zq< Criteria for the Diagnosis of Nutrient Status and Guid- ance of Fertilization and Soil Management Practices HOMER D. CHAPMAN WBm NHp -:-/. : ;.y: : y^;:z--y / y;.-;,:. :■;■. W':'y> '■■■■■ "'■;■':;-':■ V : '-' ; - CONTENTS The purpose of leaf and soil analyses 1 Initial orchard appraisal 2 Means for diagnosing nutritional status 2 Leaf analysis standards 2 Methods of leaf sampling 5 Methods of analysis 7 Soil analysis standards 8 Methods of soil sampling and handling 8 Time schedule for leaf and soil analyses 12 Method of recording results 12 Methods of controlling and correcting mineral deficiencies and excesses . . . . 12 Summary 12 Acknowledgments 13 Literature cited 49 THIS MANUAL is one of a series published by the University of California Division of Agri- cultural Sciences and sold for a charge based on returning only a portion of the production cost. By this means it is possible to make available publications which, due to relatively high cost of production or limited audience, would otherwise be beyond the scope of the Division's publishing program. LEAF and SOIL ANALYSIS in CITRUS ORCHARDS ERRATA Page 3; Column 2; Line 5 should read "(see table 7)" instead of "table 8." Page 6; Column 2; Line 21 should read "(see second U, page 7)" instead of ". . . page 6." Pages 23 and 24; Table 2; Columns 2 and 3 captions should read "table 7" instead of "table 8." Page 38; Table 5; Column 2, last section, should read "Water-soluble P by Bingham (1949) method in ppm extract" instead of ". . . dry soil." Page 45; Table 7; column 3; last entry at bot- tom of page should read ". . . correction by use of magnesium nitrate spray at the rate of 10 lbs/100 gal" instead of ". . . 10 per cent magnesium nitrate foliar spray." Page 48; Table 7; column 3; at top of page should read "...magnesium nitrate at 10 lbs/100 gal" instead of "...10 per cent concentration. . . ." Man. 25 Criteria for the Diagnosis of Nutrient Status and Guidance of Fertilization and Soil Management Practices HOMER D. CHAPMAN UNIVERSITY OF CALIFORNIA DIVISION OF AGRICULTURAL SCIENCES Agricultural Experiment Station — Extension Service LIBRARY UNIVERSITY OF CALIFORNIA DAVIS can now be taken out of citrus fertilization by systematic use of leaf anal- yses supplemented by appropriate soil tests and such other information as may be obtained from visual symptomology, general knowledge of soils, past fertilizer and management practices, and composition of irri- gation waters. This manual was prepared in order to: ( 1 ) Provide the commercial laboratory operator with the soil and plant analysis standards or criteria currently available for assessing the nutrient status of citrus orchards and the detailed methods of sampling and handling which must be followed to assure results of satisfactory accuracy. (Also included are methods of correcting mineral deficiencies and excesses.) (2) Inform citrus growers, extension service workers, and others as to the present status of these diagnostic tests and methods of control. (3) Reveal to the research man the many blind or uncertain spots in existing information. No attempt has been made to discuss the theoretical basis for soil and plant analysis. Appropriate references to published work covering these aspects are given in the text. THE AUTHOR Homer D. Chapman is Professor of Soils and Plant Nutrition, and Chemist, University of California Citrus Experiment Station, Riverside, California. JANUARY 1960 THE PURPOSE OF LEAF AND SOIL ANALYSES The successful use of leaf and soil analyses requires proper sampling and handling techniques, the use of accurate methods of analysis, periodic leaf analysis for some, although not all, constituents and periodic soil analyses. In starting a program of nutritional eval- uation and fertilizer guidance, an initial orchard appraisal is useful. After this, a complete check-up need be made only at five-year intervals, or longer, but annual leaf analyses for some constituents will be desirable at least at the outset. Rule-of-thumb fertilizer practices or gen- eral recommendations are not only of little value in citrus orchard fertilization today but may produce soil problems hard to over- come, decrease yields, and increase fertilizer costs. Experience has shown that no set program is good for all time in any given orchard. Change is one of the immutable laws of nature and it applies to soil-manage- ment practices as well as to anything else in this world. The tree must secure an adequate amount of 14 mineral elements from the soil. This in itself is not always easy to provide for and a further complication is that either because of improper balance initially, or because of wrong fertilizer prac- tices, and/or the use of certain irrigation waters, some constituents accumulate in amounts sufficient to be toxic, or unbal- ance takes place in which the solubility or absorbability, or transport, or use within the plant is interfered with. In addition to all this, plant growth is affected by many, if not all, the chemicals, other than the afore- mentioned 14, in the root zone; the nutrient requirements of various citrus species are variable, as is the foraging power or ab- sorptive ability of different rootstock -scion combinations, plus which climate, soil tem- perature, moisture, aeration, and biological factors impose many other complications and qualifying circumstances. Realizing all of these complex problems, students of soil fertility diagnosis began to recognize many years ago that soil analysis alone could not provide adequate fertilizer guidance for citrus, and began to study the possibility of using plant analysis and visual symptoms as auxiliary aids. Independent research began in several parts of the world more than thirty years ago with the result that both in South Africa and California, a system of leaf analysis and tentative leaf- analysis standards and techniques of re- markable similarity came into being (Bath- urst, South Africa, 1943, 1944, \9\4a; Chap- man et ah, California, 1943; 1944; 1946; 1949; 1950). 1 Based on more recent research and experience in Florida, Reuther and Smith (1954; 1954a) likewise developed a set of standards somewhat similar to those of Bathurst and Chapman. More recently Reu- ther, Embleton, and Jones (1958) have pub- lished a table of standards similar in general to those published previously by Reuther et al. Meanwhile, some of the large citrus estates in South Africa have been putting leaf analysis to work (private conversations with Dr. Jaap deVilliers, of Zebediela Es- tates, and Dr. C. J. Naude, of the Crocodile Valley Estates); and foliar diagnosis along with other criteria has come into commer- cial use with other crops such as sugar cane and pineapples. In Japan, Sato (1952) has made extensive studies of leaf analysis not only for citrus but also for many other fruit trees. Many other students of soil problems have con- tributed information and experience. Everyone who has studied the problem agrees that leaf analysis is an extremely valuable tool. Even so, an adequate system of fertilization and soil management must also take advantage of information derived from the soil, of visual symptomology, and such other information as can be brought to bear on the problem. The purpose of this publication is to: (1) suggest a system of initial orchard eval- uation; (2) present stich leaf and soil an- alyses criteria as currently exist; (3) give detailed directions for sampling and sample handling prior to analysis; (4) suggest a sys- tem of recording results; (5) suggest a time schedule for the continuing plant and soil analyses; and (6) outline methods for con- trolling nutrient deficiencies and excesses. Detailed methods of chemical analyses for plants, soils, and waters are being published 1 See "Literature Cited" for citations listed accord- ing to author and date. [i] separately in a companion manual under the authorship of Chapman and Pratt (1960). This and other standard works on soil and plant analysis can be consulted for analytical procedures. The theoretical and research background, upon which leaf analysis rests, has been pre- sented in previous publications by Goodall and Gregory (1947), Chapman and Brown (1950), Ulrich (1948), Reuther and Smith (1954<7), and many others. The reader is re- ferred to these writings for greater detail and background on these aspects. INITIAL ORCHARD APPRAISAL Prior to beginning a leaf and soil analysis program, an initial orchard, soil, and soil- management appraisal should be made in order to secure data on orchard condition, yield performance, special fruit and fruit- quality problems, and prevailing soil con- ditions. On the basis of this information, a decision can be reached as to whether a leaf and soil analysis program is worth the costs involved and if so, what initial analyses should be made, the extent and periodicity of continuing analyses and, as well, addi- tional information of value with respect to other aspects of orchard management. A suggested form for recording and summarizing this preliminary information is outlined in table 1. It will be immediately evident that not all of this information is needed for nutrient-appraisal purposes, but with very little extra effort much of it can be obtained and will be valuable in helping explain problems of yield, fruit quality, and tree condition, as well as providing a much better background for deciding on the ex- tent of leaf and soil analysis required. The owner or manager will be able to supply niudi of this information, and data on soil characteristics can be obtained in the course of soil sampling. Tin's information corre- sponds to the case history of a human pa- tient which, as is well known, is often the most important part of a medical examina- tion and frequently leads to a positive diag- nosis, thus reducing the number of labora- toi y tests required. Note: Tables 1 to 7, inclusive, begin on page 14. MEANS FOR DIAGNOSING NUTRITIONAL STATUS Before presenting the leaf and soil analy- sis standards for evaluating nutrient status, there are listed in table 2 the criteria now available for diagnosing both the early and more acute stages of nutrient deficiencies and excesses. Reference to table 2 shows that in the case of magnesium, manganese, iron, and zinc deficiencies, visual leaf patterns are usually sufficient for accurate diagnosis (this assumes, of course, familiarity with the simi- larity and differences between these differ- ent patterns). In other cases, positive diag- nosis or indications can be had only by a combination of plant and soil analysis, or plant and soil analysis coupled with con- firmatory tests using foliar sprays 2 or soil applications, or the combination of visual symptoms coupled with plant analysis and, in some cases, soil analysis as well. LEAF ANALYSIS STANDARDS On the basis of the various leaf-analysis standards and data developed by workers in several parts of the world, plus such other data as bear on this problem, table 3 has been prepared, showing for each element a range of values indicating deficiency, low range, satisfactory range, high range, and excess range. The data on which table 3 rests are pre- sented in table 4 as a means of not only giving proper credit to the many people who have contributed significantly to the development of present standards, but more important to reveal the similarities and differences in the leaf values as found by various workers associated with different nu- tritional states. The data also reveal the gaps in current information and some of the uncertainties still present. In the author's first tabulation of suggested leaf-analysis cri- teria (Chapman 1919), three ranges were given: (1) Those values associated with or suggestive of deficiency; (2) range and aver- age in high performance orchards; and (3) values associated with or suggestive of excess ■deVilliers in South Africa (private correspond- ence) finds thai dipping single leaves in a spray solution and tagging the leal is a rapid method of detecting responses. 21 or nutrient unbalance. Reuther and Smith (1954) and later Reuther, Embleton, and Jones (1958) published tables of tentative standards in which five ranges are listed: deficient, low, optimum, high, and excess. The author has adopted this latter system in the present publication since it provides for a better characterization of leaf values; although, as may be readily seen from tables 3 and 4, there are uncertainties about the exact limits of each range and a degree of arbitrariness in the ranges chosen for table 3. In using table 3, three points need empha- sis: (1) the need for proper leaf sampling, handling, and analytical techniques (to be described in the section that follows); (2) realization that these standards are tenta- tive, and based on leaves of known age; and (3) realization that the values found at any one time represent only current status. If there is a deficiency of zinc, or copper, or boron, or any other element, and this is corrected, then the values for this as well as for other elements will often change. This is one reason why the leaf-analysis operation needs to be continued from year to year in order to alter, step by step, the nutritional status and bring the tree into a balanced state. Mention should be made of the fact that even where there are no changes in fertilization or soil management, leaves of the same age will show, from year to year, small up and down fluctuation in values. This is a further reason why it is necessary to continue the leaf-analysis program on a more or less regular basis. In this way an idea of the magnitude of normal orchard fluctuation becomes possible and affords, as stated, a continued check on the changes which one is trying to achieve. There is substantial evidence that range of leaf values shown under the "satisfactory" heading in table 3, is consistent with top performance, but does not guarantee it be- cause many factors besides nutrition affect yield and quality. If values for one or more constituents are consistently higher or lower than those regarded as satisfactory, fertiliza- tion or suitable soil-management changes should be initiated to achieve the desired changes. It may require several years to ac- complish these changes through soil applica- tions, particularly with calcium, potassium, and magnesium. Because of the danger of fertilizer burn, it is unwise to try to increase the potassium or the magnesium content too rapidly. Recently Embleton and Jones (1959) have shown that the latter can be corrected by foliar sprays (see table 8). With those elements where foliar sprays are espe- cially satisfactory such as boron, zinc, man- ganese, copper, molybdenum, and nitrogen (urea), correction can be achieved quickly. Where soil applications of boron, molybde- num, nitrogen, and sulfur are employed, a significant increase in leaf content can be readily obtained. Where phosphorus is defi- cient, it has been our experience that correc- tion can be achieved in one growing season from broadcast applications of soluble phos- phates such as superphosphate, or ammo- nium phosphate with rates of from 5 to 10 pounds P 9 5 per tree. More discussion of control methods will be found later in this paper. In initiating a program of fertilizer guid- ance by leaf analysis, it is important to make analyses initially for the first 14 of the con- stituents shown in table 3. Analyses for the remaining 19 elements need be made only if there are reasons to suspect some special soil condition, or contamination from water, fertilizer, or air pollution. As leaf analysis data accumulate for a given orchard, the number of analyses each year can be reduced until, in time, yearly analyses will not be required. In the case of deficiencies of magnesium, manganese, iron, and zinc, respectively, leaf patterns are distinctive and readily recog- nized by most qualified people, and there appears to be no need for supplemental leaf analysis unless one is in doubt about the diagnosis. Apparently fruit production and quality are influenced little, if any, in the stage where a minor degree of leaf pattern can be seen, but the presence of a few such leaves here and there in an orchard is suf- ficient to indicate an incipient deficiency which should be corrected. Some discussion of the range of values for each element is called for. Calcium. Virtually no data are available regarding excess calcium but when values in 4- to 7 -month-old leaves from fruiting termi- nals are over 6 per cent it may mean that potassium and magnesium are lacking, or low, or that some other upset in nutritional [3] balance is present. On the deficient side, there is some evidence that values below 2.0 per cent should be regarded with suspicion, and trials with calcium sulfate or nitrate additions to the soil should be initiated, or foliar spray applications be made, using 10 pounds Ca(OH) 2 per 100 gallons of water. (See table 7.) Magnesium. As with calcium, not much is known about magnesium excess but values over 0.70 per cent might suggest low potas- sium or calcium, or other nutrient unbal- ance. Analysis of leaves showing typical de- ficiency patterns usually shows values in the 0.05 per cent to 0.15 per cent range; values somewhat higher or lower than the 0.30 to 0.60 per cent range may well be consistent with top performance, but more experience is needed. Nitrogen. There is considerable evidence that with some citrus varieties in some loca- tions, values as low as 1.90 per cent N may be sufficient, and on the other side, values of 2.5 per cent and above may not be con- sistent with best quality in certain climatic zones. More data and local experience relat- ing nitrogen levels in leaves to yield, qual- ity, size, regreening, and other factors, are needed. Phosphorus. Excess phosphorus in the soil (amounts sufficient to bring on copper and zinc deficiencies), may not show up by leaf analysis; hence, on the excess end leaf an- alysis is not a satisfactory indicator. On the low side, phosphate-deficient trees almost always show leaf values under 0.10 per cent, but values of 0.08 per cent and higher may not necessarily denote phospho- rus deficiency. In short, as with most of the other elements, the satisfactory range may be wider than indicated. Potassium. Yield is not much affected un- til leaf values fall below 0.40 per cent in the experience of the author, but sizes can prob- ably be increased some when leaf values well below 1 .0 per cent are brought to values well above the 1 per cent level provided magne- sium, zinc, or manganese deficiencies are not induced. When potassium is on the low side, magnesium sulfate or dolomite should be added along with the potassium to forestall magnesium defi< ieiuy, and any zinc or man- ganese defn ieiHy brought on, eorrected with foliai sprays. Sulfur. Excess sulfate produces a leaf pat- tern somewhat similar to boron excess, and the combined use of leaf pattern and leaf analysis is helpful in diagnosing excess sul- fate conditions. No field data are available regarding sulfur deficiency, and the values given are based on limited evidence. How- ever, lack of sulfur produces a yellowing of foliage similar to nitrogen deficiency. Leaf values for sulfur will be low and nitrogen high, when sulfur is deficient. The converse is true when nitrogen is lacking. Sodium and Chloride. The usual levels of these in citrus leaves where salinity is not a problem are under 0.10 per cent. When the levels are at 0.20 per cent and above, soil salinity should be checked. Boron. Some data show that total boron above the deficient range, i.e., higher than 25 ppm may not always be a sure indication of ample boron. deVilliers and Beyers, in South Africa, found that despite leaf values higher than 25 ppm total boron, certain tree and fruit disorders not hitherto recognized as boron deficiency, are apparently due to lack of this element and were corrected by boron applications. In all such cases, they found that water-soluble boron in the leaves was low (under 8.0 ppm boron in the dry matter). From this is would appear desir- able, where total boron is between the 25- 40 ppm range, to make a determination of water-soluble boron. Copper. Some excellent orchards have been found in which leaf levels of copper are as low as 2 ppm 3 (Bradford and Hard- ing, 1957), with no sign of copper deficiency symptoms. Nonetheless, when copper levels are under 4.0 ppm, it is desirable to in- clude copper in nutritional sprays. Insuffi- cient data are at hand to establish Cu excess levels. Iron. Leaf patterns appear to be satisfac- tory for diagnosing moderate to acute iron deficiency but the very early stages may not show leaf patterns and in this case leaf an- alysis may reveal an incipient deficiency. Nothing is known about the levels indicat- ing iron excess. Manganese. Leaf analysis is useful in over- all evaluation even though exact limits for excess are not yet well worked out. There :1 As determined by spectrographs analysis. 141 are definite leaf patterns associated with ex- cess manganese and leaf analysis will serve as a double check on visual diagnosis. Molybdenum. Not enough data are avail- able to clearly establish levels indicating in- cipient deficiency or excess. The satisfactory range may be wider than indicated. Zinc. The zinc excess range is not defi- nitely known. As with manganese and iron, leaf patterns are usually sufficient to indicate mild and acute deficiency, although there are reports in which responses to zinc have been obtained even though no distinctive patterns are evident. Leaf analysis is there- fore valuable for evaluation purposes. Other Trace Elements. More experimen- tal data are needed to evaluate the signifi- cance of varying quantities of the many other trace elements found in citrus leaves. Spectrographic and other analyses of leaves from high -producing orchards (Bradford and Harding, 1957), suggest that the range for each element in the "satisfactory" col- umn is consistent with good performance. From this brief discussion it is evident that some uncertainty exists as to interpreta- tions of leaf analysis. However, the values in the "deficient" range are, in general, quite reliable; the levels in the "satisfactory" range are consistent with satisfactory performance, although the ranges may be broader than those indicated. In any case, significant in- formation of great value can be obtained, and when followed by such soil tests as may be required, much of the guesswork in fer- tility management can be removed. More- over, trends toward deficiency or excess can be detected and corrected before they occur, thus assuring better over-all performance. METHODS OF LEAF SAMPLING The success or failure of leaf analysis hinges on satisfactory sampling, handling, cleaning, and analysis techniques. Errone- ous results and conclusions are likely if care- less or improper methods are used at any stage of this process. Quick-test procedures and a hasty grab sample of leaves are likely to be a complete waste of time. A number of investigators have studied one or more phases of the sampling and/or cleaning and analysis phase of citrus leaf analysis: Smith, Reuther, and Specht (1950), Chapman and Brown (1950;, Cam- eron, Mueller, and Wallace (1952), Wallace, Mueller, and Squier (1952), Monselise and Herschberg (1953), and Steyn (1957, 1959;. The latter has made an exhaustive investi- gation of all phases of citrus leaf sampling, handling, cleaning, and preparation. The procedure to be followed will depend on the objectives. Where the purpose is only to confirm a visual symptom diagnosis, ioi example, to distinguish whether a leaf pat- tern is due to boron or sulfate excess, or sodium and chloride injury, or to confirm a tentative copper, boron, zinc, manganese, and molybdenum deficiency, the procedure then is simply to collect 100 to 200 of the leaves showing the particular visual symp- tom it is wished to confirm, follow the handling, cleaning, and analysis techniques outlined hereinafter, and make the analyses by methods of acceptable accuracy. However, when leaf analysis is to be used for purposes of continued fertilizer guid- ance, a more careful sampling system must be followed. At the outset it will be desirable to establish in large, apparently uniform blocks (10 to 50 or more acres), whether one sampling unit will suffice, or whether it is necessary to establish within the block several permanent sampling locations. This problem will be discussed in the section which follows. Preliminary Survey of Orchard and Selec- tion of Initial Sampling Units. Quite often soils are variable and one part of an or- chard may be very different in slope, tex- ture, depth, and color from another part of the orchard. Moreover, plantings in one sec- tion may be on a different rootstock or a different top-rootstock combination than an- other. Obviously, for proper evaluation and fertilizer guidance, the whole orchard must be broken down into units which assure homogeneity with respect to: (1) top-root- stock combination; (2) soil; and (3) visual tree homogeneity within these subdivisions. There may be scattered trees within these units which depart substantia llv from the general average (e.g., trees showing scaly bark, or gummosis, or iron chlorosis, or otherwise obviously off-type tree). Clearly, leaves from such trees should not be com- posited with those representing the average condition. Rather, if the cause of this ran- [5] dom departure is to be ascertained, a sep- arate sample, as stated, should be taken. It may be that the entire block, on the other hand, is virtually uniform as to variety/or rootstock, soil, growth, and appearance. In this case, such blocks, if more than five acres in extent, should be broken down into five- acre units for the initial sampling. Steyn (1957) has data to show that what- ever the size unit, no less than 20 per cent of the trees should be sampled. A five-acre block might contain 400 to 600 trees. This means that 80 to 150 trees should be sam- pled. While this represents considerable work it must be borne in mind that even more effort will go into the final analytical job. With experience, a person can select the proper leaves from a given tree in about two minutes. Thus, an average of two to three five-acre units can be sampled in one day. Selection of Leaves, and Handling. (Note: The following directions apply to all ele- ments except fluorine. In case of this ele- ment, see under "Methods of Analysis," Chapman and Pratt (1960), for special sam- pling and handling.) The leaf analysis standards shown in table 3 are based on 4- to 10-month-old spring cycle leaves selected from fruit-bearing ter- OLDER GROWTH SPRING CYCLE GROWTH Leaves 1, 2, and 3 are spring or bloom cycle leaves and any one of them suitable for sampling; leaves 4, 5, 6, 7, and 8 are older cycle leaves and should NOT be picked for leaf sample. minals. Some investigators, notably Reuther and Smith (1954), base their standards on four- to seven-month-old spring cycle leaves from nonfruit-bearing terminals. There ap- pears to be little difference in leaf analysis criteria whether the leaves come from fruit- bearing or nonfruit-bearing terminals. The author suggests the use of leaves from fruit- bearing terminals (see figure) on the grounds that it is simpler in practice to make leaf selections from this type terminal and be sure of leaf age than to identify with certain- ty the age of leaves from nonfruiting termi- nals. deVilliers (private correspondence) is of the same opinion. Though there are oc- casional years when fruit production is very low and one has to search for fruit, it is almost always possible to find enough such terminals, considering the number of trees (80 to 150) from which leaves should be taken. deVilliers (see second ^[ p. 6) suggests taking only two leaves per tree. Seldom, if ever, will citrus yields be so low that an average of at least two fruits per tree cannot be readily found. The South African work- ers have also standardized on fruit-bearing terminals, but use 10- to 1 1 -month-old leaves. Since in the present state of knowledge it appears to make little or no difference whether the four- to seven-month-old spring cycle leaves are from fruit-bearing or non- fruit-bearing terminals, the matter can rest with the preference of the individual in charge of the leaf analysis program. The sketch shows a bearing twig with several leaves which emerged with the flower. Any one of these leaves may be selected but the sampler should be sure that the leaf is not from an older cycle of growth. Se- lect four leaves per tree, depending on size, around the periphery in a band from about 1 to 7 feet from the ground. Pick average- sized leaves to represent the prevailing con- dition of this age leaf. If there are occasional leaves which show moderate or extreme iron chlorosis, or zinc deficiency, or other leaf patterns or abnormalities, avoid including these in the sample. On the other hand, if there is a prevailing leaf mottle condition such as subacute manganese deficiency, one cannot avoid picking this type of leaf. Since the main purpose of leal analysis is to guide Fertilizer and soil -management practices, particularly to pick up conditions which are [61 incipient, one must choose leaves that repre- sent average foliage conditions which pre- vail for this particular cycle of growth. A somewhat less time-consuming method is employed by deVilliers (private corre- spondence) on the Zebediela Estates in South Africa. A two and one-half acre block — near the center of a 1,600-tree block — is chosen as the permanent sampling unit. One sampler starts in on the S.W. corner and picks two leaves from every tree on a di- agonal across to the N.E. corner; another picker simultaneously picks on a diagonal from the S.E. to the N.W. corner. The two samples are combined. The two leaves per tree are picked alternately from the south and west and the north and east sides of the trees. Thus equal numbers come from all sides of the trees. Their planting dis- tances are such that about 80 trees are sam- pled per two and one-half acre block, the sample consisting of 160 leaves. Tests of reproducibility showed, in six composites picked in this manner, the following range in leaf values: N per cent 2.374 to 2.536; P per cent 0.090 to 0.097; K per cent 0.614 to 0.706; Ca per cent 4.210 to 4.705; Mg per cent 0.430 to 0.548; Fe (ppm) 119 to 133; Mn (ppm) 56 to 63; Cu (ppm) 3.6 to 4.0; Total B (ppm) 46 to 58; Water Sol. B (ppm) 28 to 36; Mo (ppm) 0.27 to 0.33. (Mo is high because of a preceding spray.) These figures represent single analytical determinations. deVilliers estimates that their total cost per sample, which includes picking, cleaning, and analysis for N, P, K, Ca, Mg, Fe, Mn, Cu, total B, water-soluble B, and Mo, at about $14 each, or about $14 a year for each sampling unit. This sampling unit repre- sents 1,600 trees. If the analysis did no more than cut nitrogen usage from L% to \i/ 2 pounds per acre per tree per year, they save more than twice the cost of the analysis. Steyn (1957) recommends that the freshly picked leaves be placed in porous cloth bags (not polyethylene bags) transported to the laboratory the same day, then transferred to polyethylene bags and immediately placed in a refrigerator pending leaf cleaning; or, as an alternative, a portable refrigeration chest could be carried to the field and the leaf sample (in this case picked into a polyethylene bag), placed immediately in the ice chest following collection, and when brought to the laboratory, placed in a re- frigerator. Washing. The samples should be removed one at a time from the refrigerator and handled as outlined and as quoted from Steyn (1957): "Take 5 polyethylene dishes (about 6-inch deep and 12 inches in diam- eter) and place about 750 ml of a 0. 1 per cent detergent solution (Dreft or Teepol, or a sudsy Ivory soap solution) in the first, 750 ml deionized or distilled water in the second and third, and 750 ml deionized or distilled water in the fourth. The fifth dish is used to collect the wet leaves. Sponge each leaf thoroughly with cotton wool in the deter- gent solution, wiping both sides, then rinse well in the three sets of water, and finally rinse each leaf in fresh, deionized water. Shake off drops of water and place in the fifth dish. When the complete sample has been washed, drain off the water as com- pletely as possible, and place the leaves on a large sheet of Whatman drying paper. Then place the leaves in a suitable-sized muslin bag, tie shut with a rubber band, and suspend inside a forced draft oven set at 65° C. Dry for 48 hours and then grind the sample in an agate ball mill, ensuring that the jar is at least half filled with the leaf sample. After grinding, place the powder in a clean screw-capped bottle, leave open in the forced draft oven for 24 hours at 65° C, and seal tightly while still warm. Store in a cool dry place and carry out the analyses within a two-month period." METHODS OF ANALYSIS Details of procedures are being published, as previously stated, in a separate volume (Chapman and Pratt, 1960). At the present time quick-test methods, as previously stated, are not recommended. The uncertainties attached to interpretation are such that it is desirable to employ accu- rate analytical procedure. Most investigators and laboratories have their own particular methods of analysis. Where large numbers of determinations are to be handled on a commercial basis and equipment is available, it is recommended that flame photometer methods be employed for Ca, Mg, Na and K, and the speetograph for B, Cu," Zn, Li, Mn, Mo, Cr, Pb, Ni, Ag, [7] Sr, Sn, Ti, V and Zr. For all other elements, methods outlined in Chapman and Pratt (1960) or in other standard works on soil and plant analysis, will be found satisfactory. SOIL ANALYSIS STANDARDS Neither soil nor plant analyses alone are sufficient to provide all of the information needed for fertilizer guidance. Plant analysis indicates current nutrient status but reveals little about total reserve in the soil. Soil analysis alone has limitations also. As is well known, the total supply of a given element often bears little relation to that portion available for plant use; nor has any extrac- tant ever been devised that can imitate the feeding action of plant roots, plus which variability among plants, variable nutrient needs at different stages of growth, micro- biological effects, and climatic interrelations, to name some of the complications, all make the results of soil analysis difficult of inter- pretation. However, soil tests will provide useful information as to whether the total or so-called available supply is high or low, whether salt is high or low and these data added to those provided by plant analysis, will add immeasurably to the whole picture. Results relating nutrient supply in the soil, as measured by one or more methods, to citrus tree performance are incomplete, and for this reason, in working up tentative val- ues, the standards outlined in table 5 are those arrived at by investigators working with a variety of other crops. For most constituents or soil conditions, remarks as to meaning and interpretation have been included in the table and there is no need to elaborate on them here. Details of the actual methods to be used in determining the various constituents can be sought in the original literature citations given and/or various compendiums of meth- ods for soil, plant, and water analyses. METHODS OF SOIL SAMPLING AND HANDLING The success or failure of soil analysis as an aid to fertilizer guidance hinges on se- curing a representative soil sample plus all subsequent handling operations including analysis. The sample finally weighed for any de- termination is the resultant of several oper- ational steps: (1) taking and mixing a series of cores from the area to be sampled; (2) sub- sampling this original sample one or more times; (3) air-drying, grinding, sieving, and mixing. The greatest element of error, as- suming proper subsampling, drying, grind- ing, and sieving techniques, is in securing a representative composite sample. Having established for leaf sampling the units which are to be regarded as the permanent sampling areas, a pattern of soil sampling within these units needs to be established. Many studies of soil sampling techniques have been made (Cline, 1944; Reed and Rigney, 1947; Barker and Steyn, 1956; Mc- Kenzie, 1955; Hausenbuiller, 1957; and Hemingway, 1955). The following princi- ples are well established: (1) a series of cores taken according to some systematic grid layout of the area of equal diameter and comparable depth (volume) must be composited; (2) separate soil cores should be analyzed or replicate sets of composites so as to determine statistical significance of analytical results on the composite; (3) the number of soil cores to be composited will depend on the variability of the soil, the degree of accuracy desired, and the particu- lar element or elements it is desired to de- termine, and the general over-all purpose, 4 (4) cultivated soils are generally more varia- ble than virgin soils, and saline and alkali soils are extremely variable; (5) separate composite samples representing different seg- ments of the soil profile or root zone should be taken; (6) contamination from soil sur- face materials (crop residues, manures, ferti- lizers, et cetera) should be avoided, as also contamination of one soil depth with that of another; and (7) in areas that are to be sampled at successive intervals, it is impor- tant to make a map showing initial sampling 1 In one study of this question, Steyn (1957) found that, in one of three ^4 -acre pl° ts °f apparently uni- form virgin soil, it would require for potassium 80 cores taken in a uniformly distributed grid pattern (o show a significance at the 5 per cent level in sample difference, exceeding 10 per cent of the mean. With the two other plots, it would require 28 to 20 cores, respectively. For nitrogen, on the other hand, it required only 20, 16, and 12 cores for the same degiee of significance in these three plots. »1 points and take subsequent samples at points somewhat removed from the preceding. Directions for Sampling Furrow-Irrigated Citrus Orchards. Furrow-irrigated orchards are especially variable and a soil-sampling scheme suitable for these likely will be suita- ble for any other type citrus planting. Hence a suggested soil-sampling method for this situation is outlined in the following para- graphs. In most furrow-irrigated orchards, two distinct soil conditions prevail: the soil which has been, and continues to be wet with irrigation water; and the soil in be- tween the irrigated spaces which, except when the orchard was young, is no longer irrigated. The area wet by irrigation water must be adequately sampled. Harding of our staff has shown that marked differences in salt levels exist in all parts of the soil profile as between the furrow closest to the tree (tree furrows), and the furrows in the middle farthest from the trees. He (1954) and others have shown that there are usually substan- tial salt and nitrate accumulations in the furrow crests, so any sampling procedure which seeks to determine mean composition should take equal numbers of soil cores from the furrow crests and furrow bottoms. There may be differences between the tree furrows on the sun side of the tree and the shadow side of the tree so equal numbers of cores should be taken from these positions. It goes without saying that various depths repre- senting most of the root zone should be composited separately and it has been a standard practice from a depth point of view to sample the surface cultivated zone (0 to 6 inches), the second 6 inches (6 to 12 inches), and then separate foot horizons down to a depth of from 4 to 6 feet. The importance of taking the deeper horizons is that salt accumulation and per cent sodium in both the soluble and exchange- able form often increase with depth, and it is important to know what the situation is in these lower horizons. On the basis of these considerations, the authors suggest a sampling grid as repre- sented on page 10. With an assumed block of 400 trees at planting distances of 18' x 18' or 20' x 20' or, comparable, the total area represented would be about 5.0 acres. In this diagram, four furrows between tree rows are visualized but variations from this are unimportant. What is important is that eight sampling zones are set up (designated as X 1S , X ish , X 2S , X 2Sh , X., s , X., Kh , X 4S , X, .). Two sampling zones are located near the head of the irrigation run, two near the ends of the irrigation run, and the others at ap- proximately 1/3 and 2/3 the distance from the irrigation stands. At each sampling zone, 4 cores should be taken, one in the tree fur- row, one in the furrow crest adjacent to the tree furrow, and comparable cores in the furrow and crest at a point midway between the tree rows. A further variation is that the X x and X 4 samples will be taken on a straight line between the tree trunks, whereas the X 2 and X 3 sample will be taken in a comparable line midway between the trees. Another variation is that the X ]S , X 2S , X 3S , and X 4S samples will begin in the tree furrow on the sunny side of the tree, whereas the X lsh , X 2Sh , X 3Sh and X 4Sh sam- ples will start in the furrow located on the shady side of the tree. Under this system, equal numbers of samples from both the sunny and shady tree furrows, equal num- bers from furrow crests and furrow bottoms, equal numbers from the middles farthest from the tree and equal numbers closest to the tree will be taken. This sampling plan involves the removal of 32 cores of soil for each soil depth. It is apparent that this plan can be con- tracted or expanded to cover a larger or smaller area but to include equal numbers of cores representing the variations men- tioned, the same number of cores (32) must be taken. In taking the initial set of soil samples, some idea of soil variability throughout the entire block can be obtained by compositing separately the four cores from each of the X locations, and taking a subsample (i/ 2 ) of each of these composites for separate analysis. The other i/ 2 portions of each of these four-core composites will, of course, be composited into the main sample rep- resenting the block as a whole. From these data one can calculate the error of the block mean for each soil constituent, and deter- mine whether differences found in future samplings are real or sampling error. In situations where localized salt ac- cumulations are suspected, it is suggested [9] Row No. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 Irrigation stand OOOOOOOOOOOOOOOOOOOO Tree No. 1 2 • • • • • *| s • • • • • • • • • • Hsh * * * * 3 4 5 7 8 9 10 1 1 • • • • •••••• •••••••••• 12 X 3s X 3sh 13 14 15 16 17 18 .v X 19 *4sh 4* 20 "F South Suggested soil sampling system for furrow-irrigated citrus orchard. Four cores to be taken at each of x locations. See diagram on page 11. Y . Sampling Zone (4 cores) on N-S line be- ^ -v Sampling Zone (4 cores) along N-S line 18 tween tree trunks beginning in tree fur- 2S [ in centers between tree squares beginning 1 ) row on shade side of tree 3S ) in tree furrow on sun side Y Sampling Zone (4 cores) along N-S line Y > Sampling Zone (4 cores) along N-S line 1 h ( between tree trunks beginning in tree v 2Sh > in centers between tree squares beginning " ' h ) furrow on shade side of tree ;!S, 'J in tree furrow on shade side I 10] CROSS SECTION 36 to 48" -> South Location of core sampling sites in an X 1S or X 4S zone; X lsh and X 4Sh similar except on north side of tree. that samples from the furrow crest and the furrow bottoms all by horizons, of course, be composited separately and analyzed. The mean salt concentration in the soil mass as a whole may not reveal local areas of high salt concentration, yet these latter may be very significant in terms of tree performance. The tool with which soil cores are ob- tained will depend on the soil. When the soil is suitable, a ^- to 1-inch soil tube is recommended. Where the soil is too stony, gravelly, sandy, or dry, jaw-type posthole diggers, barrel-(bucket) type soil augers, or a spade must be used. Whatever the method, it is obviously important to take from each sampling point and horizon the same vol- ume of soil. Where large sampling tools are used, it will be necessary to take a subsample of the core obtained. A series of large, heavy paper or canvas bags, properly marked as to horizon, can be used. When sampling is complete, a subsample can be taken and the rest discarded. This is easily accom- plished by spreading the sample out on a large piece of canvas or rubberized cloth, breaking up the lumps or borings by hand, thoroughly mixing by rolling in two direc- tions, and taking a suitable-sized subsample (about two quarts) for laboratory drying, pulverizing, sieving, and final analysis. Samples should be brought to the labora- tory as soon as possible, spread out on paper to dry (it will often save much time to crumble the moist soil cores by hand and pass the moist sample through a 6 mm sieve, discarding the coarse stones and pebbles, but not soil clods) in a dust-and fume-free loca- tion. When air-dry, the soil should then be worked through a 2 mm screen, again dis- carding small gravel but not soil crumbs. The use of a rubber stopper to help work the soil through the screen, or a mortar and rubber-tipped pestle, or wood roller to pulverize soil clods and aggregates is the usual means of reducing particle size so as to pass it through the 2 mm screen. After screening, the soil should be thoroughly mixed by rolling on an appropriate sized piece of rubberized cloth. A one-quart sample of soil will suffice for all of the chemical tests. We have found it convenient to store soils, under California [in climatic conditions, in one-quart cardboard cartons. Glass jars are commonly used and in some cases press top tin cans. TIME SCHEDULE FOR LEAF AND SOIL ANALYSIS The table below shows a suggested time schedule for the plant and soil analyses. The initial orchard evaluation involving both leaf and soil analyses represents the longest and most expensive part of the operation. Following this, far less extensive plant and soil analyses are called for, and in the second and succeeding years, rela- tively few analyses will be needed. Suggested Schedule of Observations, Measure- ments, and Operations Initial orchard evaluation 1. Appraise orchard as outlined in table 1. 2. Make complete leaf analysis, taking leaf samples in September or October (northern hemisphere) pref- erably. 3. Determine pH and salinity status and such other soil determinations as may be suggested by results of leaf analysis. 4. Initiate such fertilizer, irrigation, and other soil and orchard management practices as may be indicated by analyses and orchard appraisal. First year fallowing change in practice 1. Leaf analysis: Take leaf sample at same date as initially (preferably September or October, northern hemisphere), and make analyses for Ca, Mg, K, N, P, and such additional elements as shift in fertilizer practices may suggest as necessary. 2. Soil analysis: If initial samples showed excess salts, resample and analyze to determine effectiveness of leaching and/or other practices initiated. 3. Check visual symptomatology at same time as ini- tially. Succeeding years 1. Make such leaf and soil analyses as may be indi- cated by results of initial and first-year results and the changes in fertilizer and management practices inaugurated. In general, if changes in nutrition are being sought, yearly leaf analyses should be made until the desired changes have been achieved. METHOD OF RECORDING RESULTS Id using plant and soil analyses as a guide to soil-management and fertilizer practices it is important to maintain a running record showing yearly leaf analysis values, fertilizer and soil-management practices, pest- and disease-control treatments, together with a record of yield, sizes, fruit quality, and visual symptoms. A suggested method of recording all these results in tabular form is shown in table 6. METHODS OF CONTROLLING AND CORRECTING MINERAL DEFICIENCIES AND EXCESSES Having diagnosed either acute or sub- acute, or suspected malnutrition due to mineral deficiencies or excesses, the question of how to control, correct, or begin to ameliorate the condition arises. To provide tangible guidance on this problem, table 7 has been prepared showing for each con- dition the method or methods found useful in correcting deficiencies and excesses so far as is known. Supplementary remarks are included in the table and require no further elaboration. SUMMARY By means of leaf analysis visual symptoms and soil analysis, either singly or more often in combination, it is now possible to posi- tively diagnose not only the moderate to acute stages of mineral deficiencies or ex- cesses, but in most cases, secure positive indications of early stages of these or trends in this direction. Such leaf and soil analysis criteria as are currently available are presented in this paper, together with detailed directions for plant and soil sampling, handling, and methods for initiating the programs, record- ing the results, and, finally, control pro- cedures. It is emphasized repeatedly that the most important precaution to observe is proper sampling techniques and analyses. A lew leaves or one or two cores of soil as samples, or the use of quick-test chemical methods are likely to yield completely unreliable results. Not only is proper sampling and analysis important, but some continuation of the leaf-analysis program is called for as a check on the effects of corrective treatments. The initial costs for orchard evaluation and soil and plant analysis will be the I 121 greatest; in succeeding years the costs will diminish. Increased tree yields and decreased ferti- lizer costs resulting from such a program, and the knowledge that soil-management practices were going in the right, rather than the wrong direction, will in the long run pay dividends. As research and experience progress, bet- ter criteria and methods will emerge, thus increasing the accuracy of diagnosis and de- creasing the costs. ACKNOWLEDGMENTS The author is indebted to Dr. Jaap deVil- liers, Horticulturist of Zebediela Estates, Northern Transvaal, Union of South Africa, for critically reviewing this publication and making many valuable suggestions. He is also indebted to Mr. Edward Curran, Man- ager of the Fruit Growers Service Labora- tory, Santa Paula, California, for similar assistance; and to a considerable number of other reviewers who have made many valu- able suggestions. In addition, a great deal of basic data, upon which current leaf and soil standards rest, have emerged from the research of colleagues in the Department of Soils and Plant Nutrition, and the Department of Horticulture of the Citrus Experiment Sta- tion, as well as the research of many other investigators throughout the world. The source of all of this information is indicated and credited in the various tables and in the text, but special mention of it is made at this point, for the reason that a publication such as this would not have been possible except for the enormous amount of research and experience which has been devoted to this subject by many people. The author is indebted to Miss Harrietann Joseph, Senior Laboratory Technician of the Department of Soils and Plant Nutrition for the line drawings. [13] TABLE 1. — Suggested Form for Use in Recording and Summarizing Data of Initial Orchard Appraisal. I. LOCATION: Owner Address Manager_ Address Location of orchard MAP OF LOCATION Show nearest crossroads, towns, and other locational data DETAIL OF SOIL AND LEAF SAMPLING AREA Field No. Block No. Legend: x = tree;(x) = tree sampled; o = irrig. stand; Q= windbreak tree II. ORCHARD DATA : Age Previous cropping history Species, variety_ Top-worked Ac rea ge Roots tock Sandwich Size trees Pruning history_ Fol iage densi ty_ Dieback Source nursery trees_ No. mature trees C r owd i n g Gi rdl ing history_ Fol iage color Abnormal leaf drop_ When Periodic leaf patterns Season of appearance_ Deficiencies or excesses, or other abnormalities indicated_ Frost damage history_ Wind damage history Heat damage history Other damage history_ Other information I ii I TABLE 1. — Continued III. DISEASE INDICATIONS : Gummos i S Scaly bark_ Root rot Quick dec] ine__ Other virus disease indications Other bark or root troubles Stubborn disease Control measures used for disease Hormone sprays Other sprays Kind and amount Soil fumigation_ Other treatments IV. INSECT PROBLEMS : Sever i ty Major pests_ V. Y Control practices used in past several years IELD AND QUALITY PERFORMANCE: \ Acreage Yield Pack out data Year Field boxes Packed boxes Weight Peak sTTes % 1st grade % 2nd grade % 3rd grade % By- products % cul Is I Special fruit problems: Small sizes Creasing Granulation Rind texture Color problems Internal quality P re-harvest disease_ Post-harvest disease Maturity problems Other problems [15] TABLE 1. — Continued VI. CLIMATE: Annual average rainfall_ Seasonal distribution Mean annual temperature_ Absolute maximum Effective rainfal Character of rain Absolute minimum Frequency and periods when temperature exceeds 100° F. Frost hazard Humidity and climate: Desert Mean annual humidity (% rel.) Are fogs common % Rel. humidity, A.M. av. Orchard heating practice_ Intermediate Coastal % Rel. humidity, P.M. av._ % maximum Sunshine, hours annual_ No. months when temperatures suitable for vegetative growth_ Are nights predominantly cool Damaging winds, frequency Character and season of winds Prevai I ing winds_ Other significant climatic character istics VII. SOIL CHARACTERISTICS : Soil series and type_ Soil profile characteristics: Depth to rock or hardpan__ Homogeneous S t ra t i f i ed C I ay I ayers Plowsole Hardpan_ Compactness Desc ription of profile characteristics: 1st horizon 2nd horizon 3rd horizon 4th horizon 5th horizon 6th horizon Depth Texture Gravel, stones Color Granulation Concretions Shells Mottl inq Other Soil drainage characteristics: Depth to permanent water table_ Does water table fluctuate Good medium poor_ Does soil take water readily Do lower horizons stay wet unduly after rain or irrigation_ Other characteristics Topography: Flat- slope (% approx.) terraced , undulating^ evidence of erosion contour Soil information available or applicable: Known or obvious chemical characteristics Microbiological information available 16 1 TABLE 1. — Continued VIII. IRRIGATION: Is orchard irrigatcd_ Source of water Ana lysis of water: How many years irrigated Conductivity ECxlQ° at 25° C. j>H_ Total dissolved solids, ppro Boron (B) , ppm Fluoride (F) , ppm Bicarbonate (HCO3) , ppm Chloride (Cl), opm Sulfate (SO4) , ppm Nitrate (NO 3), ppm Calcium (Ca) , ppm Magnesium (Mg) , ppm Sodium (Na) , ppm Potassium (K) , ppm Per cent Na Na x 100 Na+K+Ca+Hg (Expressed in me/1) Residual sodium carbonate (Ca+Mg) - (HCO3+CO3) - RSC (Expressed in me/I) Remarks on water Method of irrigation: Basin, furrow, sprinkler_ Length of runs, if furrow Frequency Amount per irrigation Other data on irrigation IX. CULTIVATION : Cul tivated Noncul ti vat ion Frequency, How long_ Method Weed control materials Is organic matter used. Surface mulching Other information Kinds_ Materials Amounts X. FERTILIZER PRACTICES DURING PAST 5-10 YEARS : N i t rogen : Annua 1 arooun ts Manure and organic materials: When applied Frequency_ Green manure practice: Kinds, Mixed fertilizers: Kinds History of use Kinds_ Amounts How app I i ed_ Kinds Tonnage produced. Amounts used Fol iar sprays : Frequency_ Amendments : Kinds Lime Gypsum_ Other Other information on fertilizer practices Amounts, Amounts, Amounts [H] TABLE 1. — Continued XI. CONCLUSIONS REGARDING CLIMATE . SOIL . AND ORCHARD : Climate Are recurring climatic extremes a serious problem Heat Cold Wind Hai1_ " Humi d i ty Hurr i canes Is growing season too short for maximum varietal performance (yield, size, quality) Can top performance orchards be found in the area Are climatic handicaps too great for economical citrus production. Can climatic handicaps be overcome to some extent by proper management. Soil Is soil suitable for citrus, considering climatic situation and availability of water Does soil texture impose special management problems Do profile characteristics pose water penetration, aeration, drainage, or salinity p rob 1 eras What are probable fertility problems based on general knowledge of soils, past and present fertilizer practices, irrigation water composition Is present fertilizer practice going in right or wrong direction as near as can be ascertained I rrigation Is sufficient water available Is salinity build-up a potential threat Is irrigation practice satisfactory Periodic stresses. Should tensiometers be installed Is water penetration a problem Are there periods when soil is too wet Disease Is disease incidence or threat such that orchard should be completely replanted, or individual trees replaced Insect Is there an insect problem and are handicaps so large and costly that, considering climatic and soil handicaps, citrus should be replaced by another crop General conclusions as to reasons for orchard condition Recommended soi 1 and plant anal yses Initial appraisal Continuing program [18] XII. SOIL ANALYSIS DATA SHEET. TABLE 1. — Continued Dates sampled Area Horizon and depth Measurement 1 2 3 k 5 Average Depth represented Texture Color + pH: 1:2.5 suspension + Conductivity of saturation extract ECx103 at 25° C. * Calcium (Ca) (me/I) * Magnesium (Mg) (me/1) * Potassium (k) (me/1) * Sodium (Na) (me/l) * Sulfate (SO^) (rae/1) * Nitrate (NO3) (roe/I) * Carbonate (CO3) (me/1) * Bicarbonate (HCO3) (me/1) * Chloride (CI) (me/1) * Boron (B) (me/1) Other * Total soluble solids in ppm saturation extract * Exchange capacity, me/100 g soil * Phosphorus: Total P in ppm dry soil O.SM Na Bicarbonate soluble in ppm dry soi 1 Water soluble in ppm dry soil (Binqham, method) * Potassium: Total K in ppm dry soil Exchangeable, me/100 g Exchangeable in % exch, cap. * Magnesium: Total Mg in ppm dry soil Exchangeable, me/100 g K:Mg ratio * Calcium: Total Ca in ppm dry soil Exchangeable, me/100 g * Sodium: Exchangeable, me/100 g % Exch. Na Na Ca+Mg+Na+K * Organic matter, % * Nitrogen, total % * Nitrate prod, capacity + These determinations highly desirable. * These determinations necessary only when it is desired to confirm visual or analysis indications of excesses br deficiencies. leaf [19] TABLE 1. — Continued XII. SOIL ANALYSIS DATA SHEET (cont.) 1 — 1 Horizon and depth Measurement 1 2 3 k 5 Average * Sulfur: Total S in ppm dry soil Water sol. SOl (sat. extract) * Boron: Total B in ppm dry soil Water sol .Bin soi 1 (NcClunq Dawson (1950) method) * Copper: Total Cu in ppm dry soil 1 N-HC1 extract in ppm dry soil * Manganese: Total Mn in ppm dry soil Exchangeable Easily reducible * Zinc: Total Zn in ppm dry soil Ammonium ace tate-d i thi zone extract in ppm dry soil (Shaw* and Dean (1952) method) * Molybdenum: Total Mo in ppm dry soil Ammonium oxalate extractable in ppm dry sol 1 Other soil constituents: Evaluation, based on soil analysis: + These determinations highly desirable. * These determinations necessary only when it is desired to confirm visual or leaf analysis indications of excesses or deficiencies. I 20 1 TABLE 1. — Continued XII INITIAL LEAF ANALYSIS DATA SHEET Orchard designation Field No. " Block No. Age of leaves Sampling Unit No. trees sampled Date sampled Per cent of total trees in sampling unit from which leaves were taken Sampl ing Uni t E 1 emen t 1 2 3 k 5 6 7 Per cent in dry matter of leaf + Calcium (Ca) + Magnesium (Mg) + Nitrogen (N) + Phosphorus (P) + Potassium (K) + Sulfur (S) + Sodium (Na) + Chloride (CI) In ppm dry matter of leaf + Boron (B) + Copper (Cu) + Iron (Fe) + Manganese (Mn) + Molybdenum (Mo) + Zinc (Zn) * Aluminum (Al) * Antimony (Sb) * Arsenic (As) * Barium (Ba) * Bromine (Br) * Chromium (Cr) * Cobalt (Co) * Fluorine _(F} * Indium fin) * Iodine (1) * Lead (Pb) * Lithium (Li) * Nickel (Ni) * Silver (Aq) * Strontium (Sr) * Tin (Sn) * Ti tanium (Ti) * Vanadium JV) * Zi rconium (Zr) * Other: Evaluation based on leaf analysis: + These determinations should all be made initially. * These determinations need be made only if some unusual condition is suspected, e.g., nature of soil, water, or air pollution possibilities, unusual fertilizer or pest control practices, etc. [21] TABLE 1. — Continued XIV. RECOMMENDED CHANGES IN ORCHARD MANAGEMENT BASED ON INITIAL FINDINGS Tree changes: Pruning Gi rdl ing Top-working Other Di sease control : Insect control Cul ti vation: Organic matter use: Irrigation practice: Fertilizer management: Other: I 22 1 TABLE 2. — Means by Which Nutrient Status of Citrus Can Be Determined Condition Early stage (See tables 3 and 4 for leaf and soil analysis criteria and table 8 for control methods) Moderate-to-acute stage (See tables 3 and 4 for leaf and soil analysis criteria and table 8 for control methods; Boron Deficiency 1. Leaf analysis for total and water-soluble boron supple- mented by soil analysis for water-soluble boron will give indications. 2. Confirmation by foliar spray trials or soil applications of boric acid or borax usually necessary. 1. Leaf analysis and visual symptoms usually sufficient 2. In case of doubt make soil analysis for water- soluble boron. 3. Confirm if necessary by foliar sprays or soil applica- tion of boric acid or borax. Excess 1. Leaf pattern, confirmed by leaf analysis, usually suffi- cient. 1. Leaf pattern confirmed by leaf analysis. Calcium Deficiency 1. Leaf analysis supplemented by soil tests for pH and possibly exchangeable Ca in soils will give indications but 2. Confirmation by application of calcium compounds to soil necessary. 1. Leaf analysis coupled with visual symptoms and 2. Confirmed by soil applications of soluble calcium compounds. Excess 1. Leaf analysis coupled with soil analysis for soluble calcium (little data exist as to specific toxicity of cal- cium; hence considerable uncertainty surrounds this condition and its diagnosis). 1. Leaf analysis coupled with soil analysis for soluble soil calcium (little data exist as to specific toxicity effects of soluble calcium). Copper Deficiency 1. Leaf analysis and soil tests for total and 0.1 N HCI soluble Cu in soil will give indications. 2. Confirmation by use of foliar sprays usually necessary. 1. Visual symptomatology usually sufficient. 2. If confirmation required, make leaf analysis. 3. For further confirmation (not usually needed; try foliar sprays. Excess 1. Leaf and root analysis supplemented by 2. Soil analysis for total and 0.1 N HCI soluble copper. 1. Leaf and root analysis supplemented by 2. Soil analysis for total and 0.1 N HCI soluble copper. Iron Deficiency 1 . Leaf pattern usually sufficient but leaf analysis can be used to confirm. 2. Further confirmation can be had with foliar spray of iron sulfate or iron chelate. 3. Soil examination for pH, lime, and heavy metals and moisture status may be useful in indicating cause. 1. Leaf patterns sufficient but confirmation can be had by leaf analysis and 2. Foliar sprays using iron sulfate or iron chelates. 3. Soil examination may be useful in indicating cause. Excess No data available. No data available. Molybdenum Deficiency 1. Leaf analysis, supplemented by 2. Soil analysis for total and ammonium oxalate extract- able Mo and 3. Confirmed by foliar sprays or soil analysis. 1. Leaf patterns confirmed by leaf analysis, and trials with foliar sprays or soil applications of sodium molybdate. 2. Soil analysis for total and ammonium oxalate ex- tractable Mo (not usually necessary). Excess 1. Insufficient information on effects. Leaf and soil analysis may be indicative. 1. Insufficient information on effects. Leaf and soil analysis may be indicative. Nitrogen Deficiency 1. Leaf analysis for total N indicative but 2. Soil analysis for nitrate, or nitrate-producing capacity can help confirm. 1. Leaf color confirmed by leaf analysis for total N. Excess 1. Leaf analysis supplemented by soil analyses can give indications. 1. Leaf analysis supplemented by soil analyses. Phosphorus Deficiency 1. Leaf analysis supplemented by 2. Soil analysis for 0.5M Na bicarbonate soluble P, and confirmed by 3. Trials with phosphorus fertilizer added to the soil. 1. Leaf analysis, visual symptomatology and confirmed by 2. Soil analysis for 0.5M sodium bicarbonate soluble P. 3. Application of phosphate fertilizer to soil will provide further confirmation. Excess 1. No clear-cut criteria, but soil analysis for 0.5M Na bicarbonate P will provide some indications. 1. No clear-cut criteria but soil analysis for 0.5M Na bicarbonate P plus leaf analysis may give indications. Chlorine Deficiency No critical data established. No critical data established. Excess 1. Leaf analysis supplemented by 2. Soil analysis for water-soluble chloride in saturation or other water extract. 1. Leaf analysis and visual symptoms supplemented by 2. Soil analysis for water-soluble chloride in saturation or other water extract. [23] TABLE 2. — Continued Condition Early stage (See tables 3 and 4 for leaf and soil analysis criteria and table 8 for control methods) Moderate-to-acute stage (See tables 3 and 4 for leaf and soil analysis criteria and table 8 for control methods) Magnesium Deficiency 1. Leaf patterns supplemented if need be by 2. Leaf analysis. 3. Soil analysis useful in indicating reasons for defi- ciency. 1. Leaf patterns usually sufficient. 2. Leaf analysis will provide confirmation. 3. Soil analysis useful in indicating reasons for defi- ciency. Excess 1. Soil analysis for water-soluble Mg in saturation ex- tract indicative; determinations of total magnesium in soil and tests for presence or absence of magnesium carbonates and basic carbonates. 2. Leaf and root analysis may provide further indications. 1. Soil analysis for water-soluble Mg in saturation ex- tract useful; determination of total magnesium in soil and tests for presence or absence of magnesium carbonates or basic carbonates. 2. Leaf and root analysis will give further indications. 3. Excess magnesium may bring about iron chlorosis leaf patterns. Manganese Deficiency 1. Leaf patterns usually sufficient. 2. Leaf analysis will provide further confirmation. 3. Can further confirm with foliar sprays with manganese sulfate. 4. Soil analysis can be made but leaf patterns and analy- sis are sufficient for positive diagnosis. 1. Leaf patterns sufficient generally. 2. Leaf analysis will provide further confirmation. 3. Can further confirm with foliar sprays of manganese sulfate. Excess 1. Leaf analysis supplemented by 2. Soil analysis for total and easily reducible manganese. 1. Leaf patterns supplemented by leaf analysis. 2. Soil analysisfor total and easily reducible manganese. Potassium Deficiency 1. Leaf analysis supplemented by 2. Soil analysis for exchangeable K and 3. Confirmed by soil fertilizer tests. 1. Leaf analysis supplemented by 2. Visual symptomatology usually sufficient. 3. Soil analysis for exchangeable K, confirmed by soil fertilizer tests, will provide confirmation. Excess 1. Leaf analysis supplemented by 2. Soil analysis for exchangeable and water-soluble K will give indication, but exact criteria lacking. 1. Leaf analysis supplemented by 2. Soil analysis for exchangeable and water-soluble K. Sulfur Deficiency 1. Leaf analysis supplemented by 2. Soil analysis for total S and soluble sulfate and checked by 3. Field fertilizer tests. 1. Leaf analysis and visual symptomatology supple- mented if need be by 2. Soil analysis for total S and soluble sulfate. 3. Further confirmation can be had from field fertilizer tests. Excess 1. Soil analysis for sulfates and 2. Leaf analysis for total sulfur. 1. Soil analysis for sulfates and 2. Leaf analysis for total sulfur. Zinc Deficiency 1. Leaf patterns are usually sufficient; can confirm if necessary by 2. Leaf analysis and spray trials. 1. Leaf pattern and other symptoms are clear-cut; hardly ever necessary to confirm by leaf analysis or spray trials. Excess 1. Soil analysis for total and 0.10N HCI soluble zinc in soil and supplemented by 2. Leaf analysis. 1. Soil analysis for total and 0.10N HCI soluble zinc in soil and supplemented by 2. Leaf analysis. Salinity Excess 1. Soil analysis of saturation extract for soluble salts in various horizons of root zone coupled with 2. Leaf and root analyses. 1. Soil analysis of saturation extract for soluble salts in various horizons of root zone coupled with 2. Leaf and root analyses. Trace elements not essential for plant growth, such as lithium, nickel, cobalt, etc. Excess 1. Leaf and root analysis, and/or 2. Visual symptoms, and/or 3. Soil analysis will provide indications as to status; posi- tive in some cases, inconclusive in others. 1. Leaf and root analysis, and/or 2. Visual symptoms, and/or 3. Soil analysis will provide indications as to status. |24 1 TABLE 3. — Leaf Analysis Standards for Assessing Current Nutrient Status of Citrus Trees (Based on 4- to 10-month-old spring cycle leaves from fruit-bearing terminals) Element Calcium (Ca). . Magnesium (Mij Nitrogen (N) . . . Phosphorus (P) . Potassium (K).. Sulfur (S) Sodium (Na) . . . Chloride (CI) . . . Deficient range Low range Satisfactory range. High range Excess range in per cent of dry matter of leaf <2.0 0.05 0.15 0.60 1.90 <0.07 0.15-0.30 0.05-0.13 2.0 2.9 0.16 0.20 1.90 2.10 0.07-0.11 0.40-0.90 0.14-0.19 0.01-0.06 3.0^.0 0.30 0.60 2.20 2.70 0.12-0.18 1.00-1.70 0.20-0.30 0.01-0.15 0.02-0.15 6.1 6.9 0.7CM.0 2.80 3.50 0.19 0.29 1.8(M.90 0.40 0.49 0.20 0.25 0.20 0.30 >7.0? >1.0? ^3.60? ^0.30? >2.00? >0.50 >0.25 >0.40 in ppm dry matter of leaf Boron (B) Copper (Cu) Iron (Fe) Manganese (Mn) . Molybdenum (Mo) Zinc (Zn) Aluminum (Al) . . . Arsenic (As) Barium (Ba) Bromine (Br) Chromium (Cr)f. . Cobalt (Co) Fluorine (F) Gallium (Ga) Indium (In) Iodine (I) Lead(Pb)t Lithium (Li) Nickel (Ni)t Silver (Ag)t Strontium (Sr) Tin(SN)t Titanium (Ti) Vanadium (V)f. . . Zirconium (Zr) <15.0 <4.0 <40.0 5.0-20.0 0.01-0.05 4.0-15.0 15.0-40.0 4.1-5.0 40.0-60.0 21.0-24.0 0.06-0.09 15.0-24.0 6.0-20.0 <1.0 5.0-20.0 ? Tr.-0.20 <0.4 < 1.0-5.0 <1.0 <1.0 <0.5 <0.5 <0.5 <0.05 30.0-90.0 >1.0 0.3.30 1.5-3.0 ? 50.0-200.0 5.1-15.0 60.0-150.0 25.0-100.0 0.10-3.0 25.0-100.0 6.0-30.0 <1.0 5.0-49.0 ? Tr.-0.50 Tr.-0.4 < 1.0-20.0 <1.(M.O <1.0 <1.0 0.5-0.9 <0.5-1.0 < 0.5-0.7 30.0-90.0 >1.0 0.3-3.0 1.5-3.0 ? 200.0^250.0 15.0-20.0? > 150.0 100.0^200.0 4.0-100.0 110.0-200.0 40.0-200.0 >1.0 50.0-200.0 200.0-1000.0 1.0-? ? 25.0-100.0 5.0-10.0 1.0-2.0 2.0-20.0 1.0-5.0 1.(M.0 0.1-4.0 100.0-1000.0 4.0-12.0 4.0-20.0 ? ? > 250.0 >20.0? ? 300.0-1000.0? >100? >200? ? >5.0 ? 1000.(M0OO.0 ? ? > 100.0 ? ? ? 12.0-200.0 8.0-up ? ? ? ? ? ? * There is no evidence that these elements are essential for higher plants; nonetheless, they influence plant behavior. t Low levels of these elements in leaves may not necessarily denote absence of harmful amounts in the soil; some of these exert toxic effects on root tissue and decrease growth, but are not appreciably transported to leaves. ? Indicates that doubt exists regarding the values, but is the best current estimate available. [25] CO CD a c 03 CO 75 OC Chapman and Vanselow (1955) CD •s- O c CS E Q. CS JC o B thurst (1958) as quoted by De Villiers et al. 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L. o o o CD at c 03 03 > ■o c CD ea c re > 03 O 1- CO CO o> a> c E 3 3 U o c E o O E E CD CD "■ -1 o E — ■a CD C3) C 03 CD C 03 o >. CD C CD £ CD "" c > on Cfi o»J= «^ CD C 03 SZ 3 ' -3 ~ CD 5 a> U > — c vt- 3 CB rt -7; w »r > CD Sg e h- a ^ * "w H — CD CO 03 S3 E 3 E I _3 < E 3 03 00 03 O o E ■o 03 o E 3 1 1 E 3 03 -a 1 o c V) o 53 E 3 '■5 OS c 03 > [33] TABLE 5. — Analysis Values Useful in Evaluating Soil constituent Method and/or fraction and basis of expressing result Range* Deficient or un- satisfactory range Low range Ample or satis- or measurement Extreme Usual factory range Soil pH Glass electrode on 1:2.5 soil- water suspension 3.0-10.0 4.5-8.5 <4.5 4.5-5.2 5.5-7.5 Electrical conduc- tivity (Ec X NPat 25° C.) Ec X 10 3 at25°C.(millimhos/ cm) on saturation extract of soils (these determinations should be made on successive 1 -ft. horizons of the soil to a depth of 5 or 6 feet) <0.1->20.0 0.1-10.0 t 0.2-1.0 0.2-1.9 Total soluble solids In saturation extract ex- pressed in ppm dry soil <100.0-> 3000.0 <100.0-1500.0 t 100.0-500.0 100.0-2000.0 In 1-5 soil water extract ex- pressed in ppm dry soil <1 00.0-1 5,000.0 300.0-1500.0 t 50.0-250.0 50.0-850.0 Soluble salt con- stituents (1) Bicarbonate (HC0 3 ) Saturation extract expressed as me/I of extract <0.1 0-20.0 <0.1 0-5.0 t 0.10-0.50 0.10-2.50 In 1-5 soil-water extract ex- pressed in ppm dry soil <6.0->600.0 50.0-250.0 t <6.0-50.0 < 6.0-1 00.0 (2) Carbonate (C0 3 ) In saturation extract ex- pressed as me/I of extract Trace->1.0 None t 0.0 0.0 (3) Chloride In saturation extract ex- pressed as me/I of extract <0.1->100.0 <0.1-5.0 No data available as to deficient range 0.20-2.0 < 0.2-5.0 In 1-5 soil-water extract ex- pressed in ppm dry soil <10.0-> 2000.0 < 10.0-350.0 No data available as to deficient range < 10.0-75.0 <10.0-75.0 (4) Calcium (as a salt con- stituent) In saturation extract ex- pressed as me/I of extract <0.1->150.0 <0.1-10.0 (Asa plant nutrient, see elsewhere) <0.1-1.0 1.0-10.0 (6) Magnesium fas a salt con- stituent) In saturation extract ex- pressed as me/I of extract <0.2->30.0 <0.2-5.0 (Asa plant nutrient, see elsewhere) < 0.2-3.0 <0.2-5.0 (6) Sodium In saturation extract ex- pressed in me/I of extract <0.1 -150.0 <0.1-5.0 t <0.1-2.0 <0.1-3.5 In 1 -5 soil-water extract expressed as ppm dry soil <0.1 3000.0 20.0-250.0 t <5.0 30.0 <5.0-50.0 Exchangeable as per cent of exchange capacity <1.0->25.0 < 1.0-5.0 t 1.0 5.0 1.0-10.0 * These are values derived from existing research sources: the wide lack of agreement between 1 5 saturation extract and Ec X 10 3 values is due to the varying sources from which data were obtained. t Does not apply. I 34 ] alinity and Nutrient Status of Citrus Soils High range (Corrective eatment may be necessary) 8.0-8.5 Excess range (Corrective treatment necessary) >8.5 2.0-4.0 2000.0-3000.0 850.0-1500.0 2.5-5.0 100.0-200.0 Trace 5.0-10.0 100.0-150.0 10.0-20.0 10.0-20.0 5.0-15.0 100.0-150.0 10.0-15.0 >4.0 > 3000.0 > 1500.0 >5.0 > 250.0 Tr.-1.0 10.0-> 100.0 > 200.0 >30.0 Remarks >15.0 > 150.0 >15.0 There is no one pH value "best" for citrus, but soils in the pH 5.5 to 7.5 range are often more fertile and trouble-free than those higher or lower. pH values of 5.0 or under may be indicative of both deficiencies or unavailability of such elements as Ca, Mg, P, Mo, etc., or of toxicity from increased solubility of Win, Zn, Al, B, and other elements. Addi- tions of lime or dolomite will correct calcium and magnesium defi- ciencies, overcome toxicity due to excess heavy metal solubility, and may increase phosphorus and molybdenum availability. pH values above 8.5 indicate the presence of sodium carbonate and the need to treat with gypsum, sulfur, or other materials. pH values of 8.0 to 8.5 may denote the presence of free lime; in addition, manganese, zinc, copper, phosphorus, and iron are quite often difficultly available. Electrical conductivity is an indication of total soluble salt in solu- tions. These values provide general guidance only; climate and the particular rootstock-top combination used have an important bearing. Values of Ec X 10 3 of 2.0 or over in any soil horizon of root zone should be looked upon with suspicion, and irrigation practices modified so as to reduce the salt concentration by further root-zone leaching. Total soluble solids in the saturation extract is an expression of total salinity or salt content of the soil. When values exceed 2000 ppm in any part of the root zone, irrigation practices should be modified so as to reduce the salt concentrations. One to five soil water extracts were commonly made by earlier workers to determine the salinity of soils. Some laboratories still use this procedure. The same qualifications and suggestions apply as under the above. As with total soluble salts, no precise limits can be set owing to the modifying influences of soil, climate, rootstock-scion, and the char- acter of accompanying anions; but where values in the high and excess ranges are found anywhere in the root zone, leaching should be increased. Whenever any normal carbonate is found anywhere in the root zone it should be corrected by applications of gypsum, sulfur, or other acid materials, and by leaching the products out of the root zone. See comments under bicarbonate. Little or no data are available concerning the specific toxicity of calcium itself; it is the anion (S0 4 , N0 3 , or CI) associated with it which is probably most important. Not enough is known about magnesium toxicity in relation to citrus; however, it is more toxic than calcium and amounts over 15-20 me/I in saturation extract would suggest need for leaching. Adverse effects on plant growth will result from too much soluble sodium; not only as a direct toxicant in the plant, but because of ad- verse effects on soil structure, permeability of the soil, and soil pH. The degree of toxicity of soluble sodium in the soil solution will be strongly influenced by the amount of soluble calcium present and the character of the prevailing anions. Whenever sodium exceeds 10 per cent of the exchange capacity of soils, the use of gypsum followed by leaching is indicated. Literature citations Discussions of pH in relation to plant growth may be found in nearly all textbooks on soil. See: Allaway (1957) and Millar '1955 for sample discussions. U. S. Dept. Agr. Handbook 60, L. A. Richards (Ed.) (1954) Harding and Chapman (1950) Harding, Pratt, and Jones (1958) Chapman and Harding (1956) Kelley and Thomas (1920) Harding and Chapman (1950) U.S.D.A. Handbook 60 (1954) Kelley and Thomas (1920), and Chapman, Laurance, and Harding (unpub. Calif, data) Harding and Chapman (1950) Harding and Chapman (unpub. data) U.S.D.A. Handbook 60 (1954) Kelley and Thomas (1920), and Chapman, Laurance, and Harding (unpub. data) Harding and Chapman (1950) Harding and Chapman unpub. data) U.S.D.A. Handbook 60 (1954) Harding and Chapman (unpub. data) Kelley and Thomas (1920), and Chapman, Laurance, and Harding (.unpub. data^ Martin, Harding, and Murphy (,1953^ [35] TABLE 5.-A Soil constituent Method and or fraction and basis of expressing result Range Deficient or un- satisfactory range Low range Ample or satis- factory range < or measurement Extreme Usual (7) Sulfate In saturation extract ex- pressed in me 1 of extract < 0.5-1 00.0 < 5.0-20.0 (See under sulfur as a plant nutrient) < 0.5-5.0 <5.0-20.0 In 1-5 soil-water extract expressed as ppm dry soil < 25.0- > 8000.0 <25.0-500.0 <25.0-100.0 <25.0-0.350 Potassium In saturation extract ex- pressed in me/I of extract Tr.-1.0 1.0-5.0 Exchangeable K as per cent of exchange capacity 2.0-10.0 Boron Total boron in soil expressed in ppm dry soil <2.0-> 100.0 2.0-100.0 Tr-10.0 <10.0 Water-soluble in 1 :2 soil-water suspension. Reflux method of Berger and Truog (1939) in ppm dry soil 0.1-0.5 0.5 Water-soluble 1:1.5 extract expressed in ppm dry soil 1:2 soil-water extract ex- pressed as ppm dry soil Tr.->21.0 Tr.->21.0 Tr.-0.30 Soxhlet extract by method of McClung and Dawson (1951) 0.03-0.37 Copper Total copper in soil expressed in ppm dry soil < 1.0-5000.0 2.0-100.0 1 1N HCI extract expressed in ppm dry soil < 10.0-300.0 25.0 0.1 N HCI extract expressed in ppm dry soil 0.9-1.6 Aspergillus niger expressed in ppm dry soil 0.4-1.2 >2.0 Calcium Total Ca in lime-free soils expressed as ppm dry soil 860.0-20,000.0 < 1000.0 i In saturation extract ex- pressed in me/I of extract <0.1->150.0 <0.1-10.0 <0.1-2.5 1.0-10.0 Exchangeable Ca as per cent of exchange capacity. 5.0-95.0 50.0-85.0 <25.0 25.0^10.0 75.0-90.0 pH of 1 :2 soil-water sus- pension <5.0 5.0 5.5 5.5-8.5 Iron Total iron in soil in per cent dry weight 0.2^10.0 1.5-4.5 I [ 36 1 )ntinued High range Corrective >atment may be necessary Excess range 'Corrective treatment necessary) Remarks Literature citations 20.0-30.0 >30.0->100.0 The detrimental effect of soluble sulfate is conditioned in part by the dominating cation. If it is calcium, sulfate is less detrimental than when sodium is the dominant cation. As with all other salt constitu- ents, the degree of toxicity is dependent on soil, climate, and root- stock-scion variables. Save in soils containing gypsum, high sulfate values indicate a need for leaching. Harding and Chapman unpub. data U.S.D.A. Handbook 60 1954 150.0-1500.0 > 350.0 Kelley and Thomas 1920 , and Chapman, Laurance, and Harding unpub. data 6.0-10.0 Where heavy manuring has been practiced, potassium occasionally builds up to toxic levels. Precise data are not at hand, but the data shown are of guidance value. Harding and Chapman unpub. data 12.0-15.0 >15.0 Martin, Harding, and Murphy 1953 Although total boron in soils is not a good indicator of need, it gives a base figure of value in indicating total reserves. Swaine 1955 Whetstone et al. 1942 >1.3 Deficient range values are based on crops other than citrus; none- theless, values in this range would provide guidance information. Whetstone et al. 1942 Penman and McAlpine 1949 Bray 1948 0.73-1.72 Various citrus species showed boron toxicity leaf patterns when grown in soils containing soluble boron in excess of 0.73 ppm. Eaton and Blair 1935 0.50^20.0 Leaf symptoms typical of excess boron were found on citrus trees where soluble boron was in excess of 0.50 ppm. Kelley and Brown 1928 These are values for crops other than citrus but have suggestive value. Baird and Dawson 1955 100.0 in acid soils As with other elements, total copperisnotareliableguideasto need, but gives some idea of basic reserve supply and possible excess. Reuther and Smith 1953 Swaine 1955 . Reuther 1957 Data from Florida citrus soils. Spencer 1954 Data from apple orchards. Bould etal. H950 Data on apple and pear soils. Bould etal. '1953 Total calcium in soils is of chief value in indicating reserve supply; soil pH and exchangeable calcium both total and as per cent of ex- change capacity are far more important in indicating the status of available calcium. Millar 1955 Water-soluble calcium is chiefly useful in indicating whether there is an ample supply in soil; low values do not necessarily indicate deficiency. Harding and Chapman 1950 Exchangeable calcium may be low either because of excess soil acidity high exchangeable hydrogen ion» or high exchangeable so- dium and or potassium. Other Ca forms and type of clay are also factors. Chapman unpub. data", Vlamis 1949 . Strauss and Grizzard 1947 work on peanuts by latter Of guidance and suggestive value only. Many investigators So many factors influence iron availability e.g.. pH, lime content, nature of iron-bearing minerals, heavy metals such as zinc and cop- per, moisture, temperature, and soil organisms that few attempts have been made to work out iron availability tests. Chapman 1952 [37] TABLE 5.- Soil constituent Method and /or fraction and basis of expressing result Range Deficient or un- satisfactory range Low range Ample or satis- factory range ^ or measurement Extreme Usual Magnesium Total Mg in nonearbonate con- taining soils in ppm dry soil 200.0-13,400.0 < 2400.0 Ratio of exchangeable K:Mg 0.30-0.79 0.5(M).90 0.3-0.9 0.1-0.3 0.20^6.00 Exchangeable Mg expressed as me 100 g of soil 0.04 0.20 Exchangeable Mg as per cent of total exchange capacity <6.0 Manganese Total manganese in soil in ppm dry soil 1.0-70,200.0 200.0-3000.0 Exchangeable Mn in ppm dry soil 5.0-20.0 0.5 <1.5 >1.5 Easily reducible 0.2 r c quinal in ppm dry soil <80.0 > 100.0 Soluble in 3N NH4H2PO4— ppm dry soil 5.0-60.0 <20.0 <30.0 30.0-60.0 Molybdenum Total molybdenum in ppm dry soil < 0.5-200.0 0.2-5.0 <1.0 Ammonium oxalate extract- able Mo in ppm dry soil 0.04 0.12 Nitrogen Total nitrogen in ppm dry soil 100.0-> 10,000.0 Nitrate (NCh) in ppm dry soil <5.0 Phosphorus Total phosphorus in soil as ppm Water-soluble P by Bingham 1949) method in ppm dry soil < 100.0-1 0,000.0 3000.0^4000.0 < 300.0 <0.30 < 0.30-0.50 0.50-2.0 Water-soluble P in 1 5 soil- water extract in ppm Acid-soluble P by Truog '1930 method in ppm dry soil <0.03 44.0 <30.0 900.0 <0.03 6.5 <0.03 0.03 0.30 0.30 16.0 <30.0 300.0 <30.0 <30.0 50.0 38 I )ntinued High range (Corrective atment may be necessary) Excess range (Corrective treatment necessary) Remarks Literature citations Total magnesium is of very limited value in indicating available supply but does give some idea of reserve in soil. Millar (19551 These are ranges of values found in Australia citrus soils where Mg deficiency patterns were studied by Parberry. Parberry (1935) These are values found in California citrus orchards. Bingham et al. (1956) These are values found in magnesium-deficient apple orchards. Boynton (1954 1 These are values found in Florida sandy soils where citrus shows Mg deficiency. Peech (1939) Various field and vegetable crops in New Jersey soils showed mag- nesium deficiency when exchangeable magnesium constituted less than 6 f " c of total exchange capacity. Prince et al. (1947) Total manganese is of value in indicating total reserve in soil, but not with regard to availability. Swaine (1955) Work on citrus soils. Connor (1954) Work with French beans. Fergus (1954) Data on Florida citrus soils. Peech (1939) >500 Work with French beans. Leeper (1935, 1947), Fergus (1954) Field and vegetable crops. Sherman and Harmer (1942) Data secured on soybean soils in Ohio. Hoff and Mederski (1958) Total molybdenum in soils is of chief value in indicating total re- serve, and, if on the very low side, suggestive of possible deficiency. Anderson (1956) Swaine (1955) Walker (1948) Walsh, Neenan, and O'Moore (1952) Total nitrogen is of little value in indicating available supply, but a rule of thumb figure for nitrate nitrogen is used by some commercial laboratories. The figure of 5 ppm is used as a guide; if values are less than this, fertilization is recommended; if more, nitrogen is withheld. Experience of several commercial labora- tories in California which carry on advisory service for citrus growers. Total phosphorus, save where it is very low, is of little value in diag- nosing phosphorus state; however, Aldrich and Buchanan (1954) found that many phosphorus-deficient soils showed less than 300 ppm P. Chapman (1934) Aldrich and Buchanan (1954) Limited data on citrus soils showed that those orchards where P deficiency occurred contained less than 0.30 ppm water-soluble P. Aldrich and Buchanan (1954) In pot culture and field trials witn citrus, fair correlations between phosphorus content and response to fertilizers were obtained. Chapman (1934) On noncalcareous soils, phosphorus soluble in 0.002N H SO (Truog, 1930) gives indications of value. Aldrich and Buchanan (1954) Chapman (1934) [39] TABLE 5.- Soil constituent Method and or fraction and basis of expressing result Ranges Deficient or un- satisfactory range Low range Ample or satis- factory range or measurement Extreme Usual i Phosphorus (cont.) 0.5M sodium bicarbonate extract expressed as pounds Pl'Oj per acre < 25.0-50.0 <50.0 >50.0 Potassium (see under soluble salts for toxicity point of view) Total potassium in soil ex- pressed as ppm dry soil 500.0-50,000.0 500.0-30,000.0 Exchangeable potassium ex- pressed in pounds/acre <100.0 >200.0 Sulfur (see under soluble salts for toxicity levels of sulfate) Total sulfur in soil expressed as ppm dry soil 40.0-1040.0 < 200.0 Morgan's Na acetate-acetic acid extract in ppm dry soil <3.0 Zinc Total zinc in soil expressed as ppm dry soil <5.0-> 2000.0 10.0-300.0 < 100.0 Ammonium acetate dithizone extract in ppm dry soil <1.0 ppm in soils of pH 7.0 and above >2.0 ppm in soi of pH 6.0 and lower Ammonium acetate (pH 4.6) extract expressed in ppm dry soil 0.5-3.9 <1.5 >2.0 0.1 ON HCI extract expressed in ppm dry soil 10.0 0.10N HCI extract expressed in ppm dry soil 0.5-0.9 >1.20 0.10N MgS0 4 extract ex- pressed in ppm dry soil <1.0 i I -10 1 )ntinued High range (Corrective atment may be necessary) Excess range (Corrective treatment necessary) Remarks Literature citations Values are based on field and vegetable crops; however, this method gives results of considerable guidance value for citrus. Olsen, Cole, Watanabe, and Dean (1954) Total potassium is of little value in indicating anything about available supply, save that where it is very low the likelihood of de- ficiency is increased. These data are based on experiments with field crops in Illinois and probably apply only in a very limited way to citrus; however, these figures provide some guidance value. In general, water-soluble and exchangeable potassium provide only limited information. Low values do not necessarily indicate deficiency; high values, however, probably indicate sufficiency. Bray (1948) Total sulfur provides some information of value in indicating po- tential supply, and if on the very low side the likelihood of a deficiency developing is very real unless sufficient sulfur from fertilizers, ma- nure, air pollution, rain, irrigation water, insecticides or fungicides is periodically supplied. Millar (1955) Based on experiments with cotton, clover, and tobacco. Jordan and Bardsley (1958) >200.0 Total zinc is chiefly of value in indicating potential reserve supply in soil; many factors affect availability to plants. Swaine (1955) Thorne et al. (1942) Results were obtained on a variety of soils and crops and might provide some guidance value for citrus. Shaw and Dean (1952) Work done on pineapple soils. Lyman and Dean (1942) Work on apple soils. Bould etal. (1950) Work on corn soil. Wear and Sommer (1947) > 100.0 Work on soy bean and cereal soils. Berg (1947) [41] TABLE 6. — Suggested Form for Record of Leaf and Soil Analysi* Grove designation Leaf analysis data Visual symptoms ( Year Date of sampling Per cent in dry matter of leaf ppm in dry matter of leaf Date Indicated deficiency \ < Ca Mg N P K S Na CI B Cu Mo Mn ■j. i 1 |42 1 utilizer and Pest Control Program, and Grove Performance dck No Sampling unit Soil analysis Fertilizer program Soil management practices Pest and disease control treatments Yield and quality )ate of impling Ec X 10 3 saturation extract Other Date Material applied and method Date Pest Materials used Field boxes per tree Peak size Qual- ity 0-1 ' 1-2' 2-3' 4-5' 5-6' [43] TABLE 7. — Control of Mineral Deficiencies and Excesses of Citrus Element Methods of control or amelioratiDn Supplementary remarks Soil treatment Foliar spray Other methods Boron deficiency 3 oz. borax /tree broadcast on sandy Fla. soils. Up to 35 oz. per tree used by Morris (1938) on heavy soils in South Africa. One application will usually last for several years. 1 lb borax or boric acid to 100 gal water suitable; skele- ton spray. 1. Acidification of neutral or alkaline soils will release boron. 2. Drought tends to aggra- vate boron deficiency; therefore, adequate mois- ture will help where boron is low. 1. Soil application methods prefer- able but sprays useful where quick tests or response desired. 2. Avoid too-heavy applications as boron is very toxic to citrus. 3. Many fertilizers and most organic materials contain enough boron to meet citrus needs (40,000 lbs of oranges, a heavy crop, re- move only about 0.10 lb of boron from the soil.) 4. Irrigation waters containing 0.10 ppm B or more will normally meet citrus needs. 5. Boron is less readily absorbed by sour orange roots than by some other rootstocks. Boron excess 1. Excess boron can be slowly leached out of soil; soil acidifi- cation will make boron soluble and increase rate of outgo by leaching, but temporarily in- crease injury. 2. Lime additions will decrease boron solubility. 3. Calcium nitrate fertilizer is bet- ter than other N forms where high boron-containing waters are used or soil is naturally high in boron. 4. Acidic fertilizers such as am- monium sulfate will increase B solubility and produce more in- jury temporarily, but will also speed leaching of boron. No data known to author, but nitrogen (urea) sprays might help to decrease toxicity. Determine source of boron excess and correct if possible. 1. Where excess boron is a problem due to irrigation water content, use of ample irrigation water and good amounts of Ca(N03)2 fer- tilizer will help. 2. Change to low boron content irri- gation water if possible. 3. Intercrop citrus with a crop which can be harvested and produces a good tonnage. This will help re- move boron and also aid water penetration and boron outgo from the soil. Calcium deficiency Use of Ca(N03)2 fertilizer at rates to supply nitrogen needs (2-3 lbs N/tree) should correct Ca deficiency. 2. Lime at rates of 1-4 tons per acre on acid soils. 3. Ca(SC>4)2 (gypsum) at rates of 1-5 tons per acre where Ca de- ficiency is due to high sodium content. De Villiers (private corre- spondence) in South Africa reported that 2-3 sprays with Ca(OH) 2 (10 lbs/100 gal.) corrected calcium deficiency of citrus. 1. On acid soils, lime is the best cor- rective. 2. On alkaline soils (excess sodium) Ca(S04)2 is the best corrective. 3. Use of calcium-containing ferti- lizers is recommended to supply N, and where P2O5 is needed, use single strength superphosphate. Calcium excess 1. Leaching by irrigation water to remove soluble salts. 2. Use of ammonium sulfate, sul- fur, or other acids to solubilize lime; followed by leaching; practicable only where soil con- tains less than 0.5 per cent CaCd. Excess phosphate aggra- vates Cu deficiency and phos- phate - containing fertilizers and manures may need to be discontinued. 1. Excess calcium occurs either where there is alkali salt accu- mulation and/or lime carbonate. The former can best be removed by leaching; the latter is difficult to remove except by long-con- tinued use of acid fertilizers and leaching. Copper deficiency Soil treatment not recommend- ed for citrus in general, though on acid Bands in Florida it is common to recommend 1/8 to 1/2 lb of CuSOi. 5H. ? per tree as a pre- ventive. Others have found soil applications of 1/4 lb CuSOi • 5HO per tree effective. 1. 3 lbs CuSOi and 4.5 lbs hyd. lime to 100 gal. water as a foliar spray. 2. Can be combined with zinc sulfate and manga- nese sulfate where Zn and Mn deficiencies also occur. 3. McCleery and Stokes (1929), in Australia, found a 6-4-100 Bordeaux effec- tive on oranges, lemons, and mandarins. Foliar sprays are best treatment; sometimes two sprayings are neces- sary to achieve control. Correction will usually last from 1 to 3 years. Spring, summer, or fall sprays usually give better results than winter sprays. [441 TABLE 7. — Continued Element Methods of control or amelioration Supplementary remarks Soil treatment Foliar spray Other methods Copper excess Additions of lime and/or phos- phate fertilizer will reduce copper solubility in soil. Iron chelates may be beneficial where excess copper has induced iron chlorosis. Copper excess has developed on Fla. soils from the prolonged use of Bordeaux sprays. Iron chelates, su- perphosphates, and where the soil is quite acid, lime to correct the acidity will help overcome the copper toxicity. Iron deficiency 1. Iron chelates (ethylene-diami- netetraacetic acid; various iron salts of). (EDTA) At 20-500 grams per tree on acid sandy soils applied broadcast every 1 to 2 years very effective on citrus. Cooper (1957) found that 5 grams metallic Fe equiva- lent of Chel. 138 H Fe, and RA 157 Fe were highly effective on calcareous fine sandy loam soil, pH 7.9, with 3-yr.-old Dancy tangerines on Cleo mandarin rootstock. 2. On some sandy soils, iron sul- fate at rates of 1-5 lbs per tree have proved successful but chelates are preferred. 3. Acid peat treated with FeSCh has been helpful with some crops. 4. Prefumigation of soil prior to planting citrus has proven helpful on some soils. FeSOi solutions with spreaders are somewhat suc- cessful as are chelates, but there is danger of rind injury to fruit and improvement in foliage chlorosis is temporary. Commercial practicality still somewhat in doubt. 1. Careful control of irriga- tion to prevent prolonged overmoist condition in lower root zone very often effective; alternate middle irrigation often helpful. 2. Leaching of soluble salts where present in signifi- cant amounts is often help- ful. 3. Where due to heavy metal solubility, liming to bring pH to 6.0 or 6.5 may prove helpful. Iron deficiency ^chlorosis; in citrus can be brought on by various condi- tions such as: 1. Cold soil-temperatures in winter. 2. Overmoist subsoil conditions. 3. Excessive soluble salts in soil. 4. Excessive lime in soil. 5. Excesses of heavy metals such as zinc, copper, nickel, chromium, etc. These are often solubilized when soil becomes too acid. 6. Nematodes and various patho- genic soil organisms may be a cause. Correction can often be achieved by eliminating or correcting the basic cause or causes. Iron excess Soil liming where due to exces- sive soil acidity would be a natural corrective. (See under supplemen- tary remarks.) No specific cases of excess iron on citrus are known to the author ; none- heless, there is no good reason to suppose that this condition might prevail, especially where soils are very acid, or where reducing condi- tions are present. Mag- nesium deficiency 1. Epsom salts (MgS0 4 • 7H 2 0) applied at rates of 3-30 lbs per acre. 2. On acid sandy soils, 3-16 lbs per tree effective. 3. Dolomite at 1-2 tons per acre also effective on acid soils, par- ticularly sandy soils. Amount used should be such that pH of soil not raised beyond pH 6.5. 1. Two to four sprays with 2% to 4% solutions of Epsom salts are reported by Herschberg (1951) and others to correct Mg defi- ciency of citrus. Fe, Zn, and Mn added to the sprays aided in the correc- tion of Mg deficiency. 2. Embleton and Jones (1959) have secured correction by use of 10 per cent mag- nesium nitrate foliar spray. Adequate nitrogen fertiliza- tion often clears up Mg defi- ciency of citrus (see under supplementary remarks). 1. Soil applications of magnesium sulfate are preferred where defi- ciency is due to excess exchange- able K build-up in soil; it often requires several years of repeated applications to achieve correction of Mg deficiency. 2. Moderately heavy nitrogen ferti- lization frequently brings about correction. This may be due to the fact that nitrogen fertilizers tend to increase amounts of Ca and Mg in soil solution; the Ca may re- place the K and help restore a proper balance of Ca:Mg:K in the exchange complex. 3. Slowness of recovery from Mg applications to soil may be due to slowness of absorption and or movement of Mg in the plant. [45] TABLE 7. — Continued Element Methods of control or amelioration Supplementary remarks Soil treatment Foliar spray Other methods Mag- 1. Where due to excess soluble Definite cases of magnesium ex- nesium salt, removal by leaching out of cess on citrus (save where present as excess root zone is the only corrective. 2. Where due to excessive Mg carbonate or silicates (serpen- tine soils) additions of gypsum and potassium salts might be helpful (see under supplemen- tary remarks). a component of soluble salt excesses) are unknown to author. However, in controlled experiments in the green- house, magnesium carbonate incor- porated in a sand culture severely de- pressed citrus growth. It is probable that on serpentine-derived soils or where magnesium carbonate is pres- ent, Mg toxicity is a problem. In these cases additions of soluble calcium and potassium salts might prove helpful. Man- 1. 1-10 lbs manganese sulfate per 1. Sprays containing 4 lbs 1. Some decrease in Mn de- 1. Manganese deficiency can be ganese tree annually on sandy soils of MnSCh • 2H 2 to 2 lbs ficiency can often be caused by a variety of soil condi- deficiency Florida are successful (Camp Ca(OH) 2 in 100 gal. water achieved by moderate tions as follows: and Peech, 1939). will correct leaf patterns; acidification of neutral or 1. Soil alkalinity. 2. Use of acid peat treated with must be repeated several slightly alkaline soils; acid- 2. Cold soil temperatures. MnSOi suggested by Delap times a year to maintain ity should not be reduced 3. Soil organism competition for (1949). correction on citrus trees. below pH 5.5, however. available Mn. 3. Quastel et al. (1948) have 2. Organic matter addition to 4. Low phosphate supply. found that sodium and calcium soil may be helpful. 5. High potassium content or ac- thiosulphate at rates of 100, 3. Tillage in some cases has cumulation in soils. 500, and 1000 lbs per acre re- improved manganese avail- 6. Excessive ammonium ion build- duced manganese deficiency ability, in others decreased up in soils. of oats. it. 7. Oxidizing agents and condi- 4. There is some evidence that tions which convert divalent moderate applications of super- manganese to higher valence phosphate can increase the Mn oxides reduce manganase avail- uptake of citrus and other ability; this condition is pro- plants (Reuther et al., 1949, duced by soil alkalinity. and Bingham, 1958). 5. MnSCh and superphosphate may be more effective than MnSC-4 alone (Steckel, et al, 1948). 6. Soil fumigation prior to plant- ing has been found helpful in correcting Mn deficiency on citrus and some other crops. Man- 1. Where due to excess soil acid- Manganese excess has been noted ganese ity, liming to bring pH to 6.0 or under the following conditions: excess above will usually correct. 2. Where due to poor drainage (anaerobic or partially anaerob- ic conditions), better drainage or irrigation practices. 1. On manganiferous soils. 2. Where soil acidity produces ex- cess soluble Mn concentrations in soil. 3. Under reducing conditions in soils; high moisture. 4. Excess absorption from foliar sprays. Molyb- 1. 4 8 oz. sodium or ammonium 1. 2-4 oz. sodium molybdate 1. Liming acid soils will in- Citrus appears quite tolerant to denum molybdate per acre (commonly to 100 gal. water has prov- crease Mo availability and molybdenum, but because of toxicity deficiency added to other fertilizers) has en satisfactory for the con- in some cases has obviated of Mo to animals rates of application proven effective for correcting trol of Mo deficiency of the necessity for soil ap- should in general be kept low, so as and controlling Mo deficiency. citrus. plication of Mo. not to build up too much Mo in the soil. [ 40 | TABLE 7. — Continued Methods of control or amelioration Element Soil treatment Molyb- denum excess No cases are known of excess to plants as such, but animals eating plant materials high in Mo are severely affected. Ad- ditions of CuSO i to feed or to soil have been very helpful. Nitrogen deficiency 13^ to 3 lbs N per tree per year as inorganic or organic fertilizers, or both, is sufficient in most cases to correct and meet nitrogen needs of citrus. Ample nitrogen in the tree at time of bloom appears to be especially important for good fruit set. Nitrogen excess Phos- phorus deficiency Phos- phorus excess Potassium deficiency Discontinue or apply less N fer- tilizer to soil. High phosphate ferti- lization decreases N effectiveness. 5-10 lbs P2O5 per tree as super- phosphate broadcast or in furrows; repeat applications every few years, being guided by leaf and soil anal- ysis. Organic manures also very effective as a source of phosphorus. 1. Discontinue use of phosphorus- containing fertilizers. 2. Increase use of nitrogen ferti- lizer. 3. Lime application at 1-4 tons per acre will decrease phos- phorus availability. 1. Repeated applications of 5-10 lbs K2O per tree as K2SO4 or KCI over a period of years. 2. Organic manures also effec- tive; apply materials broadcast or in furrows. Be guided by leaf and soil analysis as to need for repeated applications. Foliar spray Urea sprays containing IVi lbs of urea per 100 gal. of spray (urea should have no more than 0.25% biuret): Reuther, Embleton, and Jones (1958). Urea which contains over 0.25% biuret may cause leaf injury of citrus, whether ap- plied to the soil or as a foliage spray. Some correction can be achieved using soluble phos- phate fertilizers; but soil ap- plications are more practical in general. Correct Cu and Zn deficien- cies if they occur with appro- priate sprays (see under Cu and Zn). Potassium will be some- what absorbed by citrus leaves from sprays containing soluble potassium fertilizer, but there is danger of leaf injury. Soil applications are advised. Other methods Where legumes can be suc- cessfully grown and good ton- nages produced, as in young orchards, N requirement can be met by turning under a legume crop. Chapman et al. (1949). In calcareous soils, sulfur and other acid-forming mate- rials will increase phosphate availability temporarily. Cover crops will bring some potassium from lower hori- zons to the surface, and this increases availability position- ally. Supplementary remarks Plants are not particularly sensi- tive to Mo. Vanselow and Datta 1949; found that a several-thousand- fold increase ^from 0.25 ppm Mo to >500 ppm in leaf tissue of citrus did not affect growth. However, ani- mals feeding on such materials may be severely affected. 1. Soil treatment advocated save when there is need for a quick nitrogen build-up in tree, e.g., before or after bloom period in spring. Urea spray especially val- uable at that time. 2. Considerable N may be lost by volatilization when ammonium forms are added to alkaline soi Is. 3. There are unavoidable losses of nitrogen from soil under commer- cial operating conditions both by leaching and by volatilization. Excess nitrogen in some situations, especially where fall and winter tem- peratures are favorable for vegeta- tive growth, may depress yields and make fruit coarse. Avoid excessive application of phosphate as Cu, Zn, B, and N avail- ability may be reduced. 1 . Phosphorus excess acts principally to reduce Cu, Zn, B, and N avail- ability. 2. In many soils phosphate becomes less available and active as time goes on; the situation will gradu- ally improve if phosphorus-con- taining fertilizers are discontin- ued and nitrogen fertilizer appli- cation increased. Correction of K deficiency is some- what slow on heavy soils, but in re- peated soil applications, K moves slowly downward into root zone and correction can be successfully accom- plished. Chapman (unpub. data checked by leaf analysis the effects of K fertilization on K uptake by citrus on a wide variety of California soils, and found in all cases that it was possible to increase leaf potas- sium by soil applications, though the rate of change was slow in many instances. [47] TABLE 7. — Continued Element Potassium excess Methods of control or amelioration Soil treatment 1. Discontinue use of organic ma- nures and potassium fertilizers. 2. Add magnesium sulfate if cause of Mg deficiency is too much exchangeable potassium, at rates of 5-10 lbs per tree for several years and irrigate free- ly to flush sulfate out of root zone. Sulfur deficiency Sulfur excess Zinc deficiency Zinc excess Excess salts; chloride, sulfate, s jilium. carbonate, bicarbon- ate, etc. Add calcium sulfate at rates of 500 to 1000 lbs per acre, using leaf and soil analysis as a guide to fre- quency required. Where excessive soil acidity is caused by sulfur, add lime to raise soil pH (see under excess soluble salts). 1. Not recommended on neutral and alkaline soils in general, but applications of ZnSOt to soil under drip of tree have given control; however, there is danger of tree injury. 2. On acid soils, broadcast appli- cations of ZnSCh are some- times used. 3. Zinc chelates may have poten- tial, but more data are needed on safe values and methods. 1. Soil acidity may release excess zinc. In this case use lime to bring pH to 6.0 or 7.0. 2. Some soils are natively high in zinc. Lime and phosphate will be helpful. 3. Excess zinc may cause iron chlorosis, and iron chelates should prove helpful. 1. Leach salts out of root zone by heavier than usual irrigations. Drainage may be necessary if water table is too high. Treat soil with gypsum, sulfur, or other neutralizers or soil condi- tioners if necessary to get good water penetration. Foliar spray If chief effect of excess pot- ash is magnesium deficiency, foliar sprays of magnesium ni- trate at 10 per cent concentra- tion will help correct the mag- nesium deficiency. Some leaf absorption of sul- fate occurs from foliar sprays but correction by this means is not advocated. 1. 5 lbs ZnS0 4 , Zy 2 lbs Ca(OH) 2 to 100 gal. water applied in spring, summer, or fall. 2. Formulations with Mn,Cu, B, and other elements pos- sible, as well as various insecticides and fungi- cides. Consult spray oper- ator and insecticide manu- facturer for information on compatibility. Other methods High nitrogen fertilization appears to offset injury due to sulfate. Cover crops, manures, etc., have often proven helpful. Soil acidification has been tried but not always suc- cessful. Supplementary remarks 1 . Excess potassium commonly pro- duces magnesium and manganese deficiency. Correct these by ap- propriate methods (see under Mg and Mn). 2. Occasionally excess soluble K is found where soluble salts have built up. Applications of gypsum followed by leaching to remove soluble salts is the proper correc- tive treatment in this case. Sulfur deficiency of citrus has not been encountered in the field, but should be looked for on non-irrigated soils of low organic matter content and high rainfall conditions; espe- cially where sulfur or sulfate-con- taining materials are not added in the pest, disease, or fertilizer control program. See under Salinity Control where excess sulfate is present. 1. In severe cases, repeated foliar spraying may be necessary. 2. De Villiers (private communica- tion) reports in South Africa that MnS04 incorporated in zinc sprays improves and speeds cor- rection of zinc deficiency of citrus. 3. Steyn and Eves (1956) report that copper added to zinc sprays decreases zinc absorption by leaves. Excess zinc in soil often produces iron chlorosis of citrus (Chapman et al., 1940). Similar effects on other plants have been noted by many in- vestigators. Excessive salts may come from irrigation water or by capillary rise from saline water tables, or deposits of salt in lower horizons. With irriga- tion waters containing over 500 ppm total dissolved solids, 5 to 15 or higher per cent of water must be wasted by leaching to keep salts flushed out of soil. |4«| LITERATURE CITED Aldrich, D. G., and J. R. Buchanan 1954. Phosphorus content of soils and their par- ent rocks in Southern California. Soil Sci. 77:369-76. Aldrich, D. G., A. P. Vanselow, and G. R. Bradford 1951. Lithium toxicity in citrus. Soil Sci. 71:291- 95. Allaway, W. H. 1957. pH, soil acidity, and plant growth. In Soil. U.S. Dept. Agr. Yearbook 1957. Pp. 67-71. Anderson, A.J. 1956. Molybdenum as a fertilizer. Advances in Agron. 8:163-202. Arnot, R. H. 1947. Potassium deficiency in coastal soils. A cause of decline in citrus and passion fruit. Agr. Gaz. N.S. Wales 58:72-74. Baird, Guy B., and J. E. 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Acid-extractable zinc of soils in relation to the occurrence of zinc-deficiency symptoms of corn: A method of analysis. Soil Sci. Soc. Amer. Proc. 12:143-4. Whetstone, Richard R., William O. Robinson, and Horace G. Byers 1942. Boron distribution in soils and related data. U.S. Dept. Agr. Tech. Bui. 797:1-32. [53] In order that the information in our publications may be more intelligible it is sometimes neces- sary to use trade names of products or equipment rather than complicated descriptive or chemical identifications. In so doing it is unavoidable in some cases that similar products which are on the market under other trade names may not be cited. No endorsement of named products is in- tended, nor is criticism implied of similar products which are not mentioned. Co-operative Extension work in Agriculture and Home Economics, College of Agriculture, University of California, and United States Department of Agriculture co-operating Distributed in furtherance of the Acts of Congress of May 8, and Juno 30, 1914. George B. Alcorn, Director, California Agricultural Extension Sorvice. 5m 3,'60(A3770)MH °4«P '" ▼"is BOOK «S DU r ON T HE LAST DA By taking representative leaf and soil samples from a citrus orchard and having a competent analysis made of the samples, growers may remove most of the guesswork from their management practices. This manual discusses the steps involved in proper sampling and analyzing, and provides typical forms for surveying the orchard. 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