1 Introduction
In China,
Eucalyptus spp. (Myrtaceae) have been widely established in commercial plantations which cover about 4.5 million hectares in southern China
[1]. They include mainly cloned hybrids of
Eucalyptus urophylla and
E. grandis, other
Eucalyptus species include
E. camaldulensis,
E. dunnii,
E. globulus,
E. pellita,
E. smithii,
E. urophylla, as well as their hybrids and clones
[2–
4].
Corymbia citriodora (Myrtaceae), previously classified as a species of
Eucalyptus, has also been widely planted in southern China
[2,
3] and the two genera are collectively referred to in this paper as eucalypts.
The extensive development of eucalypt plantations in China and the relatively limited numbers of clones planted in the past two decades has resulted in the appearance of numerous pests and pathogens that have caused increasing levels of damage
[5]. Consequently, extensive surveys of eucalypt plantations have been undertaken in southern China, resulting in several important diseases being recorded. These include stem diseases caused by
Teratosphaeria zuluensis[6,
7], species of Botryosphaeriaceae
[8], species of Cryphonectriaceae
[9,
10] and
Ceratocystis[11]. Leaf diseases caused by
Calonectria spp.
[12–
14], species of Mycosphaerellaceae and Teratosphaeriaceae
[15,
16] have also emerged as serious problems. The leaf and shoot pathogen,
Quambalaria pitereka has been found on
Corymbia citriodora in the Guangdong Province of southern China
[17].
Six species of
Quambalaria occur on eucalypts. They include
Q. coyrecup,
Q. cyanescens,
Q. eucalypti,
Q. pitereka,
Q. pusilla and
Q. simpsonii and all appear to be native to Australia where their host trees also occur naturally
[18–27].
Quambalaria eucalypti has also been found on native
Myrceugenia glaucescens (Myrtaceae) trees in Uruguay, although it seems likely to have been introduced into that country
[28]. Of the six
Quambalaria spp.,
Q. eucalypti and
Q. pitereka cause leaf and shoot blight on eucalypts
[20,21,24],
Q. coyrecup causes cankers and shoot blight on
Corymbia spp.
[23], and
Q. cyanescens is generally regarded as a saprophyte
[22]. It remains unknown as to whether
Q. simpsonii is pathogenic to eucalypts
[26], and the taxonomic status of
Q. pusilla remains unresolved
[22,29].
Recently, leaf and shoot blight with symptoms typical of those caused by species of Quambalaria was observed on young C. citriodora and E. urophylla× E. grandis trees in southern China. In addition, a fungus with morphological characteristics typical of Quambalaria was isolated from cankers on the stems of E. urophylla× E. grandis trees. The aims of this study were to identify these Quambalaria spp. based on comparisons of DNA sequence data and morphological characteristics.
2 Materials and methods
2.1 Collections of fungal isolates
Leaf and shoot blight was observed on
C. citriodora trees of different provenances in two experimental plantations and an
E. urophylla×
E. grandis plantation in Guangdong Province in southern China (Figs. 1a, 1c, 1d and 1e). White masses of conidia and conidiophores characteristic of the
Quambalaria[21,
22] were common on the surface of the infected leaves and shoots (Figs. 1b and 1f). Isolations were made by scraping conidial masses from the leaf and shoot surfaces and transferring these to 2% malt extract agar (MEA) medium (20 g malt extract and 20 g agar per liter water) and incubated at 25°C. During the process of isolating the stem canker pathogen
Teratosphaeria zuluensis (unpublished data) from cankered
E. urophylla×
E. grandis hybrid trees, a fungus with the morphological characteristics of
Quambalaria species was isolated and these cultures were included in the present study. All
Quambalaria isolates were collected during August 2015 and June 2016.
Fig.1 Symptoms of infection by Quambalaria spp. on eucalypt trees. Shoot (a) and juvenile leave (b) of Corymbia citriodora infected by Quambalaria pitereka covered in white masses of conidia and conidiophores. New shoot (c) produced from the infected C. citriodora, and reinfected by Q. pitereka. Death of apical shoot (d) of Eucalyptus urophylla× E. grandis clone infected by Quambalaria simpsonii. Mature leaf (e) and young apical shoot (f) of E. urophylla× E. grandis clone infected by Q. simpsonii. Arrows indicate infected sites. |
Full size|PPT slide
After the fungi had been cultured for 10 d on 2% MEA, single germ tubes emerging from colonies were subculture on 2% MEA media to obtain pure cultures. Cultures were deposited in the culture collection of the China Eucalypt Research Centre, Chinese Academy of Forestry, Zhanjiang, China. Representative isolates were also deposited at the China Forestry Culture Collection Centre, Beijing, China (Table 1).
Tab.1 Isolates of Quambalaria species collected from eucalypt trees in southern China in 2015 and 2016 and used for phylogenetic and morphological analysis |
Identity | Isolate No.a | GenBank accession No.b | | Host | Location | Collector | Reference |
---|
ITS | LSU | |
---|
Quambalaria coyrecup | WAC12947cde | DQ823431 | DQ823444 | | Corymbia calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. coyrecup | WAC12948de | DQ823433 | DQ823446 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. coyrecup | WAC12949e | DQ823432 | DQ823445 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. coyrecup | WAC12950de | DQ823429 | DQ823447 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. coyrecup | WAC12951de | DQ823430 | DQ823448 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. coyrecup | BRIP48338d | EF444877 | N/Ag | | C. polycarpa | Darwin, Northern Territory, Australia | R Pitkethley | Pegg et al.[24] |
Q. coyrecup | BRIP48339d | EF444878 | N/A | | C. polycarpa | Darwin, Northern Territory, Australia | R Pitkethley | Pegg et al.[24] |
Q. cyanescens | CBS357.73cde = CMW5583 | DQ317622 | DQ317615 | | skin of man | Netherlands | TF Visser | de Beer et al.[22] |
Q. cyanescens | CBS876.73de = CMW5584 | DQ317623 | DQ317616 | | Eucalyptus pauciflora | New South Wales, Australia | VF Brown | de Beer et al.[22] |
Q. cyanescens | WAC12952de | DQ823419 | DQ823440 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. cyanescens | WAC12953de | DQ823422 | DQ823443 | | C. ficifolia | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. cyanescens | WAC12954e | DQ823420 | DQ823442 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. cyanescens | WAC12955de | DQ823421 | DQ823441 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. cyanescens | BRIP48396d | EF444874 | N/A | | Native C. citriodora | Beaudesert, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. cyanescens | BRIP48398d | EF444875 | N/A | | Native C. citriodora | Beaudesert, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. cyanescens | BRIP48403d | EF444876 | N/A | | Native C. citriodora | Beaudesert, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. eucalypti | CBS118844cde = CMW1101 | DQ317625 | DQ317618 | | Eucalyptus grandis | Kwambonambi, South Africa | MJ Wingfield | de Beer et al.[22] |
Q. eucalypti | CBS 119680de = CMW11678 | DQ317626 | DQ317619 | | E. grandis clone NH58 | Kwambonambi, South Africa | L Lombard | de Beer et al.[22] |
Q. eucalypti | CMW14329 | DQ317614 | N/A | | E. grandis× E. camaldulensis clone | Kwambonambi, South Africa | J Roux | Roux et al.[30] |
Q. eucalypti | CBS118615= CMW17252 | DQ317609 | N/A | | E. nitens | Rooihoogte, South Africa | ZL Mthalane & J Roux | Roux et al.[30] |
Q. eucalypti | CMW17253 | DQ317610 | N/A | | E. nitens | Rooihoogte, South Africa | ZL Mthalane & J Roux | Roux et al.[30] |
Q. eucalypti | CMW17254 | DQ317611 | N/A | | E. nitens | Rooihoogte, South Africa | ZL Mthalane & J Roux | Roux et al.[30] |
Q. eucalypti | CMW17255 | DQ317612 | N/A | | E. nitens | Rooihoogte, South Africa | ZL Mthalane & J Roux | Roux et al.[30] |
Q. eucalypti | CBS118616= CMW17771 | DQ317613 | N/A | | E. grandis clone | Kwambonambi, South Africa | J Roux | Roux et al.[30] |
Q. eucalypti | UY1036 | EU439922 | N/A | | Myrceugenia glaucescens | Uruguay | C. A. Pérez | Pérez et al.[28] |
Q. eucalypti | UY1718 | EU439923 | N/A | | M. glaucescens | Uruguay | C. A. Pérez | Pérez et al.[28] |
Q. eucalypti | PE3/MEAN 996 | JX297605 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE6/MEAN 997 | JX297603 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE27/MEAN 998 | JX297604 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE28/MEAN 999 | JX297600 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE29/MEAN 1000 | JX297602 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE30/MEAN 1001 | JX297601 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE52/MEAN 1002 | JX297606 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE53/MEAN 1003 | JX297598 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE54/MEAN 1004 | JX297599 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE93/MEAN 1006 | KR336802 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE96/MEAN 1009 | KR336803 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE151/MEAN 1012 | KR336804 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE152/MEAN 1013 | KR336805 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE153/MEAN 1014 | KR336806 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | PE154/MEAN 1015 | KR336807 | N/A | | E. globulus | Portugal | N/A | Braganca et al.[27] |
Q. eucalypti | BRIP48367 | EF444823 | N/A | | C. torelliana× C. citriodora subsp. variegata | Walkamin, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. eucalypti | BRIP48422d | EF444832 | N/A | | E. dunnii | New South Wales, Australia | AJ Carnegie | Pegg et al.[24] |
Q. eucalypti | BRIP48498d | EF444844 | N/A | | E. grandis | New South Wales, Australia | AJ Carnegie | Pegg et al.[24] |
Q. eucalypti | BRIP48507d | EF444822 | N/A | | E. grandis | Moggill, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. eucalypti | CERC8476d | KY615009 | N/A | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. eucalypti | CERC8477g | KY615010 | N/A | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. eucalypti | CERC8478 | KY615011 | N/A | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. eucalypti | CERC8479g | KY615012 | KY615050 | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. eucalypti | CERC8480g | KY615013 | N/A | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. eucalypti | CERC8481 | KY615014 | KY615051 | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. eucalypti | CERC8482g | KY615015 | N/A | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. eucalypti | CERC8483 | KY615016 | N/A | | E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. pitereka | DAR19773cde | DQ823423 | DQ823438 | | C. eximia | New South Wales, Australia | J Walker & AL Bertus | Paap et al.[23] |
Q. pitereka | CMW 6707de | DQ317627 | DQ317620 | | Corymbia maculata | New South Wales, Australia | MJ Wingfield | de Beer et al.[22] |
Q. pitereka | CBS118828de = CMW5318 | DQ317628 | DQ317621 | | C. citriodora subsp. variegata | Queensland, Australia | M Ivory | de Beer et al.[22] |
Q. pitereka | CMW23610 | EF427372 | N/A | | C. citriodora | Guangdong, China | YJ Xie | Zhou et al.[17] |
Q. pitereka | CMW23611 | EF427373 | N/A | | C. citriodora | Guangdong, China | YJ Xie | Zhou et al.[17] |
Q. pitereka | CMW23612 | EF427374 | N/A | | C. citriodora | Guangdong, China | YJ Xie | Zhou et al.[17] |
Q. pitereka | CMW23613d | EF427375 | N/A | | C. citriodora | Guangdong, China | YJ Xie | Zhou et al.[17] |
Q. pitereka | BRIP48325 | EF427366 | N/A | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Zhou et al.[17] |
Q. pitereka | BRIP48361d | EF427367 | N/A | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Zhou et al.[17] |
Q. pitereka | BRIP48370d | EF427368 | N/A | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Zhou et al.[17] |
Q. pitereka | BRIP48384d | EF427369 | N/A | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Zhou et al.[17] |
Q. pitereka | BRIP48386ed | EF427370 | N/A | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Zhou et al.[17] |
Q. pitereka | BRIP48531d | EF427371 | N/A | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Zhou et al.[17] |
Q. pitereka | WAC12957e | DQ823426 | DQ823437 | | C. ficifolia | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. pitereka | WAC12958e | DQ823427 | DQ823436 | | C. calophylla | Western Australia, Australia | T Paap | Paap et al.[23] |
Q. pitereka | QP26e | DQ823424 | DQ823434 | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Paap et al.[23] |
Q. pitereka | QP45de | DQ823425 | DQ823439 | | C. citriodora subsp. variegata | Queensland, Australia | GS Pegg | Paap et al.[23] |
Q. pitereka | BRIP48346d | EF444845 | N/A | | C. citriodora subsp. citriodora | Davies Creek, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | BRIP48317 | EF444854 | N/A | | C. henryi | Coolabunia, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | BRIP48381d | EF444858 | N/A | | C. citriodora subsp. citriodora | Silkwood, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | BRIP48383d | EF444859 | N/A | | C. citriodora subsp. variegata | Beaudesert, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | WAC12956d | DQ823428 | N/A | | C. ficifolia | Western Australia, Australia | T Paap | Paap et al.[23], Pegg et al.[24] |
Q. pitereka | BRIP48349d | EF444860 | N/A | | C. torelliana × C. citriodora subsp. variegata | Mareeba, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | BRIP48325d | EF427366 | N/A | | C. citriodora subsp. variegata | Binjour, Queensland, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | BRIP48328d | EF444872 | N/A | | Native C. citriodora subsp. variegata | Dilkoon, New South Wales, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | BRIP48432d | EF444873 | N/A | | C. citriodora subsp. variegata | Grafton, New South Wales, Australia | GS Pegg | Pegg et al.[24] |
Q. pitereka | CERC8486de | KY615017 | KY615052 | | C. citriodora provenance CERC10 | Guangdong, China | SF Chen & GQ Li | This study |
Q. pitereka | CERC8488e | KY615018 | KY615053 | | C. citriodora provenance CERC12 | Guangdong, China | SF Chen & GQ Li | This study |
Q. pitereka | CERC8489 | KY615019 | N/A | | C. citriodora provenance CERC13 | Guangdong, China | SF Chen & GQ Li | This study |
Q. pitereka | CERC8491 | KY615020 | N/A | | C. citriodora provenance CERC15 | Guangdong, China | SF Chen & GQ Li | This study |
Q. pitereka | CERC8494eg | KY615021 | KY615054 | | C. citriodora provenance CERC17 | Guangdong, China | SF Chen & GQ Li | This study |
Q. pitereka | CERC9093 | KY615022 | N/A | | C. citriodora provenance CR76 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9094 | KY615023 | N/A | | C. citriodora provenance N371 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9095 | KY615024 | N/A | | C. citriodora provenance N28 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9096 | KY615025 | N/A | | C. citriodora provenance N411 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9097eg | KY615026 | KY615055 | | C. citriodora provenance N223 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9098g | KY615027 | N/A | | C. citriodora provenance N322 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9099eg | KY615028 | KY615056 | | C. citriodora provenance CR033 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9100 | KY615029 | N/A | | C. citriodora provenance CR039 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9101 | KY615030 | N/A | | C. citriodora provenance CR92 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9102 | KY615031 | N/A | | C. citriodora provenance CR36 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9103e | KY615032 | KY615057 | | C. citriodora provenance N601 | Guangdong, China | SF Chen & Y Lin | This study |
Q. pitereka | CERC9104 | KY615033 | N/A | | C. citriodora provenance N28 | Guangdong, China | SF Chen & Y Lin | This study |
Q. simpsonii | CBS 124772de | GQ303290 | GQ303321 | | Eucalyptus tintinnans | Edith Falls, Australia | BA Summerell | Cheewangkoon et al.[26] |
Q. simpsonii | CBS 124773de | GQ303291 | GQ303322 | | Eucalyptus sp. | Lamphoon, Thailand | R Cheewangkoon | Cheewangkoon et al.[26] |
Q. simpsonii | CERC8496dg | KY615034 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8499 | KY615035 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8505d | KY615036 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8507de | KY615037 | KY615058 | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8512d | KY615038 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8514 | KY615039 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8516 | KY615040 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8517e | KY615041 | KY615059 | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8519dg | KY615042 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8526 | KY615043 | N/A | | E. urophylla × E. grandis | Hainan, China | SF Chen & QL Liu | This study |
Q. simpsonii | CERC8532 | KY615044 | N/A | | E. urophylla × E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. simpsonii | CERC8534deg | KY615045 | KY615060 | | E. urophylla × E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. simpsonii | CERC8536e | KY615046 | KY615061 | | E. urophylla × E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. simpsonii | CERC8539eg | KY615047 | KY615062 | | E. urophylla × E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. simpsonii | CERC8541d | KY615048 | N/A | | E. urophylla × E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Q. simpsonii | CERC8543d | KY615049 | N/A | | E. urophylla × E. grandis | Guangdong, China | SF Chen & JQ Li | This study |
Microstroma juglandis | R.B. 2042de | DQ317634 | DQ317617 | | Juglans regia | Germany | R Bauer | de Beer et al.[22] |
2.2 DNA extraction, PCR and sequence reactions
Isolates collected from eucalypt trees in this study were identified based on DNA sequence comparisons (Table 1). For DNA extraction, isolates were grown on 2% MEA at 25°C for 10 d after which actively growing mycelium for each isolate was scraped from the surface of the medium using sterile scalpel blades and transferred to 1.5-mL Eppendorf tubes. DNA was extracted using “method 5” described by Van Burik et al.
[31]. The concentration of resulting DNA was checked using a Nano-Drop 2000 Spectrometer (Thermo Fisher Scientific Inc., Waltham, MA, USA).
Two gene regions, the internal transcribed spacer (ITS) regions including the 5.8S gene of the rDNA operon and the conserved nuclear large subunit (LSU) rDNA were amplified as described by Chen et al.
[32]. Nucleotide sequences were edited using MEGA version 4 software
[33]. All sequences obtained in this study were deposited in GenBank (Table 1).
2.3 Phylogenetic analyses
To identify the isolates, sequences of ITS and LSU gene regions were compared to sequences of all described Quambalaria species, including the ex-type cultures of all the identified species from GenBank (Table 1). Also, in order to examine the diversity of the Quambalaria species, the haplotypes were determined from the polymorphic nucleotides within the aligned sequence data of ITS and LSU regions for isolates collected in this and previous studies.
To characterize the haplotypes from ITS sequences, all haplotypes designated by Pegg et al.
[24] were determined for all isolates of
Quambalaria spp. from this and previous studies (Table 1). For phylogenetic analyses, two isolates representing each haplotype were used. Where only one isolate was available for a particular haplotype, this isolate was duplicated in the phylogenetic analyses to determine whether it would reside in an independent clade.
Microstroma juglandis was used as the outgroup taxon (Table 1).
For haplotype determination using LSU sequences, representative Chinese isolates which included all the haplotypes determined based on the ITS sequences, and all isolates for which the LSU had been sequenced in previous studies were included (Table 1). All isolates used for haplotype determination by LSU sequences were used in the phylogenetic analyses. Where only one isolate was available for a particular haplotype, the isolates were duplicated in the phylogenetic analyses. M. juglandis was also used as the outgroup taxon for the LSU analyses (Table 1).
Sequences in ITS and LSU data sets were aligned using the iterative refinement method (FFT-NS-i settings) of the online platform of MAFFT v. 5.667
[34]. The alignments were further edited manually in MEGA version 4 software
[33]. All alignments were deposited in TreeBASE.
The phylogenetic analyses were conducted using the maximum likelihood (ML) method, the ML tests were conducted with PHYML v. 3.0
[35] and the best models of nucleotide substitution were established with MODELTEST v. 3.7
[36]. The analyses were conducted using PHYML v. 3.0
[35]. Additional ML parameters in PHYML included retention of the maximum number of 1000 trees and the determination of nodal support by nonparametric bootstrapping with 1000 replicates. The phylogenetic trees were viewed using MEGA version 4 software
[33].
2.4 Morphology
Single hyphal tip cultures of each Quambalaria sp. identified using DNA sequence data were subculture on 2% MEA media for 2 weeks at 25°C for morphological analysis. Four isolates for each identified Quambalaria sp. were used for comparisons of colony morphology. Conidiogenous cells and conidia were mounted in sterile water on microscope slides for measurements to be made using a Zeiss Axio Imager A1 microscope and a Zeiss AxioCam MRc digital camera with Zeiss Axio Vision Rel. 4.8 software (Carl Zeiss Ltd., Munchen, Germany). For each isolate, 25 measurements were made of conidia and ten of conidiophores. These measurements were compared with those published for species of Quambalaria. Results are presented as (minimum–) (mean – standard deviation) – (mean+ standard deviation) (–maximum).
3 Results
3.1 Collections of fungal isolates
A total of 41 fungal isolates showing typical morphology of Quambalaria species were isolated. Seventeen isolates were from leaves or shoots on 17 C. citriodora trees of 16 provenances in two experimental plantations in Guangdong Province, eight isolates were from leaves of one E. urophylla× E. grandis clone in one plantation in Guangdong Province, and 16 isolates were from cankers caused by T. zuluensis on the stems of E. urophylla× E. grandis clones in four plantations in Guangdong and Guangxi. Each of the 41 isolates was from a single tree and all were included in the DNA sequence comparisons and phylogenetic analyses (Table 1).
3.2 Phylogenetic analyses
The aligned ITS sequence data set consisted of 65 taxa and 634 characters (TreeBASE No. 20574). For the ML analyses, the Model Test analysis recommended a HKY+ I+ G model [Lset Base= (0.2639, 0.2186, 0.2071); Nst (number of substitution rate categories) = 2; Transition/transversion ratio= 2.6045; Rate matrix= (1.0000, 4.3151, 2.9747, 2.9747, 8.1747); Rates= gamma; Shape= 0.7544]. The phylogenetic analyses showed that isolates sequenced in this study resided in three clades that represent Q. pitereka, Q. eucalypti and Q. simpsonii (Fig. 2).
Fig.2 Phylogenetic tree based on maximum likelihood analysis of ITS sequence data of haplotypes of five Quambalaria species, Q. coyrecup (QCO), Q. cyanescens (QCY), Q. eucalypti (QE), Q. pitereka (QP) and Q. simpsonii (QS). Bootstrap values>60% are presented at branches, bootstrap values<60% or absent values are not shown. Haplotypes and isolates from eucalypts in this study are in boldface and highlighted. Isolates representing ex-type are marked with T, isolates repeated are marked with R. The tree is rooted to Microstroma juglandis. |
Full size|PPT slide
For the ITS sequences, all Chinese and all those from previous studies represented 32 haplotypes. These included three, seven, four, 12 and six haplotypes of Q. coyrecup, Q. cyanescens, Q. eucalypti, Q. pitereka Q. simpsonii, respectively (Tables 2–4, S1). The Chinese isolates collected in this study represented six haplotypes including one of Q. pitereka, one of Q. eucalypti, and four newly designated haplotypes of Q. simpsonii (Table S1).
Tab.2 Four haplotypes of Q. eucalypti as determined from the polymorphic nucleotides within the aligned sequence data of ITS region for isolates collected from species of Eucalyptus, C. torelliana× C. citriodora subsp. variegate and M. glaucescens |
Haplotype | 121a | 158 | 159 | 160 | 161 | 162 | 558 |
---|
QE1 | T | – | – | – | – | – | Tb |
QE2 | T | – | – | – | – | – | C |
QE3 | C | – | – | – | – | – | C |
QE4 | T | T | T | A | T | A | C |
Tab.3 Twelve haplotypes of Q. pitereka as determined from the polymorphic nucleotides within the aligned sequence data of ITS region for isolates collected from species of Corymbia |
Haplotype | 24a | 54 | 107 | 112 | 214 | 219 | 233 | 236 | 390 | 451 | 606 | 614 |
---|
QP1 | T | A | G | G | T | Gb | T | C | C | C | C | A |
QP2 | T | A | G | A | T | G | T | C | C | C | C | A |
QP3 | T | A | G | A | T | A | T | C | C | C | C | A |
QP4 | T | A | G | G | T | A | T | C | T | C | C | A |
QP5 | T | A | G | G | T | A | T | C | C | A | C | A |
QP6 | T | A | G | G | T | A | T | C | C | C | T | G |
QP7 | A | G | G | G | G | A | T | C | C | C | C | G |
QP8 | A | G | G | G | T | A | T | C | C | C | C | G |
QP9 | T | G | G | G | G | A | T | C | C | C | C | G |
QP10 | A | G | A | G | T | A | T | C | C | C | C | G |
QP11 | T | G | G | G | T | A | T | C | C | C | C | G |
QP12 | T | G | G | A | T | G | C | G | C | C | C | A |
Tab.4 Six haplotypes of Q. simpsonii as determined from the polymorphic nucleotides within the aligned sequence data of ITS region for isolates collected from species of Eucalyptus |
Haplotype | 4a | 171 | 553 | 605 | 621 |
---|
QS1 | Aa | A | T | T | – |
QS2 | A | A | C | T | – |
QS3 | G | A | C | T | T |
QS4 | G | A | C | T | – |
QS5 | G | A | C | C | – |
QS6 | G | G | C | C | – |
The aligned LSU sequence data set consisted of 37 taxa and 561 characters (TreeBASE No. 20574). For ML analyses, model test analysis recommended a TrN+ G model [Lset Base= (0.2492, 0.1916, 0.3025); Nst= 6; Rate matrix= (1.0000, 7.7487, 1.0000, 1.0000, 31.1002); Rates= equal]. The phylogenetic analyses showed that isolates sequenced in this study resided in three clades of Q. pitereka, Q. eucalypti and Q. simpsonii, respectively (Fig. 3).
Fig.3 Phylogenetic tree based on Maximum Likelihood analysis of large subunit sequence data of haplotypes of five Quambalaria species, Q. coyrecup (QCO), Q. cyanescens (QCY), Q. eucalypti (QE), Q. pitereka (QP) and Q. simpsonii (QS), respectively. Bootstrap values>60% are presented at branches, bootstrap values<60% or absent values are not shown. Haplotypes and isolates from eucalypts in this study are in boldface and highlighted. Isolates representing ex-type are marked with T, isolates repeated are marked with R. The tree is rooted to Microstroma juglandis. |
Full size|PPT slide
For the LSU sequences, 13 Chinese isolates which included all six haplotypes determined based on ITS sequences were used for phylogenetic analyses. These isolates and all of those sequenced in previous studies represented six haplotypes. These included two haplotypes of Q. pitereka and one each of Q. coyrecup, Q. cyanescens, Q. eucalypti and Q. simpsonii (Table S1). The Chinese isolates included in this study represented three haplotypes including one newly designated haplotype of Q. pitereka, and one haplotype for each of Q. eucalypti and Q. simpsonii (Table S1).
3.3 Morphology
Four isolates of
Q. pitereka (CERC8494, CERC9097, CERC9098 and CERC9099),
Q. eucalypti (CERC8477, CERC8479, CERC8480 and CERC8482) and
Q. simpsonii (CERC8496, CERC8519, CERC8534 and CERC8539) were used in the morphological analysis. Colonies of these species were finely floccose becoming powdery and white (Figs. 4a, 4c and 4e). The morphological characteristics of the fruiting structures of these species are summarized in Table 5 and illustrated in Figs. 4b, 4d and 4f. Conidiogenous cells of
Q. pitereka,
Q. eucalypti and
Q. simpsonii were (7.4–89.6)mm × (1.4–2.6) mm (av. 46.0 mm × 2.0 mm), (8.4–77.1)mm × (1.3–2.8) mm (av. 37.4 mm × 2.2 mm), and (7.0–82.1) mm × (1.5–2.9) mm (av. 25.6 mm × 2.4 mm), respectively. The conidia of
Q. pitereka (primary conidia narrow fusiform, av. 10.9 mm × 3.4 mm, length/width= 3.2; secondary conidia narrow fusiform, av. 6.0 mm × 2.7 mm, length/width= 2.2) are longer and narrower (by length/width) than that of
Q. eucalypti (primary conidia ellipsoid, av. 6.2 mm × 3.8 mm, length/width= 1.6; secondary conidia obovoid, av. 3.3 mm × 2.6 mm, length/width= 1.3) and
Q. simpsonii (primary conidia fusiform, av. 7.9 mm × 3.3 mm, length/width= 2.4; secondary conidia obovoid to ellipsoid, av. 3.7 mm × 2.4 mm, length/width= 1.5), the conidia of
Q. simpsonii are slight longer and narrower than that of
Q. eucalypti. The morphology of
Q. pitereka,
Q. eucalypti and
Q. simpsonii identified in this study is similar to the results of previous studies
[20,
23,
26].
Fig.4 Cultures grown on malt extract agar at 25°C after 2 weeks and the primary and secondary conidia. (a,b) Quambalaria pitereka; (c,d) Q. eucalypti; (e,f) Q. simpsonii. |
Full size|PPT slide
Tab.5 Primary conidial and secondary conidia measurements of three Quambalaria species identified in this study |
Species | Isolate No. | Primary conidia | | Secondary conidia |
---|
(L × W) sizea/mm | (L × W) meanb/mm | L/Wc | | (L × W) sizea/mm | (L × W) meanb/mm | L/Wc |
---|
Q. pitereka | CERC8494 | (7.0–)7.5–13.0(–20.5) × (2.5–)3.0–3.5(–4.0) | 10.2 × 3.3 | 3.1 | | (4.0–)4.5–6.0(–7.0) × 2.0–2.5(–3.0) | 5.2 × 2.5 | 2.1 |
| CERC9097 | (8.0–)8.5–12.5(–15.0) × (2.5–)2.5–3.5(–4.0) | 10.5 × 3.0 | 3.5 | | (4.5–)5.0–6.5(–7.0) × 2.0–2.5(–3.0) | 5.7 × 2.3 | 2.5 |
| CERC9098 | (8.0–)10.5–14.0(–16.0) × (2.0–)3.0–4.5(–5.0) | 12.2 × 3.6 | 3.4 | | 6.0–7.5(–8.0) × (2.0–)2.5–3.5(–4.0) | 6.8 × 3.0 | 2.3 |
| CERC9099 | (8.0–)9.0–12.5(–15.0) × (3.0–)3.5–4.5(–5.5) | 10.7 × 4.0 | 2.7 | | 5.5–7.0(–7.5) × 2.5–3.5(–4.0) | 6.3 × 3.1 | 2.2 |
| Averaged | (7.0–)8.5–13.0(–20.5) × (2.0–)2.5–4.0(–5.5) | 10.9 × 3.4 | 3.2 | | (4.0–)5.0–7.0(–78.0) × 2.0–3.0(–4.0) | 6.0 × 2.7 | 2.2 |
Q. eucalypti | CERC8477 | (4.5–)5.0–7.5(–8.0) × (3.0–)3.5–4.5(–4.5) | 6.2 × 3.9 | 1.6 | | 2.5–3.0(–3.5) × 2.5–3.0 | 3.0 × 2.5 | 1.2 |
| CERC8479 | (5.5–)6.0–7.0(–7.5) × (2.5–)3.0–4.0(–4.5) | 6.3 × 3.7 | 1.7 | | 2.5–3.5(–4.0) × (2.0–)2.5–3.0 | 3.0 × 2.5 | 1.2 |
| CERC8482 | (4.5–)5.0–6.5(–7.0) × (3.0–)3.5–4.0(–4.5) | 5.7 × 3.9 | 1.5 | | 3.0–4.0(–5.0) × 2.5–3.0 | 3.6 × 2.8 | 1.3 |
| CERC8480 | (5.5–)6.0–7.0(–8.0) × (3.0–)3.5–4.0(–4.5) | 6.4 × 3.8 | 1.7 | | 3.0–3.6(–4.0) × 2.5–3.0 | 3.4 × 2.7 | 1.3 |
| Averaged | (4.5–)5.5–7.0(–8.0) × (2.5–)3.5–4.0(–4.5) | 6.2 × 3.8 | 1.6 | | (2.5–)3.0–4.0(–5.0) × (2.0–)2.5–3.0 | 3.3 × 2.6 | 1.3 |
Q. simpsonii | CERC8496 | (6.0–)6.5–9.5(–11.0) × (2.0–)2.5–3.5(–4.0) | 8.3 × 3.1 | 2.7 | | (3.0–)3.5–4.5(–5.0) × 2.0–2.5(–3.0) | 4.0 × 2.4 | 1.7 |
| CERC8519 | (5.5–)6.0–8.0(–9.0) × 3.0–4.0(–4.5) | 7.1 × 3.6 | 2.0 | | (2.5–)3.0–3.5(–4.0) × 2.0–2.5 | 3.3 × 2.3 | 1.4 |
| CERC8534 | (6.0–)7.0–9.0(–10.0) × (2.0–)3.0–3.5(–4.0) | 7.9 × 3.2 | 2.5 | | (3.0–)3.5–4.5(–5.0) × 2.0–3.0 | 4.0 × 2.5 | 1.6 |
| CERC8539 | (5.5–)6.5–10.5(–12.5) × (2.5–)3.0–4.0(–4.5) | 8.4 × 3.4 | 2.5 | | 3.0–4.0(–4.5) × 2.0–3.0 | 3.6 × 2.5 | 1.4 |
| Averaged | (5.5–)6.5–9.5(–12.5) × (2.0–)3.0–4.0(–4.5) | 7.9 × 3.3 | 2.4 | | (2.5–)3.0–4.0(–5.0) × 2.0–2.5(–3.0) | 3.7 × 2.4 | 1.5 |
4 Discussion
In this study, three species of Quambalaria, Q. pitereka, Q. eucalypti and Q. simpsonii, were identified from Eucalyptus and Corymbia plantations in Guangdong and Hainan Provinces in southern China. These Quambalaria spp. were identified and characterized based on phylogenetic analysis of sequence data for LSU and ITS regions, and morphology. This is the first report of Q. eucalypti in Asia and the first report of Q. simpsonii on eucalypts in China.
Quambalaria pitereka is specific to eucalypts in the genus
Corymbia. This fungus is widely distributed in different regions/sites on different species of
Corymbia in Australia
[24,
25]. Outside Australia,
Q. pitereka has previously been reported only on
C. citriodora in one plantation in Guangdong Province
[17]. The results of this study showed that the sequenced isolates of
Q. pitereka include 12 haplotypes, only one of these was found in China and the remaining haplotypes were known only from Australia. This high level of genetic diversity for isolates from Australia supported the view
[24] that
Q. pitereka was native to that country. In the present study,
Q. pitereka was isolated from 17
C. citriodora provenances in two experimental plantations. These are relatively distant from the site where
Q. pitereka was first reported in 2007
[17] and the ITS haplotype was the same as that found in the study of Zhou et al.
[17]. These results suggest that
Q. pitereka could spread actively between different regions and
C. citriodora provenances in China.
Quambalaria eucalypti is considered to be one of the most important pathogens of eucalypts. Outside Australia, this fungus was first reported on
Eucalyptus in nurseries in South Africa
[20] and it was later found in Brazil
[37] and Portugal
[27] where it causes leaf spots, shoot infections and lesions on seedling stems.
Q. eucalypti has also been recorded in
Eucalyptus plantations in Brazil
[38], South Africa
[30], Australia
[24] and Portugal
[27] where it can result in severe shoot and leaf blight and stem cankers
[24,
27,
30]. Other than on
Eucalyptus,
Q. eucalypti has been isolated from leaf lesions on native
M. glaucescens trees in Uruguay
[28] and
Corymbia species in Australia
[24]. In this study,
Q. eucalypti was isolated from a diseased
E. urophylla×
E. grandis clone. It appears to be a pathogen of emerging importance in China.
The ITS haplotype determination showed that all four haplotypes of
Q. eucalypti determined in this study are found in Australia. Only two of the four haplotypes have been found in other countries including China, Portugal, South Africa and Uruguay. Portugal, South Africa and Uruguay share the same haplotype, the other haplotype apart from Australia was only found in China. Results in this study support the view that
Q. eucalypti is native to Australia and that this is the source of introductions to new areas
[24].
Quambalaria simpsonii was first reported from species of
Eucalyptus in Australia and Thailand, but it is unknown whether this is a pathogen
[26]. In the present study,
Q. simpsonii was consistently isolated with
T. zuluensis from cankered
E. urophylla×
E. grandis stems in four sites in Guangdong and Guangxi, China. Whether
Q. simpsonii is pathogenic to
Eucalyptus trees, and the ecological interaction between
Q. simpsonii and
T. zuluensis remains to be clarified.
5 Conclusions
The genus
Quambalaria presently includes six species. Most of these are pathogens that cause leaf and shoot blight, and cankers on
Eucalyptus and
Corymbia. They are considered native to Australia but have been inadvertently introduced into countries of Africa, Asia, Europe and South America. This has most likely occurred via the trade in eucalypt germplasm
[39]. In the present study, three
Quambalaria spp. were identified in China;
Q. pitereka on
C. citriodora,
Q. eucalypti on clones
E. urophylla × E. grandis and
Q. simpsonii isolated from stem cankers of
E. urophylla×
E. grandis caused by
T. zuluensis. These are widespread in areas of China where eucalypts are grown and they are likely to become more important to commercial forestry in the future.
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