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. 2016 Oct 3;10:85–88. doi: 10.1016/j.gdata.2016.09.013

Genome sequences of six Phytophthora species threatening forest ecosystems

Nicolas Feau a,, Greg Taylor b, Angela L Dale a,c, Braham Dhillon a, Guillaume J Bilodeau d, Inanç Birol b,e, Steven JM Jones b,e,f, Richard C Hamelin a,g,⁎⁎
PMCID: PMC5061060  PMID: 27752469

Abstract

The Phytophthora genus comprises of some of the most destructive plant pathogens and attack a wide range of hosts including economically valuable tree species, both angiosperm and gymnosperm. Many known species of Phytophthora are invasive and have been introduced through nursery and agricultural trade. As part of a larger project aimed at utilizing genomic data for forest disease diagnostics, pathogen detection and monitoring (The TAIGA project: Tree Aggressors Identification using Genomic Approaches; http://taigaforesthealth.com/), we sequenced the genomes of six important Phytophthora species that are important invasive pathogens of trees and a serious threat to the international trade of forest products. This genomic data was used to develop highly sensitive and specific detection assays and for genome comparisons and to make evolutionary inferences and will be useful to the broader plant and tree health community. These WGS data have been deposited in the International Nucleotide Sequence Database Collaboration (DDBJ/ENA/GenBank) under the accession numbers AUPN01000000, AUVH01000000, AUWJ02000000, AUUF02000000, AWVV02000000 and AWVW02000000.

Keywords: Invasive species, Oomycetes, Forest health


Specifications
Organism/cell line/tissue Six Phytophthora species, see Table 1.
Sex Not applicable
Sequencer type or array Illumina Hi-Seq
Data format Analyzed; i.e. raw data filtered and assembled
Experimental factors Genomic sequence of pure microbial cultures
Experimental features Genomic sequence of pure microbial cultures
Consent Not applicable. Data are available without restriction
Sample source location Various; see Table 1

1. Direct link to deposited data

http://www.ncbi.nlm.nih.gov/bioproject/PRJNA190823

http://www.ncbi.nlm.nih.gov/bioproject/PRJNA190824

http://www.ncbi.nlm.nih.gov/bioproject/PRJNA190825

http://www.ncbi.nlm.nih.gov/bioproject/PRJNA190826

http://www.ncbi.nlm.nih.gov/bioproject/PRJNA190827

http://www.ncbi.nlm.nih.gov/bioproject/PRJNA190828

2. Experimental design, materials and methods

Woodlands and trees are under serious threat from an increasing number of Phytophthora species [1]. Several species of these fungus-like microorganisms may attack over 100 different host species and possess the ability to infect woody tissues, making them potentially destructive in plantations and native forest ecosystems worldwide [2], [3]. Early detection, monitoring and surveillance are important aspects in preventing such outbreaks but are hindered by a lack of genomic resources. Genome sequencing and comparisons should help to develop biosurveillance tools and to predict pathogenic outcome of the interaction of these microorganisms and their host.

Here, we present the draft genome sequence of six Phytophthora species threatening trees, which were selected on the basis of their potential to cause significant economic losses and large-scale damage to forest ecosystems. Phytophthora lateralis is an invasive pathogen that infects Port Orford Cedar (Chamaecyparis lawsoniana) and has spread throughout the natural range of the tree [2], [4]. P. lateralis is a sister species of P. ramorum, a species that has been responsible for the deaths of millions of trees in North America and Europe as a result of Sudden Oak Death and Sudden Larch Death [1], [5], [6]. The P. lateralis epidemic has affected both the wood export market as Port Orford Cedar is a valued species in foreign markets as well as the nursery trade as it is also a valued horticultural species [2]. Phytophthora alni sp. alni, the cause of Alder decline has been a serious threat to riparian ecosystems in Europe over the last 20 years [7]. The emergence of this disease is linked to an interspecific hybridization event, as P. alni subsp. alni. P. alni subsp. uniformis and P. alni subsp. multiformis, initially identified as genetic variants of P. alni sp. alni [8], were shown to be the parental species of the more aggressive hybrid P. alni sp. alni [9]. Phytophthora kernoviae first found in 2003 in the UK, primarily causes bleeding stem lesions on Fagus sylvatica and foliar and stem necrosis on Rhododendron ponticum, but has also been found on other hosts [10]. Phytophthora cambivora originally associated with Castanea species is a widespread root and canker pathogen of many woody hosts, but is most problematic on hardwoods in Europe, in particular on European beech and European chestnut [11], [12], [13]. Phytophthora pinifolia was first described in Chile and caused widespread disease on the needles and shoots of Pinus radiata [14]. Phytophthora cryptogea is a widespread pathogen of numerous ornamental hosts infecting roots, stems and leaves, and is an important pathogen in the nursery industry often isolated during surveys of infected plant material [15].

Genome assemblies were obtained by generating paired-end Illumina reads using the Hiseq 2000 platform at Canada's Michael Smith Genome Sciences Centre or GSC (Vancouver, Canada). For each species, DNA was extracted from pure culture using the DNA extraction procedure of Moller et al. [16]. Two genomic DNA libraries with fragment size of approximately 250 bp and 800 bp were constructed according to British Columbia Cancer Agency Genome Sciences Centre's tube-based paired-end library protocols. One μg of high molecular weight genomic DNA was sonicated (Covaris E210) in 60 μL volume to 200-300 bp. The DNA fragments were end-repaired, phosphorylated and bead purified in preparation for A-tailing. Illumina sequencing adapters were ligated overnight at 16 °C. Adapter ligated products were bead purified and enriched with 10 cycles of PCR using primers containing a hexamer index that enables library pooling. Paired-end 100 base reads were sequenced per pool in a single lane of an Illumina HiSeq2000 instrument.

Illumina chastity failed reads were removed, and the remaining reads were filtered by looking for exact read matches against Penicillium chrysogenum (GCA_000710275.1, GCA_000523475.1, GCA_000816005.1 and GCA_000801355.1) and P. marneffei (GCA_000001985.1, GCA_000227055.2 and GCA_000750115.1) genome sequences to eliminate commensal fungi contaminants. Each library was assembled into contigs using ABySS and a range of k-values from 32 to 96. ABySS was also used to scaffold the contigs, taking care to minimize the duplication of highly repeated sequences that can proliferate on the ends of scaffolds. The best assembly was then selected based on genome size and contiguity (best N50). Completeness of the genome assemblies was assessed using BUSCO (Benchmarking Universal Single-Copy Orthologs).

Raw sequence data and the sets of gene and protein models are available using the GenBank and Sequence Read Archive (SRA) accession numbers listed in Table 2. Genome assembly statistics obtained for P. kernoviae and P. lateralis were in the range of those obtained for Illumina de novo assemblies of two same species (P. kernoviae [n = 5], assembly size: 40.3 Mbp ± 3.0; N50: 61,035 ± 2195; length of longest scaffold: 796,176 bp ± 284,587 bp. P. lateralis [n = 4], assembly size: 50.6 Mbp ± 4.8; N50: 22,373 bp ± 6314; length of longest scaffold: 300,607 bp ± 247,251) (Table 2) [17]. Sequencing completeness was estimated using BUSCO based on a set of 429 single-copy ortholog genes common to Eukaryotes [18]. For the P. alni sp. alni assembly, quality control values were largely under those obtained for the other species with an assembly size twice the expected value of 114 Mbp [19] and a N50 under 3Kb (Table 2). Only 299 (69.0%) out of the 429 eukaryotic BUSCOs were found in this genome; a majority of these were fragmented and duplicated BUSCOs (121 fragmented and 61 duplicated; 60.9%), illustrating the difficulty to obtain an accurate de novo assembly for this homoploid hybrid species [19] (Table 2; Fig. 1A). With 344 (80.2%) to 355 (82.8%) BUSCO genes found all the other genomes (Table 2; Fig. 1), assemblies looked complete relative to the published Phytophthora and Oomycete de novo assemblies (Table 2; Fig. 1) [17], [20], [21], [22].

Table 2.

Assembly statistics and gene content for the genome sequences reported in this study.

Species Isolate Genome assembly accession # Total size (Mbp) Genome coverage # of scaffolds N50 (bp) Length of longest scaffold (bp) BUSCO coverage
P. alni sp. alni CBS_117376 GCA_000439335.1 236.0 113.0 × 118,474 2791 47,541 299 (69.0%)
P. cambivora CBS_114087 GCA_000443045.1 230.6 163.0 × 72,332 4693 76,007 354 (82.5%)
P. cryptogea CBS_418.71 GCA_000468175.2 63.8 345.0 × 19,533 12,607 234,588 347 (80.9%)
P. kernoviae CBS_122049 GCA_000448265.2 39.4 474.0 × 5026 64,601 435,012 344 (80.2%)
P. lateralis CBS_168.42 GCA_000500205.2 52.4 470.0 × 9039 23,425 178,165 353 (82.3%)
P. pinifolia CBS_122922 GCA_000500225.2 94.6 470.0 × 36,928 8087 93,857 355 (82.8%)

Fig. 1.

Fig. 1

Genome completeness (BUSCO results) for six Phytophthora genomes. Searches for single-copy Eukaryote orthologs (n = 429) were conducted following Augustus gene predictions. A) Comparison of the six Illumina genomes with published genome assemblies of P. ramorum (GCA_000149735.1) and P. sojae (GCA_000149755.2). B) Comparison of the P. kernoviae and P. lateralis assemblies obtained in this study with five P. kernoviae (GCA_000333075.2, GCA_000333095.2, GCA_000333115.2, GCA_000785725.2 and GCA_000785735.2) and four P. lateralis (GCA_000318465.2, GCA_000333055.2, GCA_000338795.2 and GCA_000338815.2) Illumina assemblies downloaded from NCBI.

These genomic data were used to develop highly sensitive and specific detection assays that will have applications in biosurveillance of potentially invasive threats [23]. These genomes complete an initial collection of forest-related Phytophthora species [17], [21], [24] and will be used in comparative studies in conjunction with transcriptomic data, to identify factors related to epidemic traits such as the capacity to attack woody tissues and multiple host species.

Table 1.

Phytophthora species and isolates sequenced.

Species Isolate Host Location
Phytophthora alni sp. alni CBS_117376 Alnus sp., roots Hungary
P. cambivora CBS_114087 Abies procera Oregon, USA
P. cryptogea CBS_418.71 Gerbera sp. The Netherlands
P. kernoviae CBS_122049 Rhododendron sp. United Kingdom
P. lateralis CBS_168.42 Chamaecyparis lawsoniana Oregon, USA
P. pinifolia CBS_122922 Pinus radiata, needles Arauco, Chile

Acknowledgments

We would like to acknowledge members of the TAIGA team at UBC Vancouver Hesther Yueh, Stéphanie Beauseigle, Padmini Herath and from CFIA team Debbie Shearlaw, Miranda Newton for their help with this project. This work was funded by Genome Canada, Genome British Columbia, the Canadian Forest Service (Genomics Research and Development Initiative, GRDI), FP Innovations and the Canadian Food Inspection Agency, through a Large Scale Applied Research Program (LSARP 2112; Genome Canada grant).

Contributor Information

Nicolas Feau, Email: feaunico@mail.ubc.ca.

Richard C. Hamelin, Email: rhamelin@gmail.com.

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