'LIBRARY, A & M coztscg, c A a: P U s ' R10-1135-6m TEXAS AGRICULTURAL EXPERIMENT STATION //""“ A. B. CONNER, DIRECTOR COLLEGE STATION, BRAZOS COUNTY, TEXAS BULLETIN NO. 522 DECEMBER, 1935 f DIVISION OF Cifigtbszifi?’ f... i B A R Y _ A “ma, (‘WW0 o1 . t - 1P Sta?‘ Relatlon of the Occurrence of Cotton ROAM» Rot t0 the Chemical Composition of Soils AGRICULTURAL AND MECHANICAL COLLEGE OF TEXAS T. O. WALTON, President Soils in which cotton root rot generally occurs and causes much damage are high in fertility, as indicated by their content of nitro- gen, phosphoric acid, and potash. They are also high in basicity, contain considerable quantities of lime, and are alkaline in reaction and heavy in texture. Soils on which cotton root rot rarely occurs are generally low in fertility, have a low basicity, are neutral to slightly acid in reaction, and are light in texture. Alluvial, or river bottom, soils are usually high in fertility and basicity, but the disease does not generally occur on these soils. This indicates the action of inhibitory factors in alluvial soils not usually operative to the same degree i11 heavy upland _soils. The chemical composition of local areas of soil containing active root rot may be almost identical with that of adjacent soils on which root rot is not present. Chemical composition is simply one of a number of factors influencing the occurrence and virulence of the disease. CONTENTS Introduction ___________________________ ,_ Analysis of soils Comparative composition of soils from areas in which root rot causes high and low degrees of damagecm 1 Composition of soils in four areas as related to cotton crop losses caused biy root rof __ _ Relation of composition of soil type to the degree of damage caused by cotton root rot Phosphoric acid Nitrogen __-_____g Potash -- ____ Lime and basicity pH _____ 1 1- Composition of some alluvial soi1s_____ The composition of adjacent soils of the same type bearing diseased and disease-free cotton plants_____ General discussion Summary References _ 12 15 15 15 15 15 16 17 17 19 20 BULLETIN NO. 522 DECEMBER, 1935 RELATION OF THE OCCURRENCE OF COTTON ROOT ROT TO THE CHEMICAL COMPOSITION OF SOILS G. S. FRAPs, CHIEF, DIVISION or CHEMISTRY, AND J. F. FUDGE, CHEMIsT The plant disease commonly known as cotton root rot, caused by the fungus Phymatotrichum omnivorum, occurs over a very considerable part of the southwestern United States, having been found in Texas, New“ Mexico, Arizona, California, Arkansas, and Oklahoma. It has been found in about 200 counties of Texas (16), including practically all of the State except the Panhandle and parts of the mountainous country near the New Mexico line. Cotton root rot affects not only cotton, but a large variety of other plants, including flowers, ornamental shrubs, trees, and weeds (17). It may persist for years on the roots of cotton and other plants which have not fully decayed (5, 10, 11, 16). Sclerotia, resting-bodies of the fungus, may be formed, remain dormant for years, and then become active centers of infection (9, 10, 12, 16). Spores are occasionally formed, but it has not yet been possible to cause them to infect plants (12, 16). While cotton root rot is extensively distributed in Texas, the degree of damage caused by the disease varies in different parts of the State. In the eastern part of the State, where the soils are sandy and generally low in lime, the disease occurs only in limited areas and seldom causes much damage. In the black land areas near the center of the State where the soils are heavy in texture and calcareous, and in some other areas, the disease causes great damage. The damage done by root rot in the different sections of the State varies both with the soil and with the season. In East Texas there are some areas in which the disease occurs and causes damage, while in the black land section there are some areas in which the damage is usually low. The disease does not occur in the Panhandle of Texas, and causes only limited damage in West Texas in lands under irrigation, where at times there is some accumulation of soluble salts. Taubenhaus, Ezekiel, and others (3, 16, 18) have shown that the root rot fungus grows much better and that the disease is more prevalent in a neutral or slightly alkaline soil than in an acid soil. Ezekiel, Taubenhaus, and Fudge (4) found in laboratory studies that additions of calcium carbonate to acid soils caused greater increases in growth of the fungus than the same weights of calcium or potassium added in the form of nitrates, sulfates, or phosphates. It seems probable that there are other relations between the chemical and physical character; istics of soils and the degree of damage caused by root rot in them. The object of the work here presented was to ascertain whether such relations may exist. It was thought possible that the information secured might help in finding why the disease causes great damage in some soils and does not do so in others. 6 * BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION Analysis of Soils The soil samples used in the study were selected by members of the Soil Survey as being typical of the respective soil types in the areas from which they Were chosen. Total phosphoric acid, total potash, and nitrogen were determined by the methods already described (6). Active phosphoric acid and potash are the quantities in parts per million of soil which are soluble‘ in 0.2 N nitric acid. The quantities of lime, magnesia, and acid- 04am 0cm. “m” m: - n nu: FLOYD E v O . 1R2: w E WW w ' v ". , JAC ' ’, WW 1 I m" y: WW WWW? ‘WWWWW G “WW Fig. 1. Estimated losses from cotton root rot in 1928. The figures give the estimated reduction in yield of cotton. soluble potash reported are those dissolved by digestion for 16 hours with l hot hydrochloric acid of 1.115 specific gravity. Basicity, calculated as per cent calcium carbonate, represents the acid-consuming power of the soil (7), and was determined by‘? treating the soil with anexcess of acid and titrating the excess. The reaction (pH) of the soil Was determined RELATION OF THE OCCURRENCE OF COTTON ROOT ROT 7 either colorimetrically with a LaMotte Comparator or electrometrically with a quinhydrone electrode. » In arriving at the figures for the various constituents, as given in the several tables, the general modal value for a given soil type, rather than Texas Agricultural Experiment Station If}! ti‘ Mllkll CAI-g. 0| TQIII COLLEGE S TATION. TEXAS BASICITY Or Sou. AREAS ---- .- NOTMAPP ED E Fig. 2. Approximate basicity of Texas soil regions. an arithmetical average, was used. Some individual samples may vary considerably from the values given. No attempt was made to weigh the values by number of samples, comparative area covered by the soil type, or proportion of the area devoted to the growth of crops which are susceptible to the root rot disease. Comparative Composition of Soils from Areas in Which Root Rot Causes High and Low Degrees of Damage The decrease in yield of cotton caused by root rot in different sections of the State, as mapped by Ezekiel and Taubenhaus (2), is shown in Fig. 1, and may be compared with the basicity of soil areas in Texas as mapped by Fraps and Carlyle (7), shown in Fig. 2, based upon the general soil map of Texas soils prepared by Carter (1). A fair relation between 8 BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION the basicity of the soil and the occurrence of cotton root rot is apparent. The resemblance of the two maps might have been closer if the prevalence of the root rot had been mapped by soil areas instead of by counties as units, as was done in Fig. 1. A comparison of the two maps shows that the occurrence of cotton root rot is in general limited in soils with a Phosphoric Acid Potash _.i_____ Nitro- _ Mag- Basic- No. Soil Type gen Acid Llme nesia ity pH 0t per s0lu- Der per per Sam- Total Active cent Total uble Active Cent cent cent D168 per p.p.m. per per p.p.m. cent cent cent High damage: Houston clay. . . . . .12 7S .16 1.00 .40 200 13.00 .60 20.00 7.6 28 Houston black clay .08 100 .12 1.00 .40 350 4.00 .50 6.50 7.3 39 Houston clay loam .03 150 .07 .65 .30 100 .70 .30 2.00 7.6 7 Houston loam. . . . .03 30 .10 .80 .30 2S0 .50 .20 2.00 7.2 17 Low damage: Kirvin fine sandy loam . . . . . . . . .. .04 15 .05 .55 .10 100 .21 .13 .40 7.0 16 Norfolk fine sandy loam . . . . . . . . .. .03 25 .04 .45 .10 100 .11 .11 .27 6.7 16 Ruston fine sandy loam . . . . . . . . .. .03 15 .03 .78 .09 9S .12 .12 .20 6.6 13 Tabor fine sandy am . . . . . . . . .. .04 6 .05 .60 .25 100 .23 .26 .45 6.8 15 Luf kin fine sandy loam . . . . . . . . .. .04 20 .06 .75 .15 125 .23 .17 .40 6.5 22 High damage average . . . . . . .. .05 89 .11 .86 .35 225 4.55 .40 7.12 7.4 91 Low damage average . . . . . . . . .04 18 .05 .65 .14 104 .18 .14 .34 6.7 82 basicity of less than 1%, while it may be extensive in soils with a basicity of more than 2%. There are exceptions to this general relationship. The sandy soils of East Texas may be taken in a general way to represent those in Which there is little or no damage by cotton root rot, while the soils of the Houston series of the black land area may be taken to represent those in which the damage is high. Table 1 contains a com- parison of‘ the chemical composition of some soils of the Houston series, representing the areas in which a high degree of damage is caused by root rot, and of the Norfolk, Kirvin, Ruston, Tabor, and Lufkin series, representing the areas in which very little_ damage is caused by the disease. On an average, the soils in which root rot causes great damage are higher in total phosphoric acid, active phosphoric acid, total nitrogen, total potash, acid soluble potash, active potash, lime, and magnesia than are the soils in which the occurrence of root rot is very limited. The soils which are favorable to root rot are also high in basicity and tend to be slightly alkaline in reaction, while the soils which are unfavorable are neutral or slightly acid in reaction. The favorable soils are heavy soils, while most of the unfavorable soils are more porous and open. RELATION OF THE OCCURRENCE OF COTTON ROOT ROT 9 The soils selected for the comparison given are extreme cases. The differ- ences found may have no connection with the degree of damage caused by the disease. a Composition of Soils in Four Areas as Related to Cotton Crop Losses V Caused by Root Rot The various areas outlined by Ezekiel and Taubenhaus (2), based upon reductions in yield of cotton caused by root rot, were taken as a basis for further study. In Table 2 is given the average chemical com- position of representative samples of the principal soil types for the four regions in which most of the cotton grown in Texas is produced. As noted above, these are averages of modal values for the individual soil types, not weighed in any way. The estimated reduction in yield of cotton averaged 6.5% or less in areas A and C (Table 2) comprising in general the East Texas Timber Country and the Gulf Coast Prairies. Most of the soils of these areas Table 1. Comparative composition of surface soils from areas in which root rot causes high and low degrees of dalnage Table 2. Approximate average composition of surface soils of principal soil types of areas of varying cotton crop losses caused by root rot Re- Phosphoric Desig- duc- Acid ~ Potash nation tion Ni- of Approximate in tro- Mag- Basic. Area soil area yie :1 gen Acid _ Lime nesia ity pH in of Total Ac- per Total solu- Ac- per per per Figure cotton per tive cent per ble tive cent cent cent per cent ppm. cent per ppm. cent 1 cent A East Texas Timber Country . . . . . . . . .. 0.7 .033 15 .050 .71 .14 110 .10 .17 .35 6.5 C Gulf Coast Prairie... 4.5 .032 38 .078 .78 .17 184 .39 .24 .71 6.5. D Blackland Prairies. . 12.9 .052 56 .099 .76 .28 207 1.97 .45 3.47 7.0 E Rio Grande Plain... 16.8 .061 53 .091 1.34 .70 456 0.61 .45 _1.34 7.4 are light soils, and principally fine sandy loams. The Lake Charles soils are the only heavy soils occupying a considerable acreage. Most of the cotton crop losses, however, occurred on the occasional heavy soils of the areas. The soils are deficient or low in nitrogen, phosphoric acid, potash, lime, magnesia, and basicity, and, as a rule, are slightly acid. The average cotton crop loss was quite high (12.9% and 16.8 %) on the soils of the Blackland Prairies and tl1e Rio Grande Plain. These soils are relatively quite high in phosphoric acid, nitrogen, potash, and basicity, contain considerable limestone, and are heavy in texture and alkaline in reaction. The results in general indicate that crops grown in the more fertile soils are damaged much more by the cotton root rot than are those grown in the less fertile soils. The results here reported are not in conflict with the conclusions of fig’, . 9/! 10 BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION Table 3. Relation of chenlieal composition of soil types to the degree of damage caused by cotton root rot. Upland surface soils Phosphoric ' cid Potash Ni- Mag- Basic- N0, tro- Acid Lime nesia ity pH of Area and Type Total Ac- gen Total solu- Ac- per per per 3am- per tive per per ble tive cent cent cent ples cent ppm. cent cent per ppm. cent Blackland Prairies-High damage: Bell clay . . . . . . . . . . . . . . .. .08 1S0 . 12 1.10 .45 300 2.40 .90 4.00 7,3 19 Crockett fine sandy 10am. . .03 40 .05 .75 . 11 150 .25 .25 .75 6,4 3 Crockett loam . . . . . . . . . . . .04 30 .09 .62 .20 300 .24 . 16 1 .00 6,4 3 Crockett clay 10am . . . . . . . . 03 10 . 10 . 6O . 12 175 . 35 . 25 . 5O 6. 2 6 Crockett clay . . . . . . . . . . . . .06 8 .14 .75 .40 27S . 60 . 90 1 . 60 7-. 3 2 Houston clay loam . . . . . . . .03 150 .07 .65 .30 100 .70 .30 2,00 7,6 7 Houston loam . . . . . . . . . . . .03 30 . 10 .80 .30 250 .50 .20 2.00 7.2 17 Houston clay . . . . . . . . . . . . .12 75 .16 1.00 .40 200 13.00 .60 20.00 7.6 28 Houston black clay . . . . . . . .08 100 .12 1.00 .40 350 4.00 .50 6.50 7.3 39 Blackland Prairie-Low damage: Wilson clay loam . . . . . . . . .04 25 .08 .80 .25 150 ,55 ,35 1,00 7_0 17 Wilson fine sandy loam. . . .03 25 .07 .60 .13 85 ,30 ,15 _50 6_4 10 Wilson clay . . . . . . . . . . . . . .05 20 .08 .60 .25 150 ,80 ,40 1,75 7_() 13 Gulf Coast Prairie-High damage: Victoria fine sandy loam. . .04 100 .06 2.00 .25 S00 .50 .30 _75 7,8 12 Lake Charles clay . . . . . . . . .04 20 .12 .70 .30 125 .55 .30 1,25 5,8 26 Gulf Coast Prairie-Medium damage: Lake Charles clay loam. . . .03 20 .08 .28 .08 65 .40 .30 .80 6,6 7 Gulf Coast Prairie-Low damage: Lake Charles fine sandy loam . . . . . . . . . . . . . . . .. .02 10 .05 .16 .05 47 .12 .08 .05 5,9 1 East Texas Timber Country -Low damage: Bastrop fine sandy loam. . .03 20 .04 1.00 .25 100 .30 .20 1.00 7,2 8 Kirvin fine sandy loam. . . .04 15 .05 .55 .10 100 .21 .13 .40 7,0 16 Lufkin fine sandy loam. . . .04 20 .06 .75 .15 125 .23 .17 .40 6.5 22 Lufkin clay 10am . . . . . . . . . .02 10 .07 .64 .12 90 .30 .15 .25 6,0 5 Tabor fine sandy 10am. . . . .04 6 .05 .60 .25 100 .23 .26 .45 6.8 15 Ruston fine sandy loam. . . .03 15 .03 .78 .09 95 .12 .12 .20 6,6 13 East Texas Timber Country- No damage: Norfolk fine sand . . . . . . . . .03 25 .04 .70 .09 90 .12 ,09 ,20 6,5 43 Norfolk fine sandy loam. . .03 25 .04 .45 .10 100 .11 ,11 ,27 6_7 16 Susequehanna clay . . . . . .. g .05 10 .08 .90 .15 150 ,30 ,22 ,,_,, 5_6 5 Susequehanna clay loam. . .02 10 .05 .80 .13 140 .19 .31 .42 6,2 3 Susquehanna fine sandy loam . . . . . . . . . . . . . . . .. .03 15 .05 .65 14 125 .13 ,11 ,30 6_2 43 RiofGrande Plain-High damage: Hidalgo fine sandy 10am.. .05 85 .07 1.15 .58 573 ,99 ,34 1,18 7_7 2 Victoria fine sandy loam. .06 100 .07 1.80 .32 500 .45 .30 1,00 7,6 12 RIoIGrande Plain-Medium ' damage: ‘ Duval fine sandy 10am. . . . .03 20 .06 1.00 .30 200 .30 .20 .30 6.6 12 Victoria clay 10am . . . . . . . .16 *500 .15 1.75 .90 600 .90 .60 1.60 7,4 4 Victoria clay . . . . . . . . .. .04 25 .13 1 .00 .60 400 .85 . 70 3.50 7.3 11 Webb fine sandy loam. . . . .05 25 .06 1.20 .42 350 .40 .40 .80 7,5 11 RiofiGrande Plain-Low damage: Brennan fine sandy loam. . .04 63 . 10 1,50 .80 *550 _5() _61 L00 __~ H 3 Edwards Plateau and Roll- ing Plains-Medium damage: Abilene clay loam . . . . . . .. .06 25 . 16 1 .25 .60 500 1.00 .60 1.05 7. 2 11 Edwards Plateau and Roll- ing Plains-Low damage: Miles fine sandy loam. . . . .04‘ 40 .05 1.20 .25 200 .30 .22 .50 7.1 15 Denton clay . . . . . . . . . . . .. .07 25 .15 1.00 .45 150 .60 5.00 7.3 14 *Excluded from averages. RELATION OF THE OCCURRENCE OF COTTON ROOT ROT 11 N0. Sam- ples (MN >4 OOJQOOUHPDUI 10 wow: 19 16 21 ’ Table 4. Relation of chemical composition of soil types to the degree of damage caused by cotton root rot. Upland subsoils Phosphoric Acid Potash Ni- Mag- Basic- tro- “ Acid Lime nesia ity pH Total Ac- gen Total so1u_- Ac- per per per per tive per per ble tive cent cent cent cent ppm. cent cent per ppm. cent Blackland Prairies-High damage: Bell clay . . . . . . . . . . . . . . .. .07 70 .07 1.00 .50 200 2.50 .60 5.00 7.4 Crockett fine sandy loam. . .03 15 .06 .75 .30 1S0 .60 .40 1.25 7.0 Crockett loam . . . . . . . . . .. .04 45 .05 .65 .45 150 1.20 .80 2.50 7.0 Crockett clay loam . . . . . . . .04 10 .07 .85 .40 150 .50 .45 .70 6.3 Houston loam . . . . . . . . . . . .03 12 .06 .80 .27 50 .45 .30 1 . 10 6.5 Houston clay loam . . . . . .. .03 10 .06 .75 .50 150 2.25 .45 4.50 7.6 Houston clay . . . . . . . . . . .. .10 10 .08 1.00 .35 65 20.00 .60 10.00 7.5 Houston black clay . . . . . . . .08 35 .08 .80 .40 150 5.00 .60 5 .00 7.3 Blackland Prairies-Low damage: Wilson fine sandy loam. . . .03 15 .06 .65 .25 125 .40 .40 .95 6.6 Wilson clay loam . . . . . . . . .04 15 .07 .08 .25 125 .55 .40 1.25 7.0 Wilson clay . . . . . . . . . . . .. .04 12 .06 .09 .25 125 1.00 .40 1.50 6.8 Gulf Coast Prairies-High damage: Victoria fine sandy loam. . .05 100 .06 1.60 .40 275 .45 .35 1.00 7.6 Lake Charles clay . . . . . . .. .03 10 .07 .60 .35 150 .60 .50 1.25 6.5 Gulf Coast Prairie-Medium damage: Lake Charles clay 10am. .. .02 15 .04 .25 .12 50 .50 .40 1.00 7.2 Gulf Coast Prairies-Low damage: Lake Charles fine sandy loam . . . . . . . . . . . . . .. .02 9 .04 .20 .07 58 .13 .12 .20 5.9 East Texas Timber Country- Low damage: Bastrop fine sandy loam. . .04 10 .05 1.10 .50 200 .50 .40 .60 6.8 Kirvin fine sandy loam. . . .06 10 .05 .65 .30 100 .25 .25 .60 6.4 Lufkin fine sandy loam. . . .03 10 .05 .80 .24 100 .40 .32 .80 6.5 Lufkin clay loam . . . . . . . . . .02 13 .04 .55 .20 85 .35 .25 .60 6.0 Tabor fine sandy loam. . . , .04 7 .04 .60 .25 100 .28 .27 .55 6.8 East Texas Timber Country- No damage: Norfolk fine sand . . . . . . .. .02 15 .02 .70 .09 75 .11 .10 .12 6.3 Norfolk fine sandy loam. . .03 10 .04 .80 .15 100 .14 .12 25 6.2 Susequehanna clay . . . . . . . .06 5 .05 .75 .40 250 .25 .48 .55 5 .9 Susequehanna clay 10am. . .03 8 .04 1.30 .18 125 .20 .20 .34 5.8 Susquehanna fine sandy loam . . . . . . . . . . . . . . . . . .03 9 .04 .88 .24 125 2O .28 .53 6.0 Rio Grande Plain-High damage: Hidalgo fine sandy 10am . . . 05 100 . O6 1 .40 . 59 435 3 . 52 . 73 5 . 95 7 . 8 Victoria fine sandy 10am. . .049 100 .05 1.60 .40 350 .53 .30 2.00 7.8 Rio Grande Plain-Medium damage: Duval fine sandy 10am. . .. .041 10 .05 1.10 .30 200 .20 .27 .34 7.0 Victoria clay . . . . . . . . . . . . .03 135 . 11 1.40 .65 250 . 87 1.00 3.80 . . . .. Victoria clay loam . . . . . . . . 12 650 .06 2.00 . 75 400 2.80 .78 7.80 7.5 Rio Grande Plain-Low damage: Brennan fine sandy loam. . .03 40 .05 1.80 .57 500 .28 .47 .59 7.5 Edwards Plateau and Roll- ing Plains-Medium damage: Abilene clay loam . . . . . . . . .06 30 .09 1.25 .65 300 4.00 .60 4.50 7.5 Edwards Plateau and Roll- ing Plains-Low damage: Denton clay . . . . . . . . . . . . . .06 10 .08 1.00 .50 100 .65 .70 10.00 7.6 Miles fine sandy loam . . .. .04 15 .05 1.40 .50 250 .40 .40 .65 7.3 12 BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION Jordan et al. (8) that the use of suitable fertilizers, by acceleration of maturity, may be a means of evading losses due to progressive killing of cotton plants by root rot 0n heavily infected fields, or that the increases in total yield by means of the fertilizers may‘ more than compensate for losses that would otherwise occur. The work here reported shows that root rot iS_I1’lOI‘8 destructive on the fertile soils than in the poor soils, while the work of Jordan shows that the use of fertilizers may result in producing a larger crop of cotton before the plant is killed by the disease. Relation of Composition of Soil Type to the Degree of Damage Caused by Cotton Root Rot ~ As already stated, within the same area there are great differences in the damage caused by cotton root rot on different soil types. On some soil types crop losses may be very great, while on other soil types the damage is comparatively light. It is somewhat difficult to classify some of the soil types with respect to the damage caused by root rot, since there is a variation in the damage caused by the disease in different years. Information regarding the relative damage caused by root rot on various soil types within the same general area have been collected from exten- sive field observations by Dr. J. J. Taubenhaus of the Division of Plant Pathology and Physiology and Mr. W. T. Carter of the Division of Soil Survey. They classified the soil types according to whether the disease caused high, medium, low, or no damage to susceptible plants grown on the soils. ' The average chemical composition of surface soils (mostly 0-7" in depth) of these individual types is given in Table 3. Similar analyses for the subsoils (mostly 7”-19”) are given in Table 4. In these tables, the soil types are grouped first by the general soil region in which they occur, and then by the degree of damage caused by cotton root rot on the type as a whole. Only upland soils are given, for reasons which will be dis- cussed later. The analyses used are those of typical soils collected by the field agents of the Bureau of Chemistry and Soils in connection with their surveys of various counties in Texas. In considering the data presented, it must be remembered that indi- vidual samples of a given soil type may differ considerably in composition; the figures given are those which are considered as approximate modal values. In the case of most soil types, there may be exceptional local areas ‘not conforming to the estimate for damage or the values given for chemical composition. For example, on some areas of the Wilson clay loam, there is either no damage or it is very small. However, other areas of Wilson clay loam are known in which the loss in a given year has been as high as 60 per cent. Individual variations in composition may be responsible for part of this variation. The areas of Wilson soils on which high damage occurs are calcareous and have an alkaline reaction, while Wilson soils on which little damage by root rot occurs are non-calcareous and have a slightly acid reaction, RELATION OF THE OCCURRENCE OF COTTON ROOT ROT 13 Table 5. Relation between average chemical composition of soil types and degree of damage caused by cotton root rot High Medium 3' Low No Damage Damage Damage Damage Total Phosphoric acid, per cent: Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . .055 . . . . . . . . . . .045 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . .040 .030 .020 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .033 .032 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . .055 .070 .040 . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .060 .055 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . .053 .060 .039 .032 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 120 112 Active Phosphoric acid, parts per million: Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . 66 . . . . . . . . . . 23 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . 60 20 10 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14 17 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . 143 25 63 . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 25 32 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . 77 24 23 17 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1S0 240 Nitrogen, per cent: ' Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . .106 . . . . . . . . . . .083 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . . .090 .080 .050 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .050 .052 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . 070 .100 .100 . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 160 .100 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . .098 . 108 .069 .052 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13 . 10 Total Potash, Per cent: ~ Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . .82 . . . . . . . . . . .67 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . . 1.35 28 .16 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .74 . 70 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . 1.48 1 .24 1.50 . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1 .25 1 . 10 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . 1.00 1.07 .79 . 70 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1.75 2.00 Acid Soluble Potash, per cent: Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . .30 . . . . . . . . . . . 21 . . . . . . . . . . Gulf Coast Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . .28 .08 .05 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .16 .12 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . .45 .55 .80 . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 60 .35 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . .32 .48 .41 .12 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .75 . 77 Active Potash, parts per million: Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . 233 . . . . . . . . . . 130 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . 312 65 47 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 101 121 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . 535 392 . . . . . . . . . . . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 500 175 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . 292 355 116 121 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 300 385 Lime, per cent: Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . 2.44 . . . . . . . . . . .55 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . .53 .40 .12 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .23 .17 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . .72 .61 .50 . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1.00 .30 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . 1.89 .64 .33 . 17 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . , . . . . . . . . . . . . . . . . . . . . . . . . . . 2.91 2.87 Magnesia, per cent: Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . .45 . . . . . . . . . . .30 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . .30 .30 .08 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 17 . 17 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . .32 .48 .61 . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 60 .41 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . .41 .47 .26 .17 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .65 .55 14 BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION Table 5. Relation between average chemical composition of soil types and degree of damage caused by cotton root rot (Continued) High Medium Low No Damage Damage Damage Damage Basicity, per cent: Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . 4. 26 . . . . . . . . . . 1.08 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . 1.00 .80 .05 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .45 .24 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . 1.09 1.55 1.00 . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1.05 2. 75 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . 3.26 1.34 0.96 .24 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7.20 3.35 PH= . . Blackland Prairies . . . . . . . . . . . . . . . . . . . . . . . . . . 7.0 . . . . . . . . . . 6. 8 . . . . . . . . . . Gulf Coast Prairie . . . . . . . . . . . . . . . . . . . . . . . . . . 6.8 6.6 5.9 . . . . . . . . . . East Texas Timber Country . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6. 7 6. 2 Rio Grande Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . 7.6 7. 2 . . . . . . . . . . . . . . . . . . . . Edwards Plateau . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7.2 7.2 . . . . . . . . . . Average of all types . . . . . . . . . . . . . . . . . . . . . . . . . 7.1 7.0 6. 7 6. 2 Alluvial . . . . . . . . . . . . . . . . . . . . . . . . . . . . .._ . . . . . . . . . . . . . . . . . . . . . . . . .. 7.2 7.4 The analyses presented in Table 3 Were averaged by areas and the results are presented in Table 5. The analyses for the soil types, as grouped in Table 3 With respect to degree of damage, Were also averaged regardless of the area in which they occur, and these averages are given as “Average of all types.” Values for active phosphoric acid in the ‘ Victoria fine sandy loam and active potash in the Brennan fine sandy 10am were omitted from the averages in Table 5, because they were very much out of line With the other soil types in the same groups and for the further reason that, as noted in the last column of Table 3, the number of samples of these two types was quite small (4 and 2) and their inclu- sion would have resulted iii an incorrect weighted average. Averages for alluvial soils (see also Table 7) are given in Table 5, but are not included in the averages of the upland soil types. The final averages for each constituent were calculated to relative values with 100 as the quantity of the constituent in soil in which damage was high. These results are given in Table 6. Table 6. Relative average composition of soils on which cotton root rot caused dificrent degrees of damage I High Medium ~ Low No Damage Damage Damage ' Daliiagg Total phosphoric acid . . . . . . . . . . . . . . . . . . . . . . . . . . . 100 113 73 60 Active phosphoric acid . . . . . . . . . . . . . . . . . . . . . . . . . . 100 31 30 22 Nitrogen . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 100 110 71 53 Total potash . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 100 107 79 70 Acid-soluble potash. . . . . . . 100 153 128 53 Active potash . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 100 122 40 41 Lime . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 100 34 17 9 Magnesia . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 100 115 63 41 Basicity . . . . . . . . . . . . . . . . . . . ._ . . . . . . . . . . . . . . . . . . . 100 41 29 8 Reciprocalof H-ion concentration . . . . . . . . . . . . . . .. 100 80 44 14 Average . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 100 91 57 36 RELATION OF THE OCCURRENCE OF COTTON ROOT BOT 15 The data for subsoils are given in Table 4, but they were not sum- marized and averaged, since they show essentially the same trends as do the data for the surface soils which are presented in Tables 5 and 6. In the following discussion of the data presented in Tables 3 to 6 each element is considered separately. Phosphoric acid. Total phosphoric acid in groups of soil types on which the high damage by root rot occurred was about two-thirds greater than that in the low and no damage groups. Active phosphoric acid was about three times as great in the high damage group as in the medium damage and low damage groups, and five times as great as in the group with no damage. Nitrogen. Nitrogen in the high damage group was about one-half higher than that in the 10W damage group, and twice as high as that in the group without damage. Potash. Total potash was about one-half greater in the high damage group than in the no damage group, and one-fourth higher than in the low damage group. Acid-soluble potash showed considerable variation in the high, medium, and low damage groups, but the quantity in the high damage group Was about twice that in the group on which the disease caused no damage. Active potash in the high damage group was approxi- mately three times that i11 the low damage and no damage groups. Lime and Basicity. Lime content and basicity are intimately associated in soils, since the major part of the basicity of highly basic soils is due to the presence of calcium carbonate in the soil. Differences in lime content and basicity were greater than those secured with any other chemical constituent. Lime and basicity were ten or twelve times greater in the high damage group than in the no damage group, and several times greater than in the medium damage and low damage groups.‘ pH. The pH of the different groups does not vary greatly; all groups have pH values very close to the neutral point (pH 7.0). The pH is a logarithmic value related to hydrogen ion concentration. When the hydrogen ion concentrations corresponding to the pH values are used, differences in the several groups become apparent. The hydrogen ion concentrations in the loW and no damage groups are considerably higher than those in the high and medium groups. In the calculation of the relative concentrations (Table 6), the reciprocal of the hydrogen ion concentration was used, in order to keep the value of the high root rot group at 100, as in the other determinations. The relative value of the reciprocal in the high damage group is about five times that in the no damage group. Summary. The data can perhaps best be summarized by the state- ment that, in general, soils in which a high degree of damage is caused by root rot are those in which active phosphoric acid, active potash, lime, basicity, and pH are high. Of these, perhaps the most important are high lime and high basicity, calcareous soils in almost all cases providing an_ excellent environment for the rapid developmentof the disease. 16 BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION Composition of Some Alluvial Soils Only upland soil types have so far been discussed. Alluvial soils are soils laid down in the river bottoms, subject to occasional or frequent overflow with consequent deposition of soil material from all of the soil areas through which the streams pass, and form a special group of soils Table 7. Average composition of some important alluvial soil types Phosphoric Acid Potash Ni- Mag- Basic- No. . tro- Acid Lime nesia ity pH of Soil Type Total Ac- gen Total solu- Ac- per per per Sam- - per tive per per ble tive cent cent cent pies cent ppm. cent cent per ppm. cent Surface Soils: Ochlockonee clay . . . . . . . . .085 70 .140 .80 .33 270 .90 .45 1.70 6.8 6 Ocklockonee silty clay loam . . . . . . . . . . . . . . . .. .060 34 .055 1.35 .25 12S .74 .48 .35 5.8 6 Ocklockonee fine sandy loam . . . . . . . . . . . . . . . . . .045 30 .060 .90 .10 130 .18 .14 .50 6.6 99 Trinity clay . . . . . . . . . . . . . . 125 5O . 1S0 1 25 . 60 250 3 . 00 . 75 5 .00 7 . 3 42 Frio clay . . . . . . . . . . . . . .. .150 155 .150 1 35 .80 330 7.50 .85 15.00 7.3 12 Catalpa clay . . . . . . . . . . .. .130 35 .120 1 25 .63 275 4.00 .60 10.00 7.3 16 Frio fine sandy 10am . . . . . . .060 130 .070 1 10 .30 250 .50 .20 85 7.3 11 Frio loam . . . . . . . . . . . . . . . .085 . 200 .110 1 50 .50 430 5.00 .55 9 50 7.4 11 Miller fine sandy loam . . . . .070 200 .060 1 60 .30 250 .30 .25 60 7.3 10 Miller clay . . . . . . . . . . . . . . . 125 125 . 100 2 00 .85 300 5 .00 1 .00 10 00 7 .3 11 Pledger clay. ._ . . . . . . . . . .. .070 250 .080 2 30 1.20 250 3.00 2.50 5 00 7.5 3 Subsoils: Ocklockonee clay . . . . . . . . .045 25 .080 .75 .30 175 .70 .43 1.30 6.8 7 Ocklockonee silty clay loam .060 34 .055 1 35 25 125 24 48 35 5 . 8 6 Ocklockonee fine sandy loam . . . . . . . . . . . . . . . . . .040 15 .045 1.00 10 80 .20 . 15 45 6.0 9 Trinity clay . . . . . . . . . . . . . . 125 100 . 150 1 . 25 . 55 250 3 . 00 . 75 5 00 7 . 3 42 Catalpa . . . . . . . . . . . . . . . .. .115 35 . 125 1.25 .55 250 8.00 .75 15 00 7.4 17 Frio clay . . . . . . . . . . . . . . .. .125 35 .095 1.20 .75 150 6.50 .75 12 00 7.5 12 Frio fine sandy loam. . . . . .045 58 .050 1 .25 42 200 1.00 .30 2 00 7.4 16 Frio loam . . . . . . . . . . . . . . . .058 47 .065 0.95 32 290 5.40 .65 9 50 7.6 12 Miller fine sandy loam. . . . .050 50 .045 1.50 47 200 2.50 .40 5 00 7.7 10 Miller clay . . . . . . . . . . . . . . . 100 100 . 070 2 .00 .85 200 5 .00 1.00 10 00 7.5 12 Pledger clay . . . . . . . . . . . . . .070 250 .080 2.30 1.20 250 3.00 2.50 5 00 7.5 3 with respect to damage by cotton root rot. In general, the damage caused by root rot on alluvial soils is low, although occasional areas occur in which considerable damage is done. The disease has been artificially introduced into a typical river bottom soil (19) and reappeared on the cotton crop of the following year. This indicates that environmental factors other than the nature and composition of the alluvial soils may prevent infestation of the soil or inhibit the growth of the organism. Rea (13) found the sclerotial resting stage of the fungus in alluvial soils as well as in upland soils. The average composition of a number of important alluvial soil types is given in Table 7. In general, the soils are considerably more fertile than the general average of the soils of the various soil regions in which they occur. Lime, basicity, and pH are all considerably higher. In so far as the chemical composition of the alluvial soils is concerned, then, the disease would be expected to do a great deal of damage on these ‘soils. The fact that it does not do so RELATION OF THE OCCURRENCE OF COTTON ROOT ROT 17 l must be attributed to factors other than the chemical composition of the A soils here discussed. The Composition of Adjacent Soils of Same Type Bearing Diseased and Disease-free Cotton Plants Cotton root rot has a tendency to infect plants in irregular spots sur- rounding the center of infection. These spots vary considerably in size. The areas on which plants are not infected may be favorable to the disease, but the disease may not have progressed far enough to have reached them. The physical and chemical differences between adjacent areas on which the plants are diseased or healthy may be insignificant. In spite of this fact, it was considered desirable to make some analyses of samples of paired soils from spots bearing diseased and disease-free Table 8. Comparison of composition of adjacent samples of the same type bearing diseased (R) and (lisease-free (F) cotton plants of the same type l Phosphoric Acid Nitrogen Potash Basicity pH Total Active Total Active Depth R F R F R F in- R F R F per per R F R F per per ches per per ppm ppm cent cent per per ppm ppm cent cent cent cent cent cent Crockett fine sandy loam . . . . . . . . . . . .. 0- 7 .035 .037 12 1‘3 .062 .082 .41 .37 120 103 .27 .27 6.8 6.1 7-14 037 043 6 6 067 .083 34 37 55 49 .25 .28 6.9 5.9 - 14-24 .044 .043 5 6 .088 .092 .51 .56 91 101 .55 .30 6.1 5.5 Crockett clay loam.. 0- 7 .052 .051 11 17 .148 .111 .61 .81 175 130 1.22 .82 6.1 5.9 7-19 .058 .035 7 7 .087 .069 .80 .72 107 99 1.891.34 7.3 5.9 Lufkin fine sandy loam 0- 7 .040 .043 102 98 .061 .061 .90 .88 235 280 1.14 .33 7.4 7.1 7-19 .016 .013 13 15 .084 .084 .86 .64 147 357 1.36 1.10 7.2 6.4 Wilson fine sandyloam 0- 7 .034 .035 25 34 .132 .123 1.161.18 136 112 .38 .30 6.9 6.4 7-16 019 021 9 9 050 0531 22 1 19 58 51 .14 .18 7.1 6.5 16-24 020 019 5 6 .093 .083 .961.01 107 81 .78 .83 6.7 6.8 Wilson clay loam. . .. 0- 7 .049 8 11 .136 .146 .30 .33 105 105 .901.00 5.8 5.6 7-19 .048 .041 9 6 .114 .079 .34 .31 101 80 1.18 1.17 5.8 5.9 Wilson clay . . . . . . . .. 0- 7 .042 .027 86 14.052 .052 .74 .92 244 131 1.161.18 7.2 6.7 - 7-19 047 024 21 15 049 049 67 67 142 100 1.01 1.41 6.9 6.7 plants. The samples were collected by Dr. J. J. Taubenhaus of the Division of Plant Pathology and Physiology. Samples of soil from areas on which plants were infected or uninfected were analyzed. The results are given in Table 8. Many of the differences between the samples from the two areas are well within the range of error of the analytical determination. The reactions (pH) of the root-rot-free areas of the Crockett fine sandy loam and clay loam and the Wilson fine sandy loam were slightly lower than those for the infected areas, and may account in part for the absence of the disease in the uninfected areas. However, they are so nearly neutral that the slight increase in acidity of the uninfected area could probably have had comparatively little influence on the control of the disease (3, 16). This is emphasized by the fact that in the Wilson clay loam, the most acid soil studied, there was practically no difference in pH between the area carrying the infected plants and that carrying uninfected 18 BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION plants. The active potash in the soil of the infected area of the Wilson clay is slightly higher than that in the root-rot-free area, but 0n the other hand that of the root-rot-free area of the Lufkin fine sandy loam is con- siderably higher than that of the infected area, while there is no significant difference between the two areas with the other soil types. No other sig- nificant difference occurred. The data given in Table 8 emphasize the fact that the chemical co1npo- sition of the soil is only one of a number of factors which determine the occurrence and virulence of the cotton root disease. It should be repeated in this connection that discussion of the relation of chemical composition of the soil to the damage caused by root rot, as given in this bulletin, is based upon general, broad relationships and is not applicable to particular local areas, in which local factors other than the chemical composition of the soil may determine whether or not the disease causes serious damage at any particular time. General Discussion The preceding work shows that in general a soil which contains appre- ciable amounts of lime and is slightly alkaline, of good fertility, and a loam or clay in texture is, in general, favorable to root rot. On the other hand, a soil which is 10W in lime, slightly acid or acid, and sandy in character, is unfavorable to the disease. The extent and rapidity with which the cotton root rot fungus spreads, its virulence (or the rapidity with which it grows and kills the plant), and its persistence (or ability to continue over from one season to another), all vary in different soils and during different seasons. Of the various factors concerned with differences in the growth of the fungus due to soil differences, the most important appear to be the pH and basicity as has already been pointed out (3, 4, 16). Much work has been done on the relation of the organism to the acidity of the soil (3, 4, 16), and some of the results obtained indicate that the presence of sufficient quantities of lime are of more importance to the favorable growth of the organism than are large quantities of nitrogen, phosphoric acid, or potash (4). Variations in the relative damage to plants caused by differences in soil fertility may perhaps be associated with variations in the chemical composition of the roots of‘ the plants. Since the root rot fungus feeds upon the roots, the roots of plants which have been grown in some soils may be slightly more favorable to the growth of the fungus than they are when grown in other soils. This is a matter that requires further investi- gation. Ezekiel, Taubenhaus, and Fudge (5) have shown that extracts from the roots of monocotyledonous plants (Which are not affected by cotton root rot) contain substances which inhibit the growth of root rot and which are apparently absent in extracts from susceptible dicotyledo- nous plants. The greater persistence of the cotton root rot in some soils than in others may be due to several causes. Sclerotia may be produced in RELATION OF THE OCCURRENCE} OF COTTON ROOT ROT 19 greater numbers in some soils than in others. Some soils, by obstruc- tion of the access of air to the sclerotia or otherwise, may delay germina- tion for years, thereby causing the disease to persist for a longer time than in others. The moisture-holding capacity of heavy soils is much greater than that of light soils. The moisture may be more favorable to the growth of the organisms (20) in some soils than in others. The obstruction of air may hinder the decay of roots, so that they continue to be a suitable medium for the food of the organism for a longer period in some soils than in others. The Weeds which serve as hosts may live better in some soils than in others. These considerations lead to the conclusion that a favorable root medium may favor the formation of sclerotia, While ‘the physical character of the soil may be a factor in preserving the roots, the sclerotia, or the fungus over the winter or for a longer period. SUMMARY Soils of the Houston series, typical of the Blackland prairies, on which root rot causes a high degree of damage, are higher in total phosphoric acid, active phosphoric acid, total nitrogen, total potash, acid-soluble potash, active potash, lime, and magnesia, than are the fine sandy loams of the Norfolk, Kirvin, Ruston, Tabor, and Lufkin series, typical of the East Texas Timber Country, on which root rot is very limited. The Houston soils are also high in basicity and tend to be slightly alkaline in reaction (pH), While those on which root rot is of slight occurrence are of loW basicity and are neutral to slightly acid. Soils of the East Texas Timber Country and the Gulf Coast Prairies, on which losses of cotton due to root rot were low, are mostly light in texture, deficient or .loW in phosphoric acid, nitrogen, potash, lime, and magnesia, low in basicity, and slightly acid in reaction. Soils of the Blackland Prairies and Rio Grande Plains, on which losses of cotton due to root rot were high, are chiefly heavy in texture and high in fertility, as indicated by the content of phosphoric acid, nitrogen, and potash. They also have a high basicity, contain considerable limestone, and are alkaline in reaction. ' The principal soil types of Texas were grouped according to the degree of damage caused by cotton root rot’. On an average, soils on which no damage was caused by the disease contained only about two-thirds as much total phosphoric acid, one-half as much nitrogen, total potash, and magnesia, one-third as much acid soluble potash, one-fifth as much active phosphoric acid and active potash, one-seventh as much lime and basicity, and seven times as great a concentration of hydrogen ions in the soil suspension, as did soils on which damage was high. The average com- position of soils on which medium and low degrees of damage were caused by the disease was, in general, intermediate between that of the soils in the high damage and no damage groups, although several excep- tions occur. 20 BULLETIN NO. 522, TEXAS AGRICULTURAL EXPERIMENT STATION Alluvial soils, or soils of river bottoms, were relatively quite high in fertility and basicity. The 10W damage on these soils must be due t0 other factors Which counteract the high fertility and basicity. The chemical compositions of adjacent areas of a number of types, one area of which contained active root rot while the other was free of the disease, were practically identical, with the possible exception of pH, indicating that chemical composition is only one of many factors influenc- ing the occurrence and virulence of the root rot disease. There is a possibility that chemical composition of the soil may slightly affect the composition of the roots of the cotton plant so that plants grown on limestone soils are more susceptible to cotton root rot than are those grown on non-calcareous sandy soils. The physical or chemical charac- teristics of the soil may affect the production of sclerotia, their period of germination, the decay of roots in which the fungus may survive. and other conditions which affect the over-ivintering of the root rot fungus, ‘ so that clay or loamy limestone soils are more favorable to the carry-over of the disease than are slightly acid sandy soils. . REFERENCES 1. Carter, W. T., 1931. The soils of Texas. Texas Agr. Exp. Sta. Bul. 431. 2. Ezekiel, Walter N., and Taubenhaus, J.‘ J., 1934. Cotton crop losses from Phymatotrichum root rot. Jour. Agr. Res. 49:843. 3. Ezekiel, Walter N., Taubenhaus, J. J., and Carlyle, E. C., 1930. Soil-reaction effects on Phymatotrichum root rot. Phytopath. 20:803. 4.~ Ezekiel, W. N., Taubenhaus, J. J., and Fudge, J. F., 1931. Concen- tration of salts and soil reaction as affecting growth of the root rot fungus in the soil. Forty-fourth Annual Report, Texas Agr. Exp. Sta. Also Phytopath. 22:9 (Abst.), 1932. 5. Ezekiel, Walter N., Taubenhaus, J. J., and Fudge, J. F., 1932. Growth of Phymatotrichum omnivorum in plant juices as correlated with resistance of plants to root rot. Phytopath. 22:459. 6. Fraps, G. S., 1915-1933. Bulletins on the chemical composition of the soils of Texas. Texas Agr. Exp. Sta, Buls. 173, 192, 213, 244, 301, 316, 375, 430, 443, 482. _ 7. Fraps, G. S., and Carlyle, E. C., 1929. The basicity of Texas soils. Texas Agr. Exp. Sta. Bul. 400. 8. Jordan, H. V., Dawson, P. R., Skinner, J. J., and Hunter, H. J., 1934. The relation of fertilizers to the control of cotton root rot in Texas. U. S. D. A. Tech. Bul. 426. 9. King, C. J., Loomis, H. F., and Hope, Claude, 1931. Studies on sclerotia and mycelial strands of the cotton root rot fungus. Jour. Agr. Res. 42:827. 10. McNamara, Homer'C., and‘ Hooton, Dalton R., 1929. Studies of cotton root rot at Greenville, Texas. U. S. D. A. Cir. 85. 11. 12. 13. 14. 15. 16. 17. 18. 19. 20. 21. _Rea, H. E., 1933. RELATION OF THE OCCURRENCE OF COTTON ROOT ROT 21 Neal, David C., and Ratliffe, George T.,1931. with the cotton root rot fungus Phymatotrichum omnivorum. Agr. Res. 49:681. Neal, David C., Wester, R. E., and Gunn, K. C., 1934. and life‘ history of the cotton root rot fungus in Texas. Res. 49:539. Infection experiments Jour. Morphology Jour. Agr. Forty-sixth annual report, Texas Agr. Exp. Sta. Taubenhaus, J. J., and Ezekiel, Walter N., 1930. on Phymatotrichum root rot. Amer. Jour. Bot. 17:554. Taubenhaus, J. J., and Ezekiel, Walter N., 1930. Studies on the overwintering of Phymatotrichum root rot. Phytopath. 20:761. Taubenhaus, J. J., and Ezekiel, Walter N., 1930. and its control. Texas Agr. Exp. Sta. Bul 423. Taubenhaus, J. J., and Ezekiel, Walter N., 1933. Check list of dis-V/ eases of plants in Texas. Trans. Texas Acad. Sci. 16:5. Taubenhaus, J. J., Ezekiel, Walter N., and Killough, D. T., 1928. Relation of cotton root rot and Fusarium Wilt to the acidity and alkalinity of the soil. Texas Agr. Exp. Sta. Bul. 389. Taubenhaus, J. J., Ezekiel, Walter N., and Lusk, J. P., 1931. Pre- liminary studies on the effect of-fiooding on Phymatotrichum root rot. Amer. Jour. Bot. 18:95. Taubenhaus, J. J., and Dana, B. F., 1928. The influence of moisture and temperature on cotton root rot. Texas Agr. Exp. Sta, Bul. 386. Taubenhaus, J. J., and Killough, D. T., 1923. Texas root rot of cotton and methods of its control. Texas Agr. Exp. Sta. Bul. 307. Cotton root rot Recent studies 17