Mycal. Res. 100 (8): 897-922 (I996)
897
Printed in Great Britain
Presidential address
The xylariaceous way of life
A. J. S. WHALLEY
School of Biomolecular Sciences, Liverpool John Moores University, Byrom Street, Liverpool L3 3AF, UK
This paper outlines current positions on systematic arrangements of the Xylariaceae, discusses' the value of the different characters
used in attaining these arrangements, and reviews the activities of members of the family in nature. The taxonomic significance and
potential ecological role of the many secondary metabolites produced by xylariaceous taxa is evaluated. The importance of the
Xylariaceae in wood decomposition and as agents of disease is discussed. Aspects of their distribution in relation to host, habitat and
climate are presented.
The study of fungi provides as great, and as interesting, a
challenge as any to be found in the living world. At a time
when biodiversity is in vogue the fungi in their broadest sense
excel. According to popular consensus there are more than l' 5
million species (Hawksworth, 1991; 1993) and they exhibit an
impressive range of diversity of form, biochemical and
physiological activities, and adaptation to habitat. They rank
as one of the world's most important living resources. In a
mycological lifetime it is unrealistic to expect an individual to
understand in any depth this diversity and I have unashamedly
concentrated my efforts on a single ascomycete family; the
Xylariaceae. This is not an admission of lack of interest in
other groups but more a tribute to what a single ascomycete
family can offer.
The Xylariaceae is a large and relatively well known family
which has representatives in most countries of the world
(Dennis, 1956, 1957, 1961, 1963, 1970; Miller, 1961; Martin,
1967a, b; 1968a, b; 1969a-c, 1970; Rogers, 1979a; Rogers,
Callan & Samuels, 1987; Rogers et aI., 1988; Granmo et al.,
1989; San Martin & Rogers, 1989; Van der Gucht, 1992; Van
der Gucht & Van der Veken, 1992; Gonzalez & Rogers, 1993;
Whalley, 1993, 1996; Whalley et al., 1995). Eriksson &
Hawksworth (1993) recognised 35 genera plus three others
which they considered might belong there. Most members of
the family are wood inhabitants but there are also representatives found in litter, soiL dung and associated with
insects (Rogers, 1979a; Whalley, 1985). In spite of their
widespread distribution and occurrence in a wide range of
environmental situations Rogers, in his Presidential Address to
the Mycological Society of America, drew special attention to
our lack of knowledge about the activities of the Xylariaceae
in nature (Rogers, 1979a). We have made considerable
progress since then - hence the title of my address.
SYSTEMA TIC BASE
Genera of the Xylariaceae
The acceptable number of known genera within the
Xylariaceae, in the absence of a clear circumscription of the
family, is still open to debate. In their current outline of the
ascomycetes Eriksson & Hawksworth (1993) recognized 35
genera and indicated a further 3 which might prove to belong
there. In an index to the genera of the family Lress0e included
37 genera but admitted that a few of these are uncertain
A.J.S. Whalley
President, British Mycological Society, 1994
The xylariaceous way of life
898
Table 1. Genera of Xylariaceae
Eriksson & Hawksworth (1993)
Lil'ssoe (I994)
Whalley (this review)
Anthostomelia Sacco
Ascotricha Berk.
?Ascotrichelia Validos. & Guarro
?Astrocystis Berk. & Broome
Biscogniauxia Kuntze
Calceomyces Udagawa & S. Ueda
Camillea Fr.
Anfhosfomelia
Anfhosfomelia
?Ascofricha
?Ascotrichelia
Asfrocysfis
Biscogniauxia
Calceomyces
Camillea
?Chaenocarpus
?Coliodiscula
Creosphaeria
Daldinia
Engleromyces
Enfonaema
?EuepixyIon
Daldinia Ces. & De Not.
Engleromyces Henn.
Entonaema A. Moller
Fassia Dennis
Helicogermslita Lodha & D. Hawksw.
Hypocopra (Fr.) I. Kickx f.
Hypoxylon Bull.
Induratia Samuels, E. Miill. & Petrini
Kretschmaria Fr.
Leprieuria Lil'ssoe, I. D. Rogers & Whalley
Lopadostoma (Nitschke) Traverso
?Paucithecium Lloyd
Penzigia SacCo
Phaeosporis Clem.
Phylacia Lev.
Podosordaria Ellis & Holw.
Poroconiochaela Udagawa & Furuya
Poronia Willd.
Pulveria Malloch & Rogerson
Rhopalostroma D. Hawksw.
Rosellinia De Not.
Sarcoxylon Cooke
Sfilbohypoxylon Henn.
Sfromafoneurospora S. C. long & E. E. Davis
Thamnomyces Ehrenb.
Theissenia Maubl.
Thuemenelia Penz. & SacCo
Usfulina Tul. & C. Tul.
Versiomyces Whalley & Watling
Wawelia Namysl.
Xylaria Hill ex Schrank
Asfrocystis
Biscogniauxia
Calceomyces
Camillea
Chaenocarpus Fr.
Collodiscula I. Hino & Katum.
Creosphaeria Theiss.
Engleromyces
Enfonaema
Euepixylon Fiiisting
Helicogermslifa
Holttumia Lloyd
Hypocopra
Hypoxylon
Induratia
Krelschmaria
Leprieuria
Lopadosfoma
?Myconeesia Kirschst.
Nemania Gray
emend. Pouzar
Obolarina Pouzar
Phaeosporis
Phylacia
Podosordaria
Poronia
(as Pyrenomyxa Morgan)
Rhopalosfroma
Rosellinia
Sarcoxylon
?Seynesia Sacco
Helicogermslifa
?Holttumia
Hypocopra
Hypoxylon
Indurafia
Krelschmaria
Leprieuria
Lopadosfoma
Nemania
Obolarina
?Penzigia
Phaeosporis
Phylacia
Podosordaria
Poronia
Pulveria
Rhopalosfroma
Rosellinia
Sarcoxylon
Sfromafoneurospora
Thamnomyces
Theissenia
Thuemenelia
?Sfilbohypoxylon
Sfromafoneurospora
Thamnomyces
Theissenia
Thuemenella
?Wawelia
Xylaria
Versiomyces
Wawelia
Xylaria
(Lcess0e, 1994). However, comparison of these two recent
listings of xylariaceous genera reveals a number of important
differences (Table 1). Eriksson & Hawksworth surprisingly did
not recognise Nemania and Obolarina although these are
widely accepted (e.g. Candoussau & Rogers, 1990; Whalley &
Edwards, 1995) whilst Lcess0e (1994) assigned Daldinia and
Versiomyces to Hypoxylon. There appear to be no good reasons
to include Daldinia in Hypoxylon although they are clearly
closely related. Indeed Daldinia is structurally and distinctively
different when examined by light and scanning electron
microscopy (Gaskell, 1995) and in many aspects is more
closely related to Entonaema than to Hypoxylon sensu stricto
(Rogers, 1982; Whalley & Edwards, 1987, 1995). Versiomyces
also appears sufficiently distinctive to warrant separate generic
status (Rogers, pers. comm.). Taking these differing views into
account and allowing for the erection of new genera in the
future an upper figure of 40 or more genera seems realistic
(Table 1).
Systematic foundation
A sound systematic foundation is an essential prerequisite for
specialist investigations into any aspect of the life of members
of the family. The Xylariaceae has been the focus of
considerable attention concerning taxonomic relationships
and as a result a genuine understanding of the associations
between species and genera is evolving (Rogers, 1993, 1994;
Whalley & Edwards, 1995). It is well known that many
A.
J. S.
Whalley
899
Figs 1-6. Pigmentation, diversity and pathology in Xylariaceae. Fig. 1. Hypoxylon haemaloslroma Mont. an example of a highly
pigmented species. Fig. 2. Biscogniauxia nolhofagi. Fig. 3. Camillea leprieurii. Fig. 4. Chromatogram of secondary metabolites produced
by selected Xylariaceae. Lane 1 = Hypoxylon fragiforme, 2 = H. howieanum, 3 = H. mammalum, 4 = H. truncatum, 5 = H. atropuncialum,
6 = H. multiforme, 7 = Biscognianlia marginata. Fig. 5. Beech trees in Sicily infected by Biscogniauxia nummularia. Fig. 6. Apples trees
infected by Rosellinia necatrix.
The xylariaceous way of life
900
Figs 7-12. Fig. 7. Camillea selangorensis, stroma. (Bar = 5 mm). Fig. 8. Hypoxylon hians, stromata. (Bar = 1 em ). Fig. 9. Rhopalostroma
kanyae Whalley & Thienhirun, stroma. (Bar = 1 mm). Fig. 10. Rosellinia bunodes, stroma. (Bar = 1 mm). Fig. 11. Hypoxylon megannulatum
Talig. & Whalley, stromata. (Bar = 1 mm). Fig. 12. Hypoxylon stygium Lev., stromata. (Bar = 2 mm).
representatives of the family exhibit an exceptional range of
morphological diversity (e.g. Dennis, 1956, 1957; Martin,
1967 a; Rogers, 1979a, 1993; Petrini & Muller, 1986; Whalley,
1993; Figs 1-3, 7-14) and that characteristics other than
traditional ones are necessary to resolve many of the
taxonomic difficulties, or the confusion arising, as a result of
this diversity (Martin, 1967a; Rogers, 1979a, 1993; Whalley
& Edwards, 1995). Morphological variation in Xylaria Hill ex
A. J. S. Whalley
901
1981, 1985), stromal pigmentation (Greenhalgh & Whalley,
1970; Whalley & Whalley, 1977) the nature of the apical
Stromata leathery or woody. never
Section Hypoxylon
apparatus and ascus tip (Griffiths, 1973; Beckett & Crawford,
carbonaceous, bright coloured, usually
1973; Stiers, 1977; Rogers, 1979a; Pouzar, 1985 a, b), and
some shade of red, purple or brown,
globose, subglobose, pulvinate, or widely
cytological data (Rogers, 1964 ; 1965, 1967 a, b, 1968 a-c,
effused; ostioles umbilicate.
1969, 1970, 1972, 1973, 1975a, b; Rogers & Stiers, 1974)
Stromata globose, subglobose, pulvinate,
Section Papillata
have all provided varying degrees of discriminating inforor widely effused; ostioles papillate.
mation. The type of apical apparatus which usually presents
Stromata coloured at least when young
subsection Papillata
a typical blue amyloid reaction with Melzer's reagent has
becoming brown to black at maturity.
Stromata white or light grey when young
subsection Primo-cinerea
proved to be especially useful at the generic level (Griffiths,
becoming black and very carbonaceous at
1973; Nannfeldt, 1976; Rogers, 1979a; LiESS0e, Rogers &
maturity.
Whalley, 1989; San Martin & Rogers, 1989; Gonzalez &
Ostioles papillate and surrounded by an
Section Annulata
Rogers, 1993; Figs 19-21). The length and position of the
annular disk; stromata usually coloured.
germination slit on the ascospore is also important, particularly
Stromata restricted or indefinitely effused,
Section Applanata
carbonaceous and applanate; ostioles
in Xylaria and its allies (Beckett, 1979a, b; Rogers, 1979b,
umbilicate or papillate.
1983, 1984a, b; Rogers & Callan, 1986a, b; Ju & Rogers,
1990; Figs 14 & 15). Application of SEM to study surface
ornamentation of ascospores has proved to be extremely
valuable (Figs 27-31). At the generic level Camillea is
Schrank is especially challenging and in certain species characterized by its light-coloured ascospores with no visible
complexes knowledge of the anamorph is required in order to germ slits by light microscopy but by SEM they are
separate the closely related taxa (Martin, 1970; Rogers, 1985, distinctively ornamented with warts, spines, pits, reticulations
1993; San Martin & Rogers, 1989; Callan & Rogers, 1990). or are longitudinally ribbed (Rogers, 1977 b; LiESS0e et al.,
The danger of over reliance on gross morphological features 1989; Gonzalez & Rogers, 1993; Whalley, 1995; Whalley,
is well illustrated by reference to the dimorphic Camillea Whalley & Jones, 1996). In Stromatoneurospora the ascospores
leprieurii Mont. (Fig. 3). In its expanded or applanate form it are striate (Jong & Davis, 1973). At the species level certain
was placed in Hypoxylon as H. melanaspis Mont. but in its individuals possess characteristically ornamented ascospores.
elongated state it was accepted in Camillea (Dennis, 1957; In Hypoxylon sensu stricto a number of taxa are characterized
Miller, 1961). Examination of ascospores, anamorphic form, by ascospores ornamented with faint transverse striations
and chemical profiles proved that the two states are merely oriented perpendicular to the long axis of the spore
morphological forms of the same taxon (LiESS0e, Rogers & (Rogers & Candoussau, 1982; Van der Gucht & Van der
Veken, 1992; Fig. 28). Similar spore ornamentation is found
Whalley, 1989).
Traditionally the form of the stroma, pigmentation, shape in a number of Daldinia species (Van der Gucht, 1993). In
and dimensions of the ascospores have featured strongly in H. weldenii J. D. Rogers and Nemania chestersii (J. D. Rogers &
the earlier accounts e.g Hypoxylon (Miller, 1961), Xylaria Whalley) Pouzar the ascospores have longitudinal ridges
(Dennis, 1956, 1957) and other xylariaceous genera (Martin, running parallel to the long axis which give them a striate
1967a; Rogers, 1979a; LiESS0e & Spooner, 1994) In many appearance (Rogers, 1977 a; Rogers & Whalley, 1978; Fig.
cases the' classical' approach although convenient has resulted 29). There is insufficient data on peridial anatomy to draw
in the formation of unnatural groupings where species or conclusions and at present the cytological data obtained does
genera appear to be taxonomically closely related when in not appear to be taxonomically useful.
reality they are distinct and distant. In his monograph of
It was, however, the realization that the anamorphic state
Hypoxylon Miller (1961) divided the genus into four sections provides a previously unused source of taxonomic characters
on the basis of stromal form, texture and colour, and nature of useful in the separation of closely related species, species
the ostiole (Figs 1-3, 7-8, Il-12, 15-16, 18; Table 2). groups or often genera (Chesters & Greenhalgh, 1964;
Subsequent studies employing other characteristics show that Martin, 1967a, 1968a, b; 1969a-c, 1970; Greenhalgh &
these divisions are artificial and fail to recognise taxonomic Chesters, 1968; Jong & Rogers, 1972) which stimulated
affinity or distance between the taxa involved (Pouzar, 1979, considerable impetus for the development of a more
1985 a, b; Rogers, 1979a; Whalley & Edwards, 1987, 1995; satisfactory systematic arrangement in the Xylariaceae (Rogers,
Granmo et aI, 1989; Whalley & Greenhalgh, 1973). Thus 1979a). It can be seen that specific anamorphic forms are
Miller's subsection Primocinerea of the section Papillata linked with certain genera (Table 3). Thus Xylocladium appears
contains elements now distributed in a range of genera e.g. exclusive to Camillea (Rogers, 1975 c, 1979 a; LiESS0e, Rogers
Nemania (Pouzar, 1985a, b), Rosellinia (Petrini, 1992) and & Whalley, 1989; Gonzalez & Rogers, 1993) whilst
Euepixylon (LiESS0e & Spooner, 1994). Section Applanata Geniculosporium links with Nemania (Whalley & Rogers, 1980;
(Miller, 1961) is currently redistributed between Camillea and Pouzar, 1985 a, b; Petrini & Miiller, 1986) and Lindquistia with
Biscogniauxia (Pouzar, 1986; LiESS0e, Rogers & Whalley, the dung inhabiting Podosordarill and Porania (Jong & Rogers,
1989; Whalley, LiESS0e & Kile, 1990a, b; Van der Gucht, 1969; Rogers & Russell, 1973; Furuya & Udagawa, 1977;
1992; Gonzalez & Rogers, 1993). Undoubtedly other genera Rogers, 1985; Rogers & LiESS0e, 1992). Nodulisporium is
e.g. Xylaria, Rosellinia, will require considerable rearrangement characteristic for Hypoxylon sensu stricto, Daldinia, and many
as more data becomes available. Peridial anatomy (Jensen species of Biscogniauxia (Greenhalgh & Chesters, 1968; Jong &
Table 2. Classification of Hypoxylon after Miller (1961)
The xylariaceous way of life
Figs 13-18. Fig. 13. Poronia punetata, stromata. (Bar = 1 em ). Fig. 14. Rosellinia aquila, stromata. (Bar = 1 mm). Fig. 15. Hyporylon
stygium, stroma with papillate ostiole surrounded by ostiolar disc. (Bar = 1 mm). Fig. 16. Hypoxylon mammatum, papillate ostioles.
(Bar = 2 mm). Fig. 17. Rhopalostroma kanyae, stromal head with sunken ostioles (arrowed). (Bar = 1 mm). Fig. 18. Camillea fusiformis
M. A. Whalley, ostioles (arrowed). (Bar = 100 セュIN
902
A.
J. S. Whalley
19
903
20
21
22
Figs 19-26. Fig. 19. Kretzschmaria clavus, ascus tip with massive amyloid apical apparatus. (Bar = 10 セュIN
Fig. 20. Camillea fusiformis,
ascus tip with rhomboid amyloid apical apparatus. (Bar = 10 セュIN
Fig. 21. Hypoxylon rubiginosum, ascus tip with reduced discoid
Fig. 22. Biscogniauxia anceps (Sacc.) j. D. Rogers, Y. M. ju & Cand., biCelled
amyloid apical apparatus (arrowed). (Bar = 10 セュIN
Fig. 23. Rhopalostroma kanyae, ascospores with germination slit. (Bar = 2 セュI
Fig. 24.
ascospore with germination slit. (Bar = 10 NIュセ
Hypoxylon investiens (Schwein.) Curt., ascospore with sigmoid germination slit. (Bar = 3 セュIN
Fig. 25. Rosellinia evansii Lress0e &
Spooner, ascospore with helical germination slit. (Bar = 5 セュIN
Fig. 26. Rosellinia thelena (Fr.) Rabenh., ascospores with germination slits
gaping open prior to germination. (Bar = 2 セュIN
Rogers, 1972; Callan & Rogers, 1986; Petrini & Muller, 1986;
Figs 33-34.).
Furthermore, the routine cultivation of a wide range of taxa,
representing a diverse range of xylariaceous genera, opened
the way for chemical investigations of the secondary
metabolites they produced (Whalley & Edwards, 1987, 1995;
Fig. 4). Compounds isolated and characterized include
dihydroisocoumarins and related compounds (Anderson,
The xylariaceous way of life
904
Fig. 28. Hypoxylon rubiginosum, ascospore ornamentation.
Fig. 27-32. Fig. 27. Camillea tinetor, ascospore ornamentation. (Bar = 1 セュIN
(Bar = 1 セIN
Fig. 29. Nemania chestersii, ascospore ornamentation. (Bar = 1 セュIN
Fig. 30. Camillea selangorensis, part of ascospore
Fig. 31. Camillea fusiformis, ascospores with ribbed ornamentation. (Bar = 10 セIN
Fig.
showing warted ornamentation. (Bar = 1 セIN
32. Rosellinia bunodes, ascospores with long tapering ends. (Bar = 10 NIュセ
Edwards & Whalley, 1983), butyrolactones (Edwards &
Whalley, 1979; Anderson, Edwards & Whalley, 1982),
sesquiterpene alcohols (Anderson et a/., 1984a; 1984b; Poyser
et al., 1986; Edwards, Poyser & Whalley, 1988; Edwards et ai.,
1989), cytochalasins (Edwards, Maitland & Whalley, 1989;
Dagne et ai., 1995) and succinic acid derivatives (Anderson,
Edwards & Whalley, 1985). The distribution of these and
other compounds, such as cubensic acid (Edwards, Maitland &
Whalley, 1991), globoscinic acid and globoscin (Adeboya
et ai., 1995a; berteric, carneronic and rnalaysic acids (Adeboya
et ai., 1995 b), are proving to be valuable taxonomic pointers
at both generic and species level (Whalley & Edwards, 1995).
A.
J. S. Whalley
905
Table 3. Anamorph-teleomorph connections
Teleomorph
Anamorph
Anlhoslomella
= Nodulisporium type 2a), Nodulisporium Preuss and Virgariella S.
Hughes (Francis, Minter & Caine, 1980)
Dicyma Boulanger (Hawksworth, 1971)
7Humicola-like (Valldosera & GuaTTo, 1988)
Acanthodochium Samuels, j. D. Rogers & Nagas. (Samuels, Rogers & Nagasawa, 1987; ju & Rogers, 1990)
Geniculosporium (Eckblad & Granmo, 1978; Whalley & Edwards, 1985), Nodulisporium (Greenhalgh & Chesters, 1968;
Callan & Rogers, 1986; Gonzalez & Rogers, 1993), Periconiella (Petrini & Muller, 1986)
Nodulisporium (Udagawa & Ueda, 1988)
Xylocladium Syd. (Crane & Dumont, 1975; L""ss0e, Rogers. & Whalley. 1989; Gonzalez & Rogers. 1993).
Unknown
Acanthodochium (Samuels, Rogers & Nagasawa, 1987)
Nodulisporium (Chesters & Greenhalgh, 1964; Petrini & Muller, 1986)
Unknown
Nodulisporium (Rogers, 1982).
Geniculosporium (Whalley. 1976)
Unknown
Unknown
Unknown
Nodulisporium. Virgariella, Hadrotrichum Fuckel, Rhinocladiella Nannf. (Martin, 1967 a; Greenhalgh & Chesters, 1968; jong
& Rogers, 1972; Petrini & Muller, 1986)
Nodulisporium (Samuels. Muller & Petrini, 1987)
Hadrotrichum (Petrini & Muller. 1986)
Geniculosporium (Samuels & Muller, 1980)
scolecosporous anamorph, Liberiella-like Gu, Gonzalez & Rogers, 1993)
Geniculosporium (Chesters & Greenhalgh. 1964; Petrini & Muller, 1986)
Rhinocladiella-like (Candoussau & Rogers, 1990)
Unknown
Sporothrix Hektoen & C. F. Perkins Gong & Davis, 1974)
Geniculosporium (Rodrigues & Samuels, 1989)
Lindquistia Subram. & Chandrash. (Subramanian & Chandrashekara, 1977; Rogers & L""ss0e, 1992)
Lindquistia (Subramanian & Chandrashekara, 1977; Stiers, Rogers & Russell, 1973)
Unknown
Nodulisporium (Hawksworth & Whalley, 1985)
Geniculosporium, Dematophora R. Hartig, Nodulisporium (Petrini, 1992)
Unknown
Unknown
Unknown
Nodulisporium (Samuels & Muller, 1980)
Unknown
Nodulisporium (Samuels, 1989; Samuels & Rossman, 1992)
Unknown
Anamorph described by Minter & Webster (1983) as being geniculate but not assigned to a form genus
Typically produced on developing stromata but no form genus yet assigned. Xylocoremium flabelliforme (Schwein.: Fr.) ).
D. Rogers is associated with X. cubensis (Rogers, 1984 b; 1985)
7Ascolricha
7Ascolrichella
Astrocyslis
Biscogniauxia
Calceomyces
Camillea
7Chaenocarpus
Collodiscula
Daldinia
Engleromyces
Entonaema
Euepixylon
Helicogermslita
Holttumia
Hypocopra
Hypoxylon
Induratia
Krelzschmaria
Leprieuria
Lopadostoma
Nemania
Obolarina
7Penzigia
Phaeosporis
Phylacia
Podosordaria
Poronia
Pulveria
Rhopalostroma
Rosellinia
Sarcoxylon
Slilbohypoxylon
Stromaloneurospora
Thamnomyces
Theissenia
Theumenella
Versiomyces
Wawelia
Xylaria
Geniculosporium Chesters & Greenh. (Martin 1969 a,
ACTIVITIES OF THE XYLARIACEAE
These can be broadly grouped under decomposition of natural
substrata, their role as phytopathogens, and as endophytes.
The boundaries between these activities are often ill defined
and subject to change depending on interactions especially
between the host, or substratum, and the environment. Thus
taxa which are present in living hosts as endophytes can
become pathogenic if the host becomes stressed, and
pathogenic species may linger after killing the host by leading
a saprotrophic existence (Chesters, 1950; Whalley, 1985;
Boddy, 1994).
Role in wood decomposition
Although members of the Xylariaceae can colonize a wide
range of substrata the vast majority are wood inhabitants
(Rogers, 1979a). Earlier studies on their occurrence and host
specificity were through necessity related to the presence of
the teleomorph in the field and led to a general belief that the
Xylariaceae are only involved in the decomposition of woody
structures (Merrill. French & Wood, 1964; Rogers, 1979a;
Whalley, 1985). Furthermore their appearance in the teleomorph stage is often closely linked to the stage of wood
decomposition (Whalley, 1985). Thus Hypoxylon fragiforme
and Biscogniauxia nummularia develop on dying or recently
dead branches and stems where the wood is still in a relatively
undecayed condition (Chesters, 1950; Chapela & Boddy,
1988a-c). In contrast Euepixylon udum and Nemania conj1uens
are always associated with well decomposed, decorticated
wood, which is often water soaked (Whalley, 1985). The
ability of members of the Xylariaceae to participate in wood
decomposition is without question (Rogers, 1979a; Whalley,
1985; Rayner & Boddy, 1986, 1988). Selected species have
The xylariaceous way of life
906
Figs 33, 34. Nodulisporium anamorph of Biscogniauxia nummularia. (Fig. 33. Bar = 1 セュ[
been shown to degrade lignin (Sutherland & Crawford; 1981)
and others exhibit impressive produdion of cellulolytic
enzymes (Wei et al., 1992).
In early studies on wood decay in the laboratory involving
various Xylariaceae, Blaisdell (1939) found that D. concentrica,
a species of Hypoxylon, and a Xylaria caused significant weight
losses in three different hardwoods. Cartwright & Findlay
(1946) then demonstrated that X. polymorpha (Pers.: Fr.) Grev.
when inoculated on to beech wood blocks caused a 14 %
weight loss over a 4 month period. Weight losses from 10 to
26 % in aspen and red oak woods in 3 months were recorded
for D. concentrica, B. atropunetata B. mediterranea, H. mammalum
(as H. pruinatum (Klotzsch) Cooke) and C. punetulata (Merrill
et aI., 1964) whilst Xylaria digitata (L.: Fr.) Grev. and H.
rubiginosum caused a 16 % weight loss in aspen wood after 3
months (Rajagopalan, 1966). In a study of the chemical and
microscopic features of wood decay caused by a seledion of
Xylariaceae D. concenlrica was found to be particularly adive
causing a weight loss in birch of 62'9% after 2 months
(Nilsson et al., 1989). The Xylariaceae tested were found to
degrade preferentially the syringylpropane units of lignin and
Nilson et al. (1989) suggested this might explain their general
inability to degrade pine. Interestingly few Xylariaceae
colonize coniferous wood (Miller, 1961; Rogers, 1979a;
Whalley, 1985).
In a study of decay of oak and beech wood blocks by
xylariaceous and diatrypaceous fungi Abe (1989) found that
they all demonstrated greater tolerance to low water potentials
than the three Basidiomycotina species included in the
investigation and that they caused the greatest weight losses
in those wood blocks maintained at a low moisture content.
Abe also found that the xylariaceous and diatrypaceous
isolates, with the exception of H. howeianum Peck, removed
27-37% of the total oak wood lignin achieving a 35-51 %
weight loss after six months: he concluded that they have
great abilities for decaying wood and adapt well to dry
environments (Abe, 1989).
The Xylariaceae have, however, received considerable
attention recently in their role as latent decay fungi which
Fig. 34. Bar = 10 セュIN
cause small pockets of decay or decay columns, sometimes
extensive, depending on the host and the fungal species
involved (e.g. Rayner & Boddy, 1986, 1988; Boddy, 1994).
Investigations of attached branches of ash (Fraxinus excelsior L.)
and beech (Fagus sylvatica L.) have shown that natural
colonization of sapwood occurs in the absence of major
wounds (Boddy, Gibbon & Grundy, 1985; Boddy, Bardsley &
Gibbon, 1987; Chapela & Boddy, 1988 a, b). Although
differences were observed between patterns of early colonization of beech and ash branches these might be attributed to
differences in branching patterns, location of dying lateral
branches and in the speed of main branch death (Chapela &
Boddy, 1988a). In ash, extensive individuals of various
Basidiomycotina and Ascomycotina, including D. concentrica
and H. rubiginosum, formed very rapidly in sedors of branches,
often in less than a single growing season (Boddy et al., 1985,
1987). In beech, early colonizing fungal communities were
shown to have a distind spatial organization where decay
often started in distal regions with stain-associated fungi
which had developed from latent propagules in the wood and
bark (Chapela &...Boddy, 1988a). Hypoxylon fragiforme and B.
nummularia were frequently found to be early colonists
(Chapela & Boddy, 1988a). Although there were differences
in the pattern of colonization observed, in branches of beech
and ash, the water content of the sapwood in both trees was
strongly implicated in the eventual outcome of colonization
(Chapela & Boddy, 1988 b).
In beech, H. fragiforme and B. nummularia were found to
develop from pockets within the wood where each pocket
contained a genetically different individual. Chapela & Boddy
(1988b) concluded that for these fungi infedion is a common
event and that they do not require large wounds in order to
colonize the tree. They were therefore viewed as being
present as inconspicuous fungal propagules within the wood
which subsequently developed as 'latent invaders' once the
high water content of the wood was reduced (Chapela &
Boddy, 1988 b). The rapid appearance of teleomorphs of H.
fragiforme and B. nummularia in freshly felled beech branches
(Chapela & Boddy, 1988c) is consistent with these findings. It
A. J. S. Whalley
is now apparent that a significant number of xylariaceous taxa
fit this pattern and furthermore, they can, if suitable conditions
prevaiL become invasive and cause canker disease in their host
(see below).
Xylariaceae as phytopathogens
Although the Xylariaceae are not usually considered to be
important as plant pathogens a growing number of species are
now acknowledged to cause considerable economic loss in
natural ecosystems or under agricultural conditions (Rogers,
1979a; Whalley, 1985). Representatives of the family cause
canker in trees, root rots in a wide range of plant species, and
needle blights in conifers (Table 4).
Canker diseases. Hypoxylon mammatum is the best known and
economically the most important cause of a canker disease and
has long been recognized as the cause of serious stem canker
in aspen (Povah, 1924; Manion & Griffin, 1986; Fig. 16). It
infects mainly Populus tremuloides Michx. in North America
and P. tremula L. in Europe (French, Hodges & Froyd, 1969;
Pinon, 1979; Manion & Griffin, 1986). It was calculated that
in 1971 in Minnesota, eastern Upper Michigan, and south
western Wisconsin Hypoxylon canker was responsible for an
annual loss of $4'4 million at the time of harvest (Marty,
1972). An estimated 1-2% of aspen grown in the u.s.A. is
killed by H. mammatum each year (Anderson, 1964). The
fungus also occurs on Acer, Alnus, Betula, Carpinus, Fagus,
Picea, Pyrus, Salix, Sorbus, and Ulnus but only appears to be an
important pathogen of Populus (Manion & Griffin, 1986). In
North America the disease is prevalent throughout the
northeast, the Great Lakes region, and the northwestern
prairies. It is, however, absent from the northern Rocky
Mountains and Alaska in spite of abundant aspen and the
presence of the fungus (Juzwik, Nishijima & Hinds, 1978). In
Europe it is believed that the disease has been present in the
Alps for over 30 years (Pinon, 1979). Ascospores are assumed
to be the source of infection but ascospore inoculations have
proved unreliable and considerable research has been undertaken on the conditions governing germination in attempts to
determine the exact conditions for infection (Rogers & Berbee,
1964; Manion & Griffin, 1986).
An impressive amount of data has been accumulated on the
site of infection and the growing conditions of the trees which
then become infected. Thus good correlation has been
observed between natural cankers and one or two year old
lateral branches (Manion, 1975) and with branch galls caused
by the insect Saperda inornata Say (Anderson, Ostry &
Anderson, 1979). In spite of conflicting information there is
evidence to relate water stress in trees with higher incidence
of Hypoxylon canker (Day & Strong, 1959; Bier & Rowat,
1962; Bagga & Smalley, 1969; Bruck & Manion, 1980). It has
also been shown that under water stress conditions the proline
content of aspen increased dramatically and that radial growth
rates of H. mammatum isolates were stimulated much more by
proline than other amino acids (Griffin, Quinn & McMillen,
1986). It was later shown that there is clonal variation in the
amino acid contents of aspen induced by diurnal drought
stress and this may influence susceptibility to Hypoxylon
907
canker (Griffin et al., 1991). If the conclusion of Chapela (1989),
that H mammatum is an endophyte of aspen, proves to be the
norm then the importance of water stress becomes highly
significant
Hypoxylon mammatum is the most damaging of the canker
causing Xylariaceae and it is also noteworthy for the
production of phytotoxins. Hubbes (1964) first suggested that
a toxin or toxins might be involved in the pathological
process. Initial attempts to isolate and purify the toxic
principle, known as mammatoxin, revealed the presence of
several compounds which were active in bioassays (Schipper,
1978; Stermer, Scheffer & Hart, 1984). Recent investigation of
culture filtrates of H. mammatum has revealed the occurrence
of two families of toxins. One has been identified as a
diterpene (hymatotoxin) with a structure similar to momilactones and the second as tetralones (Bodo et al., 1987; Pinon
& Manion, 1991).
The momilactones were originally isolated from rice (Oryza
sativa cv. Koshihikan) husk and inhibit the growth of rice roots
and lettuce seeds (Kato et al., 1973, 1977). Tetralones are
similar to juglone, a compound toxic to many plants as well
as bacteria, fungi, fish, and mice (Soderquist, 1973). Hypoxylon
mammatum has also been shown to produce cytochalasin D
(Whalley & Edwards, 1995) but this does not cause the same
phytotoxic response induced by culture filtrates or pure
hymatoxins (Pinon & Manion, 1991) although the cytochalasins are well known for their tissue toxicity in plants
(Sawai, Okuno & Ito, 1982; Betina, 1989). There is an intricate
host-parasite relationship between H. mammatum and its
aspen host with pyrocatechol and other bark substances
proving inhibitory to growth (Hubbes, 1962a, b, 1964, 1966)
and with the post-infection production of phytoalexins which
inhibit ascospore germination but not mycelial growth (Flores
& Hubbes, 1979.)
Hypoxylon mammatum canker in aspen has attracted the
greatest attention but a number of species of Camillea and
Biscogniauxia cause significant canker diseases and die back
(Table 4) if only in hosts which are stressed through injury,
drought or fire damage (Rogers, 1979a; Whalley, 1985). Cork
oak (Quercus suber L.) has been declining steadily in Europe for
many years and Biscogniauxia mediterranea, the causative agent
of coal canker in oak, has been identified as an important factor
for this decline (Macara, 1974, 1975). In a 1974 survey of cork
oak stands in Portugal 41'5% of trees were recorded as
diseased, with B. mediterranea being the principal pathogen
(Macara, 1975). Surveys over the past five years indicate that
Biscogniauxia is associated with around 30 % of the dying trees
(Santos, pers. comm.). In North Africa the disease may reach
epidemic proportions (Barbosa, 1958). It is also evident that
oak canker is both more prevalent and serious in trees
suffering from water stress and there have been increases in
the disease following hot, dry spells (Macara, 1974, 1975;
Santos, pers. comm.). Biscogniauxia mediterranea is, however,
not the only reason for the decline of the cork oak since in
Catalonia (NE Spain) Botryosphaeria stevensii Shoemaker hasbeen found to be the main fungal pathogen involved (Luque
& GirbaL 1989).
Spooner (1986) recorded B. mediterranea from Britain
growing on Castanea sativa Mill. He noted that the stromata
The xylariaceous way of life
908
Table 4. Examples of diseases caused by members of the Xylariaceae
Species
Principal hosts
Canker diseases
Biscogniauxia alropunclala (Schwein.) Pouzar
B. medilerranea (De Not.) Kuntze
B. nolhofagi Whalley, LreSS0e & Kile
B. nummularia (Bull.: Fr.) Kuntze
CamiIIea punclulala (Berk. & Rav.) Lress0e, j. D. Rogers & Whalley
C. linclor (Berk.) Lress0e, j. D. Rogers & Whalley
Hypoxylon mammalum (Wahlenb.) j. H. Mill.
H. rubiginosum (Pers.: Fr.) Fr.
Xylaria arbuscula Sacco
Quercus
Quercus
Nothofagus. cunninghamii
Fagus
Quercus
Acer, Plalanus
Populus
CameIIea
Macadamia
Root rot diseases
Krelzschmaria clavus (Fr.) Sacco
K. deusla (Hoffm.: Fr.) P. M. D. Martin
RoseIIinia bunodes (Berk. & Broome) Sacco
R. desmazieresii (Berk. & Broome) Sacco
R. necalrix Prill.
R. pepo Pat.
Xylaria mali Fromme
Macadamia
Hevea
Coffea
Salix
many
Coffea
Malus
Needle blights
R. herpolrichioides Hepting & R. W. Davidson
R. minor (Hahn.) S. M. Francis
were widely effused and that the bark exhibited extensive
peeling and shedding, It was also reported that 'there was no
evidence that the fallen Castanea on which the British
collection was made had been subjected to fire damage,
although the tree grew on well-drained, sandy soil on a
hillside and may well have suffered from drought stress during
previous dry summers' (Spooner, 1986). A good correlation
was also obtained between water stress and ability of B.
mediterranea to cause canker in Quercus cerris L. where
following inoculation experiments only those seedlings
maintained under water stress conditions became diseased
(Vannini & Scarascia Mugnozza, 1991).
In 1990 the Forestry Commission of Messina (Sicily)
reported a serious decline of beech (Fagus sylvatica L.)
in the lowest region of a beech wood on the Nebrodi
mountain range. Subsequent field surveys and laboratory investigations identified B. nummularia as the associated
fungus (Granata & Whalley, 1994; Figs 5, 33-34). They
concluded that the prolonged drought and high temperatures
experienced in Sicily over the previous ten years had caused
conditions of water stress in the beech trees and made them
susceptible to the disease (Granata & Whalley, 1994). The
greatest damage was observed on the southern slopes of the
Nebrodi mountains where exposure greatly influences the
amount of water in the soil. No diseased trees were observed
in areas where the soil moisture was high (Granata & Whalley,
1994). The relationship between water stress in beech and
strip canker development caused by B. nummularia and similar
fungi has also been emphasized by Lonsdale (1983), who
queried whether fungi such as B. nummularia and Eutypa
spinosa (Pers.) Tul. & C. Tul. are directly pathogenic or just
colonize tissue which had become debilitated by another
factor. Hendry, Boddy & Lonsdale (1993) observed interactions between species of Xylariaceae and Diatrypaceae
isolated from beech with beech callus material. They found
that when B. nummularia and E. spinosa were grown in dual
Tsuga
Conifers
culture with callus significant stimulation of radial growth rate
occurred and they concluded that this 'suggests that they
possess some pathogenic ability and do not simply invade
dead tissue' (Hendry et al., 1993). Additionally they
demonstrated that undiluted culture filtrate from B. nummularia
was lethal to beech callus although at a dilution of 10- 2
growth of the callus was stimulated (Hendry et aI., 1993).
However, B. nummularia produces 5-methylmellein in culture
and there is no evidence that this or any other, as yet
unidentified, compounds are phytotoxic or are implicated in
canker formation (Anderson et aI., 1983; Whalley & Edwards,
1995).
Another Biscogniauxia species, B. nothofagi is associated
with dieback and canker in Nothofagus cunninghamii Oerst. in
Tasmania, Australia (Whalley, Lress0e & Kile, 1990a; Fig. 2).
It was found that the Biscogniauxia was most frequent on trees
which had been attacked by Chalara australis Kile & J. Walker.
The Chalara causes severe vascular disease resulting in crown
wilt and general water stress (Kile & Walker, 1987) thus
providing the necessary conditions for the Biscogniauxia to
develop and become invasive.
The association between water stress and tree diseases
caused by xylariaceous fungi has, however, been recognized
for many years. Biscogniauxia atropunctata causes a serious
drought related disease on oaks in the southern states of
North America (Thompson, 1963; Van ArsdeL 1972; Bassett,
Fenn & Mead, 1982; Tainter, Williams & Cody, 1983; Bassett
& Fenn, 1984). Also in the United States, Camillea punctulata
causes a stem canker of Quercus (Barnett, 1957) and C. tinctor
is associated with canker of American sycamore (McAlpine,
1961) and plane (Platanus occidentalis L. and P, acerifolia (Ait.)
Willd.) (Hepting, 1971). Camillea punctulata is frequently
linked with trees water stressed through prior infection with
the oak wilt fungus, Ceratocystis fagacearum (Bretz) J. Hunt
(Davis, 1966). Undoubtedly water status in the host plant is
of the utmost importance concerning the development and
A.
J. S. Whalley
subsequent presentation of disease caused by members of the
Xylariaceae. Onsando (1985) suggested that tea bushes
(Camellia sinensis (L.) O. Kuntze) are susceptible to wood rot
by Hypoxylon serpens (Pers.: Fr.) J. Kickx (= Nemania serpens
(Pers.: Fr.) Gray) following sun scorch, and Agnihothrudu
(1967; 1978) reported nine species of xylariaceous fungi,
mainly Hypoxylon, as traumatic parasites of tea. The most
unusual association, however, must be that observed between
H. rubiginosum and catalpa (Catalpa bignonioides Walt.) which
was reported from the campus of the University of Georgia,
U.S.A. (Weidell, 1942). Local fishermen obtain the Catalpa
worm (Ceratomia catalpae) for bait by beating the trunks of the
trees with clubs to dislodge them, thus causing localized injury
leading to the development of canker caused by the Hypoxylon
(WeidelL 1942).
A recent study in Poland on alder (Alnus incana (L.)
Moench) which had been weakened by industrial emissions
found that under these conditions H. fuscum (Pers.) Fr. became
a serious pathogen causing a very intensive white pocket rot
in wood of dead alders (Domanski & Kowalski, 1987).
Although Miller (1961) considered H. fuscum to be a
saprotroph on members of the Betulaceae, Rogers (1968d)
suspected that it might be parasitic on Alnus tenuifolia Nutt.
growing in North America. He did, however, stress that
infection of trees in nature takes place under very specific
conditions (Rogers, 1968d)
In the majority of cases the xylariaceous species causing
canker diseases exhibit the characteristics of endophytic fungi
which then develop as stress imposed on the fungus by the
healthy tree is alleviated as the tree itself becomes stressed,
usually water stress. This type of infection is often referred to
as latent (Rayner & Boddy, 1986).
Root rot infections. A very diverse range of Xylariaceae
causes root rot diseases (Table 4). Rosellinia and Kretzschmaria
species are the most widespread and economically important
although occasionally, and under specific conditions, some
species of Xylaria can become damaging. Rosellinia necatrix is
outstanding as a plurivorous pathogen and apparently has a
worldwide distribution (Sivanesan & Holliday, 1972 b; Rogers,
1979a; Teixeira de Sousa & Whalley, 1991). According to
Sztejnberg & Madar (1980) R. necatrix can infect over 170
plant species from 63 genera and 30 families. In a report on the
differences in susceptibility of a range of plant species Teixeira
de Sousa (1985) noted that herbaceous plants were also
infected and could be regarded as a potential source of
inoculum. Since R. necatrix rarely produces ascocarps in nature
and most identifications are through necessity based on
vegetative characters there is some uncertainty concerning the
published outstandingly wide host range and geographical
distribution (Teixeira de Sousa & Whalley. 1991). It has been
suggested that R. necatrix is probably more prevalent in
temperate areas with the closely related species, R. bothrina
(Berk. & Br.) SacCo (= R. arcuata Petch) being more usual in the
tropics (Francis, 1985; Sivanesan & Holliday, 1972 b).
Although a method for the induction of mature ascocarps in
R. necatrix has been developed (Teixeira de Sousa & Whalley,
1991), long term experiments with isolates from different
hosts and from temperate and tropical regions still need to be
909
undertaken to determine precisely the differences, if any,
between R. necatrix and R. bothrina.
There are many reports of serious problems caused by R.
necatrix on a variety of economically important plants in
Europe, e.g. apple, grape vine, pear, plum, sweet cherry,
poplar, jasmine and scented geranium (Cellerino, 1973;
Cellerino & Anselmi, 1980; Guillaumin, Mercier & Dubois,
1982; Delatour & Guillaumin, 1985; Teixeira de Sousa, 1985;
Cellerino, Anselmi & Giorcelli, 1988; Teixeira de Sousa et al.,
1995). In the Alcobac;:a region of Portugal 42 % of the orchards
are infected with Rosellinia and 14 % of the apple trees exhibit
advanced disease symptoms and are either dead or dying
(Teixeira de Sousa et aI., 1995; Fig. 6) and in Italy 'R. necatrix
represents one of the most dangerous agents of root-rot in
Poplars' (Cellerino & Anselmi, 1980) and can cause a loss of
about 0'5-1 % in total production. However, in some regions
this loss may reach 5-10 % and in some plantations it can be
as high as 20--25 % (Cellerino et al., 1988). In a study on
factors influencing the incidence of R. necatrix in poplars
Anselmi & Giocelli (1990) found that R. necatrix spread readily
on loose soil with a high sand content. Furthermore they
noted that soil moisture content near field capacity encouraged
mycelial spread from tree to tree but dry conditions rendered
the trees liable to attack (Anselmi & Giocelli, 1990). The need
to remove from the soil any woody or organic material which
might have had contact with Rosellinia was also seen to be an
important aspect of a control strategy (Anselmi & Cellerino,
1986; Anselmi & Giocelli, 1990).
In New Zealand where R. necatrix causes a serious white
root rot in walnut Uuglans regia L.) the importance of removing
remains of dead trees, especially their roots, was recognized to
be necessary for the restriction of the disease (BoesewinkeL
1977). Solarization of soil prior to planting or exposure of
infected roots to air, light and summer heat coupled with
treatment of the soil with 0'1-0'2 % suspensions of benomyl
or thiabendazole compounds seem to offer the best chance of
control at present (Teixeira de Sousa, 1985; Sztejnberg et al.,
1987; Anselmi & Giocelli, 1990). LiUle is known about the
pathogenicity of R. necatrix but the role of toxins are strongly
implicated. It produces in culture a number of interesting
metabolites including rosellinic acid (Chen, 1960, 1964),
cytochalasin E (Aldridge, Burrows & Turner, 1972; Whalley &
Edwards, 1995) and rosellichalasin (Kimura, Nakajima &
Hamasaki, 1989). Preliminary findings show that cytochalasin
E induces a number of the typical disease symptoms caused by
R. necatrix infection when applied to cut branches of apple
(Whalley, unpublished).
Rosellinia bunodes is a truly tropical species and is reported
to be widespread in tropical America, Central African Republic,
India, Indonesia, Malaysia, Philippines, Sri Lanka, Zaire and
parts of Central America (Sivanesan & Holliday, 1972 a). It
causes black root rot of tropical and subtropical woody hosts
but is most frequent on cacao (Theobroma cacao L.), quinine
(Cinchona spp.), coffee (Coffea spp.), rubber (Hevea brasiliensis
Muel!.) and tea (Camellia sinensis) (Sivanesan & Holliday,
1972a). Unlike R. necatrix it normally produces perithecia in
nature and these develop a distinctive wart-like ornamentation
(Fig. 10) and have ascospores with characteristically long
tapering ends (Fig. 32). Transmission is via mycelium
The xylariaceous way of life
impregnated organic litter or woody debris (Sivanesan &
Holliday, 1972a). There is no evidence for the production of
cytochalasin E or any of the other phytotoxic compounds
known from R. necatrix (Edwards & Whalley, unpublished).
Rosellinia pepo is another tropical species causing black root
rot. It is however, apparently restricted to central America, the
West Indies and West Africa (Booth & Holliday, 1972). Coffee
is the most important host although it is described as being
plurivorous (Booth & Holliday, 1972). Recently an interesting
ring-die back in creeping willow (Salix repens L.) has been
attributed to R. desmazieresii which attacks the roots and
underground stems causing chlorosis. wilting and death of
plants (Barrett & Payne, 198].; Ofong. Pearce & Barrett, 1991).
There also appears to be good correlation between environmental conditions occurring at the time of development of
new disease rings and conditions favourable for the growth
and development of the Rosellinia in vi/ro (Ofong et al., 1991).
It is known to produce cytochalasin D in laboratory culture
but it is not known if it is produced in the field or if it has
pathological implications (Whalley & Edwards, 1995).
Kretzschmaria deusta (= Ustulina deusta (Hoffm.: Fr.) Lind)
has long been recognized as an important pathogen of various
tree species (Wilkins, 1934). It is associated with the base of
trunks but infects through the roots (Wilkins, 1943). More
recent accounts show that in Czechoslovakian forests 11-20%
of beech (Fagus) trees were infected by this fungus (Cerny,
1970, 1975) and in the Sara mountains of Yugoslavia
Prijincevic (1982) recorded an infection rate of up to 42 % of
trees in some localities. In Britain K. deusta is a common cause
of decay in broadleaved trees, especially beech (Fagus) and elm
(Ulmus) (Burdekin, 1977). Recently Greig (1989) reported on
the decay of horse chestnut (Aesculus hippocastanum L.) caused
by this fungus. He concluded that infection was probably via
the roots and that K. deusta is much more widespread than had
previously been assumed (Greig, 1989). A tropical version of
this fungus, often referred to as UstuIina zonata (Lev.) Sacco
(Miller, 1961), is responsible for serious root rot in rubber
(Hevea brasiliensis) but it also infects a number of other
commercially important plants in West Malaysia (Varghese,
1971). Recently the disease has been on the increase in the
rubber plantations of South India although the application of
fungicides with a petroleum wound dressing has proved
effective in controlling the disease provided treatment is
undertaken at an early stage of the infection (Idicula et aL
1990). The closely related K. clavus is now proving to cause
a very damaging root decay in macadamia (Macadamia
intergrifoIia Maiden & Betche) in Hawaii (Ko, Kunimoto &
Maedo, 1977) and Taiwan (Ann & Ko, 1988). Kretzschmaria
clavus is widespread in the tropics and subtropics (Whalley,
1993, 1995) and occurs on a variety of forest trees (Ko,
Tomita & Short, 1986).
In Hawaii, most macadamia orchards with serious
Kretzschmaria root rot problems are located near forests of
Metrosideros collina (Forst.) Gray subsp. polymorpha (Gang.)
Rock. The orchard areas were originally covered by forest and
the discovery that K. clavus is a common inhabitant of
M. collina subsp. polymorpha led Ko et al. (1986) to speculate
that forest trees provided the source of the infection in
macadamia. Kretzschmaria clavus is not the only xylariaceous
910
species to infect macadamia in Hawaii. Recently Ko &
Kunimoto (1991) demonstrated the pathogenicity of Xylaria
arbuscula to macadamia but concluded that in this case
infection occurs via the trunk and not the roots. There are,
however, a number of species of Xylaria which cause root
infections. Xylaria mali is the cause of damaging black root rot
of apple in the southern Appalachian states of America
(Fromme, 1928; Dozier et al., 1974; Clayton, Julis & Sutton,
1976) but is localized. According to Sivanesan & Holliday
(1972c) X. polymorpha can act as a weak pathogen which
enters through wounds and has been associated with Acer
rubrum, Coffea arabica L., Platanus acerifolia and several other
hosts.
Needle blight diseases. Needle blights of conifers caused by
species of Rosellinia have been reported from Europe and N.
America on a number of occasions (Francis, 1986). Rosellinia
herpotrichioides has usually been judged to be responsible
causing outbreaks on young plants of Douglas fir (Pseudotsuga
menziesii (Mirb.) Franco) in forest nurseries (Salisbury & Long,
1956; Smith, 1966), on Sitka spruce seedlings (Picea sitchensis
(Bong.) Carr), (Shea, 1964) and on three-year old plants of
Picea abies (L.) Karsten (Vegh, 1984). However taxonomic
studies on these and related Rosellinia species led Francis to
conclude that all of these infections in young conifer seedlings
were caused by R. minor and not R. herpotrichioides (Francis,
1986). She also maintained separate taxonomic status for R.
herpotrichioides noting that apart from sound taxonomic
differences it had been found causing needle blight on lower
branches of mature hemlock (Tsuga canadensis (L.) Carr)
growing nearest to the stream banks along coves in the Pisgah
National Forest in N. Carolina; U.s.A. (Hepting & Davidson,
1937), and therefore a very different situation to the nursery
beds where R. minor occurred (Francis, 1986). A number of
other reports of Rosellinia causing disease in conifers (e.g.
Georgescu & Ga§met, 1954; Petrak, 1961; Burmeister, 1966)
can be attributed to R. minor (Francis, 1986). There is no
evidence to link other species of Rosellinia, e.g. R. aquila (Fr.)
De Not. and R. thelena (Fr.) Rabenh. with needle blight
diseases and current evidence indicates that R. minor can cause
serious loss in forest nursery beds (petrak, 1961); especially
where there is overcrowding, prolonged high humidity and a
growth form giving a dense lower canopy of foliage
(Georgescu & Gasmet, 1954; Burmeister, 1966; Francis, 1986;
Cech, 1990).
The Xylariaceae as endophytes
Endophyte fungi have been described as those organisms that
live inside the plant tissue for at least part of their life cycle
without causing any disease symptoms in the host (Petrini,
1991). Over the past 20 years an increasing number of
investigations of endophytic fungi have drawn attention to
the almost ubiquitous, and some times dominant, presence of
members of the Xylariaceae especially in tropical plants (e.g.
Petrini & Petrini, 1985; Rodrigues, 1994; Rodrigues &
Samuels, 1990; Rogers, Stone & Iu, 1994; Sieber-Canavesi &
Sieber, 1987; Whalley, 1993; Petrini, Petrini & Rodrigues,
1995). A total of eleven genera of Xylariaceae have been
A.
J. S.
Whalley
recorded as endophytes (Table 5) with Camillea predided to
be a future addition (Petrini, Petrini & Rodrigues, 1995).
Identification of xylariaceous endophytes is often difficult
since they fail to produce suitable diagnostic features and only
very infrequently form their teleomorph in culture. In spite of
this the pioneering work of Petrini and colleagues (e.g. Petrini,
1992; Petrini & Petrini, 1985; Petrini, Petrini & Fisher, 1987;
Petrini & Rogers, 1986; Petrini, Petrini & Rodrigues, 1995)
has resulted in the development of keys and the necessary
information to enable confident identification to be made to
generic level for temperate isolates. The situation regarding
tropical endophytic Xylariaceae is much more complex
however, as a result of their abundance and impressive
diversity (Rodrigues & Samuels, 1990; Whalley, 1993). It is
doubtful whether differentiation of species on the basis of
cultural and anamorphic features alone will ever be possible
since differences between individual species are often
insufficient to allow for absolute identifications to be made
(Petrini, Petrini & Rodrigues, 1995). However, studies with
Xy/aria indicate that a combination of morphological charaders
and biochemical analyses might enable satisfadory identifications to be made (Brunner & Petrini, 1992; Rodrigues, 1992;
Rodrigues, Leuchtmann & Petrini, 1993). There are also
indications that secondary metabolite profiles from endophytic
isolates might be 'matched' with those obtained from cultures
derived from teleomorphic material thus enabling identity to
be established (Whalley & Edwards, 1995). A preliminary
study of X. cubensis (Mont.) Fr. comparing secondary
metabolites e.g. cubensic acid (Adeboya et al., 1995 a) obtained
from teleomorphic derived cultures with those produced by
endophytic Xy/aria isolates from Euterpe o/eracea Mart. leaves
confirmed the findings of Rodrigues that they belonged to X.
cubensis (Edwards & Whalley, unpublished; Rodrigues, 1992).
Ongoing research on secondary metabolites of the Xylariaceae
will include endophytic isolates to determine the suitability of
this approach for the identification of endophytic members of
the family. Inoculation experiments to produce the teleomorphs provide another, but long term, alternative.
Although Xylariaceae are frequently isolated from living
tissues of many plants (Petrini, Petrini & Rodrigues, 1995)
their isolation can be dependent upon the isolation method
used. Chapela & Boddy (1988b) and Chapela (1989) reported
on an increase in frequency of recovery of isolates of
xylariaceous species using seledive isolation methods. Application of different drying regimes to Fagus grandifolia Ehrh.
and Populus tremu/oides resulted in the isolation of Xylariaceae
at levels of 32 % and 41% of all of the endophytic species in
these hosts. Their recovery using non-seledive methods was
rare (Chapela, 1989). It is perhaps noteworthy that H.
mammatum was recovered from P. tremuloides and H. fragiforme
from Fagus and therefore both species were isolated from the
host tree species on which they usually produce their
teleomorph in nature (Miller, 1961). In the case of H.
fragiforme there is an intricate host/fungus recognition
mechanism whereby ascospore germination is mediated by
monolignol glucosides, present in the host, ading as specific
recognition messengers (Chapela et a/., 1991). Ascospores are
primed to germinate through the process of eclosion in the
presence of the messenger and therefore germinate rapidly on
911
their desired host (Chapela et a/., 1990; 1993). There appears
to be a similar mechanism operating between D. concentrica
and Fraxinus (Gaskell, 1995).
An increasing number of studies now show that individual
xylariaceous species form a dominant part of the endophytic
biota in certain tropical plant leaves. Thus X. cubensis was the
second most frequent species isolated from leaves of Licua/a
ramsayi (Muel!.) Domin. (Rodrigues & Samuels, 1990) and an
unidentified species of Xy/aria was a frequent inhabitant of
Sty/osanthes guianensis Sw. leaves (Pereira, Azevedo & Petrini,
1993). In her study of leaf endophytes of the tropical palm, E.
olemcea, Rodrigues (1992) found X. cubensis to be numerically
the most important species although other xylariaceous
genera were present. These included species of Anthostomella,
Da/dinia and Hypoxy/on (Rodrigues, 1992).
It would be a mistake to think that aiL or even the majority,
of the Xylariaceae live as endophytes. It could be predided
that those species of Xylaria which form their teleomorph on
fallen leaves and fruits are endophytic. However, current
information suggests that they are not and that the leaves or
fruits ad as 'baits' in the litter layer. Xy/aria carpophi/a
(Pers.) Fr. only occurs on fallen beech (Fagus) cupules (Rogers,
1979 b) but it is widely distributed in the British Isles and
Europe (Dennis, 1981; Watling & Whalley, 1977) and
elsewhere e.g. North America (Rogers, 1979b) and Japan
(Yokoyama & Shidei, 1972). Incubation of beech cupules taken
diredly from the tree or 'captured' in suspended litter nets
always failed to develop stromata of X. carpophila although
the fungus was consistently present on fallen cupules in the
litter. However, incubation of cupules from the litter which
showed no signs of the Xy/aria frequently developed typical
stromata after several weeks incubation in a damp chamber
(Whalley, 1987; Whalley & Gaskell, unpublished).
Preliminary studies with fruit inhabiting Xy/aria species in
Thailand indicate a similar pattern. Similarly Lress0e & Lodge
(1994) could find no evidence that x. axifera Mont., a species
specifically associated with fallen Araliaceae petioles, could
invade attached petioles. They failed to isolate X. axifera from
either diseased or healthy senescent petioles collected shortly
before or after abscission or from healthy non-senescent
petioles obtained from the canopy. They concluded that it is
likely that the petioles are colonized by X. axifera once they
reach the ground (Lress0e & Lodge, 1994). In the same study
they suggested that X. guareae Lress0e & Lodge, a species host
specific to Guarea guidonia (L.) Sleumer, might be endophytic.
Investigation of other host specific species and those occurring
on leaves, petioles or fruits should prove interesting and
rewarding.
In spite of these unpredicted findings, the Xylariaceae occur
as endophytes of many plants on a worldwide basis although
current evidence shows them to occur more frequently in the
tropics (Rodrigues, 1994; Rodrigues & Samuels, 1990). The
outstanding questions remaining unanswered concern their
presence in healthy plant tissue, frequently in a host species on
which their teleomorph is never formed in nature, and how
they get there? In a comparison by means of somatic
incompatibility testing and gel electrophoresis of isoenzymes
of thirty strains of X. cubensis, isolated from leaves of the
Brazilian rainforest palm E. oleracea, a high degree of genetic
The xylariaceous way of life
912
Table 5. Genera of the Xylariaceae with known endophytic
representatives
Genus
Authentication
Anlhaslamella
Biscogniauxia
Daldinia
Hypaxylan
Krelzschmaria
Nemania
Rasellinia
Xylaria
Petrini
Petrini
Petrini
Petrini
Petrini
Petrini
Petrini
Petrini
& Petrini, 1985; Petrini el aI., 1987
& Miiller, 1986
& Petrini, 1985; Petrini & Miiller, 1986
Miiller,
Petrini.
Petrini,
Petrini,
& Petrini,
&
&
&
&
1986
1985; Petrini & Miiller, 1986
1985; Petrini & Rogers, 1986
1985; Petrini, 1992
1985
diversity was shown to occur (Rodrigues, Leuchtmann &
Petrini, 1993). They concluded that this diversity indicated
that the endophytic thalli of X. cubensis had been established
by ascospores. Since both teleomorphic and anamorphic
stromata were found to occur in the vicinity they suggested
that a conidial inoculum might also be involved and concluded
that colonization of the leaves probably occurred via airborne
propagules (Rodrigues et al., 1993).
In a study of ribosomal DNA length polymorphisms within
populations of X. magnoliae (Gowan & Vilgalys, 1991)
concluded that the populations are not highly clonal and that
it seemed likely that conidia or ascospores serve for longdistance dispersal. This would account for the high level of
variability found within narrow populations, and the occurrence of the same phenotype in distant localities (Gowan &
Vilgalys, 1991). Xylaria magnoliae is, however, a fruit inhabiting
species and on current evidence is unlikely to be an endophyte
but the implication that conidia may provide an infection
inoculum in this and X. cubensis, a common endophyte, is
significant. Greenhalgh & Roe (1984) reported on the presence
of differing nuclei in the conidia of a range of xylariaceous
taxa, including species of Xylaria. They found considerable
differences in germination percentages between species but
they could not correlate this with the presence of normal or
irregular nuclei and they concluded that 'it seems likely that
the conidia of these fungi possess the ability to germinate but
that certain conditions, as yet unknown, are required'
(Greenhalgh & Roe, 1984). It is tempting to suggest that a
specific host fungus recognition occurs for conidia in a similar
fashion to the eclosion phenomenon observed by Chapela et
al. (1990, 1991, 1993), for ascospores of some species of
Hypoxylon,
HOST, HABITAT, AND DISTRIBUTION
The distribution of members of the Xylariaceae as for other
fungi is influenced by a number of factors; usually interacting.
These include host specificity or preference, nature of the
habitat, and climatic interactions.
Host preference
There are few examples of absolute specificity amongst the
Xylariaceae but many where a particular taxon has a strong
host preference (Table 6; Rogers, 1979a; Whalley, 1985).
Thus, Rosellinia buxi has only been found growing on Buxus
sempervirens L. (Petrini, 1992; Whalley & Hammelev, 1988),
H. fraxinophilum is almost exclusive to Fraxinus (Pouzar, 1972)
and B. nummularia appears restricted to Fagus (Whalley &
rather than selectivity is
Edwards, 1987), Host ーイ・ヲセョ」
preferred since an appraisal of host relationships in the
Xylariaceae reveals a number of misconceptions (Granmo
et aI., 1989). In a survey of Biscogniauxia and Hypoxylon sensu
stricto in the Nordic countries they found host range to be
much wider than generally believed. A total of 1113 specimens
of H. multiforme Fr. was examined and, although Betula (37%)
and Alnus (23 %) were clearly the dominant trees involved, 13
host species were identified. Similarly H. fuscum occurred on
a total of 8 tree species but Alnus (35 %) and Corylus (29%)
were strongly preferred hosts. Biscogniauxia nummularia
(Fagus), B. marginata (Fr.) Pouzar (Sorbus), B. cinereolilacina
(J. H. Mill.) Pouzar (Tilia) and H. vogesiacum var. macrosporum
(Salix) all appeared to have specific host associations (Granmo
et aI., 1989).
In Daldinia concentrica, one of the largest and more
spectacular members of the family, host varies according to
geographical situation (Whalley & Watling, 1982). This taxon
is widely distributed throughout the world and is wellrepresented in Britain (Child, 1932; Whalley & Watling,
1982). Its frequency, however declines towards the North and
in Scotland it is uncommon, In the South of Britain Fraxinus is
the preferred host but this eventually becomes replaced by
Betula in the North of England and Scotland (Whalley &
Watling, 1980b, 1982). According to Winter (1887) and von
Arx & Muller (1954) Fraxinus and Alnus are the most common
substrata in Great Britain and on the continent but in Norway
Alnus and Betula are the usual host trees (Eckblad, 1969).
Whalley & Watling (1982) pointed out that the ability to
spread north on trees other than the most frequent host is
well-known for basidiomycetes. Thus Fomes fomentarius (Fr,) J,
Kickx is common on Betula in Scotland but frequents Fagus
south of the border (Watling, 1978) whilst Inonotus obliquus
(Pers,: Fr.) Pilat has a wide host range in continental Europe
and in Britain but although widespread in Scotland, especially
in the northern regions, it is restricted to Betula, even in mixed
communities (pegler, 1964). Daldinia concentrica, along with an
increasing number of the Xylariaceae, is a common endophyte
which occurs in a diverse range of host plants in which it fails
to produce a teleomorph (Petrini et al., 1995). It is likely
therefore that this and other species can exist as endophytes
well outside of their normal host range but can only be
detected if selective isolation techniques are applied. This
creates serious problems when mapping the distribution of
these fungi.
Although host association is fairly well documented for
many of the temperate taxa for most tropical species there is
only spasmodic host data with the exception of many of the
fruit and seed infecting species of Xylaria, those taxa confined
to palms or bamboo and the manglicolous species (Miller,
1961; Rogers, 1979b; San Martin & Rogers, 1989; Whalley,
Jones & Alias, 1994), Biscogniauxia fuscella (Rehm) San Martin
& J. D. Rogers on Celtis laevigata Willd., C. obularia (Fr.)
Lress0e, J, D. Rogers & Lodge on Delonix regia (Bojer ex
Hook) Raf. and Mangifera indica L., C. tinctor on Platanus sp.
A. J. S. Whalley
(Gonzalez & Rogers, 1993) and Cordia subcordata Lam. (Van
der Gucht, 1992), H. dieckmanii Theiss. on Planchonella obovata
(R. Br.) Pierre, H. oodes Berk. & Broome on Diospyros maritima
BI. and Excoecaria agal/ocM L. (Van der Gucht & Van der
Veken, 1992), X. guareae on Guarea guidonia, X. meliacearum
Lcess0e on fine litter of trees in the Meliaceae, including
species of Thiehilia and Guarea, and X. axifera on fallen petioles
of Araliaceae, especially Schefflera spp. (Lcess0e & Lodge,
1994) are examples of a select band for which host substratum
details are available.
Habitat selectivity
The Xylariaceae are not confined to wood but occupy a wide
range of habitats including dung, litter and associations with
insects (Table 7). Although the vast majority are wood
inhabitants there are differences in the nature of the wood
which is suitable for particular species. Thus a distindion can
be made between those which are associated with bark, those
with decorticated wood, and those with no apparent
preference. Hypoxylon fragiforme, H. fuscum and B. nummularia
are examples of taxa which occur on freshly fallen branches or
even on branches still attached to the parent tree. They are
considered to be endophytic which explains their rapid
appearance in dying or recently dead branches (see above).
Euepixylon udum and N. confluens in contrast only occur on
decorticated wood which is also well decomposed. In both
species there is strong host preference for Quercus and they
usually occur in wet oakwoods appearing mainly on water
sodden wood (Whalley & Watling, 1980a; Whalley, 1985).
The physical environment for the development of many of the
wood inhabiting Xylariaceae is also important. In the tropics
most species of Camillea, Biscogniauxia and Hypoxylon are
found in open to sun-exposed sites often occurring in
clearings or tree fall sites (Whalley, 1993; Van der Gucht &
Whalley, 1996). In contrast Kretzschmaria and Xylaria are more
usually well represented in dense, more wet, forest situations
(Whalley, 1993; Van der Gucht & Whalley, 1995)
Poronia, Podosordaria, Hypocopra and Wawelia are specifically
dung inhabitants (Rogers, 1979a; Whalley, 1985). With the
exception of Wawelia they possess ascospores with gelatinizing outer walls which are important in their attachment to
herbage (Krug & Cain, 1974a, b; Rogers 1970). All four
genera are adapted for dry conditions (Rogers, 1979a; Minter
& Webster, 1983; Lundqvist, 1992). In Hypocopra the stromata
are more or less rudimentary, frequently with an external
clypeus and the dung itself probably ads as a substitute
stroma. Poronia and Podosordaria form stalked stromata which
raises their perithecia above the substratum and improves the
efficiency of ascospore dissemination. Wawelia species appear
to be genuinely rare and are strongly associated with leporid
droppings in dry habitats (Lundquist, 1992). Minter & Webster
(1983) demonstrated the need for low relative humidity for
the development of stromata by W. oetospora Minter &
J. Webster. The appearance of a Wawelia species at several
localities in Devon following the unusually hot summer of
1995 is therefore unlikely to be coincidental (Webster, pers
comm.). Little is known about the adivities of these dung
fungi in nature but Poronia punctata (L.: Fr.) Fr. produces a
913
Table 6. Examples of host selectivity
Species
Host
Biscogniauxia nummularia (Bull.: Fr.) Kuntze
B. mediterranea (De Not.) Kuntze
B. nothofagi Whalley. lセウsP・
8< Kile
Daldinia vemicosa (Schwein.) Ces. 8< De Not.
Euepirylon udum (Pers.: Fr.) ・Pウ セ
8< Spooner
Hyporylon cohaerens Pers.: Fr.
H. cohaerens var. microsporum J. D. Rogers 8< Cando
Hypoxylon fragiforme (Pers.: Fr.) J. Kickx
H. frarinophilum Pouzar
H. rutilum Tul. 8< C. Tul.
H. voges;acum var. macrospora J. H. Mill.
Nemania conf/uens (Tode: Fr.) ・Pウ セl
8< Spooner
Rosel/inia buxi Fabre
R. desmazieresii (Berk. & Broome) Sacc.
Xylaria longipes Nitschke
Fagus
Quercus
Nothofagus
Wex
Quercus
Fagus
Quercus
Fagus
Fraxinus
Fagus
Salix
Quercus
Buxus
Salix
Acer
number of antibiotics, the pundaporonins, in culture (Edwards
et aI., 1988). Wicklow & Hirschfield (1979) had earlier shown
that P. punctata and Hypocopra merdaria (Fr.) Fr. are late
colonists of cattle faeces and that they were antagonistic to all
earlier-sporulating colonists in cultural tests.
The association between certain Xylariaceae and litter is
now well established with the growing number of reports on
species restrided to this habitat (Whalley, 1985; Lcess0e &
Lodge, 1994). Rogers (1979b) reported on a number of Xylaria
species inhabiting fallen' fruits', sometimes with clear taxon
specificity, and Lcess0e & Lodge (1994) recently discussed
host and habitat association for three litter inhabiting species
of Xylaria from the tropics. These, together, with H. terrieola
which frequents coniferous needles in the Atlantic Pyrenees
(Candoussau, 1977) form part of a discrete group of Xylariaceae
associated with this specific habitat. The frequent occurrence
of X. oxyacanthae on Crataegus berries in newly planted
Crataegus plantations in Holland was attributed to situations
where there is the right balance between shade and moisture
once the fruits have reached a certain stage of decomposition
(Reynders, 1983).
The association between the Xylariaceae and insects,
usually termites, is restrided to a few species of Xylaria
(Rogers, 1979a). Xylaria nigripes is probably the most common
and Widespread species and is associated with recently
abandoned termite nests where it often occurs along side the
basidiomycete, Termitomyees (Dennis, 1961; Sands, 1969;
Hiem, 1977). When freshly removed combs of the termite,
Maerotermes ukuzii Fuller, were incubated at 28°C at high
humidity Xylaria spp. grew from the surface after 2-3 days
and over a 2-3 week period stromata up to 30 em high
developed (Rohrmann & Rossman, 1980). Surprisingly the
Xylaria was found not to function in lignin decomposition in
the comb and it was therefore suggested that it might provide
a necessary growth factor or serve to condition the substrate
for optimal growth of the associated Termitomyces sp.
(Rohrmann & Rossman, 1980). These termite associated
Xylaria species would appear to be intricately linked although
the role of the Xylaria remains unknown. A critical examination
of their taxonomic relationships and ecological activities
would certainly prove interesting and worthwhile.
The xylariaceous way of life
914
180
'180
--- MエイlNZセK⦅スv]TQャ
-- - --- --Fig. 35. Distribution map of Camillea tinetor (closed circle) and Hypoxylon vogesiacum vaL macrospora (star). Dashed line = palm line.
Distribution
In considering the distribution of members of the Xylariaceae
the fad that records are almost exclusively based on their
teleomorphic state requires cautious interpretation. In a study
of Biscogniauxia and Hypoxylon in the Nordic countries
Granmo et al. (1989) found H. fragiforme to be restricted to the
temperate zone with distribution seemingly exclusively linked
to the distribution of Fagus, its preferred host. Hypoxylon
fragiforme, however, although considered to have a narrow
host range on the basis of teleomorph presence occurs widely
as an endophyte on many plant taxa and therefore has the
ability to extend its range well outside of its recognized
distribution (Petrini & Petrini, 1985). Distribution range might
be considerably extended by ability to grow on a wide host
range e.g. H. multiforme (Granmo et al., 1989) or as for D.
concentrica by switching host preference in the northern
latitudes (Whalley & Watling, 1982). 'Examination of the
distribution of selected species or genera indicates that while
many taxa are global in their distribution others genuinely
seem to be restricted' (Whalley, 1993). Hypoxylon Dogesiacum
var. macrospora exhibits an arctic-alpine distribution (Whalley
& Petrini, 1984; Whalley & Knudsen, 1985; Granmo et al.,
1989; Fig. 35) and in Europe R. diathrausta (Rehm) L. E. Petrini
only occurs at high altitude in the Alps and is then limited to
branches of Pinus montana Miller ssp. prostata Tubeuf or
closely related taxa. Furthermore, only trees located in
positions of extreme exposure are involved and it appears that
branches subjected to wind burn provide the highly selective
habitat for this species and, therefore, its restricted geo-
graphical range (Whalley, 1985). Interestingly Ouellette &
Ward (1970) found that R. diathrausta requires freezing
temperatures for ascospore germination or pretreatment at
_3° prior to germination at 12°. Growth is possible at 0°
with an optimum of 12-15° and as a result the species is welladapted for its situation (Ouellete & Ward, 1970; Whalley,
1985).
At the generic level there are several examples of restricted
distribution. For example it is usually stated that Camillea is
almost exclusively confined to the Americas with the largest
concentration of species occurring in the Amazon region,
including the Guianas, although the genus is quite well
represented in Central America and Mexico (Lressoe et al.,
1989; Gonzalez & Rogers, 1993). Although a clear majority of
species fit this pattern C. tinctor is one taxon with wide
distribution throughout the tropics (Fig. 35). It occurs in West
Africa (Lressoe et aI., 1989) and in Singapore (Miller, 1961) and
although Rogers et al. (1987) failed to record this, or any other
Camillea species, from Sulawesi C. tinctor regularly occurs in
Papua New Guinea (Van der Gucht, 1992), in Malaysia
(Whalley, Whalley & Jones, 1996) and in Thailand (Thienhirun
& Whalley, unpublished). The recent discovery of a new
Camillea, C. selangorensis M. A. Whalley, Whalley & E. B. G.
Jones, in Malaysia suggests that other Camillea species may
occur outside of their traditionally recognized area (Whalley
et a/., 1996). Thamnomyces is another genus known mainly
from lowland tropical America with just a single species,
T. camerunensis Henn. recorded from Africa (Dennis, 1961;
Fig. 36). It has been suggested that the spores may be unfit for
air-borne dispersal and that this might explain their limited
A. J. S. Whalley
915
fig. 36. Distribution map of Rhopalostroma (closed star), Thamnomyces (open star) and Hypoxylon hians (closed circle). Dashed line
palm line.
Table 7. Examples of habitat selectivity
Bark
Biscogniauxia medi/erranea (De NoL) Kuntze
Hypoxylon cohaerens Pers.: Fr.
H. fragiforme (Pers.: Fr.) j. Kickx
H. fraxinophilum Pouzar
Decorticated wood
Euepixylon udum (pers.: Fr.) LiESS0e &. Spooner
Nemania caries (Schwein.) Pouzar
N. confluens (T ode: Fr.) la'ss0e &. Spooner
Litter
Xylaria carpophila (Pers.) Fr.
X. magnoliae j. D. Rogers
X. oxyacan/hae Tul. &. C. Tul.
x. persicaria (Schwein.: Fr.) Berk. &. M. A. Curtis
H. /erricola j. H. Mill.
Dung
Poronia Willd.
Hypocopra (Fr.) j. Kickx f.
Podosordaria Ellis & Holw.
Wawe1ia Namysl.
Insects
Xylaria brasiliensis (Theiss.) Lloyd
X. furca/a Fr.
X. nigripes (Klotzsch) Cooke
distribution (Dennis, 1957). If Camillea and Thamnomyces are
mainly South American then the monotypic Engleromyces is
considered to be African (Dennis, 1961; Whalley, 1993). Its
sole representative E. goetzii Henn. occurs in Uganda, Zaire,
=
Kenya and Tanzania (Dennis, 1961; Kokwaro, 1983) where it
is classed as a parasite which is only found on the upper stems
of the mountain bamboo Anlndinaria alpina K. Schum.
(Kokwaro, 1983). However its discovery in the mountains of
Nepal (Otani, 1982) indicates a much wider geographical
range and examination of mountain bamboo in other regions
could well prove rewarding.
Thamnomyces is classed as predominantly South American
and Engleromyces as mainly African but Rhopalosfroma, a genus
of xylariaceous fungi with stipitate dark brown or black
stromata usually possessing abruptly expanded convex heads,
has a strong Indian and South East Asian connection. Eight of
the ten known species are found there with the other two
occurring in Africa (Hawksworth, 1977; Hawksworth &
Whalley, 1985; Whalley & Thienhirun, 1996; Fig. 36).
Another curious and distinctive member of the family,
Leprieuria bacillum (Mont.) lセウP・L
J. D. Rogers & Whalley is
widely distributed in South and Central America and has not
yet been reported from outside that region in spite of its
unique form ・PウセlH
et al., 1989). Hypoxylon hians Berk. &
Cooke also possesses a very distinctive form and seems to be
genuinely restricted to Tasmania and Victoria in Australia and
South Island, New Zealand (Miller, 1961; Whalley, 1993; Fig.
36). It therefore seems probable that regardless of the lack of
intensive collecting, especially in the tropics, a number of
xylariaceous species, or genera, exhibit recognizable distribution patterns or trends. Comparing different regions of the
world current data indicates that the Xylariaceae are generally
more numerous in the tropics with South America and Mexico
The xylariaceous way of life
possessing the highest species richness (Whalley, 1993; Van
der Gucht & Whalley, 1996). Camillea is an important
component of the xylariaceous mycota in South America and
Mexico with 15 and 14 species respectively compared with
& Whalley, 1996;
only 2 from South East Asia (Van der gセ」ィエ
Whalley et ai., 1996). Xylaria is much better represented in
South and Central America than in Africa, South East Asia,
Papua New Guinea or Europe whilst Nemania exhibits a
stronger presence in Europe than elsewhere (Van der Gucht &
Whalley, 1996). Annulate species of Hypoxylon are absent
from Europe and Kretzschmaria has a strong presence in
tropical and subtropical habitats (Van der Gucht & Whalley,
1996).
The distribution of members of the Xylariaceae is a result of
complex interadions including availability of suitable host
species, appropriate substratum conditions, and overall climatic
influences. Our understanding of their distribution can only
improve as more data is accumulated but the severe lack of
colleding by specialists, especially in the tropics, is a major
problem at the present time. The tendency for many of the
Xylariaceae to occur as endophytes, and therefore have an
extended range, imposes further restridions on our ability to
map their distribution with accuracy.
CONCLUSIONS
This consideration of the adivities of the Xylariaceae in nature
highlights their different lifestyles by examining their ability
to occupy different habitats, to decompose wood, to cause
disease in plants, and to develop under different climatic
conditions and in different geographical regions.
(i) The Xylariaceae are worldwide in their distribution and
are exceptionally well represented in the tropics especially
South and Central America.
(ii) The Xylariaceae are notable for their produdion of a
wide range of novel secondary metabolites, including
antibiotics and phytotoxic compounds.
(iii) The Xylariaceae show adaptation to life in dry habitats
well illustrated by the xerophilic Wawelia.
(iv) Most wood inhabiting species have the ability to cause
white rot.
(v) The Xylariaceae have a remarkable presence as
endophytes often appearing dominant in tropical plant species.
(vi) A number of xylariaceous species cause damaging
disease in plants but often only when the host is water
stressed.
I am grateful to many colleagues and former students for their
valuable discussions and contributions to our work on the
Xylariaceae, in particular Dr R. L. Edwards (University of
Bradford), Professor G. Granata (University of Catania), Dr T.
A. Gaskell (Liverpool John Moores University), Dr G. Hadley
(University of Aberdeen), Professor D. L. Hawksworth (LM.L),
Professor E. B. G. Jones (University of Portsmouth), Dr N. J.
Hywel-Jones (N.C.G.E.B. Bangkok), Dr G. A. Kile (CSIRO), Dr
H. Knudsen (University of Copenhagen), Dr T. Lress0e
(University of Copenhagen), Dr D. J. Lodge (USDA, Puerto
916
Rico), Dr D. J. Maitland (University of Bradford), Dr L.
Manoch (Kasetsart University), Professor A. Nawawi (University of Malaysia), Professor R. H. Petersen (University of
Tennessee), Dr L. E. Petrini (Comano), Professor J. D. Rogers
(Washington State University), Dr N. M. S. Santos (Oerias),
Dr G. P. Sharples (Liverpool John Moores University), Eng. A.
J. Teixeira de Sousa (ENFVN, Alcoba.;a), Dr B. C. Sutton
(LM.L), Dr H. K. Taligoola (Botswana), Khun S. Thienhirun
(Royal Forest Department, Bangkok), Dr K. Van der Gucht
(University of Gent), Dr R. Watling (RBG, Edinburgh),
Professor J. Webster (University of Exeter), Mrs M. A.
Whalley (Liverpool John Moores University).
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