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. 2013 Jun 10;4(1):123–131. doi: 10.5598/imafungus.2013.04.01.12

Surveys of soil and water reveal a goldmine of Phytophthora diversity in South African natural ecosystems

Eunsung Oh 1,4, Marieka Gryzenhout 2, Brenda D Wingfield 1, Michael J Wingfield 3, Treena I Burgess 1,3,5,✉
PMCID: PMC3719200  PMID: 23898418

Abstract

Phytophthora species are well-known as destructive plant pathogens, especially in natural ecosystems. It is ironic, therefore, how little is known regarding the Phytophthora diversity in South African natural woody ecosystems. In this study, Phytophthora species were isolated using standard baiting techniques from 182 soil and water samples and these were identified based on ITS and coxI sequence data. The 171 resulting Phytophthora isolates resided in 14 taxa including six known species (P. multivora, P. capensis, P. cryptogea, P. frigida, P. cinnamomi, P. cinnamomi var. parvispora), the known but as yet unnamed Phytophthora sp. PgChlamydo, P. sp. emzansi, and P. sp. Kununurra and five novel taxa referred to as P. sp. stellaris, P. sp. Umtamvuna P. sp. canthium, P. sp. xWS, P. sp. xHennops. Four of the new taxa were found exclusively in water and two of these are hybrids. The most commonly isolated species from soil was P. multivora, a species recently described from Western Australia. Phytophthora frigida was isolated for the first time from stream water. With the exception of P. cinnamomi, very little is known regarding the biology, epidemiology or origin of Phytophthora in South Africa.

Keywords: Oomycetes, Phytophthora, ITS, nrDNA, coxI, Phylogeny, Taxonomy

INTRODUCTION

Less than 2 % of the land surface of South Africa is covered with indigenous forests. The larger part of the country is grassland and dry savanna woodland such as semi-dessert with small shrubs and Acacia trees (Grundy & Wynberg 2001). Savanna woodlands cover 35–40 %, while plantation forests cover 1.5 % of the land area. Before 1940, small privately-owned plantations of Acacia or Eucalyptus species in Western Cape were associated with agriculture to protect crops from wind erosion and subsequent sand drift. After 1945, the Department of Forestry was established to protect indigenous forest by establishing a plantation industry based on non-native species such as Eucalyptus spp. from Australia and Pinus spp. from north and central America (Burgess & Wingfield 2001, Grundy & Wynberg 2001). South Africa is also home to three of the world’s 25 Biodiversity host-spots (http://www.biodiversityhotspots.org) and many studies have been conducted to document and conserve animal and plant biodiversity. In contrast, there has been relatively little work on fungal biodiversity (Crous et al. 2006, Marincowitz et al. 2008) and almost nothing is known regarding the endemic Oomycetes, which are broadly treated with the fungi.

Several common Phytophthora species have been recovered from agricultural landscapes in South Africa, notably P. cinnamomi, P. cactorum, P. citrophthora, P. citricola, P. megasperma, P. cryptogea, P. drechsleri, P. infestans, P. nicotianae, P. syringae, and P. porri (Crous et al. 2000). Eight Phytophthora spp. have been recovered from plantations of non-native species, mainly located in KwaZulu-Natal, Eastern and Western Cape, and Mpumalanga. These include P. boehmeriae, P. cinnamomi, P. cryptogea, P. nicotianae, P. meadii, P. frigida, and P. alticola (Zeijlemaker 1971, Bumbieris 1976, Wingfield & Knox-Davies 1980, Linde et al. 1994, Roux & Wingfield 1997, Maseko et al. 2001, Maseko et al. 2007). All the Phytophthora species commonly found in agriculture and forestry are considered introductions to South Africa. Phytophthora alticola and P. frigida are the only species known exclusively from South Africa, and they could be endemic to the region.

The species most studied from natural ecosystems in South Africa is the devastating pathogen P. cinnamomi (von Broembsen 1984a, von Broembsen & Kruger 1985). It is also commonly recovered from dying Proteaceae, including commercially cultivated members such as Protea spp., Leucodendron spp., and Leucospermum spp., mostly in the Cape Province (Knox-Davies 1975, von Broembsen 1984b, von Broembsen & Kruger 1985).

In 2010, P. capensis and P. sp. emzansi1 were identified from the cultivated endemic shrubs Agathosma betulina, Olea capensis, and Curtisia dentate, and also stream water, in Cape Province (Bezuidenhout et al. 2010). The original isolates of P. capensis had been reported as “P. citricola complex” (CIT4) in an earlier study (Oudemans et al. 1994). Additionally, P. cinnamomi, P. cinnamomi var. parvispora, P. citricola, P. cryptogea, P. dreschsleri, P. multivora, P. nicotianae, and P. plurivora were identified on diseased Agathosma spp. in commercial fields and nurseries (Bezuidenhout et al. 2010). In a recent study, P. sp. PgChlamydo and several hybrid species have recently been reported from a stream within a botanical garden in Gauteng (Nagel et al. 2013b). Other than the latter two studies and the considerable body of literature on the impact of P. cinnamomi in natural and managed ecosystems in South Africa, there have been no recent studies examining the diversity, biology or impact of Phytophthora species in natural ecosystems. The aim of the present study was thus to broaden our knowledge of the genus in the country by collections of the genus from such environments.

MATERIALS AND METHODS

Sampling and isolation

Sampling was conducted in five provinces of South Africa in different climatic zones (Table 1, Fig. 1): Mpumulunga (MP; sub-tropical climate), 26 soil samples and 3 water samples from natural vegetation (one soil sample was from a Eucalyptus plantation); Gauteng (GT; temperate climate, over 2000 m elevation), 4 water samples from a botanical garden; Western Cape (WC; Mediterranean climate), 6 soil samples and 2 water samples from natural vegetation; Eastern Cape, Umtamvuna Nature Reserve (UM; temperate climate), 21 soil samples and 6 water samples for filtering from natural vegetation; KwaZulu-Natal, Pietermaritzburg (PMB; temperate climate), 16 soil samples, 12 water samples for filtering and 13 water samples for baiting from a botanical garden; and KwaZulu-Natal, Ingeli Forest Reserve (ING; sub-tropical climate), 52 soil samples, 9 water samples for filtering and one water sample for baiting from natural forest.

Table 1. Isolates of Phytophthora species collected from soil and water in this study.

Province Location Source No. samples No. +ve samples No. isolates
Mpumulunga Lydenburg Forest soil 15 3 5
Schagen Stream water (baiting) 3 2 2
Schagen Soil near stream 9 2 3
Schagen Forest soil 1 1 1
Jonkershoek Forest soil 5 2 2
Jonkershoek Stream water (baiting) 1 0 0
Western Cape Betty’s Bay, Harold Potter NBG Garden soil 2 2 3
Betty’s Bay, Harold Potter NBG Stream water (baiting) 1 0 0
Gauteng Roodepoort, Crocodile, River, Walter Sisulu NBG Stream water (baiting) 2 2 10
Centurion, Hennops River Stream water (baiting) 2 2 5
Kwa Zulu Natal Pietermaritzburg Stream water (filtering) 13 8 25
Pietermaritzburg Stream water (baiting) 13 7 14
Pietermaritzburg Soil 16 13 25
Kwa Zulu Natal Ingeli Forest Stream water (filtering) 9 5 9
Ingeli Forest Stream water (baiting) 8 1 1
Ingeli Forest Soil 58 22 30
Eastern Cape Umtamvuna Stream water (filtering) 6 3 7
Umtamvuna Soil 23 15 29
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Fig. 1.

Fig. 1.

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Diversity and distribution of Phytophthora species from six sampling sites in South Africa.

For soil baiting, 2–300 g of soil was placed in a container (12 × 22 cm stainless steel, Sunnex, UK) containing 800 mL of non-sterile distilled water. Floating litter was removed, and two intact and edge-excised Rhododendron (R. indioum Claude Goyet) and pear leaves were floated on the surface of water for up to 7 d until lesions appeared. The margin of the necrotic regions was excised and cut into to small pieces (5 × 5 mm) and placed onto Phytophthora selective medium, NARPH (Hüberli et al. 2000). The plates were incubated at room temperature, of approximately 22 °C for 3–7 d, and mycelium on the plates was transferred to cornmeal agar (CMA).

Water samples (1 L) were baited in the laboratory using a technique modified from Jung et al. (1996), where stream water was placed in a 12 × 22 cm stainless steel container (Sunnex, UK), baited with Rhododendron indioum leaves and whole pear and apple fruits (previously washed and surface-sterilized with 95 % ethanol). The leaves were collected after 3–4 d when necrotic symptoms were visible, and the fruits after 7 d. The baits were rinsed with sterilized dH2O and placed on paper towels to remove excess water, sterilized in 95 % ethanol for 10–20 s, rinsed in sterilized dH2O and dried with paper towel. Sections containing lesions were then excised and plated onto NARPH medium and purified as described above. Other water samples were filtered shortly after collection, through a 47 mm circle filter paper with 0.45 μm pore size (Whatman™, Kent, UK) using a filtering funnel and glass flask connected to a vacuum pump. Filters were then placed topside down onto the surface of NARPH medium for 2 d, after which they were removed and individual colonies were transferred to new plates.

Single hyphal tips of all putative Phytophthora spp. from the isolations using the various techniques were transferred to V8 agar. After purification, they were stored in the culture collection (CMW) of the Forestry and Agricultural Biotechnology Institute at the University of Pretoria.

Identification of Phytophthora species

Mycelium of isolates grown in 10 % V8 broth was harvested, washed with sterile distilled water, removed of excess water with filter paper, placed in a 2 mL microfuge tubes, and lyophilised with VirTris Advantage BenchTop Tray Lyophilizer (SP Scientific, UK) overnight. The dried mycelium was then transferred to new microfuge tubes with two 3 mm metal beads. Extraction of total genomic DNA and amplification of target genes by polymerase chain reaction was carried out using a modification of the protocol described by Winton & Hansen (2001).

The Internal Transcribed Spacer regions of the rDNA (ITS1, 5.8S, and ITS2) were amplified using the primers ITS6 (Cooke & Duncan 1997) and ITS4 (White et al. 1990) and the cytochrome oxidase subunit I (coxI) was amplified using the primers FM84 and FM83 (Martin & Tooley 2003) with annealing temperatures of 55 °C and 50 °C respectively. Amplified DNA was purified with a high pure PCR product purification kit (Roche, RSA) and sequenced with the same primers. Cloning was carried out using pGEM-T® Easy vectors (Promega, USA) following manufacturer’s instructions when the sequences of the isolates could not be read due to DNA polymorphism.

Sequences of the isolates were uploaded and aligned in Geneious v. R6 (Biomatters; available from http://www.geneious.com/). The most appropriate substitution model was determined using jModelTest (Posada 2008). The TIM3+G (ITS) and GTR+I+R (coxI) model were selected and used in the Bayesian analysis (Ronquist & Huelsenbeck 2003). All sequences for the isolates considered in this study were submitted to GenBank and given in Fig. 2–3.

Fig. 2.

Fig. 2.

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A phylogram based on ITS sequence data indicating the placement of the 14 Phytophthora species recovered in this study in relation to closely related taxa. Numbers in circles represent the Clade as designated by Cooke et al. (2000). Numbers above the branch represent the bootstrap support based on parsimony analysis.

Fig. 3.

Fig. 3.

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Phylograms based on coxI sequence data indicating the placement of undescribed Phytophthora taxa recovered in this study in relation to closely related taxa in (A) Phytophthora Clade 6 and (B) Phytophthora Clade 9. Bootstrap support is given above the line. Numbers above the branch represent the bootstrap support based on parsimony analysis.

RESULTS

Isolation

Isolation success varied between sites and the methods used (Table 1); soil samples from the Western Cape, Mpumulunga, Ingeli Forest Reserve, Umtamvuna and Pietermaritzburg yielded a success rate of 100, 28, 38, 65 and 81 % respectively. Isolation success from water-baited samples in the Western Cape, Mpumulunga, Gauteng, Ingeli Forest Reserve, and Pietermaritzburg gave a success rate of 0, 50, 100, 12.5 and 53.8 % respectively. Isolation by water filtering from Ingeli Forest Reserve, Umtamvuna and Pietermaritzburg gave success rates of 55 %, 50 % and 61 % respectively. In total, 171 Phytophthora isolates were recovered; 98 from soil, 32 from water baiting and 41 from water filtering (Table 1).

Identification of Phytophthora isolates

ITS sequence data were obtained for all isolates, and their identity confirmed by firstly conducting BLAST searched in GenBank (www.ncbi.nlm.nih.gov/genbank/) and secondly by alignment to sequences of type isolates from original publications or, if these were unavailable, to the representative isolates selected for the oomycete barcode paper of Robideau et al. (2011). A maximum of three sequences per taxa were selected for inclusion in the complete ITS phylogenetic analysis (TreeBASE 14082). There were three taxa for which the ITS could not be directly sequenced; one group residing in Clade 6 and two in Clade 9 of the phylogeny (Fig. 2). In each case, the ITS product of representative isolates from each group were cloned and 10 cloned fragments sequenced (11 isolates of P. sp. xWS, 8 isolates of P. sp. xHennops and 3 isolates of P. sp. stellaris). These were then aligned to known taxa and ITS alleles representing each of the taxa were selected for inclusion in the complete ITS phylogenetic analysis.

The aligned ITS dataset consisted of 945 characters of which 492 were parsimony informative. Analysis resulted in 24 trees of 1887 steps (CI = 0.54, RI = 0.91) (Fig. 2). Fourteen Phytophthora spp. were identified from amongst the 173 isolates (Table 1, Fig. 2). Of these, six were of known species (P. multivora, P. capensis, P. frigida, P. cinnamomi, P. cinnamomi var. parvispora, and P. cryptogea), three species matched previously designated taxa (P. sp. emzansi, P. sp. PgChlamydo, P. sp. Kununurra) and five taxa did not correspond to any known species and are designated here as P. sp. xWS, P. sp. stellaris, P. sp. xHennops, P. sp. Umtamvuna and P. sp. canthium.

For three of the unknown taxa, P. sp. xWS, P. sp. xHennops and some isolates of P. sp. stellaris, direct sequencing of the ITS region failed. After cloning of ITS amplicons, each of these species yielded at least ITS alleles corresponding in the phylogenetic analysis to other taxa. For P. sp. xWS, alleles corresponding to P. thermophila and P. amnicola in Clade 6 were obtained (12 SNPs). For P. sp. xHennops, alleles corresponding to P. hydropathica and an unknown species in Clade 9 were obtained (24 SNPs). For P. sp. stellaris, direct sequencing was not possible due to a 1bp indel in one of the ITS alleles, however the remaining variation (3 bp) between the ITS alleles was considered to be within the range of intraspecific variation. P. sp. stellaris is most similar to P. insolata but differs by 36 bp (4.4 %), P. sp Umtamvuna differs from P. hydropathica by 23 bp (2.55 %) and from P. sp. Kununurra by 19 bp (3.05 %) and P. sp. canthium differs from P. kernoviae by 42 bp (5.1 %). In the phylogenetics analysis Clade 9, separates into four sub-clades (Fig. 2).

coxI sequence data were obtained for most isolates and those of P. multivora, P. capensis, P. cryptogea, P. frigida, P. cinnamomi, P. cinnamomi var. parvispora and P. sp. emzansi returned 100 % matches to corresponding species in Blast searches on GenBank (data not shown). Phylogenic analyses was conducted including all related species in Clade 6 (Nagel et al. 2013), and those for which sequence data was available from Clade 9 (Fig. 3). All isolates designated as P. sp. stellaris had identical coxI alleles. Isolates designated as P. sp. xWS based on ITS sequence data had coxI alleles corresponding to either P. thermophila or P. amnicola. Isolates designated as P. sp. xHennops had coxI alleles corresponding to either P. sp. Kununurra or P. hydropathica. The latter two taxa, P. sp. xWS and P. sp. xHennops are considered to be hybrids and are designated as such by the use of the “x”.

Distribution of Phytophthora isolates

With the exception of three isolates of Phytophthora multivora recovered from dying Rapanea collected in the Harlod Porter Botanical Garden in Western Cape Province, all other isolates were recovered from soil associated with asymptomatic plants or from water (Table 2, Fig. 1). Phytophthora multivora was the most frequently isolated species (40 % of all isolates) and was recovered from all locations except GT (Fig. 1). It was almost always recovered from the soil, except for three isolates recovered from filtered water (Table 2). P. cinnamomi (9.25 % of the isolates) was also recovered only from soil in UM, PMB and MP (Table 2, Fig. 1). Of the other known species, P. capensis (4.6 % of the isolates) was recovered from soil at PMB, UM and ING and once from filtered water in ING, P. cryptogea was recovered once from soil in ING and P. cinnamomi var parvispora was recovered once from filtered water in UMT (Table 2, Fig. 1).

Table 2.Distribution of Phytophthora species across sampling substrates and locations.

Locality Substrate Phytophthora multivora Phytophthora capensis Phytophthora sp. emzansi Phytophthora sp. xWS Phytophthora sp. PgChlamydo Phytophthora frigida Phytophthora cinnamomi Phytophthora cinnamomi var parvispora Phytophthora cryptogea Phytophthora sp. stellaris Phytophthora sp. Kununurra Phytophthora sp. Umtamvuna Phytophthora sp. xHennops Phytophthora sp. canthium
Ingeli Forest (ING) Soil 21 5 2 1 1
Water bait 1
Water filter 2 1 3 3
Umtamvuna (UTM) Soil 15 1 12 1
Water filter 1 1 5
Pietermaritzburg (PMB) Soil 20 1 1 2 1
Water bait 11 1 1 1
Water filter 1 15 3 2 4
Western Cape (W C) Soil 5
Mpumulunga (MP) Soil 4 1 1 2 1
Water bait 2
Gauteng (GT) Water bait 8 3 4
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Of the previously designated taxa, P. sp. emzansi (2.9 % of the isolates) was recovered only from Ingeli forest, where it was found in both soil and filtered water, P. sp. PgChlamydo (5.2 % of the isolates) was recovered from ING, PMB and MP, predominantly from water, but the isolate from MP was from soil on a riverbank (Table 2, Fig. 1). An isolate with a 100 % ITS sequence match to P. sp. Kununurra was recovered once from soil in MP.

The remaining isolations, with the exception of the isolate designated as P. sp. canthium from Umtamvuna, were of previously undescribed taxa recovered from water either through baiting or filtering (Table 2). Phytophthora sp. stellaris (4 % of the isolates recovered from MP and PMB) and P. sp. Umtamvuna (rarely recovered in UM), both represent novel species residing in ITS Clade 9. Hybrid taxon P. sp. xWS (20 % of the isolates) was recovered from PMB and GT and P. sp. xHennops was recovered from UMT, PMB and GT (Table 2, Fig. 1).

DISCUSSION

Fourteen Phytophthora taxa were isolated from soil and water associated with asymptomatic vegetation in natural ecosystems of South Africa. Six of the taxa were of the known species, P. multivora, P. capensis, P. frigida, P. cinnamomi, P. cinnamomi var. parvispora, and P. cryptogea, and three match previously informally designated taxa, P. sp. emzansi, P. sp. PgChlamydo, P. sp. Kununurra. The remaining five taxa did not correspond to any known species. Two of these taxa, found exclusively from water sampling, are thought to be hybrids.

Phytophthora multivora is a species recently described causing disease in natural ecosystems in Western Australia where it has a wide distribution and host range and is a pathogen of Eucalyptus spp., Banksia spp., and Agonis flexuosa (Burgess et al. 2009, Scott et al. 2009). This species was previously misidentified as P. citricola (Burgess et al. 2009) and in Western Australia it has a wider distribution within natural ecosystems than P. cinnamomi (Burgess et al. 2009, Scott et al. 2009). It is also the dominant species in the urban environment on numerous hosts in Myrtaceae and Proteaceae (Barber et al. 2012). The variability within the coxI region led Scott et al. (2009) to hypothesize that P. multivora was endemic to Western Australia. However, similar variability was seen among isolates from South Africa in this study. Additionally, P. multivora was routinely isolated from the rhizosphere of non-symptomatic vegetation in South Africa, while in Australia it is associated with dead or dying vegetation. This is obviously an important species and further studies should be undertaken to determine its origin.

Phytophthora capensis and P. sp. emzansi have been recognized only recently from cultivated endemic plant species in the Western Cape (Bezuidenhout et al. 2010). The recovery of these species in other locations in South Africa shows they have a wider distribution within the region and additional isolates of P. sp. emanzsi will facilitate its formal description. Both species are related to P. multivora, and their presence in soil from natural forests where the vegetation was asymptomatic suggests they are probably endemic in South Africa.

Phytophthora frigida was first recovered from diseased roots or the rhizosphere of dying Eucalyptus in South Africa (Maseko et al. 2007). This species was not highly pathogenic to Eucalyptus when compared to P. cinnamomi, a known and serious root pathogen of Eucalyptus in South Africa (Linde et al. 1994). However, it may be a potential threat to other plants in the native vegetation, plantations or in agriculture due to the presence of inoculum in waterways. To date this species has not been recovered elsewhere in the world and it could be endemic to southern Africa. Interestingly, a recently described species from Western Australia, P. elongata, highly pathogenic to young Eucalytus marginata, is the closest relative of P. frigida (Rea et al. 2010).

Since the first report of P. cinnamomi in South Africa in 1933, this species has been the most widely studied Phytophthora species in the country. It is also the most destructive species in native vegetation of the Western Cape Province and in forestry plantations and fruit orchards widely distributed in South Africa (von Broembsen 1984a, 4b, Linde et al. 1994). Thus, the isolation of P. cinnamomi in this study was not surprising. Phytophtora cryptogea, although rarely encountered in this study has also been commonly isolated in agricultural systems in South Africa (Crous et al. 2006, Nagel et al. 2013a).

Phytophthora sp. PgChlamydo has been recovered from stream water, soil, dying plants in many parts of the world including countries of Europe, North and South America, Australia and South Africa (Brasier et al. 2003, Greslebin et al. 2005, Burgess et al. 2009, Reeser et al. 2011, Nagel et al. 2013b, Hüberli et al. 2013). It is morphologically very similar to P. gonapodyides and differs only in its production of chlamydospores. Both species are frequently present in waterways and it is considered a weak pathogen and litter decomposer (Brasier et al. 2003, Jung et al. 2011).

Phytophthora sp. xWS differs from all known species or designated taxa in ITS Clade 6 (Jung et al. 2011). Polymorphism is observed in the ITS sequence data and two separate coxI alleles are obtained, one of which corresponds to P. thermophila and the other corresponds to P. amnicola; both these species have been described recently from Western Australia (Jung et al. 2011, Crous et al. 2012). Phytophthora sp. xWS appears to match a stable hybrid recently characterized from both Australia and South Africa (Hüberli et al. 2013, Nagel et al. 2013b).

One isolate designated as P. sp. canthium was recovered from soil in Umtamvuna Nature Reserve. This isolate is interesting because, based on ITS and cox1 sequence data, it resides in Clade 10. This is a sparsely populated Clade, basal to the Phytophthora phylogeny, presently comprising of only four species, P. morindae, P. kernoviae, P. gallica, and P. boehmeriae. Phytophthora boehmeriae is a species with a global distribution, including South Africa (Roux & Wingfield 1997). The other species in this Clade have a limited geographic distribution, with P. kernoviae being an invasive and damaging pathogen on ornamental and wild plant species in the UK (Brasier et al. 2005).

Four undescribed taxa found in this study reside in ITS Clade 9; one is an exact match for P. sp. Kunnunara, P. sp Umtamvuna is closely related to P. hydropathica and P. sp. stellaris resides in the sub-clade containing P. insolata and P. polonica. The remaining taxon, P. sp. xHennops, appears to be a hybrid; it has two ITS alleles, one of which is an exact match for the type isolate of P. hydropathica. There are also two alleles of the coxI among isolates of P. sp. xHennops (i.e. each isolate only has one coxI allele but was designated as P. sp. xHennops based on having two distinct ITS alleles), one is identical to P. hydropathica, the other to P. sp. Kununurra. Several species belonging to ITS Clade 9 have recently been described from irrigation water (Hong et al. 2008, Hong et al. 2010), however, the pathogenicity of those species is unknown and, like many Clade 6 Phytophthoras, they may be saprophytes of green litter (Brasier et al. 2003, Jung et al. 2011).

Phytophthora sp. stellaris has a single coxI allele, but two ITS alleles. Similarly, P. amnicola returned single alleles for five gene regions, while two ITS alleles, differing by a single indel of 5bp, were obtained (Crous et al. 2012). For P. sp. stellaris, an indel in the ITS allele of some isolates of P. sp. stellaris precluded direct sequencing, however the alleles differed by only by 3–5b p and we consider this to represent intraspecific variation.

This study has contributed considerably to the knowledge of Phytophthora species associated with natural vegetation in South Africa. Given that the relatively few locations considered resulted in a large number of undescribed taxa, additional surveys will undoubtedly reveal an even more substantial Phytophthora biodiversity in South Africa.

Acknowledgments

We are grateful to the Department of Science and Technology (DST)/National Science Foundation (NRF) Centre of Excellence in Tree Health Biotechnology (CTHB) for financial assistance to undertake this study. We also acknowledge support from the University of Pretoria that provided a post-doctoral fellowship for E. O. Various students and colleagues provided technical support, particular regarding the collections of samples and we specially acknowledge Jan Nagel and Hugh Glen in this regard. We kindly thank Chuan Hong and Patricia Richardson for providing coxI sequence data for several Phytophthora aquimorbida, P. hydropathica, P. irrigate, and P. parsiana.

Footnotes

1Informal names have been used in the past for some species discussed here, and also for some that are newly reported. This practice is adopted pending fuller information being obtained, and formal names will be introduced where appropriate in a future publication

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