INFORMATION TO USERS The most advanced technology has been used to photo­ graph and reproduce this manuscript from the microfilm master. UMI films the original text directly from the copy submitted. Thus, some dissertation copies are in typewriter face, while others may be from a computer printer. In the unlikely event th at the author did not send UMI a complete manuscript and there are missing pages, these will be noted. Also, if unauthorized copyrighted material had to be removed, a note will indicate the deletion. Oversize m aterials (e.g., maps, drawings, charts) are re­ produced by sectioning the original, beginning at the upper left-hand corner and continuing from left to right in equal sections with small overlaps. Each oversize page is available as one exposure on a standard 35 mm slide or as a 17" x 23" black and white photographic print for an additional charge. Photographs included in the original manuscript have been reproduced xerographically in this copy. 35 mm slides or 6" x 9" black and white photographic prints are available for any photographs or illustrations appearing in this copy for an additional charge. Contact UMI directly to order. UMI A ccessing th e World’s Information since 1938 300 North Z eeb Road, Ann Arbor, Ml 48106-1346 USA O rder N um ber 8900101 Cherry tree decline in Michigan: Associated pythiaceous species, pathogenicity and control Smither, Margaret Lydia, Ph.D. Michigan State University, 1988 UMI 300 N. Zeeb Rd. Ann Arbor, MI 48106 PLEASE NOTE: In all cases this material has been filmed in the best possible way from the available copy. Problems encountered with this docum ent have been identified here with a check mark V . 1. Glossy photographs or pages _ 2. Colored illustrations, paper or print_______ 3. Photographs with dark background_____ 4. Illustrations are poor copy_______ 5. Pages with black marks, not original co p y _______ 6. Print shows through as there is text on both sides of p a g e ______ 7. Indistinct, broken or small print on several pages 8. Print exceeds margin requirem ents______ 9. Tightly bound copy with print lost in sp in e________ 10. Computer printout pages with indistinct print_______ 11. P age(s)____________ lacking when material received, an d not available from school or author. seem to b e missing in numbering only as text follows. 12. Page(s) 13. Two pages num bered_______.. Text follows, 14. Curling and wrinkled p ag es______ 15. Dissertation contains pages with print at a slant, filmed a s received 16. Other_____________________________________________________ UMI CHERRY TREE DECLINE IN MICHIGAN: ASSOCIATED PYTHIACEOUS SPECIES, PATHOGENICITY AND CONTROL By Margaret Lydia Smither A Dissertation Submitted to Michigan State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY Department of Botany and Plant Pathology 1988 ABSTRACT CHERRY TREE DECLINE IN MICHIGAN; ASSOCIATED SPECIES, PATHOGENICITY, AND CONTROL PYTHIACEOUS By Margaret Lydia Smither Montmorency those sour cherry trees in planted on heavy soils, poor growth The problem and discolored and Michigan, especially exhibit decline symptoms diminished root of systems. is most severe in orchards with trees grafted onto Mahaleb rootstocks. Isolations soil. from for Pvthium species were made from roots and Pythium was commonly associated with orchards with heavy clay soils but not with trees from orchards in heavy soils. rootsof roots of with light sandy soils, and populations soils were high compared to populations in £. trees irregulare was isolated most light frequently from discolored and necrotic cherry roots and from cherry orchard soils. Other species isolated included: £. svlvaticum. £. ultimum. £. Pythium rostratum. spp.. necrosis and several infrequently isolated In greenhouse trials root discoloration and a reduction in root and shoot growth occurred on Mahaleb seedlings inoculated with £. irregulare. reductions and necrosis were greater when and seedlings Growth were flooded, but unflooded seedlings exhibited symptoms as well. None after of 3 the seedlings inoculated with £. months. £. irregulare may irregulare contribute died to a reduction in growth of cherry trees planted on heavy soils. Orchards in and woodlands in composition sylvaticum. of and Michigan were found to Pythium species. £. differ irregulare. £. £. ultimum were frequently isolated orchard soils but were not isolated from Pythium group 'HS' was isolated most woodland from soils. frequently from woodland soils, followed by Pvthium group ’X ‘, £. rostratum. and Pythium group ’Y'. Populations of £. irregulare. E. sylvaticum. and £. ultimum in two orchards sampled over 2 yr and one orchard over 1 year, varied independently. Seven pythiaceous species associated with the roots of sour cherry in Michigan were tested for their sensitivity to metalaxyl and phosphorous acid in culture. All fungi were inhibited by both fungicides and sensitivity varied species. 400 and between Mahaleb seedlings exhibited phytotoxic symptoms at was more effective than fosetyl-Al in preventing fungus induced root necrosis 800 /^g/ml metalaxyl. Metalaxyl and growth reduction to 9-wk-old Mahaleb seedlings growing in soil infested with £. irregulare. Eh- megasoerma. and Eh- cactorum. To my father ii ACKNOWLEDGEMENTS I wish to thank Dr A. help and of L. Jones my major professor for his financial support. my guidance committee; Stephens, Dr G. Adams, I am grateful to the members Dr J. T. Stephens latter for Lockwood, R. encouragement. T. for financial and moral support during the I wish to thank Dr Ed financial and other assistance. G. C. Especial thanks are due to Dr part of this project. Bielenin, Dr and Dr R. L. Perry for their faith in me, support and encouragment. C. L. Ehret and R. E. I also thank Klos Dr Comstock for help A. and I wish to thank my fellow graduate students for their assistance; especially Dr. V. F. Stanis for help in the initial stages of this work, and Reginald Mandego for collaborating in the soil compaction experiment. I wish to thank Laura Wolf for financial help. my husband Ben for his understanding, support. iii I encouragement thank and TABLE OF CONTENTS Page LIST OF TABLES ...................................... viii LIST OF FIGURES.......................................... xi INTRODUCTION AND GENERAL LITERATURE REVIEW......... 1 LITERATURE CITED..................................... 7 PART I PYTHIUM SPECIES ASSOCIATED WITH THE ROOTS OF SOUR CHERRY AND THE EFFECT OF £. IRREGULARE ON THE GROWTH OF MAHALEB CHERRY 13 ABSTRACT.............................................. T M w n A T \n n n » T A iT i t u i v j y u v j i 1WL1............................................................................................................................... . a a 14 MATERIALS AND METHODS................................ 15 RESULTS............................................... 19 DISCUSSION............................................ 30 LITERATURE CITED..................................... 33 iv PART II SPECIES AND POPULATIONS OF PYTHIUM ISOLATED FROM SOUR CHERRY ORCHARD AND WOODLAND SOILS IN MICHIGAN Page ABSTRACT.............................................. 36 INTRODUCTION.......................................... 37 MATERIALS AND METHODS................................ 38 RESULTS............................................... 40 DISCUSSION............................................ 44 LITERATURE CITED..................................... 50 PART III EFFECTS OF PHYTOPHTHORA METALAXYL AND AND FOSETYL-AL ON GROWTH PYTHIUM SPECIES ’IN VITRO' AND ON OF THEIR PATHOGENICITY TO MAHALEB CHERRY ABSTRACT,,............................................ 53 INTRODUCTION......................................... 53 MATERIALS AND METHODS................................ 55 RESULTS............................................... 58 DISCUSSION............................................ 74 LITERATURE CITED..................................... 76 v APPENDICES APPENDIX A DESCRIPTIONS OF PYTHIUM SPECIES ASSOCIATED WITH MONTMORENCY SOUR CHERRY IN MICHIGAN............................ 79 APPENDIX B EFFECT OF PYTHIUM AND PHYTOPHTHORA ISOLATED IN MICHIGAN ON GROWTH OF MAHALEB SEEDLINGS Page INTRODUCTION.......................................... 86 MATERIALS AND METHODS................................ 86 RESULTS............................................... 88 DISCUSSION............................................ 91 LITERATURE CITED..................................... 92 vi APPENDIX C THE EFFECTS OF INCREASED SOIL COMPACTION LEVELS WITH PYTHIUM IRREGULARE AND PHYTOPHTHORA MEGASPERMA ON GROWTH OF MAHALEB SEEDLINGS, AND ETHYLENE LEVELS IN SOIL Page ABSTRACT.............................................. 94 INTRODUCTION.......................................... 94 MATERIALS AND METHODS................................ 95 RESULTS............................................... 98 DISCUSSION............................................... 101 LITERATURE CITED........................................ 102 APPENDIX D VARIATION IN SUSCEPTIBILITY OF CHERRY ROOTSTOCK CULTIVARS TO INFECTION BY PHYTOPHTHORA SPECIES AND PYTHIUM IRREGULARE ABSTRACT.............................................. 105 INTRODUCTION.......................................... 106 MATERIALS AND METHODS................................ 107 RESULTS............................................... 109 DISCUSSION............................................ 114 LITERATURE CITED..................................... 115 vii LIST OF TABLES PART I Table 1. Species of Pythium isolated from the roots of sour cherry trees with reduced terminal growth or from the roots of Mahaleb seedlings.... Table 2. Populations of Pvthium species as estimated by dilution-plate counts from soil taken from sour cherry orchards.................... Table 3. Effect of nine isolates of Pythium irregulare on the growth of Mahaleb seedlings growing in unflooded soil.......................... Table 4. Analysis of variance for shoot and root dry weights of Mahaleb seedlings growing in soil infested with Pythium irregulare and two Phytoohthora species in single and combined treatments under flooded and unflooded conditions. Table 5. Effect of Pythium irregulare (£.) and two Phytoohthora (Eh-) species on the growth of Mahaleb seedlings in single and combined treatments under flooded and unf 1 coded coudibiouis Table 6. Reisolation of Pythium irregulare and two Phytoohthora species from Mahaleb seedlings (experiment 2) grown for 15 weeks with periodic flooding.......................................... viii PART II Page Table 1. Populations of Pythium species as estimated by dilution-plate counts from soil taken from sour cherry orchards planted on two soil types 42 Table 2. Populations of Pythium species as estimated by dilution-plate counts from soil taken from sour cherry orchards..and woodlands.......... 43 PART III Table 1. EDg0 values for Phytophthora and Pythium species to metalaxyl and phosphorous acid in culture............................................... 63 Table 2. Effect of various concentrations of metalaxyl on growth of 1-yr-old Mahaleb seedlings in Phytophthora and Pythium infested soil in the greenhouse............................................ 68 Table 3. Effect of fosetyl-Al and metalaxyl on growth of 1-yr-old Mahaleb seedlings in Phytophthora and Pythium infested soil under lath.................................................. 71 Table 4. Effect of fungicides metalaxyl and fosetyl-Al on growth of Mahaleb seedlings in soil infested with Phytophthora species and Pythium irregulare............................................ 72 APPENDIX B Table 1. Virulence of Pythium and Phytophthora species isolated from Michigan sour cherry orchards to Mahaleb seedlings....................... ix 89 APPENDIX C Page Table 1. Effects of soil bulk density and Pythium irregulare on growth of Mahaleb seedlings............................................ 99 Table 2. Effects of soil bulk density, Pvthium irregulare and Phytophthora megasperma on growth of Mahaleb seedlings................................ 100 APPENDIX D Table 1. Relative susceptibility of dormant excised shoot tissue of cherry rootstock cultivars to infection by Phytophthora species and Pythium irregulare during 1983.............................. Ill Table 2. Relative susceptibility of dormant excised shoot tissue of cherry rootstock cultivars to infection by Phytophthora species and Pythium irregulare during 1984.............................. 112 Table 3. Growth of cherry rootstock cultivars planted in soil infested with Phytophthora species and Pythium irregulare under lath.................. 113 x LIST OF FIGURES PART I Figure 1. Roots of representative Mahaleb seedlings grown in a growth chamber for 18 wk in a soil/sand/peat mixture infested with Pythium irregulare. Soil in the pots was a) uninfested, or infested with p. irregulare isolated from orchard B, b) root and c) soil; orchard C, d) root and e) soil; orchard J, f) root and g) soil; orchard L, h) root and i) soil; and orchard P, k) soil. The treatments were not flooded............................................. Figure 2. Shoots (A) and roots (B) of representative Mahaleb seedlings grown in a greenhouse for 3 mo in a soil/sand/peat mixture. Soilin the pots was (a) uninfested and unflooded, (b) uninfested and flooded, or flooded and infested with (c) Pythium irregulars C6, (d )Phytophthora megasperma. avirulent isolate M224, (e) P. irregulare C6/Ph- megasperma. avirulent M224, Ph. megasperma. virulent isolate M333, and p. irregulare C6/Ph. megasperma. virulent M 3 3 3 Figure 3. Shoots (A) and roots (B) of representative Mahaleb seedlings grown in a greenhouse for 3 mo in a soil/sand/peat mixture. Soil in the pots was (a) uninfested and flooded, or flooded and infested with (b) Pvthium irregulare C6, (c)Phyt(g/ml.................... 65 Figure 2e. Radial growth of Pythium irregulare in culture amended with phosphorous acid at rates of 0, Figure 2 f . Radial growth of Pythium sylvaticum in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and l O O ^ g / m l ....................... 66 Figure 2g. Radial growth of Pythium ultimum in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and 100yttg/ml....................... 67 Figure 3. Phytotoxic symptoms caused by metalaxyl at rates of (a) 0, (b) 100, and (c) 400 /(g/ml on leaves of Mahaleb cherry............................. 69 xiii Page Figure 4. Roots of representative Mahaleb seedlings grown in a) uninfested soil, or soil infested with b) Phytophthora cactorum. c) Ehmegasperma and d) Pythium irregulare. Roots in columns were x) untreated, or treated with y) metalaxyl, and z) fosetyl-Al........................ 73 APPENDIX A Figure la. Pythium ixreflfllare sporangia ......... 82 Figure lb. Pythium irregulare irregularly shaped oogonium and aplerotic oospore.............. 82 Figure 83 2a. Pythium sylvaticum hyphal swelling .. Figure 2b. Pythium sylvaticum oogonium surrounded by branched antheridial cells........... 83 Figure 3a. Pythium ultimum oogonium with paragynous antheridium attached close to the oogonial stalk....................................... 84 Figure 3b. Pythium ultimum oogonium with paragynous antheridia and an aplerotic oospore 84 APPENDIX B Figure 1. Roots of representative Mahaleb seedlings grown in a growth chamber for j . o w k _lh a soil/sand/peat mixture infested with (A) Phytophthora species and (B) Pythium species. Soil in the pots was (a) uninfested and non­ flooded, or flooded and infested with (b) P h . fifls.tgc.mn. (c) £h. citricola, (d) Eh- drechsleri. (e) £h. mega&perma> (f) £. irregulare. (g) £. sylvaticum. and (h) £. ultimum...................... xiv 90 INTRODUCTION AND GENERAL LITERATURE REVIEW Michigan accounting is the leading state in sour cherry for about two thirds of the total production the United States (27). 1981 was set at producing Michigan. areas in The economic value of the crop for over 40 million dollars (26). The are in the west along the shores Concentrations northwest production of production around Traverse City, cherry of occur Lake in the in the west central region around Hart and Shelby, and in the south west around Benton Harbor. of High resulted with prices cherries in the last in a 14% increase of land under cherry a total of 4.5 million trees planted However decade production by 1982 (27). as cherry production increased so did instances of poor tree vigor and decreased longevity. Tree life decline is a comprehensive term encompassing and replant problems (47,55). short Tree decline problems have been identified throughout the world and recognised for over two hundred years (42). The main symptom is reduced vigor with a possible reduction in life span. Root systems are Cankers weak develop causal abiotic and poorly developed on the trunk. or necrotic. Often there is no clearly may defined agent but rather a combination of several biotic and factors (22,23,47,55). 1 These may include; environmental drought factors such as cold injury, or oxygen defeciency caused injury caused by damaging cultural factors of infection by mycoplasma-like-organisms, insect infestation; toxicity from plant waterlogging, practices; bacteria, and and by stresses due to pathogenic fungi, nematodes; physiological and viruses, injury factors from such as and spray residues, and biochemical and hormonal imbalances distinguished between specific replant disorders which occurred when one species followed the (55). same or a Savory closely related species and nonspecific replant disorders affecting all tree crops (42). This distinction has also been used to classify other of tree decline problems (47). tree decline has been types The literature pertaining to reviewed in several articles (42,47,55). Stone Fruit Decline was the subject of a Michigan which State University in 1982 (46). were pplant selected as most critical pathogenic viruses, root rots, and improvement, mechanical harvesting, structure. grant A conference Areas of at research included study of rootstock selection and trunk and tree was awarded to study root rot of cherry in Michigan through the Stone Fruit Decline Project. Root rot of sour cherry in Michigan caused by Armillaria occurs on sandy sites from the Hart/Shelby area north to the Traverse City area. isolated from Three species of Armillaria have been from these orchard sites which have woodlands of oak and pine on which been the cleared Armillaria species were Phytophthora although The endemic (39,51). Root rot caused occurs throughout the cherry production area, symptoms are most severe on poorly drained symptoms by soils. include extensive lateral root necrosis and development of a canker on the lower trunk below the union (6). A preliminary survey associated Pythium species with decline only on heavy poorly drained soils. graft The root rot symptoms include extensive necrosis and eventual absence of lateral branchlet roots. closely related genera Pythium and Phytophthora (13) and may present under similar conditions. pathogens are most be expected are to be Symptoms for the three severe when the trees are planted on Mahaleb (Prunus mahaleb L . ) rootstocks although orchards on Mazzard (£. avium L . ) rootstocks are also affected. The genus Pythium which have from diverse pathogens economic a world wide distribution and can and habitats. Many are the closely genus isolated plant cause severe including strawberry (35,52), related species be under suitable conditions can wheat (9), of soil-bourne losses on a wide range of crops, (1,21,37), Unlike contains a large number beans and grape (48). Phytophthora not all species are pathogens. Pythium species survive in soil by saprophytic production growth and structures (13,50). conditions competitors of resistant resting They tend to be more successful under high soil moisture with of a well (29,49), established but soil are poor microflora (4,13,49). Pythium species have the ability to colonise host tissue (13,28,50), and produce a variety of cellulytic pectolytic enzymes (10,50). and The literature about the genus Pythium has been reviewed (13,50). The and objectives of this study were to examine associated the pathogenicity with decline on Pythium species cherry heavy trees sites; of isolate, Pvthum showing species poor woodland found growth to investigate the in orchard and identify and ecology soils; of and to examine possible control measures of rootstock selection and chemical control. The literature on root and collar rot of cherry deciduous and other fruit tree crops caused by pythiaceous species will be reviewed in the remainder of the introduction. Environmental levels influence pythiaceous higher conditions the species. under particularly development of soil disease Populations of Pvthium conditions of high soil moisture caused species moisture by are (4,29,49). Tree loss due to Phytophthora infection is typically greater in poorly mounds, for drained areas (25,33). trees on thus improving drainage, was reported as beneficial reducing losses caused by £h. Subsoiling reduced Planting before losses Improvement was cactorum on apple (25). planting improved peach tree growth due to peach tree short life (41). believed due to greater stability in moisture levels. improves tree vigor will tend to ameliorate disease by Pythium species. Any practice which reduces and soil stress and caused Pythium cherry species trees isolated from roots of have been reported as pathogenic seedlings (12). diseased growing to Mahaleb Pythium species isolated from roots of trees were (14,15,28,38). to poorly pathogenic to peach seedlings However, the importance of Pythium species peach tree decline has been questioned by some workers, as disease pathogenicity which the symptoms tests. were Unfortunately experiments were run not research reproduced in the temperatures was not at reported (20,29,30,36), and pathogenicity of the Pythium species been shown to be dependent on temperature (7). In addition total Pythium populations were not correlated with decline symptoms (29). Pythium apple. species Several cause decline and replant Pythium species including problems £. of irregulare Buisman and £. sylvaticum Campbell and Hendrix isolated from roots of declining trees or soil from replant pathogenic to roots contribute to apple replant problems in New York (16) Europe (34,43). with collar rot seedlings (17). was found of apple seedlings and sites thought Pythium species isolated from apple in New York were were pathogenic to to and trees apple Pythium ultimum from apple trees in Poland to cause a trunk canker (5). Pythium species also caused a retardation of tree growth in an apple orchard in Australia (45). Phytophthora species have been implicated as the causal agents of root and crown rots of fruit trees. primary Root and collar rot of sweet cherry on wet sites in California was first shown to be caused by Phytophthora in 1976 (32). The following species have since been found to be pathogenic to Mahaleb; CEZPtPgaea £h- cambivora (Petri) Pethyb. Tucker (32,54), and and Ph. Laff. Buisman (6,53,54), (32,54), £h- Ph. drechsleri megasperma Drechsler (6,32,53,54), Eh- cactorum (Leb. and Cohn)Schroet (6,24), and Eh. syringae (Kleb.)Kleb. (19). £h- cambivora. Eh- cryptogaea. and Eh- megasperma have been isolated from soils in South Australian cherry orchards (8). as Mahaleb rootstocks have been reported more susceptible to Phytophthora infection than Mazzard and other cherry rootstocks (24,33,54). A root and collar rot of peach was caused by Phytophthora sumamsmi (32), Eh. cactorum (11,28) and £h. syringae (19,56). Apple collar and root rot is caused by £h- cactorum and the disease has a world wide distribution (2,3,8,25,44). P h . cambivora (18), and £h- Ph. citricola (44), Eh- megagperms (17,40), syringae (44) have also been reported to cause collar rot of apple. The stone role of Phytophthora species in rapid decline of fruit trees has recieved more attention than that of Pythium species because of the greater relative virulence of Phytophthora. tree In stone fruit growing regions with declines a more thorough investigation of the role Pythium species should be undertaken. slow of LITERATURE CITED 1. Adegbola, M. 0. K . , and Hagedorn, D. J. 1969. Symptomatology and epidemiology of Pythium bean blight. Phytopathology 59:1113-1118. 2. Aldwinkle, H. S., Polach, F. J . , Molin, W. T. , and Pearson, R.C. 1975. Pathogenicity of Phytophthora cactorum isolates from New York apple trees and other sources. Phytopathology 65:989-994. 3. Baines, R. C. 1935. Phytophthora trunk canker of apple. (Abstr.) Phytopathology 25:5. 4. Barton, R. H. 1958. Occurrence and establishment of Pythium in soils. Trans. Brit. Mycol. Soc. 41:207-222. 5. Bielenin, A., Borecki, Z., and Millikan, D. F. 1976. Identification of Pythium ultimum in the collar rot complex of apple. Phytopathology 66:127-129. 6. Bielenin, A., and Jones, A. L. 1988. Prevalence and pathogenicity of Phytophthora spp. from sour cherry trees in Michigan. Plant Disease 72:473-476. 7. Biesbrock, J. A., and Hendrix, F. F . , Jr. 1970. Influence of soil water and temperature on root necrosis of peach caused by Pythium spp. Phytopathology 60:880882. 8. Bumbieris, M . , Wicks, T. J . , and Windle, B. E. 1982. Phytophthora species in apple and cherry orchards in South Australia. Australasian Plant Path. 11:28-29. 9. Chamswarng, C. and Cook, R. J. 1985. Identification and comparative pathogenicity of Pythium species from wheat root and wheat-field soils in the Pacific Northwest. Phytopathology 75:821-827. 10. Deacon, J. W. 1979. Cellulose decomposition by Pythium and its relevance to substrate-groups of fungi. Tra n s . Br. mycol. Soc. 72:469-477. 11. Dunegan, J. C. 1935. A Phytophthora disease of peach seedlings. Phytopathology 25:800-809. 7 8 12. Fliegel, P., Parker, K. G . , and Mai, W. F. 1963. The fungous flora of nonsuberized roots of poorly growing cherry trees. Phytopathology 53:1368-1369. 13. Hendrix, F.F.Jr., and Campbell, W.A. 1973 Pythiums as plant pathogens. Ann. Rev. Phytopathology 11:77-98. 14. Hendrix, F. F . , Jr., Powell, W. M . , and Owen, J. H. 1966. Relation of root necrosis caused by Pythium species to peach tree decline. Phytopathology 56:12291232. 15. Hine, R. B. 1961. replant problem. The role of fungi in the peach Plant Dis. Rep. 45:462-465. 16. Jaffee, B. A., Abawi, G. S., and Mai, W. F. 1982. Fungi associated with roots of apple seedlings grown in soil from an apple replant site. Plant Dis. 66:942944. 17. Jeffers, S. N . , Aldwinkle, H. S., Burr, T. J . , and Arneson, P. A. 1982. Phytophthora and Pythium species associated with crown rot in New York apple orchards. Phytopathology 72:533-538. 18. Julis, A. J . , Clayton, C. N . , and Sutton, T. B. 1978. Detection and distribution of Phytophthora cactorum and £. cambivora on apple rootstocks. Plant Dis. Rep. 62:516-520. 19. Kouyeas, H. 1971. On the apoplexy of stone fruit trees caused by Phytophthora spp. Annls. Inst. Phytopathol. Benaki. N.S. 10:163-170. 20. Lownsbery, B. F . , English, H . , Moody, E. H . . and Shick. F. J. 1973. Criconemoides xenoplax experimentally associated with a disease of peach. Phytopathology 63:994-997. 21. Lumsden, R. D . , Ayers, W. A., Adams, P. B . , Dow, R. L . , Lewis, J. A . , Papavizas, G. C . , and Kantzes, J. G. 1976. Ecology and epidemiology of Pythium species in field soil. Phytopathology 66:1203-1209. 22. Mai, W. F . , and Abawi, G. S. 1978. Determining the cause and extent of apple, cherry and pear replant diseases under controlled conditions. Phytopathology 68:1540-1544. 23. Mai, W. F . , and Abawi, G. S. 1981. Controlling replant diseases of pome and stone fruits in Northeastern United States by preplant fumigation. Plant Dis. 65:859-864. 9 24. McIntosh, D. L. 1953. A trunk and crown rot of sweet cherry in British Columbia. Phytopathology 43:402403. 25. McIntosh, D. L. (Ed.) 1975. Proceedings of the 1974 APDW workshop on crown rot of apple trees. Can. Plant Dis. Surv. 55:109-106. 26. Michigan Agricultural Statistics. 1982. Michigan Agricultural Reporting Service, Lansing. 88 pp. 27. Michigan Orchard and Vineyard Survey. 1982. Michigan Agricultural Reporting Service, Lansing. 49 pp. 28. Miller, C. R . , Dowler, W. M . , Petersen, D. H . , and Ashworth, R. P. 1966. Observations on the mode of infection of Pythium ultimum and Phytoohthora cactorum on young roots of peach. Phytopathology 56:46-49. 29. Mircetich, S. M. 1971. The role of Pythium in feeder roots of diseased and symptomless peach trees and in orchard soils in peach tree decline. Phytopathology 61:357-360. 30. Mircetich, S. M . ,and Fogle, H. W. 1968. Occurrence and pathogenicity of Pvthium in peach orchard soils. (Abstr.) Phytopathology 58:886. 31. Mircetich, S. M . , and Keil, H. L. 1970. Phytoohthora cinnamomi root rot and stem canker of peach trees. Phytopathology 60:1376-1382. 32. Mircetich, S. M . ,and Matheron, M. E. 1976. Phytoohthora root and crown rot of cherry trees. Phytopathology 66:549-558. 33. Mircetich, S. M . , and Matheron, M. E. 1981. Differential resistance of various cherry rootstocks to Phytoohthora species. (Abstr.) Phytopathology 71:243. 34. Mulder, D. 1969. The pathogenicity of several Pvthium species to the rootlets of apple seedlings. Neth. J. Plant Path. 75:178-181. 35. Nemec, S., and Sanders, H. 1970. Pvthium species associated with strawberry root necrosis in southern Illinois. Plant Dis, Rep. 54:49-51. 36. Nyczepir, A. P., and Lewis, S. A. 1984. Incidence of Fusarium and Pythium spp. in peach feeder roots as related to dibromochloropropane application for control of Criconemella xenonlex. Plant Dis. 68:497-499. 10 37. Pieczarka, D. J. , and Abawi, G. S. 1978. Populations and biology of Pythium species associated with snap bean roots and soils in New York. Phytopathology 68:409416. 38. Powell, W. M . , Owen, J. H. and Campbell, W. A. 1965. Association of phycomycetous fungi with peach tree decline in Georgia. Plant Dis. Rep. 49:279. 39. Proffer, T. J . , Jones, A. L . , and Ehret, G. R. 1987. Biological species of Armillaria mellea isolated from sour cherry orchards in Michigan. Phytopathology 77:941943. 40. Robertson, G. L. and Dance, H. M. 1971. The association of Phytophthora megasperma with crown rot of apple trres. N. Z. J. Agric. Res. 14:509-514. 41. Savage, E. F . , Hayden, R. A., and Ward, W. E. 1968. The effect of sub-soiling on the growth and yield of peach trees. Ga. Agr. Expt. Sta. Res. Bui. 30. 42. Savory, B. M. 1966. Specific replant diseases causing root necrosis and growth depression in perennial fruit and plantation crops. Research Rev. 1. Commonw. Bur. Hort. Plant. Crops. East Mailing, Maidstone Kent, England. 64 pp. 43. Sewell, G. W. F. 1981. Effects of Pythium species on the growth of apple and their possible causal role in apple replant disease. Ann. Appl. Biol. 97:31-42. 44. Sewell, G. W. F . , Wilson, J. F . , and Dakwa J. T. 1974. Seasonal variations in the activity in soil of Phytophthora cactorum. P. sxringae. and P. citricola in relation to collar rot disease of apple. Ann. Appl. Biol. 76:179-186. 45. Sitepu, D . , and Wallace, H. R. 1974. Diagnoses of retarded growth in an apple orchard. Austral. J. Expt. Agr. and Animal Husb. 14:577-584. 46. Stone Fruit Decline Workshop Proceedings. 1982. Michigan State University, E. Lansing. 128 pp. 47. Traquair, J. A. 1984. Etiology and control of orchard replant problems: a review. Can. J. Plant Pathol. 6:54-62. 48. Utkhede, R. S., and Vielvoye, E. 1984. Cause and control of decline of grapevines in British Columbia. Plant Dis. 68:820-822. 11 49. Van der Plaats-Niterink, A. J. 1975. Species of Pvthium in the Netherlands. Neth. J. PI. Path. 81:22-37. 50. Van der Plaats-Niterink, A. J. 1981. Monograph of the genus Pythium. Studies in Mycology No 21 Centraal Bureau voor Schimmelcultures, Baarn. 242 pp. 51. Wargo, P. M . , and Shaw, C. G. III. 1985. Armillaria root rot: The puzzle is being solved. Plant Dis. 69:826-832. 52. Watanabe, T . , K. Hashimoto, amd M. Sato. 1977. Pythium species associated with strawberry roots in Japan and the strawberry stunt disease. Phytopathology 67:1324-1332. 53. Wilcox, W. F . , Jeffers, S. N . , Hayes, J. E. K . , and Aldwinkle, H. S. 1985. Phytophthora species causing root and crown rot of cherry trees in New York. (Abstr.) Phytopathology 75:1347. 54. Wilcox, W. F . , and Mircetich, S. M. 1985. Pathogenicity and relative virulence of seven Phytophthora species on Mahaleb and Mazzard cherry. Phytopathology 75:221-226. 55. Yadava, U. L . , and Doud, S. L. 1980. The short life and replant problems of deciduous fruit trees. Pages 1-116 in J. Janick, ed. Horticultural Reviews. Vol 11. AVA publ. Co., Inc., Westport, Conn. 56. Young, R. A. and Milbraith, J. A. 1959. A stem canker disease of fruit tree nursery stock caused by Phytophthora. syrinaae. Phytopathology 49:114-115. PART I PYTHIUM SPECIES ASSOCIATED WITH THE ROOTS OF SOUR CHERRY AND THE EFFECT OF £. IRREGULARE ON THE GROWTH OF MAHALEB CHERRY 12 ABSTRACT Isolations early for Pythium species were made during summer of 1984-1985 from 73 sour cherry trees Michigan orchards, nursery, and from soil samples from nine orchards. was commonly from Mahaleb seedlings in a heavy soil but not with roots of trees with light soil, compared in Pythium orchards from orchards and populations in heavy soils were to populations in light soils. E. 12 commercial associated with roots of trees from with the high irregulare was isolated most frequently from discolored and necrotic cherry roots and from cherry isolated included: and several soils. infrequently isolated Pvthium discoloration sp p . . and necrosis were obtained on Growth reductions seedlings exhibited symptoms as well. seedlings inoculated with £. months. cause None irregulare died after but of 3 This suggests that £. irregulare is not a primary in the decline and death of cherry trees in orchards, cherry In Mahaleb necrosis were greater when seedlings were flooded, unflooded the species a reduction in root and shoot growth and seedlings inoculated with £. irregulare. and Other £. sy.lvaticm n, E- ultimum. £. rostratum. greenhouse trials, root orchard but it may contribute to a reduction in growth of trees between seedlings Michigan planted Pvthium when on heavy soils. No and Phytoohthora was detected £. irregulare castorum and Eh. megasoerma. was inoculated interaction on Mahaleb with Ph. 14 INTRODUCTION Root rot cherry L. is Montmorency trees ( P r m u s cerasus L . ) grafted on Prunus (Mahaleb) species for an important problem on seedling rootstocks in causal drained for soils soils (1). where identified as Phytophthora Although damping-off naturally with (11). be primary heavy poorly- Populations of Pythium were high the cause of unpublished). a root rot on sites agents soils of Phytoohthora were reported to agents cause Three of Armillaria reported to be primary causal species many mahaleb Michigan. root rot on sites with light well-drained Five sour root tree and death crown (M. rot L. infested orchard soils, it is not was Smither, Pythium has been reported (2) of young Mahaleb seedlings in grown considered to in a pathogen of sour cherry trees and the presence of Pvthium is usually Recent ignored for Phytoohthora. reports suggest Pythium may be involved in root problems The when making isolations on role of apple (6,12), particularly in replant Pythium has not been defined and rot sites. therefore warrants further study. The overall objective of this study was to determine Pythium. rot of in addition to Phytoohthora. sour Subobjectives cherry on sites with were to isolate and if was involved in root poorly drained identify the soils. Pvthium species associated with sour cherry trees and orchard soils, 15 to test the effect of the predominant Pvthium irregulare on the growth of Mahaleb species cherry, P. and to investigate the effect of £. irregulare and two Phytoohthora species combined on the growth of Mahaleb cherry. MATERIALS AND METHODS Isolation of Pythium from cherry roots. Root pieces were collected from sour cherry trees with reduced growth of terminal Kent, shoots. Mason, The orchards were located in Oceana, and Van Buren counties. trees were sampled per orchard. Berrien, Four to six A total of 73 trees from 12 orchards were sampled during the early summer of 1984 and 1985. In addition, 22 Mahaleb seedlings received by a local nursery from a supplier on the West Coast were sampled prior to planting in Michigan. The samples were transported to the laboratory in plastic bags in an ice chest, soaked overnight in tap water, then thoroughly washed paper towels, pieces 5 mm to remove soil particles, dried on and rinsed in sterile distilled water. Rootlet in length were pressed into corn meal agar (CMA) (Difco) amended with 10 mg pimaricin (0.4 ml of a 2.5% suspension), 250 mg ampicillin, pentachloronitrobenzene M O ) (6). PARP), samples 10 mg rifampicin, and 50 mg (Sigma Chemical Co., Saint Twenty-40 plates of amended corn meal agar each with 10 root pieces, collected from each were prepared from tree. The plates Louis, (CMAroot were incubated at 21 C in darkness and examined regularly with a 16 binocular microscope for fungal growth. transferred from Hyphal tips were all Pythium colonies to fresh CMA-PARP plates and then to CMA prior to identification. Isolation Pythium from orchard soil. The population of Pythium in soil from sour cherry orchards was estimated by surface soil dilution plates (9). taken of between the drip line and the trunk from each trees per orchard. with a were of ice and stored at 4 C until processed. 5- and 1.68-mm-mesh sieves. each bulk sample, plated at 1:10, replicate through A 1 g subsample was taken from suspended in 0.2% water agar, and dilution 1:50, and 1:100 on fresh CMA-PARP selective Diluted of a Soil samples were air dried and then passed sequentially surface in Samples were transported to the laboratory in chest medium. 10 The cores were taken to a depth of 15 cm Hoffer soil sampler and bulked for each tree plastic bag. an Four cores of soil the samples (1 ml) were distributed over the agar with a plates sterile were made per glass dilution. rod. Three After 42 hr incubation in darkness, the soil was removed by washing each plate under running tap water and the counted. Hyphal tips were transferred 15 colonies Pvthium colonies from the edge of 5 to per sample to CMA-PARP plates and then after incubation for 48 hr at 21 C to CMA. Identification of Pythium species. Fungal structures were examined after 1-2 wk and identifications were made based on colony morphology, sporangia, hyphal growth rates, swellings, and characteristics oogonia, antheridia, of and 17 oospores The using the key of Van der identification sylvaticum each of the Plaats-Niterink heterothallic (13). species Campbell and Hendrix was confirmed by £. crossing suspect isolate with strains ATCC 18195 and ATCC 18196 of £. sylvaticum on potato-carrot agar (13). Effect on the growth of Mahaleb virulence roots was cherry seedlings. of nine isolates of £. irregulare isolated and soil in five orchards were compared. conducted in a growth chamber seedlings. The basic prepared with procedure Mircetich and Matheron (10). The The 6-wk-old was from as test Mahaleb described by Inoculum of £. irregulare was by growing each isolate at 21 C for 8 days on 200 ml vermiculite and 20 g oat kernels moistened with 100 ml V8 juice Camden, solution NJ), (200 ml V-8 2 g CaCO^, juice and (Campbell 800 ml distilled sterilized in 500 ml Erlenmeyer flasks. washed funnel the with distilled water over cheesecloth in a to remove unassimilated nutrients, (1/1/1 by volume). with vermiculite/oat replicates. The minimum was 18 C. daytime The nighttime The seedlings were fertilized biweekly (Peters Professional, W. plastic received Maximum temperatures were 21 C with 14 hr of light. at soil/sand/peat controls mixture without fungus. was Buchner then mixed Seedlings were planted in 4 L six Co. water) The inoculum rate of 20 cc per 1000 cc of sterilized pots Soup 20:20:20, Peters Fertilizer Products, R. Grace and Co., Fogelsville, PA). terminated after 18 wk. The experiment was Isolations from root tissue were 18 made on roots CMA-PARP selective medium. and shoots repeated. Dry weights were recorded. The of the experiment was Data were analyzed by an analysis of variance for a completely randomized experimental design. Interaction of PzAhlum lr.ggfiVllar.fi and Phytophthora spp. . Four isolates of £. irregulare (isolates B306, C6, J210, and L215) were used in single and combined treatments with cactorum (B2) M333). Eh. and two isolates of Eh. Ph. megasperma (M224 and All isolates were from cherry orchards in Michigan. megasperma M224 was avirulent and M333 was virulent Mahaleb cherry in Inoculum of irregulare and of prepared as described in the preceding section kernels grown £. a previous pathogenicity test Phytophthora to (1). spp. was except oat were omitted from the mixture and the isolates were for 5 wk. Inoculum was mixed per 1000 cc sterilized soil/sand/peat as follows: control treatments, cc of vermiculite treatments, without 20 cc fungus; and without fungal containers bench. inoculum + combined species combined fungal inoculum. L fungus; single 20 cc treatments 40 species vermiculite treatments, 40 cc The seedlings were planted in 1 and arranged in eight blocks on a All of in one half of each greenhouse block were flooded for 48 hr every 2 wk by immersing the pots in water. The experiment temperature was conducted during was maintained at 21 C, the winter, with 16 hr of The plants were fertilized as previously described. experiment was terminated after 15 wk. Isolations the light. The from 19 root tissue were made on CMA-PARP selective medium and on Phytoohthora selective medium (3). £. a irregulare populations in soil were monitored with a soil assay on CMAPARP selective medium. were recorded. analyzed for randomized versus The experiment was repeated. a 2x8 isolate split-plot complete blocks. nonflooding involving Dry weights of the shoots and roots was factorial Data were design The main factor of split single isolates, across four with flooding treatments three treatments involving of P.irregulare plus one isolate of one Phytophthora. plus an uninoculated control. RESULTS Pythium species isolated from roots. sylvaticum. Pythium and spp. from the irregulare from two £. ultimum Trow., £. £. irregulare. rostratum roots of Mahaleb liners was isolated most frequently. orchards were located on sites with orchards and were isolated from roots of sour cherry trees (Table 1). It was isolated trees in all orchards except N and U. other Butler, £. except orchard RW where These P. latter sandy soil. All the trees were declining due to X-disease, were located on sites with heavy soils. Pvthium orchards species isolated from soil. The six sour cherry on clay soils had Pythium populations estimated at 54.3 to 746.4 propagules per gram of soil (Table 2). The Table 1. Species of Pvthium isolated from the roots of sour cherry trees with reduced terminal growth or :?rom the roots of Mahaleb seedlings Pvthium species isolated3 P. irreaulare Year 1984 1985 Orchard code Fraction of trees B E J L N. Nd U 3/4 4/5 3/4 6/6 5/5 0/5 0/5 B D F J JC L P * RW® Xe Ye 6/6 5/5 4/5 3/4 5/5 5/5 4/4 4/5 11/12 10/10 Totals 78/95 V* 1:1 1:1 22 — 36 24 20 1£ IS 72 79 IS - - P. svlvatlcum P. ultimum Fraction of trees * Fraction of trees 1/4 0/5 2/4 2/6 1/5 0/5 0/5 1 4 4 — 0/4 0/5 0/4 1/6 2/5 0/5 0/5 0/6 0/6 2/5 4/4 2/5 2/5 0/4 0/5 10/12 8/10 0 O 9 8 7 19 0 0 - 0/6 0/5 1/5 2/4 0/5 2/5 1/4 0/5 11/12 0/10 34/95 20/95 P. rostratum % 0 Fraction of trees 0 1 - 1/4 0/5 0/4 1/6 1/5 0/5 0/5 0 0 7 10 0 7 IS 0 — 1/6 0/5 0/5 0/4 2/5 0/5 1/4 0/5 0/12 2/10 - 10/95 % 1 Pvthium so d . “ Fraction of trees % 0 2 — 0/4 1/5 2/4 0/6 0/5 0/5 0/5 1 0 - 2 0 0 0 2 0 2 0 - 2/6 0/5 1/5 0/4 4/5 0/5 1/4 0/5 2/12 0/10 2 0 0 0 3 0 2 0 - - 0 - 13/95 aSamples were collected in early summer Twenty to 40 plates of CMA-■PARP medium (6) containing ten rootlet or bark pieces were prepared from each tree. Two or more fungal species were often isolated from the same tree. “Values for Pvthium incidence are expressed as a percentage of the total number of plated tissue pieces. '"Combined total of remaining Pvthium spp. “Orchards were located on sites with sandy soil. el8olations were from Mahaleb liners from the Hest Coast. Table 2. Populations of P v t h i u m species as esti m a t e d by d i lution-plate counts from soil taken from sour cher r y orchards Pvthium p o p u l a t i o n by species Year: Orchard (propagules per gram 1984 code: (ppg))a 1985 ub B E J L N irreaulare 52.5 56.0 52.5 32.6 74.3 1.0 0.0 52.1 279.2 64.0 1.5 P. svlva t i c u m 6.1 5.4 122.6 12.5 157.4 0.0 1.0 25.2 17. 2 0.0 0.0 P. ultimu m 9.9 6.9 19. 8 3.2 52 .0 0.0 0.0 23. 1 259 .2 11.3 1.8 P . rostr a t u m 6.8 2.3 13. 1 6.0 52.4 0.3 1.0 1.9 18.0 4.2 0.3 Pvthium spp.c 0.8 6.1 10.9 0.0 100.5 1.7 0.6 16.1 0.0 0.0 0.0 54.3 437.0 3.0 2.6 746.4 79.5 3.5 P. Total 76.1 76.4 219.0 Nb J 119.3 L P RWb a Samples were c ollected once in early summer. E a c h v a l u e is the mean of ten soil samples per orchard. E ach soil sample is the composite of four sub samples collected a r ound one tree. “Orchards were located on sites w i t h sandy soil. c Combi n e d total of rema i n i n g Pvthium spp. 22 three very orchards on sandy soil (orchards N, low Pythium populations propagules per gram of soil. species from estimated U, and RW) had at 2.6 3.5 £. irregulare was the isolated most consistently (50% of all clay soils in both years, (19%) and by £. to followed by ultimum (15%). Pythium propagules) £. sylvaticum Estimates for £. sylvaticum were high in soils from orchards J and N in 1984, and for £. ultimum in soils from orchard N in 1984 and orchard L 1985. £. rostratum (6%) was found in primarily in orchard N in 1984. Effect of Pythium irregulare on growth of Mahaleb seedlings. The dry weights of shoots and roots of Mahaleb seedlings soil inoculated (£=0.05) seedlings with were significantly reduced over the dry weights of the noninoculated (Table obtained in 3, £. irregulare Figure 1). both experiments, Similar results were although dry weights were lower for all plants in experiment 2. with £. Seedlings inoculated irregulare exhibited many discolored rootlets diminished exhibited root systems while noninoculated root and shoot growth were reduced, seedlings were killed. There was no consistent in isolates. virulence reisolated between £. and seedlings healthy roots and a greater density of Although in rootlets. none of the difference irregulare from the roots of plants grown in infested was soil but not from roots of plants grown in noninfested soil. Interaction of initial Pythium analysis irregulare and Phytophthora. of variance, no significant In an differences Table 3. Effect of nine Isolates of Pvthium i rregulare on the growth of M a h a l e b seedlings growing in unflooded soil Experiment 1 Shoots3 ■Isolate number® Dry weight (9) Relative growth <*> Experiment 2 Roots3 Dry weight (g) Rootsa Shoots3 Relative growth (*) Dry weight (9) Relative growth («) Dry weight (g) Relative growth (*) 10.4 abc 82 3.0 be 73 2.7 b 45 1.4 b 48 B306 9.0 be 71 2.9 be 71 2.6 b 43 1.5 b 52 C6 6.1 c 48 2.6 be 63 2.5 b 42 1.4 b 48 C304 6.1 c 48 2.7 be 66 3.3 b 55 1.6 b 56 J210 6.0 c 47 2.6 be 63 2.7 b 45 1.2 b 41 J301 6.0 c 47 2.2 c 54 2.3 b 39 1.5 b 52 L215 7.8 be 61 2.7 be 66 2.6 b 43 1. 2 b 41 L304 8.3 be 65 2.9 be 71 4.9 ab 82 2.3 ab 79 P309 8.5 be 67 3.5 ab 85 3.8 ab 63 1.9 ab 66 100 4.1 a 100 6.0 a 100 2.9 a 100 B17 Control 12.7 a aSix-wk-old Mahaleb seedlings were transplanted into soil infested with 20 cc of inoculum per 1000 cc of soil. The experiment was conducted in a growth chamber for 3 mo. There were six replicates. “The letter preceding each isolate number codes for the orchard of origin. cValues followed by the same letter do not differ significantly (P=0.05) using Duncan's multiple range test. 24 Figure 1. Roots of representative Mahaleb seedlings grown in a growth chamber for 18 wk in a soil/sand/peat mixture artificially infested with Pythium irregulare. Soil in the pots was (a) uninfested; or infested with E. irregulare isolated from orchard B, (b) root and (c) soil; orchard C, (d) root and (e) soil; orchard J, (f) root and (g) soil; orchard L, (h) root and (i) soil; and orchard P, (k) soil. The treatments were not flooded. 25 were detected inoculated in the dry with the weights four of isolates Mahaleb of Therefore, only irregulare were presented in Tables 4-5 to seedlings P.irregulare. the results obtained with isolate C6 of p. illustrate the results obtained with all Pvthium isolates. Dry weights (P=0.01) of Mahaleb seedlings were significantly reduced in both experiments by flooding for 48 every 2 wk (Table 4). hr In the uninoculated controls flooding reduced shoot dry weights by 43.1-46.7% and root dry weights by 20.7-40.7% (Table 5, Figure 2). Significant differences (P=0.01) inoculation were in dry weights among the detected interaction the in both between flooding under but no treatments was detected by the significantly seedlings analysis reduced shoot and root dry inoculated with P. Dry weights i rregyilare and were not significantly different from dry seedlings inoculated of alone, except reduce the treatments significantly P h .megasperma weights of shoots as and it failed with either to reduce the control (Table much as root 5). the 2-3. No seedlings inoculated with P. were killed (Table 5). a fungus not other dry weights The reduced growth from roots and shoots from inoculation is evident Figures of the M224 in experiment 1 did dry from of weights Phytophthora sp. weights and p. irregulare. Ph. megasperma. and Ph. flooded and unflooded conditions. Mahaleb significant any of the inoculation treatments variance (Table 4). cactorum experiments, treatments in irregulare In inoculation treatments involving 26 Table 4. Analysis of variance for shoot and root dry weights of Mahaleb seedlings growing In soil infested with Pvthium irregulare and two Phytoohthora species in single and combined treatments under flooded and unflooded conditions Source of variation Degrees of freedom Shoot dry weight Root dry weight Mean square Mean square F value F value Experiment 1 Replication Flooding Error Treatments Treatment x flooding Error 7 l 7 7 7 98 1.424 131.828 1.713 14.933 0.798 0.935 0.83 76.95** a 15.97** 0.85 0.432 0.79 77.969 142.95** 0.545 2.244 11.16** 2.04 0.411 0.201 Experiment 2 Replication Flooding Error Treatments Treatment x flooding Error 7 1 7 7 98 3.526 1.28 124.228 45.04** 2.758 10.735 9.51** 1.196 1.06 1.129 a** indicates that values were significant (P=0.01). 1.443 37.303 0.672 1.940 0.362 0.524 2.15 55.50** 3.70** 0.69 Table 5. Effect of Pvthium Irregulare (P.) and two Phytophthora (Ph.) species on the growth of Mahaleb seedlings in single and combined treatments under flooded and unflooded conditions Shoots Unflooded Fungus and isolate number Dry Relative weight growth*1 (*) (g) Roots Flooded Dry weight (g) Unflooded Relative Mean growth® dry (*) wesight Dry weight (g) Relative growth® (X) 2.1 2.7 2.1 2.3 2.5 1.9 2.0 2.7 77 101 93 85 92 70 71 100 Flooded Relative Mean Dead Dry weight growth® dry weight (*) (9) Experiment 1 P. irreaulare C6 Ph. meaasoerma M224 Isolates C6 + M224 Ph. megasperma M333 Isolates C6 + M333 Ph. cactorum B2 Isolates C6 + B2 Control 3.8 4.6 3.0 3.0 3.5 2.8 2.7 5.8 Flooded means 3.6 65 79 52 . 52 60 48 47 100 1.4 2.8 1.3 1.2 1.0 1.2 1.0 3.3 42 85 39 36 30 36 30 100 2.5 cc 3.7 b 2.1 c 2.1 c 2.2 c 1.9 c 1.8 c 4.5 a 1.6 2.3 1.1 1.3 0.6 0.4 0.3 0.5 0.4 1.6 33 81 37 25 19 31 25 100 1.4 bc 2.0 a 1.3 b 1.4 b 1.4 b 1.1 b 1.2 b 2.2 a 0 0 0 1 3 1 2 0 48 61 48 52 39 48 43 100 1.8 b 1.7 b 1.7 b 1.8 b 1.4 b 1.7 b 1.6 b 2.6 a 0 0 0 3 1 2' 1 0 0.7 Experiment 2 P. irrequlare C6 Ph. meaasoerma M224 Isolates C6 + M224 Ph. megasperma M333 Isolates C6 -1-M333 Ph. cactorum B2 Isolates C6 + B2 Control 3.3 2.9 3.4 3.7 3.0 3.9 3.7 6.2 Flooded means 3.8 53 47 55 60 48 63 60 100 1.4 1.8 1.8 1.7 1.1 1.8 1.3 3.3 1.8 42 54 54 51 33 54 39 100 2.4 b 2.4 b 2.6 b 2.7 b 2.1 b 2.8 b 2.5 b 4.7 a 2.5 2.0 2.3 2.4 1.9 2.3 2.2 2.9 2.3 86 69 79 83 65 79 76 100 1.1 1.4 1.1 1.2 0.9 1.1 1.0 2.3 1.2 aSix-wk-old Mahaleb seedlings were transplanted in soil infested with 20 cc of.inoculum per 1000 cc of soil, flooding was for 48 hr every 2 wk. The experiment was conducted in a greenhouse for 15 vie. There were eight replicates. ®Values are expressed as a percentage of control. cValues followed by the same letter do not differ significantly (P=0.05) using Duncans Multiple Range test. 28 gsufl ^^wrTTJrr^'• r ' \ V i r ; ?f '*.iSK\ » ' < * « < i ft. ■ i <- ' , Figure 2. Shoots (A) and roots (B) of representative Mahaleb seedlings grown in a greenhouse for 3 mo in a soil/sand/peat mixture. Soil in the pots was (a) uninfested and non-flooded, (b) uninfested and flooded,or flooded and infested with (c) pythium. irregulare C6, (d) Phytoohthora. megasperma. avirulent isolate M224, (e) £. irregulare C6/Ph. megasperma. avirulent M224 (f) Ph. megasperma. virulent M333 (S ) P- irregulare C6/£h- megasperma. virulent M333 29 Figure 3. Shoots (A) and roots (B) of representative Mahaleb seedlings grown in a greenhouse for 3 mo in a soil/sand/peat mixture. Soil in the pots was (a) uninfested and flooded, or flooded and infested with (b) Pvthium. irregulars C6, (c) Phytophthora. cactorum B2, (d ) p. irregulare C6/fh. cactorum B2. 30 a Phytophthora sp., the experiment, 1-3 seedlings were dead at the end except no seedlings were killed of in treatments involving Ph. megasperma M224 (Table 5). Soil populations propagules 270 of £. irregulare J210 averaged per gram of soil for the unflooded treatment and propagules per gram of soil for the flooded P. irregulare Ph. treatment. was not reisolated from soil taken from uninoculated treatment, and 250 cactorum but p. were the irregulare, Ph. megasperma. reisolated from the single and combined treatments (Table 6). DISCUSSION There was an universal association of Pvthium species and particularly of p. irregulare with sour cherry trees located on heavy soils but not with trees located on sandy soils, and Pythium populations in heavy soils were high compared to populations associated States in sandy soils. Pythium species have with peach tree decline in the (4,8). One southern study correlated Pvthium been United populations with decline symptoms (4), while another using total Pvthium found Mahaleb trials no relationship (8). p. irregulare failed to cherry seedlings in greenhouse and chamber suggesting that Pythium is not the primary cause death of cherry trees in Michigan. consistently and However P. of irregulare caused reductions in shoot and root growth these trials indicating that P. cherry growth kill in irregulare is a pathogen of may contribute to the reduction in growth of 31 Table 6. Reiso l a t i o n of Pvthium irregulare and two Phytophthora species from M a h a l e b seedlings (experiment 2) grown for 15 weeks wit h periodic flooding Reisolations3 Fungus and isolate number P. irregulare*3 Phytoohthora0 J210 8/8 0/8 P h . megasperma M224 0/8 5/8 P h . megasperma M224/ P. irregulare J210 7/7 3/7 Ph. megasperma M333 0/5 5/5 P h . megasperma M333/ P. irregulare J210 6/6 4/6 Ph. cactorum B2 0/6 6/6 Ph. cactorum P . irregulare B2/ J210 6/6 6/6 1/8 0/8 P. irregulare Control aFraction of Mahaleb seedlings from which P. irregulare or Phytophthora were reisolated. “Reisolations were made on CMA-PARP selective medium. cReisolations were made on Phytophthora selective medium. 32 cherry trees. Recently Bielenin and Jones (1) identified Ph. megasperma. £h- gflytexvm, Eh- QambiYQKa (Petri) Busiman, £hcryptogea Pethyb. as causal trees agents in the decline and death of in soils. Michigan located on sites with sour cherry poorly drained In the present study, infection by £. irregulare in combination increase In and Laff., and £h. syringae (Kleb.) Kleb. with Eh- the megasperma and Eh- death of seedlings over cactorum did not Phytophthora alone. single and combined treatments reductions in dry weight were similar for £• that competition between trees for infection sites may indicating have the genera in the combined treatments. £. occurred In mature irregulare appears to be confined to the roots (7), (1.14) irregulare and Phytophthora while Eh. and £h. lateral cactorum is associated with the crown megasperma with the lateral and main roots (1.11.14). Pythium has been implicated in the apple replant (5,12) and and has been repeatedly shown to cause discoloration necrosis development trials. of of In demonstrated lateral roots, the present study, significant in necrosis and apple seedlings in statistically Root disease inhibition greenhouse of inoculation necrosis of roots reduction inoculation trials with in root and growth Mahaleb were cherry. and reduced weights were obtained even seedlings were inoculated but not flooded, reduction in growth and deterioration of young a although roots when the were 33 greater with flooding. However, there was no indication of a replant problem in the orchards studied here, as growth of the young Stunting, trees was good for the first few years. decline and death of the trees developed when the trees came into bearing. LITERATURE CITED 1. Bielenin, A., and Jones A. L. 1988. Prevalence pathogenicity of Phytophthora spp. from sour cherry trees in Michigan. Plant Dis. 72:473-476. 2. Fliegel, P., Parker, K. G . , and Mai, W. F. 1963. The fungous flora of nonsuberized roots of poorly growing cherry trees. Phytopathology 53:1368-1369. 3. and Harris, D. C . , and Bielenin, A. 1986. Evaluation of selective media and bait methods for estimating Phytophthora cactorum in apple orchard soils. Plant Pathol. 35:365-374. 4. Hendrix, F. F . , Jr., Powell, W. M . , and Owen, J. H. 1966. Relation of root necrosis caused by Pythium species to peach tree decline. Phytopathology 56:12291232. 5. Jaffe«; B: A., Abawi, G. S., and Mai, V!. F. 1982. Fungi associated with roots of apple seedlings grown in soil from an apple replant site. Plant Dis. 66:942944. 6. Jeffers, S. N . , and Martin, S. B. 1986. two media selective for Phytophthora species. Plant Dis. 70:1038-1043. 7. Miller, C. R . , Dowler, W. M . , Petersen, D. H . , and Ashworth, R. P. 1966. Observations on the mode of infection of Pythium ilLtimum and Phytophthora cactorum on young roots of peach. Phytopathology 61:357-360. 8. Mircetich, S. M. 1971. The role of Pythium in feeder roots of diseased and symptomless peach trees and in orchard soils in peach tree decline. Phytopathology 61:357-360. Comparison of and Pythium 34 9. Mircetich, S. M . , and Kraft, J. M. 1973. Efficiency of various selective media in determining Pvthiurn populations in soil. Mycopathol. Mycol. Appl. 50:151161. 10. Mircetich, S. M . , and Matheron, M. E. 1976. Phytophthora root and crown rot of cherry trees. Phytopathology 66:549-558. 11. Proffer, T. J . , Jones, A. L . , and Ehret, G. R. 1987. Biological species of Armillaria isolated from sour cherry orchards in Michigan. Phytopathology 77:941-943. 12. Sewell, G. W. F. 1981. Effects of Pythium species on the growth of apple and their possible causal role in apple replant disease. Ann. Appl. Biol. 97:31-42. 13. Van der Plaats-Niterink, A. J. 1981. Monograph of the genus Pythium. Studies in Mycology No 21 Centraal Bureau voor Schimmelcultures, Baarn. 242 pp. 14. Wilcox, W. F . , and Mircetich, S. M. 1985. Pathogenicity and relative virulence of seven Phytophthora species on Mahaleb and Mazzard cherry. Phytopathology 75:221-226. PART II SPECIES AND POPULATIONS OF PYTHIUM ISOLATED FROM SOUR CHERRY ORCHARD AND WOODLAND SOILS IN MICHIGAN 35 ABSTRACT Pythium populations were high (54.3 to 746.4 viable propagules per gram of soil) in eight orchards on clay soil and four low orchards 1985. to (1.2 to 3.5 propagules per gram of soil) in on sandy soil sampled in western Michigan in 1984Populations were also high in two woodlands adjacent orchards in 1986, central Michigan Michigan species. were in found and in six woodlands in 1987. Orchards and to differ in composition of in Pythium In soil from orchards, £. irregulare was isolated sylYatis.um (26%), £. followed by £. ultimum (13%), £. rostratum (6%), and Pythium group 'HS' (8%). In soil from woodlands, ’HS* was isolated most frequently (60%) Ezthi.um and woodlands most frequently (47% of Pythium propagules), group western group ’X* (29%), group ’Y ' (9%). soils of all woodlands, £. rostratum (2%), Pythium followed and by Pythium The first two species were isolated from while the latter two species isolated from two woodland sites. No £. were irregulare. £. sylvaticum. or £. ultimum were isolated from woodland soils. Populations of £. irregulars. £. sylvaticum. and £. ultimum in two orchards sampled over 2 yr and one orchard over 1 yr, varied independently. 37 INTRODUCTION cherry ( Prunus cerasus L. Sour southwestern Michigan are planted on sites were beech-maple woodlands. orchards decline Montmorency) orchards in that formerly It was observed that trees in planted on heavy clay soils frequently exhibited symptoms of poor growth and decreased longevity and had root systems that exhibited extensive discoloration decay of lateral roots. Trees in orchards on sandy and soils grew well and had root systems with little discoloration lateral roots. isolated Pythium irregulare (Buisman) was frequently from roots of trees with discolored lateral roots, growth of conducted and Isolates of £. Mahaleb in of the seedlings greenhouse necrotic irregulare reduced in and and pathogenicity growth chamber the trials (17). Seedlings of Prunus mahaleb L. are the most common rootstock used for propagation of cherry trees. Although Pythium species are soilborne pathogens wide range of crops (6,19), an soils undisturbed are sites been tree decline (7,12). One study Pythium populations with decline (11). from have correlated using soils species with another in Pythium associated while peach Species common infrequently present in (18). a they are poor competitors among established soil microflora (2,6). cultivated of total Pythium found symptoms no (7), relationship Pythium species isolated from peach decline orchards 38 in Georgia were also isolated from forest southeastern United States (4). of studies soils in the There have been no reports on the composition of populations of Pvthium species in cherry orchard soils, nor have there been reports of comparisons in Pythium populations between cherry orchard soils and woodland soils. The objectives species from of this study were to investigate and populations of Pythium in clay and sandy cherry orchard sites and in soil from the soils woodlands adjacent to orchards. MATERIALS AND METHODS Sampling clay sites. Eight commercial sour cherry orchards on soil exhibiting poor growth and two on sandy soil with healthy trees were sampled in 1984 and four orchards on clay soil and two on sandy soil were sampled orchard was sampled once in early summer. of the orchards on in 1985. Each In addition, two clay soil (orchards J and were a third sampled four times both in 1984 and in 1985, orchard on clay soil (orchard P) was sampled four times 1985. and L) in Two sour cherry orchards and adjacent woodlands were sampled once in early summer in 1986 and six woodlands were sampled once in October in 1987. The woodlands were composed primarily of beech (Fagus grandifolia (Afi££ rubrwn L.), maple (A- Ehrh)., red maple silver maple (A- saccharinum L . ) and hard saccharum Marsh). All sites were in Berrien and Van Buren counties of western Michigan except woodland sites 39 MSU F and MSU G were located in East Lansing (Ingham county) in central Michigan. Isolation Pythium of Pythium species from soil. The populations species plates (13). (CMA) were estimated by surface soil of dilution The isolation medium used was corn meal agar (Difco) ampicillin, amended 10 with mg pentachloronitrobenzene 10 mg pimaricin, rifampicin, (CMA-PARP) and per liter 250 mg 50 mg (9). Four cores of soil were taken between the drip line and the trunk from each sampled of 10 trees per orchard. like orchard sites, Woodland sites were except 5 rather than 10 per site were sampled in 1987. trees The cores were taken to a depth of 15 cm with a Hoffer soil sampler and mixed for each tree in a plastic bag. The samples were transported to the laboratory chest in an ice stored at processed. Soil sequentially through 5- and 1.68-mm-mesh sieves. subsample samples and until passed A 1 g from each bulk sample was suspended in 0.2% water selective medium. distributed Three C were air dried and then agar and dilution plated at 1:10, CMA-PARP 4 over replicate the plates 1:50, and 1:100 on fresh Diluted samples (1 surface with a were made per dilution (nine plates per tree). sterile ml) were glass rod. subsample and per After 42 hr incubation in darkness at 21 C, the soil was removed by washing each plate under running tap water and the number of Pythium counted. colonies 40 Identification 15 of Pythium species. Hyphal tips from 5 colonies per sample were transferred to CMA-PARP and then, after incubation for 48 hr at 21 C, plates to Growth rates were recorded after 24 hr incubation on CMA 25 C. to CMA. at Fungal structures were examined after the cultures had grown for 1-2 wk. Identifications of the various Pythium species were made with the aid of the key of Van der PlaatsNiterink (19). Identification of the heterothallic species £. sylvaticum was confirmed by crossing each suspect isolate with strains ATCC 18195 and ATCC 18196 of £. sylvaticum on potato-carrot agar (19). RESULTS Pythium species identified. colony morphology, sporangia, £. Hendrix, group irregulare. oogonia, £. were as described by Two identified, were swellings, and charachteristics antheridia, sylvaticum Campbell of and and £. ultimum Trow . , £. rostratum Butler, and Pythium 'HS* (19). growth rates, hyphal oospores. Identifications were based on made groups of Pythium Van der Plaats-Niterink isolates could not be as oogonia were not produced, even when crosses on potato-carrot agar. These Pythium group ’X* and Pythium group ’Y'. were designated Colony morphology was radiate on CMA although Pythium group ’X' had a variable rosette pattern. Growth rates of Pythium group Pythium group *Y' were 20 and 13 mm, at 25 C on CMA. Pythium group respectively, ’X' produced ’X' and in 24 hr numerous 41 terminal and intercalary hyphal diameter on CMA and in water. swellings 20-25 Pythium group 'Y' m in produced sparse, ovoid intercalary hyphal swellings on CMA. Pythium sour populations in soil. Samples of soil from cherry orchards on clay soils had Pvthium estimated (Table very at 54.3 1). low populations gram of soil Samples from four orchards on sandy soil Pythium propagules to 746.4 propagules per eight populations per gram of soil. estimated £. at 1.2 had to irregulare was 3.5 isolated most consistently (47% of all propagules) from clay soils in both years, (13%). followed by £. sylvaticum (26%) and Estimates for £. ultimum these latter species were high soils of some orchards but not in both years. £. (6%) primarily and Pythium group ’HS* (8%) were found in rostratum in orchard N in 1984, and in orchard C in 1985. The seven estimated 2). woodland sites had Pvthium populations at 180 to 1153 propagules per gram of soil (Table Pvthium group ’HS' and Pvthium group ’X' were isolated from soil taken from each of the sites. was isolated group ’X' most frequently (60%), (29%); £. rostratum (2%) woodland J in 1986 and MSU F in 1987; (9%) was Pythium group ’HS' followed was by Pvthium isolated from and Pvthium group ’Y' isolated from woodland sites C and J in 1986 and site B in 1987. Sequential over season isolations from soil taken from two two growing seasons and one orchard over showed that populations of Pythium one species orchards growing varied 42 Table 1. Populations of Pvthium species as estimated by dilution-plate counts from soil taken from sour cherry orchards planted on two soil types Pvthium population by species (propagules per gram (ppg))a Orchard Soil £• E* E> Ecode type irregulars sylvaticum ultimum rostratum E. E. ’HS* spp. Total (PPg) 1984 growing season B Clay 52.5 6.1 9.9 6.8 0.0 0.8 76.1 C Clay 26.2 26.7 0.0 0.0 2.8 0.0 55.7 6 Clay 56.0 5.4 6.9 2.3 6.1 0.0 76.4 H Clay 52.3 17.4 26.2 5.0 23.7 0.0 124.6 J Clay 52.5 122.6 19.8 13.1 10.9 0.0 219.0 L Clay 32.6 12.5 3.2 6.0 0.0 0.0 54.3 P Clay 47.8 0.8 16.4 8.2 0.0 1.5 74.7 N Clay 74.3 157.4 52.4 52.4 100.5 0.0 437.0 N Sand 1.0 0.0 0.0 0.3 1.7 0.0 3.0 0 Sand 0.0 1.0 0.0 1.0 0.6 0.0 2.6 1985 growing season J Clay 52.1 25.2 23.1 1.9 16.1 0.0 119.3 L Clay 279.2 17.2 259.2 18.0 0.0 0.0 746.4 P Clay 64.0 0.0 11.3 4.2 0.0 0.0 79.5 C Clay 67.1 189.5 0.0 26.1 160.5 0.0 443.2 C Sand 0.6 0.6 0.0 0.0 0.0 0.0 1.2 RW Sand 1.5 0.0 1.8 0.3 0.0 0.0 3.5 Each value is the mean of ten soil samples per orchard. Each soil sample is the composite of four sub-samples collected around one tree. Sites were sampled on one occasion. Table 2. Populations of Pvthium species as estimated by dilution-plate counts from soil taken from sou]? cherry orchards and woodlands Pvthium population bv species (prooaoules per crram fppa))a Site Soil P. P. P. P. type irrequlare svlvaticum ultimum rostratum P. 'HS' P. 'X' P. •Y~ ■total (PP9) Clay Clay Clay Clay 0 238 0 165 0 147 6 258 240 1153 181 900 102 0 0 0 0 0 340 420 260 260 180 560 May 1986 C C J J orchard woodland orchard woodland 46 0 72 0 60 0 <17 0 0 0 30 0 11 0 0 51 123 768 26 426 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 18 0 204 262 130 88 126 504 October 1987 Woodland sites Bb Sand Clay H Sand Lc Clay MSU F Sandy loam MSU Gb Sandy loam C° 0 0 0 0 0 0 34 168 130 132 36 56 aEach value is the mean of ten soil samples taken in 1986 and five soil samples in 1987. Each soil sample; is the composite of four subsamples collected around one tree. PSites were adjacent to sour cherry orchards. cSite was not close to a cheriy orchard. 44 independently of each other (Figure 1-3). Estimates total Pythium populations in soil from orchard J from a high of 313.2 propagules per gram in October 1); fluctuated low of 107.0 propagules per gram in July 1984 to from 1984 orchard L, 1985 and from 54.3 propagules per gram in from orchard P, from a (Figure to 1009.0 propagules per gram in October 1985 2); of May (Figure 79.5 propagules per gram in May 1985 to 351.1 propagules per gram in August 1985 (Figure 3). . DISCUSSION Soils from orchards and from woodlands in Michigan were found to differ in their composition of Pythium species. Pythium group ’HS' were isolated rostratum and habitats, indicating that these species were competitive in both cultivated and woodland soils. the most frequent isolate from farmland soils in England (1,5), isolated worldwide woodland. parkland; and has £. rostratum has been found to has be pathogenic or weakly pathogenic on a wide variety of (19). irregulare. £. isolated soil from £. distributions a nonhosts sylvaticum. and £. ultimum were from soil from orchards but were not woodlands. and however its pathogenicity from a variety of habitats (1,5,18), distribution, both Pythium group ’HS' was to crop plants has not been investigated. been from £. All three species detected have in worldwide and have been isolated from a wide variety of 45 200 150- - P.irregulare - P.sylvaticum . P.ultimum - Pvthium spp. O) O. a 100- M ay Ju l Aug O ct M ay Jun Aug Oct TIME Figure 1. Fluctuations in population (propagules per gram of soil) of Pythium species as estimated by dilution-plate counts for soil samples taken from sour cherry orchard J in southwest Michigan during 1984 and 1985. Species identified were £. irregulars, £• szlyflticum, £. ultimum. and Pythium spp. . 46 800 700- 600- 500 - 400 - 200- io o H E "T " May T Jul — I---------P' " I Aug Oct May 1 ....... 1 Jun Aug I 1 Oct TIME Figure 2. Fluctuations in population (propagules per gram of soil) of Pvthium species as estimated by dilution-plate counts for soil samples taken from sour cherry orchard L in southwest Michigan during 1984 and 1985. Species identified were £. irregulare, £. sylvaticum, £. ultimum. and Pythium spp. . 47 200 150O) a a ^ ioo- X I— >Q_ 50- May Ju l Aug O ct TIME Figure 3. Fluctuations in population (propagules per gram of soil) of Pythium species as estimated by aiiution-plate counts for soil samples taken from sour cherry orchard P in southwest Michigan during 1985. Species identified were I) £. irregulars, S) £. ay.lgatis.ma. U) £. ultimum. and P) Ezthlum s p p . . 48 hosts (19). Among deciduous orchard crops, is reported as pathogenic to apple (8,16), and to cherry (17); £. P. irregulare to peach (7,12), sylvaticum to apple (16); and £. ultimum to apple (3) and to peach (7,12). The sites Pythium species found in soils from were seven similar regardless of soil type, orchard sites, and location in Michigan. woodland proximity The to predominant species of trees in all woodland sites were beech and maple, indicating that the areas had previously belonged to the beech-maple climax community, which was common over southern Michigan. been The trees in the sites had obviously previously clean cut or selectively felled, varying degrees of disturbance, orchard sites. between the There and the sites showed but had never been used appears to be a stable isolated Pvthium species and as association the beech/maple community as indicated by the similarity between the Pvthium species isolated from diverse counties in Michigan. Populations of Pvthium species in soils taken from cherry orchards were high in clay soils and low soils. The physical and chemical properties of soil Pythium populations. sour in sandy affect Pythium populations were reported to be higher under conditions of high soil moisture (1, 11, 18) and high conditions and soil soil organic content (10), (5). and lower under Clay soils favor retention of organic matter in the soils of acid moisture, orchards was increased due to mechanical cultivation. Populations of Pythium species from orchards on clay 49 soils varied over time. bean field response soils to Populations of Pythium species in were reported to vary temperature organic matter (10). parkland, and (10,14), and independently in incorporation of The predominant species in woodland, farmland soils in England were reported to because £. show seasonal fluctuations in population (1). This study irregulare was seedlings soil (17). found to implications reduce the growth chamber of studies. appears at 10 fold greater population from Mahaleb orchards on clay soils than on £. densities sandy soils It may limit the growth of cherry trees planted sites with clay possibility sandy, Pythium would well species. increase One method for avoiding be to establish new cherry this orchards Additionally the on on pathogenic species were not detected in woodland soils even on so on newly cleared sites on clay soils it possible present soil. drained sites. clay soils, be practical in greenhouse and growth irregulare in has to prevent the introduction of However in it woodlands these Pythium is possible that these species at under cultivation. undetectable levels may and are could This is in contrast to root rot caused by Armillaria species which are endemic on pine and oak and cause disease in orchards planted cleared from these woodlands in Michigan (12). on sites 50 LITERATURE CITED 1. Ali-shtayeh, M. S., Lim-ho, C. L . , and Dick, M. W. 1986. The phenology of Pythium (Peronosporomycetidae) in soil. Journal of Ecology 74:823-840. 2. Barton, R. H. 1958. Occurrence and establishment of Pythium in soils. Trans. Brit, mycol. Soc. 41:207- 222. 3. Bielenin, A., Borecki, Z., and Millikan, D. F. 1976. Identification of Pythium ultimum in the collar rot complex of apple. Phytopathology 66:127-129. 4. Campbell, W. A. and Hendrix, F. F. 1967. Pythium and Phytophthora species in forest soils in the southeastern United States. Plant Dis. Rep. 51:929-932. 5. Dick, M. W . , and Ali-shtayeh, M. S. 1986. Distribution and frequency of Pythium species in parkland and farmland soils. Trans. Br. mycol. Soc. 86:49-62. 6. Hendrix, F.F.Jr., and Campbell, W.A. 1973 Pythiums as plant pathogens. Ann. Rev. Phytopathology 11:77-98. 7. Hendrix, F. F . , Jr., Powell, W. M. , and Owen, J. H. 1966. Relation of root necrosis caused by Pvthium species to peach tree decline. Phytopathology 56:12291232. 8. Jaffee, B. A., Abawi, G. S., and Mai, W. F. 1982. Fungi associated with roots of apple seedlings grown in soil from an apple replant site. Plant Dis. 66:942944. 9. Jeffers, S. N . , and Martin, S. B. 1986. two media selective for Phytophthora species. Plant Dis. 70:1038-1043. Comparison of and Pythium 10. Lumsden, R. D . , Ayers, W. A., Adams, P. B . , Dow, R. L . , Lewis, J. A., Papavizas, G. C . , and Kantzes, J. G. 1976. Ecology and epidemiology of Pvthium species in field soil. Phytopathology 66:1203-1209. 11. Mircetich, S. M. 1971. The role of Pvthium in feeder roots of diseased and symptomless peach trees and in orchard soils in peach tree decline. Phytopathology 61:357-360. 51 12. Mircetich, S. M . , and Fogle, H. W. 1969. Role of Pythium in damping-off of peach. Phytopathology 59:356-358. 13. Mircetich, S. M . , and Kraft, J. M. 1973. Efficiency of various selective media in determining Pythium populations in soil. Mycopathol. Mycol. Appl. 50:151161. 14. Piekzarka, D. J . , and Abawi, G. S. 1978. Influence of soil water potential and temperature on severity of Pythium root rot of snap beans. Phytopathology 68:766772. 15. Proffer, T. J., Jones, A. L. and Ehret, G. R. 1987. Biological species of Armillaria mellea isolated from sour cherry orchards in Michigan. Phytopathology 77:941-943. 16. Sewell, G. W. F. 1981. Effects of Pythium species on the growth of apple and their possible causal role in apple replant disease. Ann. Appl. Biol. 97:31-42. 17. Smither, M. L . , 1988. Cherry tree decline: associated Pythiaceous species, pathogenicity and control. Ph.D. Thesis, Michigan State University. 18. Van der Plaats-Niterink, A. J. 1975. Species of Pvthium in the Netherlands. Neth. J. PI. Path. 81:22-37. 19. Van der Plaats-Niterink, A. J. 1981. Monograph of the genus Pythium. Studies in Mycology No 21 Centraal Bureau voor Schimmelcultures, Baarn. 242 pp. PART III EFFECTS OF PHYTOPHTHORA METALAXYL AND AND FOSETYL-AL ON PYTHIUM SPECIES ’IN VITRO' AND PATHOGENICITY TO MAHALEB CHERRY 52 GROWTH ON OF THEIR 53 ABSTRACT Seven cherry pythiaceous species associated with roots of in metalaxyl Michigan were tested for their and phosphorus acid in culture. sensitivity acid, 7.5; The EDgQ respectively values for metalaxyl were: to All fungi were inhibited by both fungicides and sensitivity varied species. sour and between phosphorus Phytophthora cactorum. 0.06 and £h. citricola. 0.17 and <7.5; Eh- drechsleri. 0.26 and 27.0; £h. megasperma. 0.49 and 80.0; £• sylvaticum. 0.5 and 78.1; and E- ultimum 0.06 and 7 8 . 7 ytig/ml. 1-yr-old 1.52 and 49.5; Pvthium irregulare. Phytotoxic symptoms were observed Mahaleb seedlings at 400 and 800 ^g/ m l on metalaxyl. Significant (E=0.05) reductions in shoot and root dry weight occurred with 9-wk-old Mahaleb seedlings growing in soil infested with £. irregulare. Ph.megasperma. and £h. cactorum in a growth chamber. Metalaxyl was more effective fosetyl-Al in preventing fungus induced necrosis and than growth reduction. INTRODUCTION Root rot of sour cherry trees occurs in orchards planted on poorly drained soils in Michigan. are considered Phytophthora species to be the primary causal agents of cherry root and crown rot in Michigan (2), California (22), and New York (29). Pythium species, and £. irregulare in 54 particular, were found to be associated with lateral root necrosis of cherry trees, and caused reductions in growth of Mahaleb seedlings in greenhouse trials (M. L. Smither, unpublished). Metalaxyl used and experimentally to blight induced thus by Pythium and (23,26). been diseases damping-off Variations in to metalaxyl occur between species (6,8,17,21), variations in the degree of metalaxyl has control by Phytophthora (1,5,11,13,15,28) sensitivity and an acylalanine fungicide and it commercially induced and is can control exerted be expected on the Phytophthora and species associated with cherry decline. by Pythium The development of resistance to metalaxyl has occurred (4,10). Fosetyl-Al (aluminium tris(0-ethyl phosphonate)) has been used effectively to control diseases induced by Phytophthora (11,13,16,24). required Coffey to High inhibit Phytophthora ’in convincingly fungicidal (18,19). concentrations demonstrated of fosetyl-Al v i t r o 1. that the are Fenn and effective agent is the breakdown product phosphorous acid As with metalaxyl variations in sensitivity occur between species (7,8,18). The development of resistance to phosphorus acid has been demonstrated experimentally (3). The objectives of this study were to test the sensitivity of pythiaceous species isolated from the roots of cherry to metalaxyl and phosphorus acid in culture, the effectiveness control of of metalaxyl and and to fosetyl-Al determine for root rot of Mahaleb cherry seedlings caused the by 55 various pythiaceous species. MATERIALS AND METHODS Sensitivity culture. (Leb. of species to metalaxyl Single & PyftMum (Bl) Ph. citricola (HI) Tucker, Ph. megasperma irregulars (L215) Campbell and Hendrix, from cherry sensitivity orchards to fosetyl-Al Buisman, and P. p. Sawada, (Bl) sylvaticum ultimum (B302) Trow, in Michigan were margin Disks and amended tested (C201) isolated for phosphorous acid and metalaxyl in their culture. placed in the center of metalaxyl replicate initial experiment. twice at rates of 0, 10, plates phosphorous 0.01, 0.1, The experiment was repeated. of phosphorous acid were 0, an six or Concentrations of metalaxyl were 0, in agar 5 mm in diameter were taken from the colony with 100 ^g/ml. Ph. Drechsler, The fungal isolates were grown for 5 days on corn meal (CMA). in isolates of Phytophthora cactorum (Bl) Cohn) Schroet., drechsleri and acid. 1, 10, and Concentrations 10, 50, 100, 250, and 500 /|g/ml The experiment was repeated 25, 50, 75, and 100/(g/ml. plates were stored in darkness at 21 C and growth was measured daily for 7 days. radial The colony ®^50 va-*-ues were calculated from linear regression lines obtained by plotting the mean percent inhibition of mycelial growth against the concentration of metalaxyl and phosphorus acid. Fungicide trials. Fungal inoculum for the three 56 fungicide trials was prepared by growing the isolates at C for 5 wk on 200 cc vermiculite moistened with 100 ml juice solution (200 ml V-8 juice, distilled (22). water) The in a Buchner funnel and sterilized in 500 ml V-8 and 800 Erlenmeyer mixed at to remove the rate of 10 soil/sand/peat (1/1/1). ml flasks inoculum was washed with distilled water cheesecloth nutrients sterilized 2 g CaCO^, 21 over unassimilated cc/1000 cc with Controls recieved the vermiculite mixture but no fungus. Experiment one was conducted in a greenhouse with dormant 1-yr-old Mahaleb infested with isolates of Eh- (HI), Eh- ultimum megasperma (G7). seedlings planted (CA), directly cactorum (Bl), £. soil P h .citricola irregulare (C6), 4 L complete containers, blocks with which six were and with 14 hr of light. arranged nighttime £. three replications. daytime temperatures were 24 C, was 18 C, into The experimental units consisted of in randomised maximum seedlings as The minimum Fungicide solutions were applied to the soil after 8 days at rates of 0, 10, 25, 100, 400, The 800 M g /ml metalaxyl in 250 ml and distilled experiment was terminated after 3 mo. water. Dry weights of roots and shoots were recorded. Experiment with dormant into soil Eh-fiiirisala (L215), two was conducted outside, shaded 1-yr-old Mahaleb seedlings planted infested (HI), and £. with isolates of Eh- megasperma sylvaticum (C201). Eh(CA), by directly cactorum E. lath, (Bl), irregulare The experiment was set 57 up as for experiment one. 6 wk after planting. 250 ml Fungicide treatments were applied Metalaxyl was applied at 100^g/ml in distilled water as a soil drench. Fosetyl-Al was sprayed onto the foliage to run-off with a hand sprayer, rates of 1.5 terminated and 3.0 g a.i. after 3 mo. L. The at experiment Dry weights of roots and was shoots were recorded. Experiment three was conducted in a growth chamber using 9-wk-old Mahaleb seedlings, and isolates of £. irregulare (C6), cactorum (B2) and Eh- meaasperma (Bl). Combined Phytophthora and £. irregulare treatments used 10 fungal inoculum from each isolate. Seedlings were in 1 L pots with eight replicates. at the rate of 70 soil drench Fosetyl-Al hand the seedlings at had been monthly g a.i./L. every roots was intervals. transplanted. Maximum 18 C. shoots were recorded experiment was repeated in a greenhouse. were The nighttime Dry weights after a daytime The seedlings were flooded for 48 2 wk and fertilised biweekly. and was applied Fungicides temperatures were 21 C with 14 hr of light. minimum planted sprayed onto the foliage to run-off with sprayer at a rate of 4 reapplied of ^ g a.i./ml in 50 ml distilled water, as a after was Metalaxyl cc 10 wk. of hr the This 58 RESULTS Sensitivity in of species to metalaxyl and phosphorous culture. Rates increasing of fungal growth were acid reduced metalaxyl concentration (Figure 1). with Growth of P h . cactorum and p. ultimum was completely inhibited above 1 y^g/ml. Growth of £. 100 M S / m l irregulare and P. sylvaticum at 10 and only occurred during the initial 24 hours. Slow growth of Ph. drechsleri and Ph. megasperma continued at 100 ^g/ml. The EDg0 values were lowest, cactorum and P. ultimum (Table 1). highest EDgQ value, Rates of phosphorous fungal 1.52 0.06xxg/ml, Ph. megasoerma had the jus/ ml, of the fungi tested. growth were reduced <10 M S / ml. Ph. increasing Growth Ph. most sensitive of the species tested, of with an ED^ q (Table 1). of 49.5 The three Pvthium were least sensitive with EDgQ values between and 80 Mg/ml all citricola was megasoerma had the highest ED_~ value. ou ^g/ml of the Phytoohthora species tested. species with acid concentration (Figure 2) isolates was prevented with 500 Mg/ral. the for P h . 78.1 The experiments were repeated with similar results. Fungicide Mahaleb trials. seedlings In experiment one, for all fungal treatments weights were of highest jl{g/ml (Table 2). symptoms of leaf margin necrosis occured at 400 with metalaxyl concentrations from 10-100 Phytotoxic dry and 800 MS/™! (Figure 3). A factorial analysis showed that 59 40 0.0 0.01 30 ■ -O- 10 -V- 100 o 20 ■ at 10 ■ 0 2 3 4 5 6 7 8 TIME (d ay s ) Figure la. Radial growth of Phytophthora cactorum in culture amended with metalaxyl at rates of 0.0, 0.01, 0.1, 1, 10, and 100 iia /ml. 40 B '■ o.o - i f 0.01 -V- 100 30 ■ o 20ac 10 ■ 0 2 3 TIME 4 5 6 7 a (days) Figure lb. Radial growth of Phytophthora citricola in culture amended with metalaxyl at rates of 0.0, 0.01, 0.1, 1, 10, and 100 i\g/nl. 60 40 -O - 10 -V - 100 O 20- 10 ■ TIME (day s) Figure lc. Radial growth of Phytophthora drechsleri in culture amended with metalax/l at rates of 0.0, 0.01, 0.1, 1, 10, and lOO^g/ml. 40 o.o 0.01 30 ■ -O- 10 100 o 20- ac 10 • 0 2 3 TIME 4 5 6 7 8 (day s) Figure Id. Radial growth of Phytophthora megasperma in culture amended with metalaxyl at rates of 0.0, 0.01, 0.1, 1, 10, and 100 ng/ml. 61 40 - B " o.o 0.01 30 - - O - io - V - 100 10 • 0 2 4 3 TIME (d ay s) S 6 7 8 Figure le. Radial growth of Pythium irregulare in culture amended with metalaxyl at rates of 0.0, 0.01, 0.1, 1, 10, and 100 ^g/ml. ~B ■■ o.o -A— 0.01 0.1 100 O 20at 10 ■ TIME (day s) Figure If. Radial growth of Pythium sylvatlcum in amended with metalaxyl at rates of 0.0, 0.01, 0.1, and 100 /Mg/ml. culture 1, 10, 62 40 0.0 0.01 0.1 30 • -O- 10 -4?- 100 10 ' 0 1 2 3 4 5 6 7 8 TIME (d a y s ) Figure lg. Radial growth of Pythium ultimum in culture amended with metalaxyl at rates of 0.0, 0.01, 0.1, 1, 10, and 100 /j(g/ml. 63 Table 1. ED5Q values for Phytophthora (Eh.) and Pythium (£•) species to metalaxyl and phosphorus acid in culture E D 50 Fungus Metalaxyl ^g/ml values Phosphorus acid M g / ml CO o o X Ph. cactorum 7.5 Ph. citricola 0.17 <10y Ph. drechsleri 0.26 27.0 Ph. megasperma 1.52 49.5 P. irregulare 0.49 80.0 P. gylyaticum 0.50 78.1 T 5 i, . A •uu AA V rr r> „ 1 J.4 U J . V0.4I4LUU t O •«7t Values were calculated from means of six replicate plates. The experiment was repeated with similar results. The value was too low to be calculated by this concentration range. 64 40 'A " 1 10 25 30 • - G - 75 s?— 10 100 ■ a 0 2 3 4 5 6 7 8 TIME ( d a y s ) Figure 2a. Radial growth of Phytophthora cactorum in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and 100 yUg/ml. 40 25 30 ■ 100 o 20- 10 ■ TIME ( d a y s ) Figure 2b. Radial growth of Phytophthora citricola in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and 100 ;Ug/ml. 65 40 25 30 ■ -O- 7i -V - 100 O 20 ■ 10 ■ TIME ( d a y s ) Figure 2c. Radial growth of Phytophthora drechaleri in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and lOO^g/ml. 40 - A — 10 25 30 • -V - 100 O 20- 10 ■ 0 2 4 3 TIME ( d ay s ) 5 6 7 3 Figure 2d. Radial growth of Phytophthora magaaP-SEma in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and 100 yUg/ml. 66 40 25 —t~ 50 - O - 75 30 • 100 “ 10 ■ o 2 3 4 5 6 7 a TIME ( d a y t ) Figure 2e. Radial growth of Pythium irregulare in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and 100 /t^g/ml. 40 25 30 ■ 50 - O - 75 -^ 7— 100 O 20- 10 ■ 0 2 3 4 5 6 7 3 TIME ( days ) Figure 2 f . Radial growth of Pythium sylvaticum in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and 100 /(g/ml. 67 40 30 RADIAL GROWTH ( mm) -o20 10 0 TIME ( d a y s ) Figure 2g. Radial growth of Pythium ultimum in culture amended with phosphorous acid at rates of 0, 10, 25, 50, 75, and 100 /WS/ml. Table 2. Effect of various concentrations of metalaxyl on growth of 1-yr-old Mataleb seedlings in Phytophthora and Pythium infested soil in the greenhouse Shoot dry weight (g)a Root dry weight (g)a Concentration ___________________________________________________________________________________________________________ of metalaxyl" Ph. Ph. Ph. L L Ph. Ph. Ph. P. P. (ng/ml) Control cactorum c itric o la megasperra irregulare ultimum Control cactoruis c itric o la irsaasperra irregulare u ltim a 0 9.7 abc 7.2 ab 6.8 b 13.2 a 7.7 ab 12.9 a 2.9 abc 1.3 c 2.1 a 3.4 ab 2.6 ab 3.8 a 9.8 ab 13.1 a 3.3 abc 3.1 ab 2.5 a 4.1 a 2.6 ab 3.8 ab 3.5 ab 3.7 a 3.3 a 2.0 a 3.6 ab 3.6 abc 2.1 a 3.0 a 4.1 a 2.2 abc 10 11.0 ab 10.5 a 10.9 {ib 11.9 a 25 13.9 a 11.8 a 13.7 ci 9.9 a 12.0 a 12.4 a 100 13.9 a 8.9 a 10.7 ib 11.5 a 11.7 a 9.7 a 4.9 a 12.6 a 8.6 ab 8.9 b 2.3 be 1.4 c 1.6 a 2.7 a 2.7 ab 1.6 c 9.7 a 6.4 a 8.7 ab 1.4 c 1.5 a 2.4 a 1.6 b 1.7 be 400 9.8 ab 8.8 a 9.3 ab 800 8.0 b 7.9 a 7.1 t 2.2 be 1.2 c a0ormant 1-yr-old Mahaleb seedlings were transplanted in so il infested with 10 cc of inoculum per 1CC0 cc of so il. The experiment was conducted in a greenhouse for 3mo. There were six replicates. ^Metalaxyl(250 ml per container) was a l l i e d as a so il drench cValues in coluire followed by the sama le tte r do not differ significantly according to Ouican'stultlple range te st (P=0.05). Figure 3. Fhytotoxic symptoms caused by metalaxyl at rates of (a) 0, (b) 100, and (c) 400 M g /ml on leaves of Mahaleb cherry. 70 there were no significant variations in shoot and root weights due to soil infesting fungi or metalaxyl, dry as there was a high degree of variability between experimental units. Analyses of variance calculated separately for each of soil infesting fungi indicated that metalaxyl (£=0.05) increased root dry weight of the significantly Mahaleb seedlings planted in soil infested with £h. cactorum. In experiment two, shoot and root dry weights of Mahaleb seedlings tended to be lower when grown in infested soil or treated no with significant fungi or fosetyl-Al (Table 3). There variations in dry weight due to soil the fungicides metalaxyl and were infesting fosetyl-Al as estimated by a factorial analysis. In experiment three, £, irregulare. significant 4, alone weights of combination all caused the significant between fungicide treatments. significant controlled in P h . megasnerma. and A factorial analysis also found (£=0.05) differences no or cactorum. reductions in shoot and root dry weights (Table Figure 4) were Eh- interaction effects. There Metalaxyl soil infesting fungi as shoot and root metalaxyl treated seedlings grown in dry infested « soil were treated not significantly reduced control. from the Fosetyl-Al reduced shoot and metalaxyl root dry weights of seedlings growing in uninfested soil. Dry weights of not fosetyl-Al treated seedlings grown in infested soil were significantly different from the treated The experiment was repeated with similar results. control. Table 3. Effect of fosetyl-Al and enatalaxyl on growth of 1-yr-old Mahaleb seedlings in Phvtoortnora and Pvthiun infested soil under lath Shoot dry weight (g)a Treatment and rate Root dry weight (g)a P. fL EL EL EL Ei Ei EL EL EL Control cactorum citricolci meoaspenra irreoulare svlvaticum Central cactorum c itric o la meoaspenra irreoulare svlvaticum Control 7.1b 5.2 4.5 5.4 6.7 6.4 3.0 1.8 2.5 2.0 2.5 2.4 Fosetyl-Alc 1.5 g a .i./L 5.2 2.5 3.9 4.1 4.7 4.2 2.8 0.5 1.4 1.7 2.2 2.8 Fosetyl-Alc 3.0 g a .i./L 6.4 2.7 4.5 4.1 4.8 4.8 3.0 1.0 1.7 2.1 2.3 1.8 Metalaxyl1* ICOjug/mi 6.6 5.1 2.9 4.1 5.6 5.5 2.6 2.0 1.0 1.6 3.0 2.6 a0orrant 1-yr-old Mahaleb seedlings wera transplanted in soil infested with 10 cc of inoculum per 1CGQ cc of so il. The experiment was conducted outside, shaded by lath, for 3mo. There were six replicates. ^Values in colusns followed by the sate le tte r do not d iffer significantly according to Duncan'smultiple range te s t (P=0.05). cFosetyl-Al was sprayed onto the foliage to run-off with a hand sprayer a t a ^Metalaxyl(250 ail per container) was applied as a so il drench. Table 4. Effect of fungicides metalaxyl and fosetyl-Al on growth of Mahaleb seedlings growing in soil infested with Phytophthora species and P v th iu e Irreoulare Dry weight (g) Fungicides Control Metalaxyl1' Shoot Root Control 2.7 a* 1.4 a X 2.6 a X 1.2 a X 2.0 a X 1.0 a X Ph. cactorum 1.0 b X 0.4 b X 1.7 a X 1.0 a X 1.3 a X 0.6 Ph. meaasnerma 1.5 b X 0.8 b XY 1.7 a X 1.2 a X 0.8 a X P. irreoulare 1.0 b Y 0.4 b Y 2.2 a X 1.2 a X 1.4 y 0.7 Ph. cactorum/ 1.1 b Y 0.5 b Y 2.8 a 1.4 a X 1.3 a y 0.7 a Y Ph. megasperma/ P. irregulare 1.1 b y 1.6 a X 1.3 a y 0.S a Y Treatment8 a Shoot Fosetyl-Al1' 0.3 b Y Root X 2.6 a x Shoot a Root a X 0.3 a Y a Y aSlx-wk-old Mahaleb seedlings were transplanted in soil infested with 20 cc of inoculum per 1000 cc of soil. The experiment was conducted in a greenhouse for 2 .mo. There were eight replicates. Plants were flooded for 48 hr every 2 wk. “Metalaxyl was applied at the rate of 70 M a a.i./ml in 50 ml distilled water, as a soil drench after the seedlings had been transplanted. cFosetyl-Al was sprayed onto the foliage to run-off with a hand sprayer at a rate of 4 g a.i./L. “Values in columns (a,b) acid rows (x,y and X.Y) followed by the same letter do not differ significantly according to Duncan'smultiple range test (P»0.0S). There was no interaction between the main effects according to a factorial analysis. 73 Figure 4. Roots of representative Mahaleb seedlings grown in a) uninfested soil, or soil infested with b) Phytophthora .cactorum, c) Eh. megasperma and d) Pythium irregulare. Roots in columns were x) untreated, or treated with y ) metalaxyl, and a) fosetyl-Al. 74 DISCUSSION The fungal cherries in metalaxyl tested species Michigan differed in their Eh. cyifrhnrnm The phosphorous the most confirms another of Of the sensitive high sensitivity of acid Pythium was rot sour sensitivity and phosphorous acid in culture. fungicides. three associated with root Eh. report to fungi to citricola (7). both to The species showed a similar low sensitivity phosphorous acid. £. metalaxyl, irregulare and £. svlvaticum were less while £. ultimum had a high sensitivity to to sensitive. The fungicide effective trials showed that metalaxyl was than fosetyl-Al in increasing shoot and root more dry weights of plants growing in soil infested with Phytophthora species and £. irregulare. However at high concentrations of metalaxyl phytotoxic symptoms ocurred with reduced Reductions of dry weights of plants growing in growth. uninfested soil when treated with fosetyl-Al was probably due to stress caused from by the chemical. the first uncontrolled experiments, two The inconclusive results experiments temperatures and previous were during probably the course contamination of the obtained due of to the 1-yr-old Mahaleb seedlings with Phytophthora and Pvthiurn species. Effective present at disease the site control requires that a fungicide of infection at a high is enough 75 concentration to inhibit or kill the invading organism. Diseases successfully controlled by metalaxyl include collar rot of apple (15) and foot rot of citrus (13,16,28,), where a canker is produced on the trunk and control is effected by concentration Metalaxyl of has applied as the fungicide controlled a soil drench at the root rot of infection woody site. plants with nursery or container when grown plants (1,5). Control of the lateral root necrosis associated with cherry decline requires that the fungicide is present at an inhibitory is strongly was concentration the roots. Metalaxyl adsorbed to soil organic matter and in loam found applied in to stay in the top 7.5 cm as a soil drench as no (27). soils Metalaxyl basipetal is translocation occurs (14,30), and it is questionable if on the heavy soils of symptomatic orchards metalaxyl would reach all the feeder roots. Fosetyl-Al is applied as a foliar spray as basipetal translocation occurs (14,24), however it is not known if the concentrations reaching the feeder roots are high enough to prevent infection. The species longterm with prospects these for control of chemicals are not good as pythiaceous there several reasons for doubting the long term effectiveness these chemicals. fungicides, together Resistance are of Species differ in their sensitivity to the and as more than one species are commonly found selection of the more tolerant species will occur. to metalaxyl has already occured, particularly 76 with foliar pathogens (4,10), has been demonstrated reports of the induced by Eh- and resistance to experimentally failure of metalaxyl to megasnerma and Eh- (3). control drechsleri fosetyl-Al There are diseases (20), and Pythium species (12,25). LITERATURE CITED 1. Benson, D. M. 1979. Efficacy and in vitro activity of two systemic acylalanines and ethazole for control of Phytophthora cinnamomi root rot of azealea. Phytopathology 69:174-178. 2. Bielenin, A., and Jones, A. L. 1988. Prevalence and pathogenicity of Phytophthora spp. from sour cherry trees in Michigan. Plant Dis. 72:473-476. 3. Bower, L. A., and Coffey, M. D. resistance to phosphorus acid in Phytopathology 74:811. 1984. Development of Phytophthora capsici. 4. Bruin, G. C. A. and Edgington, resistance in Peronosporales to Plant Path. 3:201-206. L. V. 1981. metalaxyl. 5. Bruck, R. metalaxyl fraseri. 6. Coffey, M. D . , and Bower, L. A. 1984. In vitro variability among isolates of six Phytophthora species in response to metalaxyl. Phytopathology 74:502-506. 7. Coffey, M. D . , and Bower, L. A. 1984. In vitro variability among isolates of eight Phytophthora species in reponse to Phosphorous acid. Phytopathology 74:738742. 8. Coffey, M. D . , phosphorus acid 9. Coffey, M. Variability Adaptive Can. J. I. and Kenerley, C. M. 1983. Effects of on Phytophthora cinnamomi root rot of Abies Plant Dis. 67:688-690. and Joseph, M. C. 1985. Effects of and fosetyl-Al on the life cycle of Phytophthora cinnamomi and Ehcitricola. Phytopathology 75:1042-1046. D . , Klure, L. J . , and Bower, L. A. 1984. in sensitivity to metalaxyl of isolates of PhztQPhthora cinnamomi and Phytophthora citricola. Phytopathology 74:417-422. 77 10. Coffey, M. D . , and Young, L.H. 1984. Responses to metalaxyl of sensitive and resistant isolates of Phytophthora infestans. Phytopathology 74:615-620. 11. Cohn, Y. and Coffey, M. D. 1986. Systemic fungicides and the control of oomycetes. Annu. Rev. Phytopathol. 24:311-338. 12. Cook, R. J . , Zhang, B. X., and Doerr, A. 1983. Failure of metalaxyl to control all of the Pythium population pathogenic on roots of Pacific Northwest wheat. Phytopathology 73:957. 13. Davis, R. M. 1982. Control of Phytophthora root and foot rot of citrus with systemic fungicides metalaxyl and Phosethyl Aluminium. Plant Dis. 66:218-220. 14. Edgington, L. V. 1981. Structural requirements of systemic fungicides. Ann. Rev. Phytopathol. 19:107124. 15. Ellis, M. A., Grove, G. C . , and Ferree, D. C. 1982. Effects of metalaxyl on Phytophthora cactorum and collar rot of apple. Phytopathology 72:1431-1434. 16. Farih, A., Menge, J. A., Tsao, P. H . , and Ohr, H. D. 1981. Metalaxyl and efosite aluminium for control of Phytophthora gummosis and root rot on citrus. Plant Dis. 65:654-657. 17. Farih, A., Tsao, P. H . , and Menge, J. A. 1981. In vitro effects of metalaxyl on growth, sporulation and germination of Phytophthora parasitica and £. citrophthora. Plant Dis. 65:651-654. 18. Fenn, M. E . , and Coffey, M. D. 1984. Studies on the in vitro and in vivo antifungal activity of fosetyl-Al and phosphorous acid. Phytopathology 74:606-611. 19. Fenn, M. E . , and Coffey, M. D. 1985. Further evidence for the direct mode of action of fosetyl-Al and phosphorus acid. Phytopathology 75:1064-1068. 20. Hamm, P. B . , Cooley, S. J . , and Hansen, E. M. 1984. Response of Phytophthora spp. to metalaxyl in forest tree nurseries in the Pacific Northwest. Plant Dis. 68:671-673. 21. Hunger, R. M . , and Hamm, P. B . , Horner, C. E. and Hansen, E. M. 1982. Tolerance of Phytophthora megasperma isolates to metalaxyl. Plant Dis. 66:645649. 78 22. Mircetich, S. M. , and Matheron, M. E. 1976. Phytophthora root and crown rot of cherry trees. Phytopathology. 66:549-558 23. Morton, H.V., Kern, C.L., and Taylor, T. D. 1982. Control of Pythium damping off and Phytophthora root rot of soybeans with metalaxyl. (Abstr.) Phytopathology 72:971. 24. Munnecke, D. E. 1982. Apparent movement of Aliette and Ridomil in Persea indica and its effect on root rot. Phytopathology 72:971. 25. Sanders, P. L. 1984. Failure of metalaxyl Pythium blight on turfgrass in Pennsylvania. 68:776-777. 26. Sanders, P. L . , Burpee, L. L., Cole, H . , Jr., and Duich, J. M. 1978. Control of Pythium blight of turf grass with CGA-48988. Plant Dis. Rep. 62:663-667. to control Plant Dis. 27. Sharom, M. S., and Edgington, L. V. 1982. The adsorbtion, mobility, and persistance of metalaxyl in soil and aqueous systems. Can. J. Plant Pathol. 4:334340. 28. Timmer, L. W . , and Castle, W. S. 1985. Effectiveness of metalaxyl and fosetyl-Al against Phytophthora parasitica on sweet orange. Plant Dis. 69:741-743. 29. Wilcox, W. F . , Jeffers, S. N . , Hayes, J. E. K . , and Aldwinkle, H. S. 1985. Phytophthora species causing root and crown rot of cherry trees in New York. (Abstr.) Phytopathology 75:1347. 30. Zaki, A. L . , Zentmeyer, G. A., and-LeBaron, H. M. 1981. Systemic translocation of C-labeled metalaxyl in tomato, avocado, and Persea indica. Phytopathology 71:509-514. APPENDICES APPENDIX A DESCRIPTIONS OF PYTHIUM SPECIES ASSOCIATED WITH CHERRY TREES 79 80 Colony morphology and growth rate. irregulare Buisman,£. Colonies of Pythium svlvaticum Campbell and £. ultimum Trow, were radiate on CMA and produced aerial mycelium. irregulare had a finer growth pattern with a maximum diameter of 6 /<3 , and 800 ml distilled water) ml sterilized in 500 Erlenmeyer flasks. The inoculum was washed with distilled water over cheesecloth in a Buchner funnel to remove unassimilated mixed at the soil/sand/peat rate of 20 cc per (1/1/1 by volume). nutrients, 1000 cc of then sterilized Seedlings were planted 88 in 4 L received plastic pots with six vermiculite/oat mixture but no daytime The control treatment, controls fungus. temperatures were 21 C with 14 hr of nighttime minimum was 18 C. were replicates. Maximum light. The The seedlings, apart from one were flooded for 48 hr every 2 wk. fertilized biweekly. All Dry weights of the roots shoots were recorded after 18 wk. on CMA-PARP selective medium. and Reisolations were made This experiment was repeated twice in the greenhouse and twice in the growth chamber with other isolates of these fungi. RESULTS Pathogenicity qaS-tarum, test. E. irregulare. £. drechsleri and shoots significantly reduced dry weights of of Mahaleb seedlings grown in a growth (Table 1, Figure 1). citricola caused the greatest reduction and £. soil drechsleri. dry £. sylvaticum weights. One and E. sylvaticum isolated from All flooded treatments had significantly growth as compared to the non-flooded control. by irregulare resulted in extensive root £. decay, Phytophthora and chamber did not significantly reduce dry weights of roots shoots. and roots Eh- cactorum. and £h. least reduction in shoot and root isolate of Eh- Eh- .ci£riqp.la, Eh- megasperma and one isolate of Eh- £h- the ultimum. similar to symptoms observed in and reduced Infections discoloration the orchards. infections caused cankers on the collar region main tap root. Pythium and Phytophthora species were 89 Table 1. Virulence of Pythium and Phytophthora species isolated from Michigan sour cherry orchards to Mahaleb seedlings Shootsx Fungus and isolate number Dry weight (g) Relative growth Y (*) Rootsx Dry weight (g) Relative growth Y (*> Pvthium irreaulare L215 2.0 cdz 41 1.0 de 42 Pvthium sylvaticum J310 3.2 be 65 1.9 be 79 Pvthium ultimum B302 2.0 cd 41 1.4 cde 58 Phytoohthora cactorum B1 0.7 d 14 0.6 e 25 Phytoohthora citricola H2 1.5 cd 31 0.6 e 25 Phytophthora drechsleri B1 JC16 3.3 be o c ^ 67 1.6 cd 66 X • *0 r? a sJ\J Phytoohthora meaasoerma B1 2.4 cd 49 Control noninoculated flooded noninoculated nonflooded 4.9 b 7.3 a M •V CO < ■ ! ■ » ■ + 100 149 ^UC 1.3 cde 2.4 ab 2.8 a 54 100 116 ^ix-wk-old Mahaleb seedlings were transplanted in soil infested with 20 cc of inoculum per 1000 cc of soil. The seedlings apart fran the non-flooded control were flooded for 48 hr every 2 wk. The experiment was conducted in a growth chamber for 3 mo. There were six replicates. ^Values are expressed as a percentage of flooded control. zValues followed by the same letter do not differ significantly (P=0.05) using Duncans Multiple Flange test. 90 Figure 1. Roots of representative Mahaleb seedlings grown in a growth chamber for 18 wk in a soil/sand/peat mixture infested with (A) Phytoohthora species and (B) Pythium species. Soil in the pots was (a) uninfested and non­ flooded, or flooded and infested with (b) Ph. cactorum. (c) £h- sitrisolfl, (d) Ph. drechsleri, (e) Ph- megasperma. (f) p. irregulare, (g) £. gylvaticum, and (h) P. ultimum. 91 routinely reisolated from seedlings growing in infested soil but not from control plants. These results were similar to those from two experiments conducted in a greenhouse and two experiments conducted in a growth chamber. DISCUSSION All the species tested caused reductions in dry of Mahaleb seedlings. considered and to Although Phytophthora species be the primary causal agents of cherry crown rot (1,5,8,9), with Pythium indicates weight the consistent species, that these over fungi a results series should of also are root obtained experiments, be considered pathogens of cherry. The large isolated number from of Phytoohthora and Pythium cherry orchards in Michigan may retard development of a suitable control stratagy using or host resistance. active against Phytophthora all the species which fungicides may be present. root and crown rot is associated with soils, and is Pythium species are also associated L. the A suitable method of control must be drained soils (M. species Smither, intensified unpublished). by flooding with poorly(10). poorly-drained Therefore the most effective means of control maybe to improve soil conditions by and selecting sites drainage systems. with well-drained soils, using 92 LITERATURE CITED 1. Bielenin, A., and Jones A. L. 1988. Prevalence and pathogenicity of Phytophthora spp. from sour cherry trees in Michigan. Plant Dis. 72:473-476. 2. Fliegel, P., Parker, K. G . , and Mai, W. F. 1963. The fungous flora of nonsuberized roots of poorly growing cherry trees. Phytopathology 53:1368-1369. 3. Jeffers, S. N. , and Martin, S. B. 1986. two media selective for Phytoohthora species. Plant Dis. 70:1038-1043. 4. Jeffers, S. N . , and Aldwinkle, H. S. 1987. Enhancing detection of Phytoohthora cactorum in naturally infested soil. Phytopathology 77:1475-1482. 5. Mircetich, S. M . , and Matheron, M. E. 1976. Phytoohthora root and crown rot of cherry trees. Phytopathology 66:549-558. 6. Ribeiro, 0. K. 1978. A source book of the genus Phytoohthora. J. Cramer, Lehre, Germany. 420 pp. 7. Waterhouse, G. M. 1970. The genus Phytoohthora de Bary. Diagnosis (or descriptions and figures) of the original papers. Commonw. Mycol. Inst., Mycol. Pap. 122. 59 pp. 8. Wilcox, W. F . , Jeffers, S. N . , Hayes, J. E. K . , and Aldwinkle, H. S. 1985. Phytoohthora species causing root and crown rot of cherry trees in New York. (Abstr.) Phytopathology 75:1347. 9. Wilcox, W. F . , and Mircetich, S. M. 1985. Pathogenicity and relative virulence of seven Phytoohthora species on Mahaleb and Mazzard cherry. Phytopathology 75:221-226. Comparison of and Pvthium 10. Wilcox, W. F., and Mircetich, S. M. 1985. Effects of flooding duration on the development of root and crown rot of cherry. Phytopathology 77:1132-1137. APPENDIX C THE EFFECTS OF INCREASED SOIL COMPACTION LEVELS WITH PYTHIUM IBBEOTLABE AND PHYTOPHTHORA MEGASPERMA ON GROWTH OF MAHALEB SEEDLINGS AND ETHYLENE LEVELS IN SOIL 93 94 ABSTRACT Sectioned pipes were used to study the effects of soil compaction levels of 1.0, 1.3, and 1.7 g/cc, and PhytOBhthaca megasoerma and Pvthium irregulare on growth Mahaleb seedlings. (£=0.05)in bulk were significant reductions dry weights of Mahaleb seedlings with density reductions There levels. in £. irregulare caused dry weight in one of two experiments. with seedlings. £. sections aerograph of with irregulare populations were higher increasing bulk densities. basal £. (propagules gram) ppg with no Mahaleb seedlings and 248.7 ppg Mahaleb ppm increased significant irregulare populations were an average of 104.3 per of Ethylene levels the pipe was measured 1400 gas chromatograph. using in a the Varian Ethylene levels over 1 were detected in treatments with Mahaleb seedlings at planted on clay soils in Michigan tend to 1.7 g/cc soil bulk density. INTRODUCTION Cherry exhibit trees poor growth and pathogenic (3,12). to Phytoohthora species to cherry have been isolated from trees and soil Pythium irregulare has been found to be pathogenic cherry, associated survival. and with unpublished). high populations of heavy clay soils Pvthium (M. species L. are Smither, 95 Soil compaction occurs frequently on clay soils. compacted zones impede root growth resulting in a restricted root system (5). reduced water movement The shallow, Reduced diffusion of gases and cause waterlogging and sites anaerobiosis which may predispose trees to infection Phytophthora species Pythium species germinating (17). which infect by motile zoospores which sporangia infect by zoospores are stimulated by or of and directly fluctuations in matric potentials which occur near the surface (6). Ethylene is a growth regulator produced by microorganisms including concentrations fungi (8,18). and may directly affect plants causing in extension senescence the host (7). to and Ethylene increase in soils under anaerobic conditions (9,15), root plants (16) and leaf chlorosis and It is not known if ethylene infection (1,2,13,14), although reductions premature predisposes increased ethylene concentrations often occur after infection (1,4). The objectives were to study the effects of soil compaction levels and the pathogens, Phytoohthora megasoerma and Pythium irregulare. to investigate on growth of Mahaleb seedlings, and variations in soil ethylene concentrations caused by these factors. MATERIALS AND METHODS Pasteurized sandy loam orchard soil was sieved through 10 and 30 mesh sieves to retain soil particles between 0.05 and 96 2 mm in 2.5, diameter. 5.0, and 7.5 PVC pipe of 7.5 cm diameter was cut into cm sections. A 5 mm hole drilled 4.0 cm from the base of the 7.5 cm section was closed with a rubber septum. The 7.5 cm sections were covered at the base piece of Whatman No 1 filter paper under two with a layers of cheesecloth held in place with a rubber band. The sections were filled trays were half with soil and placed in aluminum filled with water. More soil was which added maintain the level with the top of the sections as the subsided upon wetting. g/cc were obtained soil the by placing 135.5, densities soil Soil densities of 1.0, 1.3 and 1.7 176.2, and 230.4 g of at 18% moisture in the 2.5 cm section and higher to with a flat weight. compressing The 2.5 cm and the 5.0 cm section was taped over the saturated soil, section was taped in place over the compressed section and filled to the surface with soil. The completed cores were left surface until water had risen to the through the COmpciG'uOcL x a.yS2T . Roots from of four-wk-old Mahaleb seedlings were washed free soil and cut back to 1.5 cm before planting in the top section. Inoculum of Pythium and Phytophthora species was prepared by growing each isolate at 21 C for 5 wk on 200 cc vermiculite moistened with 100 ml V-8 juice solution (200 ml V-8 juice, 2g CaCOg, and 800 ml distilled sterilized in 500 ml Erlenmeyer flasks (12). was washed with distilled water water) The inoculum over cheesecloth in a 97 Buchner funnel to remove unassimilated nutrients. (2cc) was Inoculum placed in a 1 cm furrow in the soil around the foil pie periphery of the core. The pans cores and light. were placed in individual aluminum kept The in a growth chamber at cores were watered by 65 C with 14 hr of applying of 50 ml distilled water to the top of the cores as required. Ethylene samples (1 cc) were taken each week from the basal portion of the cores through the rubber septum. samples The were tested for ethylene concentration (ppm) with a Varian aerograph 1400 gas chromatograph. After 8 wk the experiment was terminated. were made of root and shoot dry weights. Pythium propagules The population of in soil was determined with soil dilution plate assay (11). with a 5 mm diameter cork borer. taken Measurements Samples a were prepared in collected Three sub samples from the top and bottom sections of each each soil sample, surface d i l u t i o n s of 1:10, 1:50, were core. From and 1:100 were molten sterile 0.2% water agar in test tubes. Diluted samples (1 ml) were distributed over the surface fresh (0.4 corn meal agar (Difco) amended with 10 mg ml of a 2.5% suspension), rifampicin, Chemical sterile each and Co., Saint glass rod. dilution. plastic 50 mg of pimaricin 250 mg ampicillin, 10 mg pentachloronitrobenzene, (Sigma Louis, MO) (CMA-PARP) (10) with a There were three replicate plates for The plates were bags in the dark at 21 C. incubated inverted After 42 hr, in the soil 98 was removed by washing each plate under running tap A colony count was made and the number of water. propagules per gram of dried soil was determined. An with initial 3 Mahaleb experiment was set up as a levels of compacted soil; seedlings; and no no fungus or 3x2x2 plant factorial or Pythium irregulare. There were five replications for each treatment. experiment was Phytophthora conducted as a 3x2x3 megasperma as the additional 3-wk-old A second factorial with treatment. The procedures followed were those previously described. RESULTS Increasing (£=0.05)in initial bulk root density caused dry experiment significant significant weight of Mahaleb (Table 1). £. reductions in dry weight. were not significant. £. reductions seedlings in irregulare the caused Interaction effects irregulare populations in the top sections at 1.0, 1.3, and 1.7 g/cc bulk density were 93, 250 and 217 ppg respectively. the basal detected The population was 3 ppg in section at 1.0 g/cc but £. irregulare in the basal sections from higher bulk Populations was not densities. were not determined in treatments with Mahaleb seedlings. Increasing bulk density caused significant reductions dry weight of Mahaleb seedlings in the second in experiment (Table 2). In this experiment neither £h. megasperma nor P. irregulare caused reductions significantly greater than 99 Table 1. Effects of soil bulk density and Pvthium irregulare on growth of Mahaleb seedlings Treatment Root Dry Dry weight weight reduction (*) (g) Dry Dry weight weight reduction (*) (g) 1.0 0.31z 0.51 1.3 0.24 23 0.38 25 1.7 0.22 29 0.20 61 Mean 0.26 1.0 0.22 29 0.39 24 1.3 0.23 25 0.28 45 1.7 0.18 42 0.19 63 Mean 0.21 0.29 1.0 0.26 0.45 1.3 0.24 0.36 1.7 0.20 0.20 LSD (P=0.05) 0.06 0.02 (g/cc) Control P .irregulare^ Mean Shoot* Bulk density 0.36 xFour-wk-old Mahaleb seedlings were transplanted into pasteurized soil in 7.5 cm diameter PVC pipe. The experiment was conducted in a grcwth chamber for 8 weeks at 21 C. ^Inoculum of P. irregulare was applied in a 1 cm furrow around the periphery of the core. ZA factorial analysis showed significant differences (P=0.05) between the main effects and no significant interaction. 100 Table 2. Effects of soil bulk density, Pythium irregulare and Phytophthora megasperma on growth of Mahaleb seedlings Treatment Shoot* Bulk density (g/cc) Root Dry Dry weight weight reduction (g) (*) Dry weight Dry weight reduction {*) (g) 1.0 1.52 1.3 1.2 20 0.7 30 1.7 1.3 13 0.3 70 Mean 1.3 1.0 1.5 0 0.8 20 1.3 1.2 20 0.6 40 1.7 1.2 20 0.3 70 Mean 1.3 1.0 1.2 20 0.7 30 Ph. megasperma^ 1.3 0.8 47 0.7 30 1.7 1.1 27 0.4 60 Control P .irregulare^ i * 4 W W M * Mean 1.0 0.7 0.6 r\ U • 1.0 1.4 0.8 1.3 1.1 0.7 1.7 1.0 0.3 LSD (P=0.05) 0.3 • - 0.2 xFour*-wk-old Mahaleb seedlings were transplanted into pasteurized soil in 7.5 an diameter PVC pipe. The experiment was conducted in a growth chamber for 8 weeks at 21 C. YInoculum of P. irregulare and Ph.meqasperma were applied in a 1 cm furrow around the periphery of the core. ZA factorial analysis showed significant differences (P=0.05) with bulk density for both shoot and root dry weights. Fungus treatments did not cause significant differences, nor were there interaction effects. 101 those without effects. 1.0, 87, the pathogens. There were no interaction E- irregulare populations in the top sections 1.3, at and 1.7 g/cc with no Mahaleb seedlings were 100, and 126 ppg; and with Mahaleb seedlings were 183, and 367 ppg. E- basal of the non- seedling treatment at 1.0 section 196, irregulare at 26 ppg was detected in the g/cc. £. irregulare was not detected in the other treatments. Ethylene was concentrations treatments not were detected at 1.0 <0.01 in the at 1.3 g/cc bulk density; density were <0.01 ppm, 2.02 ppm, ppm g/cc bulk density; Mahaleb seedling and at 1.7 g/cc bulk control; 0.04 ppm .Pvthium control; Mahaleb control; 1.13 ppm, Mahaleb and Pythium; and 1.1 ppm Mahaleb and Phytophthora. DISCUSSION Increased soil compaction levels were shown to reduce dry weights of Mahaleb seedlings. There was no interaction effect between soil compaction and reduction in dry caused by increased £. with significantly but neither significant experiment. megasperma irregulare. soil Populations of compaction levels. £. irregulare £. irregulare reduced dry weights in the first £. irEfigyilars reductions in nor dry Eft. weight The reason for this is not clear, requires periodic flooding (19), and none of the seedlings grew well. experiment, megasperma in for weight the caused second although P h . pathogenicity 102 These findings can be correlated with instances of growth in Several factors which occurs orchards with high may be involved soil compaction in the poor under such conditions. Root levels. root growth penetrance reduced through zones of compacted soil (5). may predispose plants to infection (17,19). poor is Anaerobiosis Root growth is decreased upon exposure to increased ethylene concentrations (7,16). ethylene However there is no clear evidence that increased concentrations predispose plants to infection (1,2,13,14). LITERATURE CITED 1. 2. Abbatista, G. I., and Matta, A. 1975. Production of and some effects of ethylene in relation to Fusarium wilt of tomato. Physiol. Plant Pathol. 5:27-35. Archer, S. A., and Hislop, E. C. 1975. Ethylene in host-pathogen relationships. Ann. Appl. Bio. 81:95126. 3. Bielenin, A., and Jones, A. L. 1988. Prevalence and pathogenicity of rhytopht hora spp. from sour cherry trees in Michigan. Plant Disease 72:473-476. 4. Cohn, R . , Riov, J . , Lisker, N . , and Katen, J. 1986. Involvement of ethylene in herbicide-induced resistance to Fuaarium oxysporum f . sp. melonis. Phytopathology 76:1281-1285. 5. Drew, M. C . , and Lynch, J. M. 1980. Soil anaerobiosis, microorganisms and root function. Ann. Rev. Phytopathol. 18:37-66 6. Duniway, J. M. 1975. Limiting influence of low water potential on the formation of sporangia by Phytophthora drechsleri in soil. Phytopathology 65:1089-1093, 7. El-Beltagy, A. S., and Hall, M. A. 1974. Effect of water stress upon endogenous ethylene levels in Vlcia fa b a . New Pytol. 73:47-60. 103 8. H a g , L . , and Curtis, R.W. 1968. Production of ethylene by fungi. Science 159:1357-1358. 9. Jackson, M. B . , Gales, K . , and Campbell, D. J. 1978. Effect of waterlogged soil conditions on the production of ethylene and on water relationships in tomato plants, J. Exp. Bot. 29:183-189. 10. Jeffers, S. N . , and Martin, S. B. 1986. Comparison of two media selective for Phytophthora and Pythium species. Plant Disease 70:1038-1043. 11. Mircetich, S. M . , and Kraft, J. M. 1973. Efficiency of various selective media in determining Pythium popula­ tions in soil. Mycopathol. Mycol. Appl. 50:151-161. 12. Mircetich, S. M . , and Matheron, M. E. 1976. Phytophthora root and crown rot of cherry trees. Phytopathology 66:549-558. 13. Pegg, G. F. 1976. The response of ethylene-treated tomato plants to infection by Verticillium albo-atrum. Physiol. Plant Pathol. 9:215-226 14. Pegg, G. F . , and Cronshaw, D. K. 1976. Ethylene production in tomato plants infected with Verticillium albo-atrum. Physiol. Plant Pathol. 8:279-295. 15. Smith, A. M . , and Cook, R. J. 1974. Implications of ethylene production for biological balance of soil. Nature 252:703-705. 16. Smith, K. A., and Robertson, P. D. 1971. Effect of ethylene on root extension in cereals. Nature 234:148- 17. Stolzy, L. H . , Zentmyer, G. A., Klotz, L. J . , and Labanauskas, C. K. 1965. Water and aeration as factors in root decay of Citrus sinensis. Phytopathology 55:270-275. 18. Walther, H. F . , Hoffman, H. F . , and Elstner, E. F. 1981. Ethylene formation by germinating Drechslera gramineainfected barley (Hordeum sativum) grains: A simple test for fungicides. Planta 151:251-255. 19. Wilcox, W. F . , and Mircetich, S. M. 1985. Effects of flooding duration on the development of Phytophthora root and crown rots of cherry. Phytopathology 75:14511455. 20. Yang, S. F . , and Hoffman, N. E. 1984. Ethylene biosynthesis and its regulation in higher plants. Annu. Rev. Plant Physiol. 35:155-189. APPENDIX D VARIATION IN SUSCEPTIBILITY OF CHERRY ROOTSTOCK CULTIVARS TO INFECTION BY PHYTOPHTHORA SPECIES AND PYTHIUM IRREGULARE 104 105 ABSTRACT A dormant excised twig assay was used to determine relative resistance infection by Phytophthora species and Twigs The of cherry rootstock cultivars Pvthium resulting necrosis above the agar surface was 163091, to irregulare. were placed base down in previously inoculated after 10 days. the agar. recorded During 1983 dormant shoots of Mahaleb clones 193688, 193693, 194096, Mazzard, MxM #2, MxM #14, MxM #39, MxM #60, MxM #97, Meteor, and Vladimir were tested with Eh- ga.Ct.or.um, irregulare. MxM cactorum, drechsleri. Eh- megasperma and £. During 1984 dormant shoots of Mahaleb seedlings and clone 163091, #60, Eh. #97, Mazzard, Vladimir, MxM #2, and MxM #14, MxM #39, MxM Colt were tested with Ph. £h- citricola, £h. drechsleri. Eh. megasperma and £. irregulare. The assays showed that rootstocks differed in relative resistance to infection by Phytophthora species and £. irregulare. significantly -C.actgr.um, but Dry weights of Mahaleb and MxM #60 reduced when grown in soil infested with were Ph. Eh. drechsleri, Eh. megasperma and £. irregulare. dry weights of MxM #2, significantly correlations reduced. MxM #39, There were and MxM #46 were significant (E=0.05) of 0.463 and 0.521 between the rootsock and twigs assays of 1983 and 1984. not trial 106 INTRODUCTION Sour cherry production is of major economic importance to Michigan. root In and orchards planted on heavy soils losses collar rot are often severe. from Phvtophthora species cause root and collar rot of cherry in Michigan (4), California (10,17), and New York (16). Pvthlum irregulare Buisman has been associated with poorly growing cherry trees in Michigan (M. L. Smither, unpublished). Mahaleb (Prunus frequently L.). is used mahaleb L.) is the with Montmorency sour cherry Mahaleb is preferred to Mazzard (£. more resistant to crown gall and root (7,12). rootstock However (£. most cerasus avium L . ) as it lesion nematodes Mahaleb grows poorly on heavy soils (7), and is more susceptible than Mazzard to diseases induced Phytophthora both species (10,11,17). seedling rootstocks and by Mahaleb and Mazzard are therefore differences in resistance to infection can be expected between individuals. Several other resistance rootstocks have been developed and to diseases induced by Phvtophthora and their Pvthium needs to be evaluated. Excised examine twig assays have been used as a rapid method variations in pathogenicity and virulence of fungal isolates (2,9,13), to infection seasonal to to investigate variations in associated differences (3). with host genotype In one assay bark resistance (1,14), discs and were 107 removed from the mid-way point of inoculum was applied, measured after placed excised fungal and the resulting necrotic area several days (6). A second assay twigs with the bark stripped from the base inoculated with a fungal pathogen. length twigs, was method in agar The resulting necrosis above the agar was measured after several days (8). The second assay method was used in this work. The objectives were to examine the relative resistance of cherry rootstock irregulare cultivars to Phytophthora species and infection with an excised twig assay P. and rootstock trial. MATERIALS AND METHODS Excised rootstock dormant twig assay Dormant shoots of cherry cultivars were tested for relative resistance to infection by Pythophthora species and p. irregulare using an excised twig assay (8). Fungi were grown on 30 ml corn meal agar (CMA) plus agar ( 17 g CMA, 5 g Bacto agar, and 1 L mg distilled Chemical water Co., beakers. beakers amended Saint Control were Greenwich, Louis, beakers covered with 6-10 MO]) in pimaricin sterilized contained Parafilm no [Sigma 250 fungus. (American ml The Can Co., Ct 06830) over aluminum foil and maintained at 21 C in darkness for 7 days. from with 10 mm in Dormant cherry rootstock diameter were cut into disinfested in 0.6% NaOCl for 5 min, 7 cm shoots segments, rinsed three times distilled water and dried on paper towels. in Five mm of the 108 base of each twig was removed with disinfested pruning shears and a cut 1 cm in length by 2 mm in depth was made in each side at the base to expose the cambium. Single twigs from each cultivar were placed base down into the medium the edge of the fungal colony, so that the cambium at was exposed to the fungus. There were fifteen replicate beakers. The beakers were covered again and maintained as before. After 10 days the twigs were stripped of bark and the length of necrosis in the periderm above the agar level was recorded. Rootstock (Route # material was obtained from 2, Hartford, Hilltop Nurseries MI) in February of 1983 and During 1983 dormant shoots of Mahaleb clones 163091, 193693, MxM 193688, 194096, Mazzard, MxM #2, MxM #14, MxM #39, MxM #60, #97, Meteor, resistance £. to Eh- Schroet., and 1984. and Vladimir were assayed infection by £h. drechsleri Tucker, irregulare. cactorum Eh- for (Leb relative & Cohn) megasnerma Drechsler During 1984 dormant shoots of Mahaleb seedlings and clone 163091, Mazzard, MxM #2, MxM #14, MxM #39, MxM #60, MxM #97, Vladimir, and Colt (provided by R. L. Perry, Horticulture) were assayed for relative resistance to infection £h. by saS-tOEUm, d rach sleri, Eh- megasperma Rootstock trial with soil. and Eh- citricola Sawada, Eh. and £. irregulare. The experiments were conducted under lath rootstock cultivars planted in uninfested and infested The basic proceedure was as described by Matheron (10). Inoculum of Phytophthora and Mircetich Pvthium 109 species wk on was prepared by growing each isolate at 21 C for 200 cc vermiculite moistened with 100 ml solution (200 ml 7-8 juice, water) in washed with of 500 ml Erlenmeyer 10 flasks. The pots with vermiculite inoculum distilled water over cheesecloth in a cc per 1000 cc (1/1/1 by volume). six of was Buchner then mixed at the sterilized soil/sand/peat Rootstocks were planted in 4 L plastic replicates. mixture juice 2 g CaCOg, and 800 ml distilled funnel to remove unassimilated nutrients, rate V-8 5 but The controls no fungus. The received the rootstocks were flooded for 48 hr every 2 wk and fertilized biweekly. Dry weights wk. In an of the roots and shoots were recorded after 15 initial experiment dormant 1-yr-old seedlings Mahaleb and Mazzard and dormant rooted cuttings of MxM #14, MxM of #2, MxM #39, MxM #60, MxM #97, and Meteor were planted in uninfested soil and soil infested with Eh- sitc is-sla, Eh- megaspsrma. E- Irre g u la rs, cactorum. P h . and £. sylvaticum. A second experiment used actively growing 1-yr-old seedlings of Mahaleb and Mazzard, #39, MxM uninfested #39, MxM #46, soil and soil drftc h sle ri, Eh- and rooted cuttings of MxM #2, MxM and MxM #60 which were planted in infested with megasperma. and E- Eh- cactorum. P h . irregulare. RESULTS Excised twig assay. Necrosis developed on twigs of all rootstock cultivars inoculated with Phvtophthora species and 110 £. irregulare. rootstock No necrosis cultivars. The developed length of on uninoculated necrosis produced differed significantly between cultivars (Table 1-2). results varied between the two years, but a The correlation coefficient of 0.396 gave a significant (P=0.05) correlation between the greater during necrotic two assays. Necrosis length 1984 than 1983. area was produced cas.t, Eh’ drechsleri. and 194096 by p. irregulare. area was produced MxM #60 During 1983 on Eh- Mahaleb generally the longest 193688 by Ph. megasperma. and on Mahaleb A significantly longer necrotic by the than on the other was Phvtophthora species on MxM #2 and MxM cultivars. The shortest necrotic area was produced on Vladimir by Ph. drechsleri and Ph. megasperma. During 1984, the longest necrotic area was produced on MxM #2 by Ph. cactorum and Ph. citricola. and on Mahaleb 163091 by Phirregulare. Colt by Ph. The drechsleri. shortest cactorum and Ph. drechsleri and P. Ph. megasperma. and p. necrotic area was produced citricola. irregulare. and on on on Mazzard by P h . Vladimir by Ph. megasperma. Rootstock trial Results from the initial experiment were not significant due to poor establishment of the rootstocks. In the second experiment shoot dry weights of Mahaleb reduced in soil infested with Ph. cas.torum. Ph- megasperma. and p. irregulare. and root soil infested with 3). Ph. Shoot Ph. cactorum. and Ph. were drechsleri. dry weights in megasperma (Table dry weights of Mazzard were not significantly Ill Table 1. Relative susceptibility of dormant excised shoot tissue of cherry rootstock cultivars to infection by Phvtophthora species and Pvthium irregulare during 1983 Necrosis length on shoot (mm)^ Cultivar Ph. cactorum Ph. drechsleri Ph. megasperma P. irregulare Mahaleb 163091 11.2 cz 11.1 e 12.5 be 193688 23.8 a 24.6 a 19.2 a 11.6 b 193693 11.0 c 7.9 e 7.3 d 10.6 b 194096 16.0 b 18.1 be 17.2 ab 18.8 a Mazzard 18.5 b 9.6 e 7.1 d 4.6 c MxM #2 16.5 b 18.9 b 15.6 ab 4.1 c MxM #14 1.1 d 10.3 e 4.5 de 4.0 c MxM #39 9.2 c 8.1 e 6.2 d 3.6 c MxM #60 19.6 ab 13.8 cd 16.9 ab 3.5 c MxM #97 6.4 c Meteor 1.3 d 6.8 e 3.2 e . 2.9 c Vladimir 7.5 c 1.6 f 0.1 e 7.8 be 8.2 be 7.9 cd ^Mean length of necrosis above agar level from 15 replicate shoot pieces. V a l ue s followed by the same letter are not significantly different using Duncan's multiple range test (P=0.05).. Table 2. Relative susceptibility of dormant excised shoot tissue of cherry rootstock cultivars to infection by Phvtophthora species and Pythium irregulare during 1904 Necrosis length on shoot (tnn)^ Cultivar Mahaleb Ph. cactorum Ph. citricola Ph. drechsleri Ph. meqaspeima Pv. irrequlane 26.9 afc? 25.3 ab 16.5 a 16.4 a 12.1 be 163091 22.3 be 25.9 ab 15.5 a 16.1 a 17.7 a Mazzard 17.3 cd 18.3 c 3.5 d 9.5 b 5.2 d MxM #2 29.0 a 30.1 a 12.1 abc 11.8 ab 17.3 ab MxM #14 14.8 d 24.9 ab 7.7 cd 9.5 b 11.9 be MxM #39 17.3 cd 21.9 be 9.2 be 11.7 ab MxM #60 24.4 ab 28.7 a 13.5 ab 11.7 ab 11.3 c \ 14.3 abc MxM #97 17.7 cd 22.1 be 11.3 abc 12.9 ab 13.3 abc Vladimir 17.7 cd 27.9 a 9.0 d 9.7 cd 9.3 e 17.0 c 11.4 ab 13.4 abc Colt 11.8 abc yMean length of necrosis above agar level from 15 replicate shoot pieces Values followed by the same letter are not significantly different Duncan's multiple range test (P=0.05). Table 3. Growth of cherry rootstock cultivars planted In soil Infested with Phvtophthora species and Pvthium Irregulare under lath Shoot dry weight (g)Y Root dry weight (g) Cultivar Ph. Ph. Ph. Ph. Ph. P. Ph. P. Control cactorum drechsleri meoasDerma irregulare Control cactorum drechsleri megasperma irregulare Mahaleb 17.2 a2 9.8 b 14.0 be 14.0 be 12.3 be 8.9 a 4.0 b 7.4 a 5.0 b 8.0 a Mazzard 13.8 b 13.5 b 17.0 a 13.1 b 14.3 ab 9.9 a 3.7 b 11.7 a 4.5 b 12.3 a MxM #2 5.1 a 4.6 a 4.6 a 6.4 a 4.7 a 3.8 a 3.0 a 3.9 a 4.7 a 3.6 a MxM #39 4.3 a 3.3 a 4.9 a 5.3 a 4.7 a 4.5 a 2.7 a 4.5 a 4.3 a 3.4 a MxM #46 7.7 a 4.8 a 6.7 a 5.3 a 7.2 a 6.3 a 4.3 a 4.7 a 5.1 a 6.2 a MxM #60 6.4 a 3.7 b 3.1 b 3.6 b 7.9 a 5.6 a 3.0 b 2.6 b 3.5 ab 5.5 a ^Actively growing rootstocks were transplanted in soil Infested with 10 cc of inoculum per 1000 cc of soil. The experiment was conducted under lath. There were six replicates. zValues across raws followed by the sane letter are not significantly different using Duncan's multiple range test