£3. SW5? {)8 mg fifiGSPHC‘fifiS SU‘WLYENG M’Wiks 3? SOME MECZ‘éEGAN 3&3 $303!: £0? £1: thyme afi 233:1. 13. MiCEiEGAR SEX? COLiEfiE C§amficé C. {2?an 3%; W52 THESIS This is to certify that the thesis entitled "The Phosphorus Supplying Powers of Some Michigan Soils" presented bg .' Clarence C. Gray has been accepted towards fulfillment of the requirements for Ph. D. . Soil science _____ degree m _____ 5. >77. 7:344. Major professor / Dam November 25, 195? 0-169 \ "a -._ ~—- —. -.u§ . -~ :6" . -.- ,. I - f‘a-iq rr 1“];- —-—~A-rq:---4 4: l .. ;_ A.STUDY OF THE PHOSPHORUS SUPPLYING POWERS OF SOME MICHIGAN SOILS By Clarence C. Gray III lull-n. 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 DOCTOR OF PHILOSOPHY Department of Soil Science 1952 THESIS .ACKNOWLEDGEMENT The writer eXpresses his sincere appreciation to Dr. Kirk Lawton to whom he is greatly indebted for the keen interest, valuable assistance, and able guidance that made this investiga— tion possible. Particular acknowledgement is given to Doctors L. M. Turk and R. L. Cook for their ready assistance and cooperation through. out the course of this investigation and in the preparation of this manuscript. To his wife, Lillian, the writer is eternally grateful for her abiding faith and confidence which aided immeasurably in the completion of the writer's program of adyanced study. 303G323 A STUDY OF THE PHOSPHORUS SUPPLYING POWERS OF SOME MICHIGAN SOILS By Clarence C. Gray III AN'ABSTBACT 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 DOCTOR OF PHILOSOPHY Department of Soil Science 1952 Approved by x m‘ M Clarence C. Gray III ABSTRACT .A Study of the Phosphorus Supplying Powers of Some Michigan Soils An investigation was undertaken to determine the phosphorus supplying powers of several representative Michigan soils. Forty-one different soils representing approximately eleven million acres of agricultural land in the southern half of the lower peninsula were selected for greenhouse and laboratory studies. Alfalfa was grown on each of the soils for eleven months under controlled conditions in the greenhouse. Available soil phosphorus was measured by several arbitrary chemical analyses making use of both rapid tests and more quantitative laboratory methods. Phosphorus fixation by the soils was evaluated by two different methods. One method measured the fixation of phosphorus at different rates of application and the other measured the amount of fixation with and without the free iron oxides. Forty-one Michigan soils varied greatly in their ability to pro- duce alfalfa without added phosphorus. No superiority of any textural group in producing alfalfa was recognized. Yields of alfalfa were increased on all soils by the addition of phosphorus. Chemical analysis of the alfalfa revealed that the addition of phosphorus to the soils approximately doubled the percentage phos- phorus composition. The recovery of phosphorus applied to the soils averaged 38.# percent. The amounts of chemically available phosphorus removed by the Clarence C. Gray III analytical methods employed varied with the soil and with the ex- tracting agent. No clear relationships between soil properties and soil phosphorus could be established with any of the test methods. Definite relationships were established between soil phosphorus and alfalfa yields which showed clearly that chemically available phosphorus can'be a good measure of the ability of a soil to supply phosphorus. A high degree of linear correlation was found between alfalfa yields and soil phosphorus extracted with reagents containing the fluoride ion. The Bray.Adsorbed Phosphorus test, which was well correlated with alfalfa yields, percentage phosphorus composition, and total phosphorus uptake, was the best rapid test method. Phosphorus fixation studies of twenty-two soils using several rates of applied phosphorus revealed no apparent relationship to any of the measured soil prOperties. The quantities of retained phos- phorus varied with the soil and with the amount of applied.phosphorus. The character of the fixation curves suggested that the mechanisms of fixation differed. The removal of free iron oxides from the soils reduced phosphorus fixation from 0.6 percent to 75 percent. No relationship, however. could.be established between the amount of fixation and free iron oxide content. .A classification of forty-one Michigan soils as to their phos- phorus supplying powers was presented based on yield and composition of continually cropped alfalfa, soil tests for chemically available phosphorus, and phosphorus fixation studies. TABLE OF CONTENTS INTRODUCTION 0 e e e a e e e a e e e PLAN OF INVESTIGATION . . . . . . . EXPERIMTAL PROCEDURE . . . . . . . Description of Soils Used . . . . Physical and Chemical Determinations Greenhouse Experiment with Alfalfa Phosphorus Determinations . . . . Soils . . . . . . . . . . . . . Alfalfa .........’... Fixation Studies . . . . . . . . . Rate of.Applied Phosphorus . . . Removal of Free Iron Oxides . . RESULTS AND DISCUSSION . . . . . . . Greenhouse Experiment . . . . . . Alfalfa Yields . . . . . . . . . Phosphorus Content of Alfalfa . Soil Phosphorus . . . . . . . . . Rapid Tests for Phosphorus . . . Bray Laboratory methods . . . . Fixation Studies . . . . . . . . . Rate of.Applied Phosphorus . . . Removal of Free Iron Oxides . . PAGE O\O\U\ 16 17 24 25 26 26 27 28 28 28 35 1+1 49 53 53 63 PAGE Relation Between.Alfalfa Yields and 5011 Phosphorus . . . . . 68 Spurway Reserve Test . . . . . . . . . . . . . . . . . . . 69 Bray Available Phosphorus Test . . . . . . . . . . . . . . 72 Bray Adsorbed Phosphorus Test . . . . . . . . . . . . . . . 72 Bray Total Acid-Soluble and.Adsorbed Phosphorus ... . . . . 77 Organic Phosphorus . . . . . . . . . . . . . . . . . . . . 80 Bray Total Acid—Soluble, Adsorbed, and Organic Phosphorus . 80 Relation Between Soil Phosphorus and Soil Properties . . . . 85 Relation Between Phosphorus Fixation anthlfalfa Yields . . . 89 The Phosphorus Supplying Powers of Forty-one Michigan 80113 . 91 SUMMARY . . . . . . . . . . . . . . . . . . . . . . . . . . . . 94 1’1me CITE O O O O O O O O O O O O O O O O I O O O O O O 99 INTRODUCTION The phosphorus supplying power of soils for agricultural plants is of considerable scientific and economic importance. Interest in the ability of a soil to furnish both native and applied phosphorus to plants has increased greatly in the last few years. The impetus for the increased interest and accompanying scientific activity has come from the introduction of improved methods of investigation, the ever increasing requirements for phosphate fertilizers, and the need for the efficient use of applied phosphates. Workers at the new Jersey Agricultural Experiment Station have conducted extensive investigations of the phosphorus supplying powers (31) and the phosphorus-adsorbing capacities (43) of New Jersey soils. Their studies have supplied worthwhile information as to the relative need of New Jersey soils for phosphate fertili- zation. .Additionally, their results indicate that the phosphorus- fixing capacity of a soil can be a useful guide in determining the amounts of phosphorus to apply. In Wisconsin, experiments have'been conducted to determine the relative phosphorus supplying powers of Wisconsin soils and to correlate available soil phosphorus with crop yields. Rich and Attoe (I3) growing six successive crops of oats on several different Wisconsin soils recovered 32 to 62 percent of the applied.phosphorus and obtained good correlation between the decrease in available soil phosphorus, as measured by 0.002 N H280“ and cat yields. .Attoe and Truog ( 2) also found a high degree of correlation between yields of alfalfa and clover hay and levels of available phosphorus soluble in 0.002 N 32804. The development of the fluoride methods for the extraction of soil phosphorus by Bray and his co-workers at the Illinois Agri- cultural Experiment Station has provided additional procedures for measuring available soil phosphorus (8,9,10). Bray has attempted to fractionate the inorganic soil phosphorus on the basis of chemical form. His methods, which purport to measure both the "adsorbed" and "acid—soluble" forms of phosphorus show promise for better correlations between soil tests and crop growth. Fluoride extractable phosphorus is well correlated with yields of general crops in Illinois when other soil nutrients are not limiting. Michigan.Agricultural Experiment Station workers Lawton, Robertson, Cook, and Rood (20) recently conducted an extensive study of the relation between crop phosphorus and potassium. The experiment was conducted over a two—year period (1946-47) on sixty- six locations in thirty—six counties of Michigan. "Available" soil phosphorus was determined by the rapid test methods of Bray, Peech, and Spurway. Linear correlation between hay yields and critical soil test levels was low. This was attributed to the wide variety of soils studies. Though they found that no individual soil test was definitely superior they concluded that in separating phosphate responsive soils from.nonpphosphate responsive soils, soil tests using weak acid extractants were superior to those using strong acid extractants. 3 In 19h7, Bowers ( 5) working with several Michigan soils in a greenhouse study reported little correlation.between soil phosphorus as measured by Bray's ”Total Adsorbed,.Acid-Soluble, and Organic“ phosphorus extractants and alfalfa yields. Smith (38), in 19h9, had considerable success in relating Bray‘s rapid soil tests to wheat yields. In an extensive greenhouse experiment, using twenty Michigan soils he compared several rapid soil tests for phosphorus including Bray's 'Adsofbed" and AAvailable“ phosphorus tests. Using the principles of Mitscherlich as modified by Bray (12), Smith found that Bray's phosphorus extractions corre- lated well with wheat yields and were definitely superior to the Spurway Reserve test. It should be pointed out that though Bowers and Smith both made use of fluoride extraction methods for the removal of phosphorus, the methods differed considerably in the amount of fluoride used and the time of extraction, hence the amounts of phosphorus extracted.varied greatly and perhaps were not comparable. Arnold and Schmidt ( 1) recently reported the results of twenty- five field trials with tomatoes in the Chicago area of Illinois and southern Michigan. Their objective was to compare the tomato yields of unphosphated plots with yields from plots that had received sufficient phosphorus to supply the plants with all they could utilize. The results indicated that Bray's soil phosphorus test for acid-soluble plus adsorbed phosphorus was well correlated with the response of tomatoes to phosphate fertilizer. They concluded that it Bray's soil test for phosphorus was a valid index of the phosphorus fertility of the soils studied. Despite the fact that phosphorus studies on Michigan soils have given varied results and in some instances have appeared conflicting and confusing, much valuable information has been obtained. However, the need for a better understanding of phosphorus levels and avail- ability in Michigan soils still exists. The main objective of this investigation was to secure additional information relative to the phosphorus supplying powers of several Michigan soils as indicated by plant growth, chemical tests, and phosphorus fixation. PLAN OF INVESTIGATION This investigation was undertaken with the intention of securing data on as many representative Michigan soils as was reasonably possible. The following general plan was adopted: 1. Study the ability of several soils to supply phosphorus for’plant growth by subjecting them to the continuous root action of a phosphorus responsive plant. 2. Measure several arbitrary soil phosphorus fractions as extracted by chemical soil tests and relate them.to plant growth and phosphorus uptake. 3. Study the relative phosphorus fixation by the selected soils and relate this capacity to the phosphorus supplying powers and to specific soil compounds. EXPERIMENTAL PROCEDURE Description of Soils Used During the summer and fall of 19b9, Doctor Kirkpatrick Lawtonl, under whose guidance this research was planned and conducted, collected representative Michigan soils and set up a phosphorus and potassium greenhouse experiment with alfalfa. This experiment, including the soils and the alfalfa grown an them, provided the basis for this investigation. Lawton selected forty-one soils from ten counties in the south- ern half of the lower peninsula of Michigan. The locations by counties are shown in Figure l and the legal descriptions are given in Table I. The soils represent twentyaone soil types which according to Veatch (#5) comprise approximately eleven million acres of agricul- tural land. According to Miller (25) most of these soils were developed from material deposited by glaciers, and consequently, they are heterogenous in composition and represent a wide range in physical and chemical properties with resultant variations in fertility and productivity. Miller points out that the mineral soils, particularly the loans, silt loans and clay loans, are usually more deficient in phosphorus than in any other plant food element. The work previously cited by Lawton, et a1 (20) substantiates this 1 Associate Professor, Soil Science Department, Michigan State College. 47' ”C x N 449%! a j‘. 7.3160 mm “sz (Imam mwr‘o 05am ucom m ”scan. 06mm Iasca “' “v mom can a 1mm: “0 no” mum: MECOSYA mama mum 36 3 9 3 ruscou maul: Figure 1. Location of $0118 Wm curler WIMWB by Counties. 5 32 arm “*1 5.2 ”1 sense: ““5" 0mm 101m amen 3m m‘. 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S .020. mm w E ~38..qu Sufism noafiofim .3 mam an? em .08 4 am am 329.30 3333 Muflflom 3 3mm 58 an .o 2% Maw 932333.... £392: inflow mm mam awe mm .3» w. 32. 4 3m saucepan handmdm hobonoo mm 5956 ooumskcudm nobonoo an @m 239 mm .oom am am is n85: sum 28; mm sea 20%. m 68 am eases 332m Sufism .38 mm see 299 am 68 as @358 awn ~33: an new 32. mm 63 2m Maw 933» sum aflsflafl R see nos. na .25 am am manna 3.32m panama seafloor“ mm a ma. om 6% «an I gunmen cicada an soapnasomoeilfimloq p58 8 H om 4444.8 mAHow ho HonaguhHEQH AdofinafiuooV H g8 10 for they found that phosphorus was the element most needed on the soils studied. veatch (1&9 has recently presented a comprehensive description of each of the soil types utilized in this experiment. A brief summary of each series follows: Bellefontaine Series. This soil series usually occurs as sandy loams occupying ridges and plateaualike uplands. Widely dis- tributed in both large and small bodies these soils are generally of medium fertility. Soil number 17, a.Bellefontaine sandy loam, was secured from.the farm of E. Lahrkey in St. Joseph County. Pre- vious history shows that it was of low fertility and had been in small grain in l9h8. Brookstog Series. This soil series occurs as loams and clay loans on level plains and in valleys. Mere than two million acres are found in extensive areas on lake bed plains. The plow soil is dark colored and underlain with wet, mottled, gritty clay. Generally, Brookston soils are high in organic matter and are very productive. Four representatives of this type were selected, soils number 7, 27, 32, and #1. Soil number 7 was secured from the experimental plots on the Lee Ferden farm in Saginaw County. Soil number 27 was obtained from the Prairie Farm in Saginaw County. Soil number #1 was secured from.the farm of Frank Indlehofer in Saginaw County. Clyde Serie . This series occurs as loans and clay loans in swampy and marshy land and comprises not more than 50,000 acres. Clyde soils are generally high in organic matter and when drained are very productive. Soil number 35 was secured from the Prairie Farm in Saginaw County. Conozeg Series. This series occurs as dark-colored loams and silt loams on smooth plains. Widely distributed in the southern and eastern parts of the state, Conover soils are high in fertility and.produce good yields of alfalfa, grains, and hay. Soils number 8, 9, 3?, and 38 represent the Conover series in this investigation. Soil number 8 was obtained from the Rudd farm in Ionia County. Soil number 9 was obtained from the farm of M; Pancake in Kalamazoo County. Soil number 37 was obtained from the S. Survoy farm.in Shiawassee County. Soil number 38 was Obtained from the farm of L. Bitterman in Saginaw County. Emmet Series. This series occurs as deep, penetrable sands and sandy loans on the ridges and.plateau highlands. They are character- ized‘by a light gray leached sand at the surface and brown sand or sandy loan at six to twelve inches. Emmet soils are widely distri- buted and the sandy loams where not too hilly are of fair fertility. Soil number 25 was secured from.the farm of E. Height in Oceans County. Past history shows that it was heavily fertilized with 0-20-20 fertilizer in 19h8 and cropped with beans. Fox Series. This series occurs as light brown and brown sandy loans and loans over reddish sandy and gravelly clay on level plains, terraces, and old beach ridges. Fox soils are widely distributed and when lined and fertilized produce good yields of general craps, truck craps, and small fruits. Three soils of the Fox series, numbers 12, 13, and 18 were selected. Soil number 12, a Fox sandy 12 loam, was obtained from the 13 Berry farm in St. Joseph County and had.been in sod for the past five years. Soil number 13 was obtained from.Kalamazoo County while number 18 was from Ingham County. Gragby Series. This series occurs as dark colored loams and sandy loans in flat areas such as low plains or borders of lakes and muck swamps. The series is found as small areas in association with the more calcareous sandy soils. Generally, the areas are too wet or in too small bodies to be of high agricultural value. 8011 number 5 was secured from the Michigan State College farm in Ingham County and past records show low to average yields were produced from this area. Hillsggle Serieg. This series occurs as light brownish and yellowish loans and light loans on hilly to smooth rolling uplands. Hillsdale soils are widely distributed and are of medium.to high value for general agriculture when managed properly. Soil number 11, secured from the K. Lawton farm.in Ingham County, was strongly acid and in a state of low chemical fertility. Soil number 31 was taken from a site in the southern part of Ingham County and had a high con- tent of native phosphorus in “available" forms. Isabella Series. This series occurs as light brownish loam and clay loam soils on gently rolling to moderately hilly upland clay plains. These soils are widely distributed and have a relatively high value for general farming. Soil number 23 was obtained from the farm of C. Fritz in Ottawa County and the evidence available indicated med- ium.fertility. Soil number 2h, obtained from the W. Schoenborn farm 13 in Ottawa County, was taken from an old peach orchard where severe erosion had taken place. Kalkaska Series.- This series occurs as dark brown sands and light sandy loams on level and.pitted plains, and dry, bench land. Kalkaska soils comprise extensive areas and produce low to fair yields because of their low water holding capacity. Soil number 19 was obtained from the D. Postema farm in Oceana County and had a past history of low fertility. It had been marled in 1948. Soil number 20 was obtained from the farm of O. Tibbits in Oceana County. It had received no lime or fertilizer in the past five years but had been manured in l9h8. Kawkawlin Series. This series occurs as dark colored loamy soils over compact, granular and gritty clays on level clay plains of old lake beds. Kawkawlin soils are of relatively high fertility and are of medium to high agricultural value. Soil number 33 was Obtained from the farm of L. Walter in Bay County and had received no fertilizer or manure in the past three years. Eggt Segieg. This series occurs as light brown and gray heavy silt loans and clay over plastic compact, and relatively impervious clays. Kent soils are distributed mostly in small areas on level, upland clay plains and are used mostly for hay and small grains. Soil number 21 was obtained from the F. Schneider farm in Muskegon County and past cropping data indicated it was in a state of medium fertility. Soil number 22 was taken from a roadside site in an eroded area in Kent County and was probably mixed.with some subsoil. 1h Magomb Series. This series occurs as dark brown and dark gray coarse friable loams. Generally found in small bodies on flattish swampy land, Macomb soils are similar to Brookston soils but coarser in texture. High in the element of chemical fertility, these soils when properly drained are productive. Soil number 6 was obtained from the L. Ferden farm in Saginaw County and was considered to be in a medium condition of fertility. MiamiASeries. This series occurs as light brown loans and silt loams over brownish, compact, retentive but granular clays on gently rolling upland clay plains. Miami soils comprise one of the more important series in aggregate acreage under agricultural production. They are widely distributed soils and rank high in fertility. They are extensively used for general farming purposes. Four Miami soils were selected for this investigation. Soil number 1 was obtained from the Gannsley farm in Shiawassee County. Soil number 2 was db- tained from the R. Cook farm in Clinton County and was of moderate fertility. Soil number 3 was obtained from.the farm.of E. Shaw in Ingham County and.was taken from.an eroded area. Soil number 26 was taken from a farm site in Clinton County and was known to be of low fertility at least with respect to phosphorus. Eppanee Serigg. This series occurs as gray and light brown silts and clay loams over very compact yellowish clays. Generally found on level and rolling uplands, the Napanee soils are not widely distribu. ted. Soil number 28 was secured from the farm of W. German in Lenawee County and was in a medium state of fertility. 15 Plainfield Series. This series occurs as light brown sands and light sandy loans on level sand.plains and dry sandy valleys. Plain- field soils are low in organic matter and the mineral elements of fertility. They are widely distributed and total a large aggregate acreage in crop production. They are low in value for general agriculture but when fertilized and irrigated can be used successfully for truck and small fruit farming. Soil number 30 was Obtained from an abandoned area in Clinton County. Soil number 15 was Obtained from the Babcock farm in St. Joseph County. ' Selkirk Series. This series occurs as grayish clay soils under- lain.with plastic limy clays. Fairly widely distributed in the northern part of the lower peninsula, Selkirk soils are usually found on flat clay plains containing numerous wet depressions. Though these soils are difficult to drain and till they are suitable for hay, small grains, and pasture and can be moderately productive. Soil number 39 was obtained from the R. Stilgenbauer farm in Isabella County and from farm records was considered to have a moderate fertil- ity status. Soil number #0 was obtained from.the farm of R. Campbell in Isabella County and was moderately productive. Toledo Segigg. This series occurs as dark colored wet soils on flat clay plains and is distinguished from the Brookston series by the more plastic nature of the underlying clay which is lacustrine in origin and free from imbedded pebbles and'boulders. The relatively small areas of Toledo soil are unimportant agriculturally, although they can be made highly productive when properly drained. Soil number 16 29 was secured from the Campbell Soup Company Experimental Plots in Lenawee County. Wargaw Series. This series occurs as dark sandy loams, loans and silt loans on level dry plains. The total acreage is rather small but is mostly under cultivation. In most cases the soil is rather productive. Soil number 16 taken from an uncultivated road- side site in Kalamazoo County. Waukggha Serigg. Waukesha soils include well drained, dark colored prairie soils and are equivalent to the warsaw. Soil number 10 was obtained from a field on the C. Peters farm in St. Joseph County, which had been in sod since l9h8. Eisner Series. This series occurs as light gray loans and clay loamb over plastic wet clays and silt loams. The total acreage of Wiener soils is small. Generally they are found in low lying wet areas. They are limy at the surface and are relatively fertile when properly drained. Such soils are moderately productive for alfalfa, small grains, beans, and beets. Soil number 4 was obtained from the Wiergorski farm in Tuscola County. Soil number 36 was obtained from the famm of H. Hunsch in Bay County. No fertilizer or manure had been applied on the latter soil for two years. Beans had been grown in 1949. Physical and Chemical Determinations of Soils Used In order to evaluate the difference between the soils under investigation, several physical and chemical determinations were 17 carried out. The particle size distribution by the method of Bouyoucous is presented in Table II. The soils varied in texture from coarse sandy soils to heavy clay loans. The cation exchange capacity, total exchangeable bases, pH, and the organic matter content of the soils are shown in Table III. Cation exchange capacity and pH were determined by the methods of Peech.(28) and total exchangeable bases were measured as outlined by Bray and Wilhite ( 7). Organic matter was determined by a dry com- bustion method essentially as described by Piper (30). In reaction, the soils ranged from strongly acid to alkaline with the hydrogen concentration varying inversely with the degree of‘base saturation. The cation exchange capacities ranged from.h.3 milliequivalents per 100 grams of soil in the case of the acid Plainfield loamy sand to 30.0 milliequivalents in the case of the alkaline Granby sandy loam high in organic matter. The percentage of organic matter varied from a high of 12.67 percent to a low of l.#2 percent. It can be observed that the values for exchange capacity vary directly with the percent of clay and organic matter since high exchange capacities were associated with high percentages of clay and organic matter. Greenhouse Experiment with.Alfalfa The greenhouse experiment as designed by Lawton was set up to measure the phosphorus and.potassium supplying powers of the soils. The treatments on each soil were: TEBLE II THE PARTICLE SIZE DISTRIBUTION OF SOILS USED* Percent composition Size of pagticles in millimetezs Wer 2.00—0.05 Log-0.002 0-00; 1 Miami sandy loam. 55.0 26.0 19.0 2 Miami clay loam 52. 28.0 20.0 3 Miami clay loam 57.0 23.0 27.0 4 Wiener sandy clay loam 64.0 15.6 20.4 5 Granby sandy loam 69.2 16.2 14.6 6 Macomb sandy loam 62.0 23.6 14.4 7 Brookston sandy clay loam 54.0 16.0 34.0 8 Conover loam 44.0 35.0 21.0 9 Conover loam 45.0 30.0 25.0 10 Wankesha sandy loam 64.8 17.2 18.0 11 Hillodale sandy loam 65.0 22.0 13.0 12 Fox loamy sand 82.0 9.0 9.0 13 re: loam 50.0 33.0 17.0 14 Bellefontaine sandy loam 54.0 30.0 16.0 15 Plainfield sandy loam 74.0 12.0 14.0 16 Warsaw loam 52.0 30.0 18.0 17 Bellefontaine sand 87.5 7.0 5.5 18 Fox sandy loam 74.4 13.2 12.4 19 Kalkaeka Band 88.0 6.0 6.0 20 talkaeka sand 92.0 3.5 4t5 21 Kent sandy clay loam. 55.4 18.6 26.0 22 Kent clay loam 44.0 18.0 36.0 23 Isabella sandy clay loam. 50.8 28.2 21.0 24 Isabella sandy clay loam. 58.0 22.0 20.0 25 Enmet sandy loam 78.0 14.0 8.0 26 Miami loam 52.4 28.0 19.6 27iBrookston sandy clay 56.4 8.0 35.6 28 Napanee sandy clay loam 48.4' 26.0 25.6 29 Toledo clay loam 42.0 25.6 32.4 30 Plainfield loamy sand 83.6 10.2 6.2 32 Brooketon loam 44.0 30.0 26.0 33 Kaukawlin sandy clay loam 61.0 18.0 21.0 34 Wiener sandy clay loam 49.0 21.4 29.6 35 Clyde clay loam 35.0 28.6 36.4 36 Viener sandy clay loam 50.0 20.0 30.0 37 Conover sandy clay loam 58.0 22.0 20.0 38 Conover sandy clay loam 48.0 26.4 25.6 39 Selkirk loam 48.0 36.6 16.0 40 Selkirk sandy clay loam 62.0 8.0 30.0 41 Brookgtgn sandy loam ‘ 64.0 21.0 15.0 * Determingdfaccording to Bouyoucos (4) 19 :m3 0:3 8.: and same .933 33.333 on max: 3.3 8.8 8% .33 and. 833 an an.: 0:.03 ow.om o~.m seed adds henna ooscamm mm Hm.: om.HH om.- mm.m undo hence noamuocam um 38. 86 3.3 8% 5.3 33: mm 8.3 8.n o:.3 mad 53 has: posse mm 8.3 3% 86 86 .33 and. seem. .3383 :u 3.m 88 8.6 8;. 5.3 a3... seam. 3383 mm 23 8.3 8.3 8;. .33 a3». menu 3 84.. :m.m 8.3 and 53 mean seam. name de. en.” 86 m:.3 86 earn 3.33 8 :03 8.: 88 8.5 and... 3.33 3 Re. meta 8.3 88 53 88. men 3 :m3 on.m 86 £6 ede- efimedeaefiem 3 HQ: 8;. 8.3 00m 33 amend: 3 8.~ on; 8;. on...“ 33 seem. 33.233.” 3 2.3 8.3 8.3 8.: .33 and... enameaeaeflem :3 man 3.m 8.3 38 53 men 3 :33 8.3 3.: and“ same .233 sea 3 onto. 3.m and 3.: 53 been. 38333 3 8.: man 8.3 86 33 acne. 3.3.8: 3 main :3: 8.8 88 53 H.388 a 8.: 8.3 :33 86 .33 .8550 m 8.: 8.3 8.3 mad 53 and. been deemaeeam a and 8.3 8.3 8.m .33 see... page: a 8.3 8.3 8.8 8;. 5.3 .38.. 383 m Hm.w nm.m ow.ma om.n seed acne mecca some“: a mum 6:6 8.3 82. .53 a3“. Ema: n 3.~ Rd 8.3 38 53 a3”. 33: m man 38 8.3 8.a 53 .39... sag H g man—”om Ema ho "339200 Essa: ondumo Bad .mammm fiaeasa 3.3.3. .EH330 neaofi 83 .3 Ba HHH as 20 .833 53338. .95 m .2. V 0333: 23 8pm .8 853 23 .3 382938 N 4va goomm on M38803 dong—.333 H mm.m max: 8.3 3.0 adoa .383 nopgoonm .3 :m.m 88 8.3. 84. 933 930 .38. Minnow 0: Raw 8.“. No.3 mud 53 3338 an exam :3: 03m omfi ado." hdao. 883 .3233 mm mm.m 8.0 N39” 36 ado." made .338» 925380 mm 8.m 3.0..” 00.3” 3.5 533 830 55a .85.; mm 8.8 3.3 8.8 86 33 930 8.39 mm was: 833 3.2..” 8.5 503 .830 .383 .83.; #m mum 8.3 3.3 8.8 53 83o .398 533:3 mm Ho.m N99 8.3” 3.5 ado." nouoxoonm mm 'ludllllvnoono 23. Him 003 wan madam 0.0qu 13.: a» jam unmade. 1393.80 Hum .50 ohfiomndmrouo HEMP 093383 mmdmn mm 1M!“ E 338 a .8 3338 33:: 2288 as. 68.2 333803 .393 .3323 8303 83 .mm was 336383 H3 339 21 keatment llementg Applied Check Nitrogen 1 Nitrogen and Potassium 2 Nitrogen and Phosphorus 3 Nitrogen, Potassium, and Phosphorus This investigation was concerned only with treatments 1 and 3. It was assumed that a comarison of the results of these two treatments would give the most reliable information concerning phosphorus. Each treatment was replicated three times. According to Lawton, the soils were limed, fertilized, and planted to alfalfa in one-gallon glazed pots on August 25, 19149. In Table IV information is presented relative to the amounts of the individual soils used and a summary of the initial fertilizer treat- ment. Potassium and nitrogen were applied at the approximate rates of 525 pounds potassium and 110 pounds nitrogen per acre respective- ly as potassium chloride and ammonium sulfate. The phosphorus treat- ed soils received phosphorus at the approximate rate of 2&6 pounds of phosphorus per acre as mono-calcium phosphate. Lime requirement was determined by the method of Bradfield and Allison (6). After emergence, the alfalfa seedlings were thinned to twelve per Jar. By periodic weighings the soils were kept approximately at the moisture equivalent. The alfalfa was grown on the soils for approximately eleven months. Seven harvests were taken on the following dates: TfiBLE IV INITIAL FERTILIZER TREATMENT OF GREENHOUSE SOILS =5 Weight 3011 of soil Grams of chemicals per pot Number per pot ' KCl & grams CaCOq (NH4)504 Ca(EZPOy)2-HZO 1 #000 None 1.0 2.0 2 #000 6.# 1.0 2.0 3 #300 None 1.1 2.2 # #000 None 1.0 2.0 5 #000 None 1.0 2.0 6 #300 None 1.1 2.2 7 #000 6.# 1.0 2.0 8 #000 None 1.0 2.0 9 #000 10.6 1.0 2.0 10 #000 18.2 1.0 2.0 11 #000 13.0 1.0 2.0 12 #500 5.2 1.1 2.2 13 #000 8.6 1.0 2.0 1# #200 18.0 1.1 2.2 15 #500 10.6 1.1 2.2 16 #000 15.0 1.0 2.0 17 #500 7.7 1.1 2.2 18 ##00 7.2 1.1 2.2 19 #500 3.0 1.1 2.2 20 #500 7.7 1.1 2.2 21 #000 16.1 1.0 2.0 22 #000 None 1.0 2.0 23 #000 0.3 1.0 2.0 2# #000 10.7 1.0 2.0 25 #500 7.2 1.1 2.2 26 #000 15.0 1.0 2.0 27 #000 No e 1.0 2.0 28 #000 8.6 1.0 2.0 29 #000 10.6 1.0 2.0 30 #500 10.2 1.1 2.2 31 #000 3.0 1.0 2.0 32 1:000 3.0 1.0 2.0 33 0200 0.0 1.1 2.2 3# #000 None 1.0 2.0 35 1:000 10.7 1.0 2.0 36 1:000 None 1.0 2.0 37 #100 15.0 1.1 2.2 38 #100 6.# 1.1 2.2 39 #500 4.3 1.1 2.2 #0 #000 #.3 1.0 2.0 1»; £00 8,6 ;.0 in 22 23 First Harvest -- October 23-26, l9#9 Second Harvest - December 3-6, 19149 Third Harvest - January 17-20, 1950 Fourth Harvest - March 20-27, 1950 Fifth Harvest - May 15, 1950 Sixth Harvest .- June l#-16, and 23-2#, 1950 Seventh Harvest -- July 15-20, 1950 As indicated by the number of harvests growth was rapid especially in the spring of 1950. Additional fertilizer treatments were made at four times during the course of the experiment. On October 30, l9#9, the equivalent per acre of 110 pounds of N as NEhNOB, 10 pounds of eusoup5szo, 10 pounds of 00(N03)2, 10 pounds of NazBuO'polOHzO, 5 pounds of ZnSOu, and 1 pound of (NH4)2 M001, were added to each Jar in solution. On December 10, l9#9, 0.5 grams of (REQZSOL, (approximately 50 pounds per acre of nitrogen) and 1.0 grams of K01 (approximtely 263 pounds per acre of potassium) were added in solution to each pot. At the same time there was applied an additional 1.0 gram of Ca(H2P04)2-H20 per pot (approximately 123 pounds of phosphorus). On February 12, 1950 the nitrogen and minor element application of October 30, l9#9 was repeated. On April 10, 1950 an additional equivalent of 333 pounds per acre of W03 was applied in solution. The total amounts of the nutrients applied during the course of the experiment were: Entries: Essndssnsrnésns Nitrogen #99.55 to 51#.23 2# Nutrient Pounds per Acre Phosphorus 3149.56 to 383.66 Potassium 7#6.66 to 819.50 Copper 2.55 Cobalt 2.03 Zinc l.1# Molybdenum O .#5 Boron 2.15 Phosphorus Determinations §o__i1_s_. The soils for phosphorus analysis were air-dried and screened through a 20-mesh sieve, They were stored in paper cartons until ready for use. Soil phosphorus was extracted by the methods of Spurvay and Lawton (39) and Bray (11,12). The soil test extrac- tion procedures are summarized as follows: ML! Reserve Phosphoru . Five grams of soil were shaken for exactly one minute in 0.135 N H01. Lraqu Adsorbed Phosphorus. One gram of soil was shaken exactly #0 seconds in a solution of 0.03 N NW in 0.025 N H01. 1.3.1213. Available Phogphom. One gram of soil was shaken exactly #0 seconds in a solution of 0.03 N w in 0.1 N H01. £32113 M Aci -Soluibl_e_ and Adsorbed Phosphorus. One gram of soil was shaken in 0.1 N H01 for 30 minutes after which time one gram of solid N HuF was added and the mixture shaken for an additional hour. 25 §;§y1§_Total Acid-Soluble. Adsorbed, and Organic gagg— phgzgg. One gram of soil was digested on a steam.bath for 30 minutes with 15 milliliters of 30 percent H202 and 10 milliliters of water. Then, 10 milliliters of 0.5 N H01 and sufficient water were added to make the total volume 50 milliliters. This soil solution suspension, 0.1 N with respect to H01, was shaken for 30 minutes after which one gram of solid NHuI was added and the suspension shaken for an additional hour. §ggylg_0rganic Phosphorug. (According to Bray (11), organic phosphorus is calculated by subtracting the total acidpsoluble and adsorbed phosphorus from the total acidpsoluble, adsorbed, and organic phosphorus. For the extractions longer than one minute, a reciprocating type shaking machine was used. Phosphorus in the soil extracts was determined colormetrically using Bray‘s procedure (12) and a Coleman Spectrophotometer utilizing a 6500 Angstrom wavelength band. Alfalfa, The seven harvests of alfalfa tops were oven dried at 6000, weighed, and ground in a Wiley semi-micromill to pass through a ZO-mesh screen. Ten percent of the weight of each of the harvests was taken and composited into one sample for phosphorus analysis. These composited samples were stored in sealed thirty millimeter glass bottles for future use. The roots and crowns were removed from the soils by screening through a one—quarter inch galvanized wire screen. They were washed free of soil particles and dried, weighed, ground, and stored in the same manner as the tops. 26 For total phosphorus analysis, one gram samples of plant material were dried over night at 65°C and wet digested using the perchloric, sulphuric, and nitric method as described by Piper (30). Digested samples were made up to 100 milliliter volume and phosphorus determined on an aliquot using the same procedure as used with the soil extracts. Fixation Studies Rate of Applied Phosphorus. Twenty-four soils representing each soil type under investigation were selected to measure the fixation of phosphorus applied at increasing rates. The method employed was as follows: A 20 gram sample of 20-mesh soil and 10 milliliters of distilled water were placed in a one-half pint mason jar. While being mechanically stirred, 10 milliliters of a KZHPOI, solution con- taining a calculated amount of phosphorus was added. After thorough mixing was effected, the sample was placed on a rack and allowed to evaporate to dryness. One week was required to completely air-dry all samples. The rates of phosphorus applied to duplicate samples were 0, 25, 100, and 150 parts per million on a soil basis. The amount of phosphorus fixed was measured by the amount not removed from the air-dry soil by a #0 second extraction with Bray's 0.025 N H01 and 0.03 N NHLJ‘ solution. The soils were treated with phos- phorus on June 30, 1952 and the phosphorus determinations were made July 10—11 , 1952. 2? Hgmpval of Free Iron Oxides. In an effort to evaluate the influence of free iron oxides on phosphorus fixation in the soils being studied, they were removed from all of the soils by the sodium.hydrosulphite method as described by Deb (l6). Phosphorus fixation was measured on the untreated (original soil) and treated (iron oxides removed) soils in the following manner: 50 milliliters of 10 parts per million phosphorus solution made from I2HPOu.was added from.a‘burette to a one gram sample in a one-half pint mason jar. Using normal H01 and NaOH and.a.Beckman glass electrode pH meter, the pH was adjusted to that of the orig- inal untreated soil. 4All of the treated soils had to be adjusted because the acid wash in the iron oxide removal had left them strongly acid. Some of the untreated soils which were strongly buffered did not require adjustment. In no instance was more than two drops of NaOH or H01 needed to reach the desired pH. Investiga— tion indicated that the pH as adjusted did not drift appreciably in a #8 hour period. After treatment the Jars were sealed and.placed on a rack and left at room temperature. Each day the jars were shaken to insure thorough mixing of the soils and the phosphorus solutions. Thoroughly sealed to prevent evaporation loss, the Jars were allowed to stand for a period of fifteen days. On the last day, a five milli- liter aliquot of the supernatant liquid was removed and analyzed for phosphorus. The amount of phosphorus fixed.was calculated from the difference in the phosphorus concentration of the solution at the beginning and at the end of the incubation period. 28 RESULTS AND DISCUSSION Greenhouse Experiment Alfalfa yields. .A summary of the observations of alfalfa growth during the course of the experiment is given in Table V. Legume growth on the phosphorus treated soils was good in all instances. With the exception of the appearance of slight potassium deficiency symptoms after the sixth harvest on several soils, there were no apparent limitations to growth. The symptoms were only slight and perhaps had no appreciable effect on dry weight yields. Growth 0n the nonpphosphated soils varied from good to poor depending on the soil type. In a few cases the differences in growth which resulted from the phosphorus treatments were not easily distinguished, especially in the early stages of the experiment. However, on most soils the response to the phosphate fertilizer was plainly evident from the beginning. «After the sixth harvest, the phosphorus supply had‘become so limited in most of the unphosphated soils that growth was severely checked. .As a consequence, it was decided to end the experiment after the seventh harvest. The yields of tape and roots fer-seven harvests are given in Table VI. The soils are arranged in order of hay yields without phosphorus fertilizer. The yields show that the soils varied greatly in their ability to produce alfalfa without added phosphorus. The yields for seven harvests range from a low of 33.1 grams per pot on the Nalkaska sand to 103.? grams on the Hillsdale 10am.with the TABLEV OBSERVATIONS ON AIEALFA GROWTH 0N FORTY—ONE MICHIGAN SOILSa ‘1 V'Treatment Soil pumber and type No phosphopps Phosphorup_ 1 Mdami sandy loam F to P 0b 2 Miami clay loam F 0* 3 Miami clay loam F 0* # Wiener sandy clay loam F 0 5 Granby sandy loam M. F 0* 6 Macomb sandy loam G to P 0* 7 Brookston sandy clay 10am 0 0* 8 Conover loam M to F 0 9 Conover 10am M 0* 10 Waukesha sandy loam G to P 0* 11 Hillsdale sandy loam F to P G 12 Fox loamy sand P to VP 0 13 Fox loam 0 G 1#’Bellefontaine sandy loam F to VP 0 15 P1ainfield.sandy loam 0 to F 0* 16 Warsaw loam F to P 0 l7 Bellefontaine sand 0 to F 0 18 Fox sandy loam 0 0 l9 Kalkaska sand P to VP 0 20 Kalkaska sand F to P 0* 21 Kent sandy clay loam. G to M 0 22 Kent clay loam F 0 23 Isabella sandy clay loam 0- F 0 2# Isabella sandy clay loam F to VP 0 25 Emmet sandy loam. G G 26 Miami loam P to VP 0 27 Brookston sandy clay ' 0 to M 0 28 Napanee sandyciay loam P G 29 Toledo clay loam P 0 3O Plainfield loamy sand 0 to F 0 31 Hillsdale G 0 32 Brookston loam M to F 0 33 Iawkawlin sandy clay loam F 0 3# Wiener sandy clay loam P 0 35 Clyde clay loam F G 36 Wiener sandy clay loam P 0 37 Conover sandy clay loam F 0 38 Conover sandy clay loam F to P G 39 Selkirk 10am P 0* #0 Selkirk sandy clay loam 0 to M 0 EL 1' 0 fig Broogston sang; 10am ‘1 ;HAverage relative appearance of the seven harvests. P = poor, f 8 fair, M a medium, 0 = good. * Slight potassium deficiency symptoms apparent on seventh harvest. 29 30 o.maa 0.0m n.mmH m.sa m.ae ~.om e.sa o.ss Aeflv onsosnomoaaom om H.00H a.me m.esa m.ma m.ms m.e~ e.em a.me Am 2 sonata mm a.moe m.as a.mea a.aa m.ne o.~m 5.5m a.ae Ammv oaaonooa mm m.em H.e: m.smH «.mo a.mm ”.ma «.mm a.me Anny nouns: am m.mo~ m.mm H.Hsa m.ma H.mm e.wm o.moH H.ms Ammv oeoaoe mu m.~HH e.mn s.HeH 5.0a o.mm 5.0m e.on o.om namv nooonoo mm o.ma m.om m.~ea m.Hm m.de n.om fl.aoa m.om Ammv oonsnoa em m.osH o.ma m.aoa n.ma «.0: m.a~ H.m~H H.Hm Aw v spoon: mm m.~oH a.mm m.ema m.ea. 0.0m ”.mm ~.eoe m.am Amnv nooonoo mm «.ma n.se ... ... ~.ooa m.mm Aaev noonsoonm Hm m.mo w.mm n.m~a m.om 5.0m m.em m.Ha ~.wn Aomv neonsdnu om m.oo a.am m.aNH mpnm m.mn n.5m m.sa a.wm AN V “so“: as a.so m.mn n.0mfi e.oa H.~n ~.am m.am «.mm Ammv noomsoonm we o.mm e.am m.mma H.om m.mm m.nm m.aoa m.se Ammv snow as m.me a.m~ apnea m.sOH o.w: o.mm a.mm m.mn Am v “so“: we m.om “.ma m.m~H s.oHH 3.0: a.oe .e.mm a.mo “adv oneness: we n.ms a.om o.dsd H.moa e.mm «.mm w.~o~ m.oa Am V no>onoo ea m.e~ «.ma a.a¢a a.~HH m.m¢ m.mm e.ma ~.ea Aomv neoconsoam ma ~.H~ e.eH m.~ma a.~HH a.wm m.mm w.mm ~.aa Aamv anon ma n.m~ H.- e.amH a.mofl a.mm H.mm a.mm o.aa Am v noonsoonm Ha o.mH a.HH H.mma e.aHH m.me m.He n.mm m.aa AHHV odoenaasm 0H m.e~ m.o~ ~.Hea o.mHH a.me H.Hs e.mm m.aa Away eaoamnsoam m m.mH s.HH m.HmH a.aHH o.mn m.mn «.mm m.am Aaav onsonnoMoHHom m Him H.0N as... .3... M60.” :.mm A03 Mnflfiom n a.ma m.HH e.HeH o.e~H n.mm m.mm H.moa m.Hm Anny oeaao o m.o~ m.mH m.amfi upema nee: m.os «.maa e.mm Amuv posse m H.ea s.mH e.asa n.mNH «.mm 0.3m «.mofl m.sm Aamv nosnsooum e m.HH m.HH o.msH m.eme m.oe m.o: N.aoa a.mm Andy «on m o.m H.m e.an m.msa m.am «.0: e.moe m.NoH Away son a ~.m e.m e.emH m.osa H.Hn «.mn m.mHH a.noH .AHmV odnemaflam H phoneme Macaw M.“ m 02 a. m 02 m m on ituiofiuom Adam m 0583? m 02 m madam dwrpoom sanctum sebum . .33...» on mass me go; “Ewan: bun Hence Illnlstslmasuafilusalsflmn. .33 fig menopause s.“ oncoaosmw Mean mammbmdm Em ll mah 4334 ac mDmommmomm Bang ho aofiE an. H> Hag 31 :33 soon es... 000300390." 00.23 no owsuobd s... .823: .300 33390 n. rum 0. finals n.aa~ 0.0a 0.N:H «.00 :.am H.m~ H.00H H.mn “mac nannnaou a: 0.Haa a.m0 5.0:H a.am 0.0: ~.Hm «.00H n.0n Aamv snssaom 0: 0.:0H 0.00 0.0:H 0.00 0.0: H.:m 0.:0H 0.0m A:~V oflaonona 0m 0.a0a 0.m0 0.0:H 0.a0 0.0: 5.00 m.00H m.0m A0 2 noeonoo mm :.a:H 5.00 0.0mH 0.m0 0.d: H.- 0.mm m.am A002 «son: an 0.N0H m.00 0.0mH «.00 n.0m 0.m~ 0.50 0.00 ad 0 «and: 0m H.00H 5.00 0.::a 0.m0 0.5m n.0a :.00H p.00 x0m0 noon": mm 0.:HH 0.0: «.mma m.ma ~.d: 0.Nm 0.50 0.0: ANHV nos :m ~.~0H 0.50 :.amfl :.a0 H.0: ”.00 n.00H n.d: A: V nouns: mm 0.m~a n.H0 ”.mmfl n.00 a.m: 0.m~ 0.mm a.d: AOHv sense: an 0.0na 0.00 a.:ma H.Ha :.:m 0.5m n.00a 0.0: Anny addressee an annoyed macaw m m 02 m m 02 m m 02 m 02 M1 3.0% mWoom HmeoEsm s0>om 30.3 0» secs co sans» ensue: awn doooa a: ..osnm0_mwiammwoa awn wnaesooon dd magnum” g Ml mamg Em I... mQAHHH 433 .20 mDmommmomm nan—”Ea .mo Boas Ema Aeonnaonoov H» mamas 32 average yield on the forty—one soils at 60.9 grams. This wide difference in total dry weight was reduced where phosphorus was added. The yields on the phosphorus treated soils ranged from 88.# grams per not on the Waukesha sandy 10am to a high of 123.1 grams on the Raconb sandy loan with the average yield at 100.5 grams. Yield increases due to added phosphorus varied from.3.l grams in the case of the Fox sandy 10am to 72.0 grams in the case of the Macomb sandy loam with an average increase of 39.6 grams per pot.. From a percentage standpoint, the increases were more imp pressive. The greatest percent increase was 216.8 percent on the Kalkaska sand and the lowest was 3.0 percent on the Fox sandy loam. The average percent increase in yield caused by the phosphorus fertilizer was 65.0 percent. These yield data indicate that an almost perfect inverse relationship existed between the response to added phosphorus and the yields without phosphorus. For example, soils 31, 18, 13, and 27, which ranked one, two, three, and four respectively in total yield (without phOSphorus), ranked forty, forty-one, thirtyanine, and thirty-six in percentage increase caused by the addition of phosphorus. Conversely, soils 19, 39, 2#, and 9 which ranked forty-one, forty, thirty-nine and thirty-eight in the total yields, ranked one, two, four and three respectively in percent increase in yield caused by added phosphorus. A similar yield relationship holds for the remainder of the soils. An examination of the data on dry weights of the roots shows that on the unphosphated soils the root yields were approximately 33 one-half the total top yields for the seven cuttings or about one- third of the total weight of plant material produced. The average dry weight of the roots was 30.# grams. Considering all the soils added phosphate increased the root yields by approximately one- third to #0.0 grams per pot. However, the ratios of root weight to top weight and of root weight to total weight were decreased by the phosphate applications. A comparison of the total dry weights of tops and roots shows that the phosphorus treated soils yielded an average of 5#.6 per- cent more dry plant material than did the unphosphated soils. The yield data in Table VI show that the heavier.soils did not produce larger yields of alfalfa than did the sandy or sandy loam soils. The data show that relatively high and low yields were obtained from'both the coarse and fine textured groups. It is interesting to note that though one-fourth of the soils were originally above pH 7, the fifteen highest yielding soils without added phosphorus were, with one exception, acid soils. It should be remembered however, that most of these soils had been limed. In every instance, added phosphorus produced an increase in yield indicating that none of the soils contained sufficient phosphorus for maximum production of alfalfa under greenhouse conditions. In several instances the yield increases were small. 0n the basis of response to added phosphorus under greenhouse conditions and when properly limed, the soils were arranged in order of their relative need for phosphate. 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Eden 3 whenu hence Medan: .m Eden bane hence sedan: .n seen keno buses ennepeen . .3- aeen bone .35. xuflnom . m N Eden aebeneo . dude fining . n gt A inflofluaIIIl emonBHEnoo EDGE“. fig 433 he gnaobncmnn E Nah maggdfim mDmomnnmomm Enadflmm fig 09 gnag an 958 anmog EOIMBMOR ho Emboflo Hnb HHS 35 presented in decreasing order of response to added phosphorus. It should be remembered that the soils differed in their past cropping and fertilization histories and as a result tended to reflect their level of fertility. However, if response to added phosphorus can be considered a valid measure of the relative need for phosphorus fert- ilization the arrangement has merit. For an example, it shows that under the conditions of this experiment the Hillsdale, Brookston, Plainfield, and Kent soil types have relatively low requirements for phosphorus as compared with the Wiener and Isabella types. In contrast, alfalfa grown on the Conover, Kalkaslm, Miami and Belle- fontaine soils showed considerable variation in its response to phosphate fertilizer. Phosphorus Content of Alfalfa. The data recorded in Table VIII show the effect of soil type and phosphorus fertilization on the total phosphorus content of alfalfa tops and roots. The percentage of phosphorus in the tops from the unphosphated soils ranged from 0.277 percent, in the case of soil number 31, ‘which ranked first in total weight of tops produced, to 0.111} percent in the case of soil number 36. The average phosphorus content of alfalfa tape on the unphosphated soils was 0.167 percent. An examination of these data show no exact relationship between total yield of tape and the per- centage composition of phosphorus, but generally higher than average percentage phosphorus compositions. were associated with high yields. Added phosphate almost doubled the percentage composition of alfalfa in the tops. The average for the phosphorus treated plants was 0.323 TABLE VIII PERCEKTAGE OF TOTAL PHDSPEORUS IN SEVEN HARVESTS 0F ALFALFA.AHD ROOTS Seven Harvests* Roots* Soil series No P P No P* P and number Apercent .percent percent percent 1 Miami .165 .392 .090 .208 2 Miami .142 .408 .079 .267 3 Miami .180 .330 .110 .256 4 Wiener .165 .341 .078 .280 5 Granby .155 .311 .078 .235 6 Macomb .115 .359 .074 .246 7 Brookston .185 .338 .090 .305 8 Conover .162 .319 .125 .272 9 Conover .152 .290 .061 .202 10 Waukesha .190 .317 .129 .229 11 Hillsdale .201 .345 .120 .244 12 Fox .171 .432 .089 .248 13 Fox .216 .446 .116 .283 14 Bellefontaine .171 .339 .091 .224 15 Plainfield .228 .370 .069 .198 16 Warsaw .169 .338 .089 .172 17 Bellefontaine .194 .405 .160 .338 18 Fox .222 .352 .172 .285 19 Kalkaska. .153 .352 .088 .243 20 Xalkaska .18u ..394r .126 .287 21 Kent .224 .370 .129 .294 22 Kent .162 .307 .069 .231 23 Isabella .165 .344 .072 .251 24 Isabella .127 .268 .070 .191 25 Emmet .241 .358 .213 .345 26 Miami .129 .262 .081 .230 27 IBrookston .152 .308 .071 .275 28 Napanee .128 1 .248 .070 .213 29 Toledo .146 .242 .074 .227 30 Plainfield .199 .289 .145 .296 31 Hillsdale .277 .375 .195 .332 32 Brookston .153 .278 .071 .227 33 Kawkawlin .156 .271 .069 .251 34 Wiener .140 .217 .075 .227 35 Clyde .159 .268 .100 .264 36 Wiener .114 .255 .067 .249 37 Conover .127 .253 .096 .260 38 Conover .145 .263 .097 .231 39 Selkirk .120 .315 .071 .300 40 Selkirk .159 .262 .079 .183 91 Bzgokston .123_ .3151 .090 .250 Aggggge .167 .3g3 .098 ,252 * Average of three replications. 37 percent. As for the roots, the percentage of phosphorus in the unphosphated and phosphated alfalfa was 0.098 percent and 0.252 percent respectively, a greater percentage increase than occured in the tops. The data presented in Table IX show the effect of soil type and phosphorus fertilizer on the total amount of phosphorus removed by the alfalfa from each pot. 0n the unphosphated soils, the amounts of phosphorus in the tops varied widely, from a low of 43.8 milligrams to a high of 227.6 milligrams per pot. The average for all soils was 104.7 milligrams. The corresponding average for the roots was 33.0. More than three times these amounts of phosphorus were found in the tops and roots of alfalfa grown on the phosphated soils. The average in the tops was 324.2 milligrams and in the roots 101.? milligrams. In terms of total amounts of phosphorus removed by the tape and roots, the plants on the phosphorus treated soils removed an average of 427.6 milligrams per pot whereas those on unphosphated soils removed an average of 138.0 milligrams. The percentage increase in total phosphorus removed was 209.8. An account of the recovery of applied phosphorus in 18.111ng and percent is given in Table I. The recovery of applied phosphorus was obtained by subtracting the uptake values on the unphosphated soils from the respective values on'the soils which received phos- phorus. This method ofcalculating the recovery of applied phosphor- us hae been used by other investigators. Prince, et a1 (31) used it in their phosphorus studies and more recently Rich and Attoe (23) 38 TABLE IX THE TOTAL CONTENT OF PHOSPHORUS IN SEVEN EARVESTS OF ALEALEA.AND ROOTS No Phosphorus* Phosphorus Added* Seven Seven Soil series Harvests Roots Total Harvests Roots Total and number mgms, ggmg, mgms1 __mgms, mgms, ggms, 1 Miami 63.7 21.2 84.9 382.2 79.7 461.9 2 Miami 80.8 21.7 102.5 386.0 88.9 474.9 3 Miami 123.8 39.6 163.4 325.7 117.8 443.5 4 Wiener 63.2 20.4 83.6 369.3 134.7 504.0 5 Granby 71.2 20.8 92.0 294.2 117.3 411.5 6 Macomb 58.8 20.2 79.0 441.9 113.7 555.6 7 Brooknton. 143.6 25.3 168.9 337.0 121.1 458.1 8 Conover 114.9 47.8 162.7 324.1 107.2 431.3 9 Conover 56.1 12.6 68.7 307.1 82.0 389.1 10 Wankesha 132.4 52.5 184.9 280.2 92.5 372.7 11 Hillsdale 156.4 49.9 206.3 308.8 106.4 415.2 12 Fez. 69.3 29.2 98.5 375.8 102.2 478.0 13 10: 207.1 47.4 254.5 478.1 115.5 593.6 14- Bellefontaine 75.2 27.5 102.7 320.7 93.6 41433 15 Plainfield 177.6 69.5 247.1 364.1 84.6 448.7 16 Warsaw 70.5 21.0 91.5 314.3 77.6 391.9 17 Bellefontaine 158.7 57.4 216.1 377.5 130.5 508.0 18 Fox 227.6 69.3 296.9 371.7 84.9 456.6 19 Kalkaska 50.6 20.3 70.9 370.0 90.9 460.9 20 Kalkaska 103.4 43.6 147.0 361.7 88.1 449.8 21 Kent 172.9 45.8 218.7 346.3 113.8 460.1 22 Kent . 104.5 17.7 122.2 312.8 78.3 391.1 23 Isabella 79.0 23.0 102.0 336.6 113.5 450.1 24 Isabella 46.7 16.9 63.6 280.9 80.2 361.1 25 Emmet 225.1 86.9 312.0 404.2 152.8 557.0 26 Miami 48.8 17.9 66.7 245.0 95.5 340.5 27 Brookston 144.1 24.6 168.7 333.3 107.8 441.1 28 Napanee 65.0 21.4 86.4r 248.3 89.0 337.3 29 Toledo 71.7 19.5 91.2 249.3 86.5 335.8 30 Plainfield 147.7 55.8 203.5 267.0 145.9 412.9 31 Hillsdale 183.6 84.2 267.8 424.9 136.5 561.4 32 IBrookston 90.6 22.2 112.8 271.1 95.6 366.7 33 Xarkavlin 67.9 19.0 86.9 271.8 86.3 358.1 34 Wiener 67.3 13.6 80.9 200.1 72.9 273.0 35 Clyde 145.5 32.5 178.0 276.3 101.1 377.4 36 Wiener 45.3 12.9 58.2 271.3 93.6 364.9 TABLE IX.(continued) 39 THE TOTAL CONTENT OF'PHDSPHORUS IN SEVEN HARVESTS OF ALEALEA AND ROOTS N0 Phosphozgs* Phosphogug Added* Seven Seven Soil series Harvests Boots Total Harvests Roots Total amalgamber sEaas____AEae.__maaaa_.1msms____sremui_ssmsl__ 37 Conover 63.5 19.9 83.4 269.2 91.0 360.2 38 Conover 74.7 22.4 97.1 274.1 70.7 344.8 39 Selkirk' 43.8 15.1 58.9 334.5 127.5 462.0 40 Selkirk 132.6 271.2 41 Brookston 68.7 315.6 Average 104.7 33.0 138.0 0324.2 191.2 422.6 A e e Increase erce t) :_r 202,8 4: Average of three replications. TABLEX RECOVERY" OF APPLIED PHOSPHORUS Phosphorusterontanti".I Recovery Seven Harvests of.Applied Soil series of Tops Roots Total P and number .EEE§- mama. mgms. percent 1 Miami 313-5 58.5 377.0 51.2 2 Miami 305.2 67.2 372.4 50.5 3 Miami 201.9 78.2 280.1 35.6 4 Wiener 306.1 114.3 420.4 57.1 5 Granby 223.0 96.5 319.5 43.4 6 Macomb 383.1 93.5 476.6 60.6 7 Brookston 193.4 95.8 289.2 39.3 8 Conover 209.2 59.4 268.6 36.5 9 Conover 251.0 69.4 320.4 43.5 10 Wankesha 147.4 40.0 187.4 25.4 11 HillsdAle 152.4 56.5 208.9 28.4 12 ’0: 306.5 73 .0 37905 14803 13 Fox 271.0 68.1 339.1 46.0 14 Bellefontaine 245.5 66.1 311.6 39.6 15 Plainfield 186.5 15.1 201.6 25.6 16 Warsaw 243 .8 56.6 300.4 40.8 17 Bellefontaine 218.8 73.1 291.9 37.1 18 Fox 144.1 15.6 159.7 20.3 19 Xalkaska 319.4 70.6 390.0 49.6 20 Ialkaska 258.3 44.5 302.8 38.5 21 Kent 173.4 68.0 241.4. 32.8 22 Kent 208.3 60.6 268.9 36.5 23 Isabella 257.6 90.5 348.1 47.2 24 Isabella 234.2 63.3 297.5 40.4 25 Emmet 179.1 65.9 245.0 31.2 26 10.81111 196.2 77.6 273.8 37.2 27 Brookston 189.2 83.2 272.4 37.0 28 Napanee 183.3 67.6 250.9 34.1 29 Toledo 177.6 67.0 244.6 33.2 30 Plainfield 119.3 90.1 209.4 26.6 31 Hilledale 241.3 52.3 293 .6 39.8 32 Brookston 180.5 73.4 253.9 34.5 33 Kawkawlin 203.9 67-3 271.2 34-5 34 Wiener 132.8 59.3 192.1 26.1 35 Clyde 130.8 68.6 199.4 27.1 36 Wiener 226.0 80.7 306.7 41.6 37 Conover 205.7 71.1 276.8 35.2 38 Selkirk 199.4 48.3 247.7 33.6 32 Selkirk; 290.7 112.4 403.1 51.3 Avegggg 220.9 6817 289.6 3854 * Obtained by subtracting phosphorus content of alfalfa grown on soil to which no phosphorus was applied from that of alfalfa grown on phosphorus treated soils. ** Average of three replications. 41 used it in their investigation of the phosphorus supplying powers of Wisconsin soils. Certainly this method is questionable since it cannot be proved that the difference in uptake came from the applied phosphorus. However, since the soil and plant roots were confined to the relatively small area of the pots and the roots had no access to any unfertilized soil, it is quite likely that the difference does represent the portion obtained from the applied phosphorus. 0f the total quantity of phosphorus applied, the portion recovered ranged from 20.3 percent on Fox sandy loam to 60 percent on the Wiener sandy loam. The average recovery was 38.4 percent. Low and high recoveries do not necessarily indicate high and.low fixation by the soils. Perhaps the recoveries were influenced by original levels of available native phosphorus more than any other factor. Considering the magnitude of phosphorus fixation in most soils, the amounts recovered indicate a greater utilization of applied phosphorus than is normally expected in field soils. The results are similar to those obtained by Rich and.Attoe (31). They recovered 36 to 62 percent of the applied phosphorus in six successive crops of oats on Wisconsin soils. Prince, et a1 (31), recovered from 4.2 to 41.9 percent of the phosphorus applied in either harvests and the roots of alfalfa grown on twenty New Jersey soils. Soil Phosphorus The work of Smith (38) showed that the method of analysis my affect the results obtained from correlations between soil phosphorus 42 determinations and crop yields on Michigan soils. Specifically, the type of extractant and the soil extracting solution ratios were shown to be important. Consideration of these factors prompted.a prelim— inary comparison between the alfalfa yields obtained in this experi- ment and the results obtained from several phosphorus extracting and testing methods. The results are summarized in Table XI. The best correlation was obtained with 0.03 N NHnF in 0.025 N H01. With this extractant, the soil-extracting solution ratio did not apprec- iably affect the correlation. This conclusion agrees with reports by Bray (12) that both ratios extract a proportional amount of the adsorbed phosphorus. The Spurway test for phosphorus is usually made at a 1 to 4 soil-extracting solution ratio, but for comparison purposes the ratios of 1 to 10 and l to 50 were used; consequently, the results obtained may have been somewhat different from those which would be obtained at the ratio for which the test hae'been calibrated. 0n the basis of the preliminary measurements of soil phosphorus, three rapid test methods were chosen for the rapid soil phosphorus determinations. They were: (1) Spurway reserve test (0.135 N H01) at a 1.4 ratio, (2) Bray adsorbed test (0.03 N 11'1qu in 0.025 N HCl) at a 1 to 10 ratio, and (3) Bray available phosphorus (0.03 N new in 0.1 N 301). In addition to these rapid test methods, more quanti- tative laboratory methods by Bray for phosphorus, as previously described, were used. The results are summarized in Table XII. Rapid Tests for Phosphorus. The smallest amount of phosphorus 43 .amospooep memomAmoma on scam mdaoflw so .maflom Hmeflwwno no modaana sea mason ma monogamoma Huom s [\ll om,l H a mOqu eeoom dam mpmo>hmm mo>om omfiqo .moeoeaem eoeom on :74: Homlmnwmmqqnu monogamomm osaowom n.563h:Am awe.o (meoem om :74 e .1. was mumobumm mobom mm:.o (mumo>mem do>om on I a a moose eeeom 0H n.m\ . use memosamm mo>om emeqo eemowmsm sooom 0H : H How a H 0 ea ma monogamomm sameaasbd m.meam Nomqo eeeem ems: a a one mpmopaem nobom . .mwmdo maaopmmm mm>om 0m 1.4 a mom.o (madam o” L141. 3 one mpmophsm sebum amuse mmmoeeem eoeom 04,: a How zjwwoqd ea meme 2 acqo umaomamomm dopaoadd a.hmam any soaemaossoo .HO udomMflmmooo eeAMv daofiw dmammad eeaeeaem.mmmmmmummm o» eANv amoa adom Hwom Mo afifimm mAHom ZdGHmouz MBmOh no mnefiHH mfiqdfifld and mDMommmomm HHom mom mamfia HHom nmmdm Hdflflbfim ho Bomemmzoo HMdZHEHAHmm HM fiAde mm: HS in mm mm 2 see. asses 33833 on mm: mm :3 an .3 E. .33” beds evades mN 0mm mam mom i: m m seed some sees. 8882 mm :8 emm 03 cm mm 8 seas beams 5.58on am 4 mm: 9N mam S n n seed Eon. mm 2 mmm new con mm 8 8 are” sees. omega mm Rm mmm com S n m eeoa seas sees. £333 3.. om... 8m «mm 3 m we seed seas sees. 2283 mm m3 mmm mmm am a 3 53 .88 snow «m mam Sn :8 am mm 9 seem meme ease do. 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The average amount of phosphorus removed by Spur- way's extractant was 24.4 parts per million on a soil basis, which was higher than the average removed by the Bray adsorbed phosphorus extractant. The latter value of 18.5 parts per million was lower than the average amount removed by the Bray available phosphorus extractant which was “0.8 parts per million. The variation in amounts removed by the Bray adsorbed phosphorus and available phos- phorus tests ranged from 5 parts per million to 68 parts per million and 10 parts per million to 93 parts per million respectively. The effect of cropping on the phosphorus content of soils is presented in Table XIII. Bray's adsorbed phosphorus extracting agent was used to determine changes in phosphorus level. It must be kept in mind that some of the crapped soils were limed, consequently, exact comparisons are probably not in order; however, some idea of the effect of cropping on the levels of available phosphorus can be gained. It is generally recognized that the supply of available phosphorus for plant use throughout a given growing period may exist in the soil in different forms of variable availability. In order to correlate soil phosphorus with plant growth a good test should measure either the total amount available or a prOportionate amount of that total. .According to Spurway (39) his reserve test measured the amounts of the TABLE XIII PEOSPHORUS CONTENT OF SOILS BEFORE AND AFTER CROPPING" 47 Original No Phosphorus Soil Phosphorus Added Soil type and number ppm ppm ppm 1 Miami sandy loam 5 4 18 2 Miami clay loam 7 5 22 3 Miami clay loam 16 6 24 4 Wiener sandy clay loam 10 5 20 5 Granby sandy loan 24 18 33 6 Macomb sandy loam 23 4 36 7 Brookston sandy clay loam 16 7 25 8 Conover loam 14 7 23 9 Conover loam 6 5 17 10 Waukesha sandy loam 46 22 62 ll Hillsdale sandy loam 30 15 56 12 Fox loamy sand 12 7 37 13 Fox loam 28 14 42 14 Bellefontaine sandy loam l4 9 42 15 Plainfield sandy 108m 1&5 22 69 16 Warsaw loam 14 8 37 17 Bellefontaine sand 44 25 74 18 Fox sandy loam 39 14 55 19 Kalkaslca sand. 7 5 24 20 Kalkaska sand 18 11 55 21 Kent sandy clay loam 23 11 42 22 Kent clay loam 9 7 22 23 Isabella sandy clay loam 5 22 24 Isabella sandy clay loam 5 4 25 25 Emmet sandy loam 68 33 74 26 Miami loam 6 5 23 27 Brookston sandy clay 35 8 24 28 Napanee sandy clay loam 5 5 16 29 Toledo clay loam 11 6 23 30 Plainfield loamy sand 33 18 51 32 Brookston loam 14 8 28 33 Kawlmwlin sandy clay loam 9 5 37 34 Wisner sandy clay loam 15 10 59 35 Clyde clay loam 23 12 32 36 Wiener sandy clay loam 10 7 21 37 Conover sandy clay loam 9 5 20 38 Conover sandy clay loam 6 5 22 39 Selkirk loan 5 4 49 4O Selkirk sandy clay loam 17 9 24 B o ks c a ll 2 Soil Phosphorus Aft er Cropping? 'i As measured by Bray's Adsorbed Phosphorus Solution. “I Some soils were limed, less soluble soil nutrients. If this concept is applied to the element phosphorus, a strong acid extractant such as 0.135 N E01 may dissolve rock phosphate and other acidpsoluble forms which may or may not be available. Such an extractant would be expected to give positive tests on soils containing large amounts of acid-soluble phosphorus, but in most instances would probably give unsatisfactory tests when adsorbed forms of phosphorus were present in appreciable quantities. Bray (10) has presented evidence that acid extractants do not effectively remove adsorbed phosphates. Bray and Dickman (8) have shown that adsorbed forms, when present in relatively large amounts, are much more available than acid-soluble forms. Hence, poor correlations of crop yields with phosphorus removed by strong acids may result. When soil phosphorus is comprised largely of acid- soluble forms the Spurway extractant would more than likely give a clear picture of the total amount of inorganic phosphorus present, which may or may not be available for plant use. Examination of the amounts of phosphorus removed from the different soils by this extractant indicates a wide range in levels of acid~soluble phosphorus. Despite the fact that Bray's adsorbed phosphorus extractant was much.weaker with respect to acidity and that the extraction time was one-third shorter, it removed more phosphorus from quite a few soils than did the stronger Spurway reagent. Bray's available phosphorus extractant which was slightly weaker with respect to acidity and.which ah» employed a shorter extraction period removed more phosphorus in all 249 but two soils than did the Spurway reagent. These results indicate clearly that the fluoride ion was effective in removing phosphorus which was not removed by the acid. An attempt to explain the role of the fluoride ion in the release of adsorbed phosphorus has been made by several investigators. Swenson, Cole, and Sieling (he) expressed the view that the fluoride ion formed stable complexes with iron and aluminum compounds thereby liberating phosphorus. Turner and Rice (1+4) substantiated this opinion by presenting evidence that neutral NHQF reacted with.A1(OH)3 gels to form (NHu)34A1F6 and that phosphorus adsorbed by the gels was more or less completely released by the action of the fluoride. On the other hand, their results showed that Fe(OH)3 gels are not attacked by the fluoride and the adsorbed phosphate was not released to any appreciable extent. Close examination of the soils in this eXperiment and the amounts of phosphorus removed by Bray's adsorbed extractant shows a somewhat general relationship between the amount of adsorbed phos- phorus and the percent of sand. The soils having large proportionate amounts of sand, in most instances, gave high tests for adsorbed phosphorus. tAdditionally it should be mentioned that the soils above pH 7.0 generally gave low to medium.va1ues for adsorbed phosphorus. BraylgvLaboratony»Method§; The more quantitative methods of Bray for the extraction of soil phosphorus which make use of a greater amount of fluoride and a longer extraction period removed considerably 50 larger quantities of phosphorus than the rapid test methods. The amounts of total acid-soluble and adsorbed phosphorus ranged from 142 parts per million to 420 parts per million with the average at 290.8. The total organic, acidpsoluble, and adsorbed phosphorus in the soils varied from 313 parts per million to 990 parts per million with the average amount at 663.8 parts per million. The organic phosphorus ranged from.73 parts per million to 652 parts per million with an average of 372.6 parts per million. In most instances, he amounts of the total acidpsoluble and adsorbed fractions were proportionate to the amounts removed by the rapid test methods. The test values obtained are somewhat higher than those obtained by Bowers (5) in a similar study. The differences can probably be attributed to the type of shaking machines used. Bowers used a slowly revolving endpover-end machine that did very little shaking, whereas in this study a reciprocating type shaker which effected a vigorous shaking was used. Consideration of the extracting solution with respect to concentration of acid and fluoride and the length of extraction leaves little doubt that the total amounts of acid-soluble and sdsorbed phosphorus were not removed. Certainly this extraction removes a greater quantity of the more resistant and insoluble phosphorus than the rapid soil tests. By the use of hydrogen peroxide and a steam bath, the organic phosphates were brought into solution and measured along with the inorganic forms. The difference without the peroxide and heat treat- ments represents the organic phosphorus. The full reliability of this 51 procedure is open to question, especially since the hydrogen peroxide and the increased temperature may bring additional inorganic phosphates into solution. However, the method does give a measure of the phosphorus in organic combination. Bray's method is less tedious than some of the other methods for the measurement of the organic phosphorus and may be Just as reliable. The values obtained compare favorably with measures of organic phosphorus ob- tained.by other investigators on similar soil types. The levels of organic phosphorus in the soils of this investigation varied con- siderably ranging from 73 parts per million to 570 parts per million on a soil basis. In general, the values for organic phosphorus were directly related to the organic matter content of the soils. In several cases, the results indicated that perhaps phosphorus other than Just the organic was included in the values obtained. The preliminary correlations of soil phosphorus tests with alfalfa yields indicated that perhaps Bray's adsorbed phosphorus test was the best measure of the phosphorus supplying powers of a soil. For this reason, Bray's adsorbed phosphorus tests results were used to arrange the soils in order of their supplying power for phosphorus. In Table XIV the soils were arranged in descending order of their phosphorus soil tests and were arbitrarily grouped into high, medium, and low categories. Comparison of this arrange- ment with that of Table VII in which the soils are listed according to their need for phosphorus as indicated by growth response to added phosphorus, shows a rather striking agreement. Soils in the 52 AH V AsNV AmNV AmmV AmmV AeNV A0 V AN V AmHV AmmV ANNV amoa meson “Hafiz adoa hmao Adamo waaopmmH awed node hdsmm omndmcz awed adds henna mafixaom adoa mode apnea nm>oqoo awoa aadfiz good umbonoo awed hmao «Hafiz deem nxmmmadm seed hmao human maaogmmH Hood hdao poem awed AmmV ache sense qhflzessma AamV adoa Adan henna nobonoo .msnommmomm qofiaaaa mom mason obopc was ON I swam m .mspommmomm soaaawa non apnea ma 0» Ha I.adfico: N .mdnommmoma nodaaaa pom apnea ea c» o I roe a .mnonEdn Haom Homfiwfiuo on» on Homes nanompnoudm ma whopadz s Awmwmdoa Moan wwnem seam“: .mm .0: A: Vadoa hmao hence some“: .mm AmNV .mm AHeV .am ANHV .mm AsHV .mm Am V .em AmHV .mm AmmV adOH moan ovoHoe mafia apnea nonmxoonm doom mecca Mom adoa henna oedmpsomoaaom awed uo>onoo awed amuse: adoa nepmxoonm .Nm Ammvadoa hmao hdddn nomad: .Hm Am V .om Au V .om AoeV .mm AONV awed mean fies“: sdoa mode henna doumxoonm adoa zwao Adamo anxaom seam mammadmm QWN .m~ AmmV AHNV Aw V Am V AmHV .em .mm .mm .HN AHaV AomV AamV .om .ma .mH AmHV .ma AmHV .ma AmHV .ma AOHV .da thV seed aoHo oeaao amoa adds poem .adoa mason paoomz awed human hpsmno adoa Mom awed mecca oaedmaawm deem mecca dfloameaeam adds meson nopmxoonm Hood henna Mom demo osampnomoaaom amoa meson daoamoficam sdoa meson deceasez adoa hence poeam Haoq ll} Masada: nnmdm Emma mDmommwomm QHmMOmQHN_fiAmda 53 "High” category of Table XIV fall in the “Least" and "Moderate“ categories of Table VII. On the other hand, soils which have ”Greatest" and “Marked” requirements for phosphorus on the basis of response to phosphorus are found in the "Low" supplying group as indicated by the soil test. This agreement between these two entirely different methods of measuring a soil's ability to supply phosphorus was close enough to substantiate the soil test as a valid method. Fixation Studies Rate of Appdied Phosphoru . The amounts of phosphorus fixed by several soils when applied at the rates of 25 parts per million, 50 parts per million and 100 parts per million per 20 grams of soil are presented in Table XV. The results indicate a wide difference in the capacity of the soils to fix phosphate against extraction with 0.03 N NHuF in 0.025 N HCl. The average amount of phosphorus fixed at the four rates of application ranged from 17 to 79 percent. In addition, the data show that the amount of fixation by an individual soil varies with the amount of phosphorus applied. In Figures 2 through 7, graphical presentation is given to indicate the character of the fixation by the individual soils. The soils included in this fixation study vary widely in chemical and physical preperties. It has'been generally accepted that most of the retaining power of a soil for phosphorus lies in the finer mechanical fractions, especially the clay. Hibbard (17) determined 51+ .woamsdu oncogene mo upguem _.. II I ‘ III IIII IHII ad «m c.a¢ ma m.~H ea o.c m ~.~ as «m cm e.e~ ad m.cH cm m.~H em c.c 0: mm ma ~.ac om e.ou ea m.HH mm m.c mm mm mm «.ma on 0.0m mm c.c~ mm o.n~ mm am on e.e: mm c.- em ~.aH mm c.m on an mm e.ma ms m.~e mm o.cm ow o.o~ mm on an s.mm mm m.mn me e.e~ an ~.m mm an em ~.em em e.eu em m.ma mm o.m cm me am 0.0m a: m.ms cc m.mm ooa o.mm mm mm mm 0.3m mm o.- mm e.cfl em c.ma em cm on 0.3m ma «.ma ma c.a ea m.n am an an 0.5: an o’em mm ewe” me ~.NH ad am am 0.0: mm o.mm mm c.HH em o.c ca mm ma o.om ea c.mH mm m.~a ms s.HH ea am an c.am an o.am cc o.om 00H o.m~ me me on o.oc mm e.mm om ~.o: ooH o.m~ NH an we o.mc mm «.mw Ha c.n ma c.e oa as an ~.mm no m.~c am s.m: ooa o.m~ m mm mm m.~e o: c.mm em o.mm mm o.mm c am He e.~m ea 2.0a me «.me ooa o.m~ m mm on o.sm an m.em an o.mH NH o.m e mm cu e.em mm m.~m cm o.ma mm m.m a coma dong 1 €an 401me flee IcSnIHhuI Iaumq I . _. _ .doflwh. . . . . 8mm . . . ”0.935.. d accused semen eeune semen eases Hecm amassed asoonem agonmmomm unooaem maommmomm psoouom agommaonm adoaom uafimuonm I313.” age 8” men ow mead“ . ...I-..i eawmmIumImmmmmIaMImq1uuaamq¢1umummqqqamuuquummm¢. yin" mama gnaw 94 mgHom 830% Mm Boga—“ah mbmomnHmomm gag 55 5:3 loo." bug 306 aspen he. ESE-SE no no.3“: .m chug 33.x:- uoa cause 5 33¢ sauna-9E on. 3. oo. 2. ova I Ioh‘I X I x IIS. v :ch\ 36.... \ O \ O \ \ no.» .2 \ \ \ \ \ \ \ \ ave ze \ :1. 2.3282... IxI \ 258.13.- IcI V. 630:00183 4 382m I I I .0“ ..OO .05 OD. nu to sum oz (q coma: red and a: pen; moquoqa 56 on. ‘ ‘I‘ .933 ado." Adam- 0337 Houston ha. afloannofln no sonnet saga? «on 9.723 3 codes echoing ‘ dI \ \05. :e 0&4. :0 cc. a» fi 00 «3 580002 I XI .3 .23.! III 3. 3.35 .mehuwuh. 0 N on I) fi 00. no: 30 sun 02 sq mu chromium 30 can“: cod and 57 on. nu. .anue- idea 33 donor: mp noses» Eggnog 5 a: 83H“.- .89 nah-A 3 codes nanosecond 00. on On 33 seaeetIoI 3N. :Io=—IIII 3; .8deI . 3. 35.80 l I) N .0» A n h 00. “it“. ad and u: put; moquoqg ~58 .uuuo- Isofi_hsae ease ashore. hn.oeuemauona no scavengn .n enough .EidfllLSA efflnsafifiéfiwsfiaafléfln on. nu. 00. n» on 0N d d J 4 - 3V 2.22 I x I 33 2:...» I I I I 33 euro I" N .00 I) y. 00. tuu;uwnnd?azlq lflrflmllfliItflfllflIflIUHflumfiMmg 59 on. ON. 332. need he? has. as»: .3 .833 Banana .c 0.33.— 333! use 3.3m a.“ 6033 causing 00. as a \ \ \o \\ \ e cox... :3 \ss \\ \fi. \ $ \ i + \ vs: LI 1...... as. abs-om $3 2.3:. IxI 33.33.80 II II . 33 35cc... IxxI .00 .ns 00. “0' :0 “Ii-l9 02 1Q can“: and and u: pen; chromium 3.38 .353 Hench: hp 333.." nausea-SE .5 arm 8:3.— .Se 8.8g 3 cases 3.33.5 on. mm. 00. 2. on 3 b +\ a nuuiux x \I\m \\ I x III.“ \I. x\\\. I. ..\\\ mu oo.n:..\\ \ n \ \ \ \+o.2. :e + \ ._ \\ \ .Avo I and :c .Voh «3:323... Ix I 33333.3: III . 33.3.. I OO- nos 30 Imus oz lq serum ad sand u: put; madam 61 the retention of phosphate by three soil fractions that were retained on l-millimeter, hO-mesh, and loo-mesh sieves. The soil that passed through a loo-mesh sieve fixed the greatest amount of phosphate while the least fixation occurred in the l-millimeter fraction. Perkins, Wagoner, and King (29) divided a soil sample into six mech- anical fractions and found that on a weight basis, phosphate retention increased with decreasing particle size. On a surface-area basis a direct relationship was noted. A.study of the data in Tables 11 and XV revealed no particular relationship between the percentage of clay in the soils and the amount of phosphorus fixed by the soils. Russell and Prescott (35), Hibbard (17), Davis (15), Kurtz, DeTurk, and Bray (19) have shown that fixation of phosphorus increases as the ratio of phosphorus to soil increases. Examination of the amounts of phosphorus fixed by the soils in this investigation show a similar increase as the amount of applied phosphorus increased. The relationship between phosphate fixation and phosphate concentra— tion generally follows the familiar Freundlich adsorption isotherm. Chemical precipitation processes also give results which fit the Freundlich adsorption isotherm, thus it cannot be implied that the fixation was an adsorption process. With respect to hydrogen ion concentration, it is generally accepted that in the acid range the greatest fixation of phosphorus occurs below pH 6.5 and in the alkaline range between pH 8.0 and 9.0. Roszman (34) found that the greatest fixation.with the electrodialized clay fraction of Putman silt loam was at pH 3.0 to 4.0 with little 62 retention above pH 10. Coleman (14), working with montmorillonitic and kaolinitic clays, showed that most phosphorus fixation took place at pH 3.0. Black (3) obtained similar results with Cecil clay, in which the greatest retention of phosphorus occurred at pH 3.0 to 4.0. On the other hand, Scarseth (37) found that the greatest fixa— tion by an electrodialized bentonite was at pH 6.0 to 7.0. .An inspection of the data obtained in this study shows that hydrogen ion concentration had no effect on the amount of phosphorus fixed. Since the cation exchange capacity of a soil can be taken as a measure of its chemical reactivity, it was thought that perhaps some relationship might exist between this characteristic and the amount of phosphorus fixed. .An examination of the data, however, showed that such a relationship did not exist. It has been established that phosphorus fixation by soils is influenced by the type of clay mineral present, with 2:1 types, such as montmorillonite, generally fixing less phosphorus than the 1:1 types, such as kaolinite. The variation in fixation could not be explained in this way, however, because this investigation did not include a mineralogical examination of the clay fraction. As indicated in the preceding paragraphs, no clear relationship exists between any one of several physical and chemical prOperties and the amounts or percentage of phosphorus fixed.by the soils at the four rates of application. It should be remembered, of course, that the method of measuring the fixation was purely an arbitrary one, and its suitability is conjectural. The diverse prOperties of 63 the soils present an impasse when an attempt is made to explain the differences in fixation. Perhaps the only reasonable explanation would.be that the amount of phosphorus fixed.by any of these soils is the resultant of the interaction of several physical and chemical phenomena that prevail in each. Removal of Free Iron Oxides. In Table XVI are presented the results of the effect of the removal of free iron oxides on the amount of’phosphorus fixated by the individual soils. As with the previous experiment, soils varied greatly in this respect. The amounts of phosphorus fixed by the untreated soils ranged from 0.044 to 0.224 milligrams per gram of soil. The soils from which the free iron oxides had been removed fixed from 0.015 to 0.155 milligrams per gram of soil. The data show that with some soils the removal of the iron oxides greatly decreased the amount of fixating but with other soils the removal of the oxides had little effect on phosphorus fixa- tion. Since Voelcker (46), in 1863, first showed that hydrogen, iron, and aluminum were active in phosphate retention in soils, many in- vestigations have been concerned with this role of iron and aluminum. In most soils, iron and aluminum are concentrated in the clay frac~ tion. In clay minerals such as the montmorillonitic types, these elements occur mainly in the octahedral structure, though aluminum may proxy for silicon in the telrahedral portion. In the kaolinitic types, aluminum is found only in the octahedral coordination. They also exist in soils as hydrated oxides and oxides; aluminum as a.o on ooo. sec. eoe. Aoev ease smashese mm e.~e m moo. eoe. ooe. Aamv ssoe aseo hoses soeesoo em m.oe an emo. soc. nee. Ammo ssoe aseo moose eososoo mm «.me me eeo. moe. aee. Ammo ssoe aseo eoseoa mm o.oe om mmo. ooo. «we. Am v ssoe soeoseo em a.o on eoo. omo. awe. Am o esoe sees ease: om ~.o oo woo. .eeo. one. Aeev asoe hoses oesoeeeem oe o.ee am mmo. «mo. one. Ammo asee sees moss. seeossse me e.o em eeo. moo. mme. Ammo _ssoe aseo asses seessersu ae m.m. NN mmo. :3”. nma. G3 are.” hoes house noose: we o.m me omo. wee. mne. Aosv ssoe hoes hoses eseeeom me m.m me emo. nee. one. Ammo arse seeseoosm ee o.oe me emo. aee. one. Ammo shoe ease: me e.o mo soo. moo. use. Ah V shoe sees. oases: me e.o we moo. owe. ewe. Ammo ssoe sees soaeo ee o.ee mm mmo. ooe. mme. Amev sooe aosss oeoeesesem oe e.- e: ooo. Nao. one. Ammo ssoe hoes seem o m.m me mao. soc. ~oe., Aoev ssoe hoses soothes: m 3.2 we mmo. one. N3... 88 asoe 536 house condemn N. $4: a. N3. nae. nee. 33 Eden” mode boom» sedans: m m.m no mao. moo. awe. Asev ssoe hoses seesosoeoeeom m m.oe me eNo. mme. one. Ao V ssoe soeoseo e wém mm 30. mod. owe. 3.3 aooe 33.33 m o.m mm duo. wme. com. 39 as: head honor your; N 0:: 2. NE”. Nmo. :NN. in V Boo." hogan magnum H .. rims. Mm Imam.” Jams Imam? use? EH eeom done.“ :2. seem .eoa anathema dong escapees degassed: egomamomm coboaom nomenom Eomamomm Zoom aduw .eoa undead on ssmomom 5 ommonoon dong 253%er madness nnnuununmw, Iri .nutsl.pewi.runwoessmhuu onadNHh mbmommmomm no wmnHNo BOMH Eh ho flbgfim Esme ho Boga mums HE" a3 65 IIIHIII IIIIIIU .oompea opemeouoeomn Heaven on» an oo>oaoa mooexo none monk so .unooads Hear emsemeho * I: e.a mo moo. neo. eeo. Aaeo osss onessseeoeesm o: a.m m moo. oeo. «no. Aomv one. sesseese an e.ne an emo. ooo. soo. Aoev esoe aosss sea on o.o an emo. moo. moo. Aomv ease asooe oeoeesesem am v.5 w: mmo. mmo. mwo. Ammv awed hoods poaam mm o.o em moo. oeo. moo. Amev asoe use mm e.o so omo. woo. woo. Aomv ssoe aseeeom on o.: on eeo. eeo. moo. Amen osse assee sea mm e.oe m: eeo. moo. ooo. Ae o ssoe moose ease: mm e.ee am emo. moo. omo. Am V asoe aseo sense seeneooem em e.oe ae meo. mao. ooo. Am V ssoe aseo ease: on o.o em moo. oao. moo. Aeev shoe aosss sooseeeem om a.oe mm emo. mao. omo. Ammo sees sense soonxoosm mm a.m mm emo. mao. ooo. A: v ssee hoses noose; an m.me ee eeo. moo. moe. Aemv sooe sees hoes. seem om nillammmw seams [Jerome seems soomma,oqs squelflmmmllljwmmnfilxu Heom Edam pom masseuse doueh ssooueona deaconvop monogamonm deposem nooeuom monogamomm .Ilflflmu asemfimwa assess o» ssmowoh me omeosoon oeueh napoAAoomm woeonooos mesa 20H94NHH mnmcmmmomm_zo mmnHNO zomH ammh ho A<>szm Mme ho Bonfihfi Ema Adodnepooov H>N mqmda 66 gibbsite, and iron as hematite, goethite, limonite and magnotite. In addition, some aluminum.and iron may be present as exchangeable cations. Waksman (47) has pointed out that iron is present in soil organic matter and it is likely that aluminum occurs similarly. With the exception of acid soils, it is generally thought that the active amounts of iron and aluminum in the soil solution are small. It has been definitely established that iron and aluminum com- pounds can retain phosphorus under the conditions that normally exist in soils. Experiments with hydrogels (26), ferric hydroxide (18), and with soluble iron and alumnum (21, 27, 32, to, L1) have pro- duced an overwhelming weight of evidence to support that conclus- ion. Mattson (22,23), Scarseth and Tidmore (36), and Toth (42) have demonstrated that phosphorus fixation varies inversely with the silica—sesquioxide ratio of the soil colloids. As in this investigation, several workers have studied the effect of the removal of iron and aluminum from_soile and soil colloids on phosphorus fixation. Toth (42,43), Chandler (13), Black (3), Coleman (14), Hetzger (24), and Kelly and Midgely (18) have shown that the removal of iron and aluminum oxides from soils re— duced the amount of phosphorus fixation. The results, of course, varied with the colloid or soil under investigation, but tended to emphasize that in acid soils, iron and aluminum.are actively involved in phosphorus fixation. Removal of the iron oxides from.the soils in this study generally had a marked effect on the amount of phosphorus fixed. The results are 67 comparable to those obtained by other workers. The quantities of iron oxides removed fromvhoils were more closely related to the clay content than to any other soil prOperty. There was no apparent re- lation between the amounts of iron oxides removed and the degree of acidity of the soils. This is contrary to what had been expected since it is generally assumed that iron activity increases with acidity and consequently more iron should be removed from the more acid soils. It is possible that the fraction of iron removed was not related to the chemically active amount in the soils. However, a test for free iron oxides should give a measure of the "active" iron in a soil. The method used for free iron oxide removal was compared by Deb (16) at Rothamstead with several other recognized methods and he concluded that the method was superior to the others because it efficiently removed free iron oxides and had less destructive effect on clay minerals. In making an evaluation of the effect of the removal of the iron oxides on fixation it must be remembered that the method used in this investigation, as with methods used by other investigators, was not specific for iron and may have removed other compounds which are effective in phosphate fixation. This point is probably of particu_ lar importance in the case of the alkaline soils known to contain large amounts of calcium and organic matter. As in the hydrosulfite method, all chemical methods for the removal of free iroh oxides involve a destruction of the organic matter, reduction of the iron compounds with a reducing agent, and removal of the reduced iron by 68 suitable solvents. Though little change occurs in the structure of the clay minerals, radical changes in the overall chemical system results, and therein may be the explanation for some of the varia- tions in results. An excellent example, is the case of soil number 5, an alkaline soil which in both experiments fixed the largest quan- tities of phosphorus. The amount of free iron oxides in this soil as shown by the data in Table XVI was only 4.0 milligrams per gram of soil. Fixation of phosphorus in this soil was reduced 77 percent by the removal of these iron oxides. It was quite probable that the reduced fixation was due more to the removal of calcium than of iron compounds. This would probably be true of any alkaline soil high in organic matter. However, with highly acid soils which are low in organic matter, there is a more valid relationship between phosphor- us fixing capacity and the free iron oxides. Though it cannot be denied that iron oxides were removed from the soils in this investi- gation, the question of what other substances effective in phosphorus fixation were removed, and Just how much of the reduction in fixation in the case of each soil can be attributed to iron oxides, remains unanswered. Relation Between Alfalfa Yields and Soil Phosphorus The successful use of chemical soil tests in helping to formu- late soil management recommendations is dependent upon calibration of the test with crop yields. Critical nutrient levels, above which substantial crop response to added nutrients will not occur, must be 69 established before the fertilizer needs of soils can be prOperly appraised. In the succeeding paragraphs the relationships between the yield data secured in this study and the soil phosphorus as measured by the various methods are presented. Spgrway's Reserve Test. In Figures 8 and 9 scatter diagrams are presented of the relation of the yields of alfalfa to soil phos- phorus as measured by Spurway's reserve test. The coefficient of correlation between the yield of tops and soil phosphorus was 0.312, a rather low degree of linear correlation. When the root yields were combined with the top yields the correlation coefficient was 0.302. These results indicate that Spurway's reserve test is of doubtful value in measuring the phosphorus supplying power of the soils for alfalfa under the conditions of greenhouse crOpping in this experiment. Obviously from the data given, the strong acid extractant (0.135 N HCl) did not measure a prOportionate amount of the phosphnus which was available to the growing plant. This is further substantiated by an examination of the percentage phosphorus composition and total phosphorus content of the alfalfa. A negative correlation of 0.142 was obtained between the levels of soil phos- phorus and the total phosphorus uptake. The correlation coefficient between soil phosphorus and percentage phosphorus content of the alfalfa was 0.046. Further evidence of the failure of Spurway's test to measure forms of soil phosphorus which are available for plant use was seen in the amount of soil phosphorus extracted from certain soils. For an example, with certain heavier textured soils, 70 633. 3.3.8 E a: 3 3.33. 8 .fiofiuqfl :8 e8 3.3 53.2.4 3258 833a,. 6 5.3.— 33:- son 3.23 5 Essa-fin no» D N. 0.: 8. O. 0. Os. 0. «3.0... 0060 + thd a? 00 at o. “I” ’ ~04, 3'! ”m 30 911"“. l 7 Jonas: Eamon gm on. hp gods! 3 Esau-0AA :0- can chads 9.9.5.9 9333 .m 0.3»: 5:3- : $.23 3 33981 23 09 ON. 0: 00. 00 00 ON 06 On 0' On ON 0. O — a _ fl 4 J 4 _ a a‘ q J T - N V O . . u.... o o o o o O O O O” . 18 Nom.O-s . —¢._o+ xnn.O-> o 1.00. C C. C O e oo o JON; O o O! 00. "0“ P“ “01» " m "3 ”FUJI! 3° P1071 72 numbers 36, 34, 29, and 32, the acid extractant removed large amounts of phosphorus which were not reflected in the yields. On the other hand, with several of the lighter textured soils, numbers 30, 18, and 17, the levels of phosphorus were low and not commensurate with the high yields obtained without added phosphorus. Brayig Available Phosphorus Test. The acid concentration used in this test approximates that used in the Spurway reserve test. However, included in the extractant was sufficient ammonium fluoride to make it 0.03 normal with respect to that reagent. The evidence that the results fromIBray's available test for phosphorus were more closely related to alfalfa yields than the Spurway test values is shown in Figures 10 and 11. As previously presented in Table XII the average amount of phosphorus removed was 40.8 parts per million which almost doubled the average amount removed by the Spurway test. The coefficients of correlation between soil phosphorus and yield of tops and between soil phosphorus and total yields were 0.635 and 0.599 respectively. The decided improvement in the correlations over those obtained with the Spurway test was attributed to the in- creased amounts of phosphorus removed by the fluoride ion especially from the lighter textured soils. From these data it was apparent that Bray's available phosphorus test was a good measure of the power of the soils to supply the phosphorus needed by alfalfa. Bray's.Adsorbed Phosphorus ngt. The scatter diagrams for the relation of alfalfa yields to adsorbed soil phosphorus are given in Figures 12 and 13. The respective correlation coefficients were 0.75h .33! .3395 3.33.25 in a: .3 e538 8 nanosecond 38 2:. eat £33. 8.53 8:33 .2 9:53 83:.- .Ga 3.2a 5 unsung-Ba .38 om on 2. on on 0.. 0» ON 0. O ON. 0: 00. u a q u s q fl - onm.o u. omén + xno.0u> ON ..On C IO' ion 100 L05 1 O O 1 00. 0.. do: - um In ”turn 30 non 71+ 63:: .EEaSfi .2325 scan 23 2 e238- : .Eflaufia :8 e8 3:» £37 8253 83:3" .fi 8%: gaigotfiflafififiag o: 06,. cm on 2. cm on no on o~ o. o . 4 q 1 s a a 4 4 [OO- . ON. . OV- eoodu. Loo. 3.3+ x36.» 00. am pm ado: - Inn at unvm to non 75 .eonpgn astonnsona eopuoued, .3 3:5 .3” lauds one an.eonsmaos as .uuonanogn Has. as: egos» nsasuds guesses « beam 5.333 sea 3.3a an .339-Ba Goa on o o o v o n o a o. u d a u d. d 14| cmbdu. Pfioc + Xno; u>. ON on -OQ on 00 .05 00 10a JQO. o: M " “9 ‘1 ”WI. 3° PI°$1 76 £23! 335.5 eeficoed sun on» .3 3933 8 .fiBa-nfi 38 e5. 33» £32.- 83»... 833cm .2 Bus: 8.2:. sea 3.2g 3 gang :8 oh - 00 Om 0.9 0m 0 N o . 0 .ON low . .«m o mmbd 1 c069... x31; 9.! 6 2 om. L—a. -Om. 9. noes pm «In * 0"", it owns 30 N011 77 and 0.796 indicating very high correlation in each case. The dia— grams show that differences in amounts of phosphorus removed between soils are of a smaller magnitude than those obtained with the Bray available phosphorus extractant thus increasing the difficulty of making a cursory separation of the yielding powers on the basis of their phosphorus contents. However, the differences between the levels of adsorbed phosphorus were greater than those obtained'by the Spurway reagent even though the acid concentration was only 0.025 normal. This further emphasizes the effectiveness of the fluoride ion in the removal of soil phosphorus, especially those forms well correlated with plant growth. The amounts of adsorbed soil phosphorus were reflected in the total phosphorus uptake by the alfalfa and also in the percentage phosphorus composition. With total uptake the coefficient of correlation was 0.416 and with the percentage phosphorus content it was a high 0.749. From the correlations presented, it is apparent that of the three rapid tests, Bray's adsorbed phosphorus test was the most reliable as a measure of the soils' phosphorus supplying powers. Bray's Total AcidpSoluble andpédgorbed Phosphorug, In Figures in and 15 data are presented to show the relation of alfalfa yields to soil phosphorus as measured.by Bray's method of determining total acid soluble and adsorbed phosphorus. The scatter diagrams reveal a fair degree of linear correlation between these more resistant and less soluble forms of phosphorus and the yield data. The corre- lation coefficients are 0.499 and 0.501 respectively. The phosphorus 78 On? ..fifieofl 5.3843- 3. 39.83 33 was 35... ban 2: 3 e588 3 3:» £33.- 23 5.3923 28 8253 833cm .3 one: Or.» 8:3- .Sa 3.8a 3 assigns :8. con 03 con 00' 4! a q A A a T - 00¢.On. N12... Xh..O a» ON .On .0? OO .Oh On .09 .OO. O.- 'M " M “I amt- 39 'PI’II 79 69...: 351.5 sunflower: es- eo£§ .38 in as .3 3.88: 3 ed...» $32 ea. Eggs 38 8253 833cm .3 983.— 833.. 8a. .33 fl .3323a 38 one ooe can can on a com 3. .ON .O.s..Oub INN + XNN.Ou> 10¢ .00 on J .00. . ON. 0 . O! ._ OO. OO- um um «M - ms? 91 uninv- 30 non 80 values are large as compared with those obtained in the rapid tests, and the variations between the results from different soils are sufficiently great to make possible separations into low, medium, and high yielding groups. Organic Phosphorus, In Figures 16 and 17 scatter diagrams of the relation between yields and organic phosphorus are presented. The correlation coefficients are 0.h87 and 0.532. These results are not surprising when consideration is given to the duration of the experiment and the intensive root action to which the soils were sub- jected. The length of the experiment permitted sufficient time for the mineralization of organic phosphorus for plant use. An examina- tion of the levels of inorganic phosphorus before and.after cropping showed that the phosphorus content did not decrease to any great extent. Since appreciable quantities of phosphorus were removed 'by cropping, it can be concluded that organic phosphorus was mineral- ized. The degree of correlation obtained emphasized the point that over a long growing period organic phosphates play an important role in maintaining the available supply of phosphorus and that under such conditions organic phosphorus can be an adequate measure of the phosphorus supplying power of soils. Braz's Total Acid-Soluble, Adsorbed, ggd Ozganig Phosphorus. As would.be expected from the other results, a high degree of linear correlation was obtained.between yields and the quantities of phos- phorus measured.by Bray's methods for total acid—soluble, adsorbed, and organic phosphorus. Figures 18 and 19 present the scatter diagrams. 81 .35.: gasses.” ease seen :3 3 e832: 3 83» gm? e3 383.23 :8. 8053 833cm .2 98»: Saistlfluflflfifisaom um - m9 Wt out: umn com con 8.. com can as. o J 4 4 4 4 4 . 1 q 4 n < 4 a 0“ Bed... . on 8....» + x86.» . . oe . on . on . 2. . on . . ca 0 O O . oo. . 82 .vofiol nausea-SE ease swam on» up.eousnsos as.eao«» sadness use asuosasoga «so. «wows-p soaasaom .aa enemas saunas- usa sauna as unsung-can ”sow OOO OOo OOQ OOn OON OO. O «no.0... 051'.» .7 XO..O-> ON 0' O. O. OO. ON. OO. OO. I200: out 010: - Inu¢9 at estuztv 3° vt'tx 3 8 OOO. .esso: goes cameo 3.. 63.3.3 6238.33 3% seen on... up 288.. 3 33» £36. 3. assess-3m :8 8.83 8333 .2 2%: Oom OO. .33.? sea 3.3a 3 sauna-93 .33 00% 000 000 OO? 800.0... 8.0. a. Xh0.0s> ON .0” ,. 0.. .00 .00 .05 .OO O G 100. o... Ida - ms? 11" ump- J9 um 693.: .Eofiufim ogmuo 23 vofioag 5.38.33 fiance hwum an» hp wounamoa ma uuuonmuann Ado. can data» unashad nuotoop.uauncanm .mn changu noadnua hog .0319 a“ cubonguonm Adam ooo. com co» co» com com coo can q 1 < q 1 a q q 4 q d a q o 1 cu m 1.90.. g n. av u. 3.2 + .83.» .u L n on n. w. Loo m o 1 OO..“ . on. m 0 . m 0 1. o 1 0*. I on. 85 The coefficients of correlation are 0.607 and O.6h#, respectively. With exception of two soils, 18 and 5, the correlations were very good. Soil number 18, as previously mentioned, is a light textured soil and gave proportionately low results as with the other tests. Soil number 5, an alkaline soil high in organic matter, gave high results. From an examination of the results it is apparent that these quantitative methods for measuring the more resistant and less soluble forms of phosphorus are satisfactory for distinguishing between soils on the basis of their phosphorus contents and for predicting the phosphorus supplying powers of the soils. Table XVII and.XVIII present summaries of the relationships between the various tests for soil phosphorus and the yield results, total phosphorus uptake and percentage phosphorus compositions of alfalfa. Relation Between Soil Phosphorus and Soil Properties Careful examination of the data obtained with the various chemical tests failed to reveal any exact and definite relationship between any soil property and any particular fraction or fractions of soil phosphorus. Generally, all of the tests measured relatively large amounts of phosphorus in the heavier textured soils. The amounts removed from the lighter textured soils were extremely variable. As previously shown, the variable amounts of chemically extractable phosphorus in 86 $09 hem damages ”:33 and mo madam a.“ daoaw .1. .332. .33 a do songs mom 278a ea ugomamoma Sow ... +306 wrpoom was Wade easemdd and ioapdaomndfiod ..oopsomud 339%.?er .306 mmoa eacdmso due .mapsaomlgod 739334 .3509 mtnmfim WW Nmmé 300m was mace ofisdwno 35de W R35 mace ougwao clean mm .890 mpoom one mace oapdaomlcwg use @098mb «Edam mi modd mace oapdaomugod was $8334 Passm fl mmmé 300m amigos oapdaae>oqoo .NH Amav amoa house Mom .m 38 $3 .33 same .mm 83 as. signs .sa 88 32 fisfia .m Amavamoa moose daofimsamam .Hm AHNV asoa hmao hoods psom .ma Mmav dado onaouoomoaaom .H gnaw adaum: >oA 38m 588% Ema so £53430 sauna mpMommmomm 333mm NHN.HAde 91 examination reveled that a large number of the soils in the "Low” fixing group fell in the "Least" and "Moderate" categories of Table VII. Also a greater percentage of the soils with “Greatest" and "Marked" requirements for phosphorus fell in the “High" and "Medium" fixing groups. This somewhat general relationship appeared to indicate that the relative amount of phosphorus fixed.by a soil is perhaps a fair index of its ability to supply phosphorus. A comparison of the relative fixing capacities with the levels of available phosphorus as measured by the chemical tests showed that there was little relationship between the magnitude of phos- phorus fixation and the existing level of chemically available phos- phorus. The Phosphorus Supplying Powers of Forty-one Michigan Soils The greenhouse and laboratory studies conducted throughout this investigation were designed primarily to secure a better understand- ing of the ability of the various soils to supply phosphorus. The final measure of the capacity of a soil to deliver a given nutrient element is obtained through actual plant growth on the soil. Other methods, such as soil tests and fixation studies, are useful but their value is assessed in terms of the plant growth. When several methods are used, such as was done in this experiment, a reliable estimate can be made of the nutrient supplying powers of a given soil. Consideration of the yields, phosphorus uptake, and percentage composition, soil tests, and fixation studies made possible an 92 evaluation of the phosphorus supplying powers of the forty-one soils under investigation. Presented in Table XX.is an arrangement of what was considered to be the phosphorus supplying powers of these repre- sentative Michigan soils. The soils were arranged in descending order of their phosphorus supplying power and were grouped into “High", "Medium”, and "Low" categories. The soils in the "High" category gave high phosphorus tests, low yield response to added phosphorus, and produced plants which were generally higher in phos- phorus than the mean percentage phosphorus content. On the other hand, the soils in the "Low" category gave low soil phosphorus tests, marked increases in yield to added phosphorus, and supported plants whose phosphorus contents were generally lower than the mean phos- phorus content. The soils in the "Medium" group generally gave intermediate results by each method of evaluation. 93 .maoaasm Haom amnfiwduo as .oowpmnam masonamoaa was .momo» Haom .dmflmmam mo mdaowh opapmsmaaoo no comma.sofipmsas>o s4 9 «WHV AamV Am V AamV AsNV AH V AmmV AmNV AsmV A: V AmmV Am V AmNV AamV ANHV AmNV AsHV AeHV ease eamssHsMInwae adod moan momma maaoasmH amoa noboaoo amoH made meson aswxaom amoa Hana: amoa manna “as“: amoa tho human ao>onoo seed mode human oosmasz awed hmao momma swam“: Edna Adan momma some“: awed mafia meson naazmxamm amoa asao asses awed mode hoods maaonmmH adoa mafia momma noboaoo damn named Rom amoa mean odoaoa amoa amass: awed human onfimpnommaaom HIV, 30A .0: .mm .mm .mm .mm .mm .em .mm .mm .Hm .om .mm .mm .mm .mm CJN ANNV “HeV AsmV ANmV AomV Am V Am V Aw V in V as V swan—”om awnmog Smoa ands anew mmao henna sopmxoosm shod amao house Momma: Bead noanoosm down mxmnxamm adoa nobosoo amoa hands hpsmnm awed hands naoos: adoa amao dang: amoa amao madam oopmxooum ademE. MN mqm49 .na AoaV AomV AHNV AaHV AOHV AmHV AaHV AmmV AmHV AamV AHmV AmHV a... amOH hmao human Mawxaom dado based afloamowsam Hood adds unom amoH hoses oaodnaafim amoa hogan mamoxsms seed seams eHoneasam damn oswspsomoaaom amoa moan evade awed Hem moan quom noanooam sandmaaam adoa_hugmu Mom awed henna posam isms! MZOINBMOH ho mmmxom athnmmDm mbmommmomm HmB .mH .NH .HH .0 .m .m .m .m .a .m .H 91+ SUMMARY .An investigation was undertaken to determine the phosphorus supplying powers of several representative Michigan soils. Fortyb one different soils representing approximately eleven million acres of agricultural land in the southern half of the lower peninsula were selected for greenhouse and laboratory studies. 'Alfalfa, a phosphorus responsive crop, was grown on each of the soils for eleven.months under controlled conditions in the greenhouse. Avail- able soil phosphorus was measured by several arbitrary chemical soil analyses making use of both rapid tests amd more quantitative labor- atory methods. Phosphorus fixation by the soils was evaluated'by two different methods. One method measured the fixation of phos- phorus at different rates of application and the other measured the amount of fixation with and without the free iron oxides. The results are summarized in the succeeding paragraphs. Forty-one Michigan soils varied greatly in their ability to produce alfalfa without added.phosphorus. Yields of seven harvests of alfalfa ranged from 33.1 grams to 103.? grams, with an average yield of 60.9 grams. Based on yield response to added phosphorus, the soils were arranged into what appeared to be their relative need for phosphorus fertilization. Yields were increased on all of the soils by added phosphorus. The dry weights of seven harvests were from 88.4 grams to 123.1 grams. The average yield was 100.5 grams. Percentage yield increases pro- diced‘by added phosphorus varied from 3.0 percent to 216.8 percent 95 with an average increase of 65 percent. The percentage phosphorus composition of the alfalfa harvests on the unphosphated soils averaged 0.16? percent whereas alfalfa grown on the phosphorus treated soils averaged 0.323 percent phos- phorus. The total amounts of phosphorus removed by alfalfa averaged 133.0 and #27.6 milligrams for the plants grown on the unphosphated and phosphated soils respectively. The recovery of applied.phosphorus ranged from 20.3 percent to 60.6 percent as measured by the difference in method. The average percentage recovery was 38.h. The amount of chemically available phosphorus removed by the several rapid tests varied with the soil and with the extracting agent of the test. Spurway's reserve test removed a preportion of the acidpsoluble forms of phosphorus, the amounts of which ranged from 3 parts per million to 81 parts per million. There was apparently no relationship between the amounts of phosphorus removed by this test and any of the soil prOperties. Bray's adsorbed phosphorus test is believed to remove the adsorbed phosphorus and perhaps some of the easily acid-soluble phosphorus from the soils. There appeared to be some general rela— tionship between soil texture and the amounts removed by this extractant, with soils high in sand usually, giving medium to high tests for adsorbed.phosphorus. The amounts of phosphorus removed from the soils by this method ranged from 5 parts per million to 68 96 parts per million. Bray's available phosphorus test removed proPortionate amounts of'both the acid-soluble and adsorbed phosphorus. The amounts removed ranged from 11 parts per million to 93 parts per million. Bray's more quantitative method for acidpsoluble and adsorbed phosphorus removed considerably larger quantities from the soils than did the rapid tests. However, the amounts removed were prOportionate to the amounts removed by the rapid tests. No clear relationship between soil pr0perties and soil phosphorus as measured by this method could be established. Organic phosphorus determinations by Bray's hydrogen peroxide method indicated that relatively large quantities of the total soil phosphorus existed in the soil in organic combinations. The amounts varied from 73 parts per million to 652 parts per million and generally followed the organic content of the soil. Definite relationships were established between soil phosphorus and alfalfa yields which clearly showed that chemically available phosphorus as measured by the several methods was a good index of the soils phosphorus supplying-powers. Correlation coefficients between the dry weights of seven harvests of alfalfa and soil phos- phorus as measured'by rapid soil tests were 0.312, 0.754, and 0.635, for Spurway's reserve test, Bray's adsorbed phosphorus, and.Bray's available phosphorus respectively. Considering the relationship between total dry weight of seven harvests and roots and extractable phosphorus, the coefficients of correlation were 0.302, 0.796. and 97 0.599 for the above three soil tests. With the more quantitative methods for determing soil phosphorus, the tests for adsorbed and acid-soluble, organic, and total adsorbed, acidpsoluble, and organic gave correlation coefficients of 0.499, 0.h87, and 0.607, with the yields of seven harvests of alfalfa. With the total yield of harvests and roots the correlation coefficients were 0.501, 0.532, and 0.641}. The high degree of linear correlation between alfalfa yields and soil phosphorus extracted with reagents containing the fluoride ion showed very definitely that fluoride aids in the removal and measurement of soil phosphorus which is available for plant utiliza- tion. Phosphorus fixation stumies of twenty-two selected soils using several rates of applied phosphorus revealed no apparent direct relationship with any of the measured soil properties. The quanti- ties of retained phosphorus varied with the soil and also with the amount of applied phosphorus. The character of the fixation curves for the individual soils suggested that the mechanisms of fixation also differed with the soils. The removal of free iron oxides reduced.phosphorus fixation from 0.6 percent to 75 percent. No relationship, however, could be established between the amount of phosphorus fixation or the decrease in fixation and free iron oxide content. 0n the basis of the quantities of’phosphorus fixed, the soils were arranged in order of their need for phosphorus fertilization. Comparison of the yield 98 results and the fixation studies revealed that plant response and phosphorus fixation as methods were equally satisfactory in eval- uating the need for phosphorus fertilization or conversely, the ability of soils to supply phosphorus. A classification of the fortyaone Michigan soils as to their phosphorus supplying powers was presented based on the yield and composition of continuously cropped alfalfa, soil tests, and the phosphorus fixation studies for chemically available phosphorus. (lo) (11) 99 LITERATURE CITED Arnold, C. Y., and Schmidt, W. A. 1951 8011 tests as a measure of phosphorus available to tomatoes on heavy soils. Soil Sci. 71:105-115. Attoe, 0. J., and Truog, E. 1909 Correlation of yield and quality of alfalfa and clover hay with levels of available phosphorus and potassium. Soil Sci. Amer. Proc. 14:299- 253. Black, C. A. l9#2 Phosphate fixation by kaolinite and other clays as affected by pH, phosphate concentration, and time of content. Soil Sci. Amer. Proc. 7:123—133. Bouyoucos, G. J. 1951 A recalibration of the hydrometer method for making mechanical analysis of soils. Agron. Jour. 1+3 :4314-1-68. Bowers, A. H. 19h? The relation between forms of soil phos- phorus and response of alfalfa and small grain to added phosphate. M.S. Thesis, Michigan State College. Bradfield, R., and Allison, W. H. 1933 Criteria of base saturation in soils. Trans. Second Comm. Internatl. Soc. Bray, s. H., and Wilhite, F. M. 1929 Determination of total replaceable bases in soils. Ind. and Eng. Chem.,.Anal. Ed. lzluu. , and Dickman, S. R. 19b1 Adsorbed phosphates in soils and their relation to crap response. Soil Sci. Amer. 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E. 1935 Sorption of phosphates by non-calcareous Hawaiian soils. Soil Sci. 40:129-158. Dob, B. C. 1950 The estimation of free iron oxides in soils and clays and their removal. Jour. of Soil Sci. 1:212- 220. Hibbard, P, L. 1935 Factors influencing phosphate fixation in soils. Soil Sci. 39:337-358. Kelly, J. 3., and Midgeley, A. R. 19MB Phosphate fixation -- An exchange of phosphate and hydroxyl ions. Soil Sci. Kurtz, T., and DeTurk, E. E., and Bray, R. 1996 Phosphate adsorption by Illinois soils. Soil Sci. 61:111-124. Lawton, 1., Robertson, L. 5., Cook, R. L., and Reed, P. J. 19h? A study of correlation between rapid soil tests and response of legume hay to phosphorus and potassium fertilization on some Michigan soils. Soil Sci.'Amer. Proc. 12:353-358. Mattson, S. 1927 Anionic and cationic adsorption by soil colloidal materials of varying Si 02/1112 0 / Fez o3 ratio. Proc. 1st Int. Cong. Soil Sci. 2:1 9-211. 1930 The laws of soil colloidal behavior: III Isolectric precipitation. Soil Sci. 30:“59-995. 1931 The laws of soil colloidal behavior: IV Amphoteric behavior. Soil Sci. 32:393-365. Metzger, W. H. l9h0 Significance of adsorption or surface fixation of phosphates by some soils of the prairie group. Jour. Amer. Soc. Agron. 32:513-526. (25) (26) (27) (28) (30) (31) (32) (33) (34) (35) (36) (37) (38) 101 Millar, C. E. 1948 Soils of Michigan. Michigan Ext. Bul. 290. Miller, L. B. 1928 Retention of phosphate by hydrated alumina and its bearing on phosphate in the soil solution. Soil Sci. 26:435-439. Murphy, H. F. 1939 The role of kaolinite in phosphate fixa- tion. Hilgardia 12:341-382. Peech, M., Alexander, L. T., Dean, L. A., and Reed, J. F. 1947 Methods of soil analysis for soil fertility investi- gationfi. U.S.D.A. Cir. 7570 Perkins, A. T., wagoner, C. E., and King, H. H. 1942 Phos- phorus fixation by soil separates and fractions. Soil Sci. 53:37-41. Piper, C. S. 1944 Soil and plant analysis. Interscience Publishers Inc., New York, N. Y. Prince, A. L., Toth, S. J., and Bear, F. E. 1948 Phosphorus- supplying powers of 20 New Jersey soils. Soil Sci. 65: Pugh, A. J. 1934 Laws of soil colloidal behavior: III Colloidal phosphates. Soil Sci. 38:315-334. Rich, C. I. and Attoe, O. J. 1950 Phosphorus supplying powers of soils for cats. Soil Sci. Amer. Proc. 15:219-222. Roszmann, C. A. 1927 Retention of phosphorus by soil colloids. Soil Sci. 24:465-474. Russell, E. J., and Prescott, J. A. 1916 The reaction between dilute acids and the phosphorus compounds of the soil. Jour. Agr. Sci. 8:65-110. Scarseth, G. D,, and Tidmore, J. W. 1934 The fixation of phosphates by soil colloids. Jour..Amer. Soc. Agron. ._26:l38-151. p_, 1935 The mechanism of phosphate retention by natural alumino-silicate colloids. Jour..Amer. Soc. Agron. 27:596-616. Smith, F. W. 1949 A study of the availability of native and added phosphorus in several Michigan soils as measured by chemical analysis and plant growth response. Ph.D. Thesis, Michigan State College. 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Voelcker, A. 1863 On the absorption of soluble phosphate of lime by different soils of known compositions; and remarks on the application of superphosphate and other phosphate manures. J. Royal Agri. Soc. 24:37-65. Waksman, S. A. 1938 Humus. Williams and Wilkins, Baltimore, Md. amt t ‘31! \ J'E 18 ’55 "Iii-334.15%“; LUAN [MIR-LIBRARY LOAN JE 11 583 WTI?ifitflfllfiMlWiflWfllfififiEmmi)” 293 0306