19.5 Initial Wet 8.1; 5.8 Minimum Wet 5.9 3 .5 Permeability 6.7 8.9 Volume Weight (gms/cc) 1.5 1.5 Total Pore Space, % D2 bl Per Cent Pores Drained at 0.01 Atms. l h 0.03 Atms. 6 15 0.0h Atms. 1h 21 0.06 Atms. 22 2h 0.33 Atms. 29 29 1.03 Atms. 7 31 30 Horizon ‘ - - Sample Number - 9 Initial Pore Space, 2 - - Infiltration Initial.Dry' - - Initial Wet - - Minimumeet _ - Permeability - .. Volume Weight (gms/cc) - _ - Total Pore Space, % - ’ Per Cent Pores Drained at ‘ 0.01 Atms. - - 0.03 Atho '- - 0.0h Atms. _ - 0.06 Atms. — - 0.33 Atms. - - 1.00 Atms. — - Lowest Permeability of Profile 8.00 8.90 1‘“th ~‘ns ..-J—n_4. ' I. a " . . . ,I r . Note: Infiltration and penmeability values are given in inches per hour. flit» .litx XXL-PVJ‘W. l 13.71 "I71811111111111ITS