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Number of nucleotide differences in the internal transcribed spacer (ITS) and cytochrome oxidase (cox) DNA regions of Pythium and Phyto- pythium isolates from recycling ebb-and-flood irrigation water in two com- mercial greenhouses as compared with their closest relative in The Barcode of Life Data System (Ratnasingham and Hebert 2007)

Number of nucleotide differences in the internal transcribed spacer (ITS) and cytochrome oxidase (cox) DNA regions of Pythium and Phyto- pythium isolates from recycling ebb-and-flood irrigation water in two com- mercial greenhouses as compared with their closest relative in The Barcode of Life Data System (Ratnasingham and Hebert 2007)

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Two commercial greenhouses producing potted plants in Pennsylvania using recycled irrigation water in an ebb-and-flood system have incurred significant crop losses due to Pythium aphanidermatum. In cooperation with the greenhouses, one or more of their water tanks was monitored continuously (128 tank samplings) for Pythium spp. by baiting. Nine spe...

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... total, nine Pythium and three Phytopythium spp. representing clades A, B, E, and K (Table 2) were discovered, but P. aphanidermatum was not found in any tank. The Pythium spp. ...
Context 2
... number of nucleotide differences in the ITS and cox DNA regions from their closest match on BOLD is shown in Table 2. It is apparent that the species we confidently identified had few nucleotide differences and that the putative new species have a greater number of nucleotide differences from their closest relative. ...

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... Oomycetes are also called "water molds," and most of the species in this group are found in aquatic habitats (Li et al. 2014;Link et al. 2002). These two species of Phytopythium are abundantly found in greenhouse irrigation water tanks (Choudhary et al. 2016;Parke et al. 2019), hydroponic systems (Gonçalves et al. 2016;Kanjanamaneesathian et al. 2013;Teixeira et al. 2006), ebb and flow irrigation systems , and natural rivers and reservoirs used as a source of agricultural irrigation (Hon-Hing et al. 2012;Nam and Choi 2019). ...
... P. helicoides was first documented to be present in natural forest soils of the Southeastern United States in 1968 (Hendrix and Campbell 1968). Diseases caused by P. helicoides were reported on cultivated plants in Asia (Japan Kageyama et al. 2002;Kato et al. 2013;Miyake et al. 2014;Miyazaki et al. 2009;Tsukiboshi et al. 2007;Watanabe et al. 2007], India [Roy and Hong 2008], Taiwan [Huang 2009], Korea [Han et al. 2010], China Wang et al. 2015], Turkey [Avan et al. 2020], and Iran [Azizi et al. 2013]), South America (Brazil [Gonçalves et al. 2016;Teixeira et al. 2006]), Oceania (New Zealand [Kanjanamaneesathian et al. 2013]), and North America (various states of the United States, including Florida [Chellemi et al. 2000;Marin et al. 2019;Rosskopf et al. 2005], Virginia [Yang et al. 2013], California [Fichtner et al. 2016], Pennsylvania [Choudhary et al. 2016], and South Carolina [Toporek and Keinath 2020]) (Fig. 2). ...
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... The oomycete P. chamaehyphon (previously known as Pythium chamaehyphon and Ovatisporangium chamaehyphon) has been reported to cause damping-off on seedlings of Anacardium excelsum (wild cashew), and Tetragastris panamensis (kerosin) (Davidson et al., 2000). Recent reports indicate that P. chamaehyphon is associated with potted floricultural crop losses ocurring in commercial greenhouses in Pennsylvania, USA and with the Kiwifruit Vine Decline Syndrome (KVDS) in Italy (Choudhary et al., 2016;Savian et al., 2021). Based on molecular and phylogenetic analyses, the isolated oomycetes were identified as P. chamaehyphon. ...
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... significant, causing up to 60%-100% of yield losses depending on the environmental conditions (Adeniyi, 2019). However, other oomycetes remain under-studied, even though different genera have been frequently found in other crops causing damping-off, root damage, and other diseases (Choudhary et al., 2016). Thus, it is very possible that they are also present in cacao crops, possibly affecting them. ...
... The genus Phytopythium was present not only in soil and roots, where it is typically found (Choudhary et al., 2016), but was also isolated from samples of necrotic leaves and vascular section of stems with canker. This is an interesting result because it indicates this species has a role in diseases commonly associated with Phytophthora spp. ...
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... The latter demonstrates that the heterogeneity of environmental conditions has likely contributed to the observed differences in richness and composition of fungal communities in different forest nurseries (Figures 1 and 2; Tables 2 and 3). This is in agreement with similar studies on aquatic fungi for which the diversity and composition may change depending on the source, location, and time of the year [52][53][54][55]. Indeed, as the sampling at different sites was carried out both in the autumn (Anykščiai, Kretinga and Dubrava) and in the spring (Trakai) ( Table 1), the possibility should not be excluded that this has also contributed to the observed variation in richness and the composition of fungal communities among different forest nurseries. ...
... Alternatively, this can partly be due to PCR biases that selected for shorter fragments of fungal DNA. Nevertheless, the oomycete diversity in the irrigation water may change depending on environmental conditions and the time of the year, as these factors may affect the survival and activity of individual taxa, and thus, may affect the degree of plant infections [6,16,[52][53][54][55]75,76]. ...
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... Evidence for plant pathogenicity of P. litorale is mixed. Phytopythium litorale is commonly isolated from irrigation ponds in Georgia where it was shown to cause seedling damping-off and fruit rot of squash (Cucurbita pepo) (Parkunan and Ji, 2013), but isolates from greenhouse water tanks in Pennsylvania were not pathogenic in assays with geranium (Pelargonium ·hortorum) seedlings (Choudhary et al., 2016). It is not known if P. litorale is causing disease in Nursery B. ...
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Phytophthora species cause crop losses and reduce the quality of greenhouse and nursery plants. Phytophthora species can also be moved long distances by the plant trade, potentially spreading diseases to new hosts and habitats. Phytosanitary approaches based on quarantines and endpoint inspections have reduced, but not eliminated, the spread of Phytophthora species from nurseries. It is therefore important for plant production facilities to identify potential sources of contamination and to take corrective measures to prevent disease. We applied a systems approach to identify sources of contamination in three container nurseries in Oregon, California, and South Carolina. Surface water sources and recaptured runoff water were contaminated with plant pathogenic species at all three nurseries, but one nursery implemented an effective disinfestation treatment for recycled irrigation water. Other sources of contamination included cull piles and compost that were incorporated into potting media, infested soil and gravel beds, used containers, and plant returns. Management recommendations include preventing contact between containers and contaminated ground, improving drainage, pasteurizing potting media ingredients, steaming used containers, and quarantine and testing of incoming plants for Phytophthora species. These case studies illustrate how recycled irrigation water can contribute to the spread of waterborne pathogens and highlight the need to implement nursery management practices to reduce disease risk.
... Therefore, knowing about their response to fungicides is important. Phytopythium sp. is commonly found in water tanks and areas with irrigation of water (Choudhary et al. 2016). Isolates of Phytopythium sp. ...
... Isolates of Phytopythium sp. highly sensitive (Choudhary et al. 2016;Radmer et al. 2017), intermediate (Choudhary et al. 2016), and insensitive to mefenoxam (Demott 2015) have been reported. Thus, knowledge on the sensitivity of this species to this fungicide is relevant. ...
... Isolates of Phytopythium sp. highly sensitive (Choudhary et al. 2016;Radmer et al. 2017), intermediate (Choudhary et al. 2016), and insensitive to mefenoxam (Demott 2015) have been reported. Thus, knowledge on the sensitivity of this species to this fungicide is relevant. ...
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... [22], and this fast growth pattern was proved in the present study. Clade A with mainly aquatic species [40,41] was not found in the present study. ...
... cucurbitacearum, but distinguished from Phy. vexans by having larger oogonia and from Phy. cucurbitacearum by having non-papillate sporangia [21]. This species was previously isolated from irrigation water tanks in a greenhouse, with a pathogenicity on greenhouse crops [41]. Note: Isolates W630 and W595 are morphologically similar and phylogenetically close to ex-type strain CBS118360 "Phy. ...
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Oomycetes are widely distributed in various environments, including desert and polar regions. Depending upon different habits and hosts, they have evolved with both saprophytic and pathogenic nutritional modes. Freshwater ecosystem is one of the most important habitats for members of oomycetes. Most studies on oomycete diversity, however, have been biased mostly towards terrestrial phytopathogenic species, rather than aquatic species, although their roles as saprophytes and parasites are essential for freshwater ecosystems. In this study, we isolated oomycete strains from soil sediment, algae, and decaying plant debris in freshwater streams of Korea. The strains were identified based on cultural and morphological characteristics, as well as molecular phylogenetic analyses of ITS rDNA, cox1, and cox2 mtDNA sequences. As a result, we discovered eight oomycete species previously unknown in Korea, namely Phytopythium chamaehyphon, Phytopythium litorale, Phytopythium vexans, Pythium diclinum, Pythium heterothallicum, Pythium inflatum, Pythium intermedium, and Pythium oopapillum. Diversity and ecology of freshwater oomycetes in Korea are poorly understood. This study could contribute to understand their distribution and ecological function in freshwater ecosystem.
... Some species found in aquatic habitats, especially Phytophthora Clade 6 species, appear to be facultative pathogens or aquatic opportunists that have not been associated with plant disease (Hansen et al. 2012;Jung et al. 2011;Marano et al. 2016;van der Plaats-Niterink 1981). Phytopathogens appear to constitute only a small portion of the total species recovered from streams, rivers, and irrigation water reservoirs (Brazee et al. 2017;Choudhary et al. 2016;Copes et al. 2015;Hong et al. 2012Hong et al. , 2008Loyd et al. 2014;MacDonald et al. 1994;Parke et al. 2014;Yang 2013;Yang and Hong 2013;Yang et al. 2012Yang et al. , 2014Yang et al. , 2016. Genus-level identification of Phytophthora, Pythium, and Phytopythium is therefore insufficient to assess the risks posed to plants. ...
... There are indications that oomycete species diversity in irrigation water may change with source, location, and time of the year, influencing the survival of individual species, and the risk of plant disease Choudhary et al. 2016;Copes et al. 2015;Hong and Moorman 2005;Hong et al. 2008;Loyd et al. 2014;MacDonald et al. 1994;Parke et al. 2014), but the biases of culturebased methods have limited our understanding of how pathogen communities vary in time and space within the nursery irrigation system. ...
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Recycling of irrigation water increases disease risks due to spread of waterborne oomycete plant pathogens such as Phytophthora, Pythium and Phytopythium. A comprehensive metabarcoding study was conducted to determine spatial and temporal dynamics of oomycete communities present in irrigation water collected from a creek (main water source), a pond, retention reservoirs, a chlorinated water reservoir, and runoff channels within a commercial container nursery in Oregon over the course of one year. Two methods, filtration and leaf baiting, were compared for the detection of oomycete communities. Oomycete communities in recycled irrigation water were less diverse but highly enriched with biologically active plant pathogens as compared to the creek water. The filtration method captured a larger portion of oomycete diversity, while leaf baiting was more selective for plant-associated oomycete species of Phytophthora and a few Pythium and Phytopythium species. Seasonality strongly influenced oomycete diversity in irrigation water and detection with leaf baiting. Phytophthora was the major colonizer of leaf baits in winter, while all three genera were equally abundant on leaf baits in summer. The metabarcoding approach was highly effective in studying oomycete ecology, however, it failed to distinguish some closely related species. We developed a custom oomycete ITS1 reference database containing shorter sequences flanked by ITS6 and ITS7 primers used in metabarcoding and used it to assemble a list of indistinguishable species complexes and clusters to improve identification. The predominant bait-colonizing species detected in recycled irrigation water were the Phytophthora citricola-complex, P. syringae, P. parsiana-cluster, P. chlamydospora, P. gonapodyides, P. irrigata, P. taxon Oaksoil-cluster, P. citrophthora-cluster, P. megasperma-cluster, Pythium chondricola-complex, Py. dissotocum-cluster, and Phytopythium litorale.
... For example, a plant-indexing propagation operation found municipal water to be the source of Pythium spp. at the facility. Irrigation water drawn from natural water ways and from recycling water basins potentially contain plant pathogens, such as plant pathogenic Erwinia spp., Fusarium spp., Pythium spp., Phytopythium spp., and Phytophthora spp., that may require treatment Del Castillo Múnera and Hausbeck 2015;Elmer 2008;Ghimire et al. 2011;Choudhary et al. 2016;Moorman et al. 2002;Parke and Grunwald 2012). Even with these seemingly risky water sources, water treatment is only required when pathogens capable of causing crop loss are being dispersed in irrigation water. ...
... Recent research results have shown that detection of Pythium spp., Phytopythium spp., and Phytophthora spp. in irrigation water does not confirm a plant pathogen problem Hong and Moorman 2005;Choudhary et al. 2016;Loyd et al. 2014;Parke et al. 2014;Zappia et al. 2014). Unfortunately, these results provide an additional burden for plant producers, because isolates need to be identified to species by qualified plant disease clinics and associated with past or current plant disease problems, or a high potential for disease to determine whether water treatment is required. ...
Chapter
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Sanitation involves efforts aimed to prevent introduction of pathogen propagules into a production facility, remove sources of propagules from active production areas to substantially slow disease development, and eliminate pathogen propagules from future production areas. Sanitation includes many practices such as using disease-free certified seed and propagative material, maintaining weed-free zones around production areas, use of screens to block entry of insects, use of double doors and foot paths, cleaning and sanitizing production areas between crops, sanitizing tools and equipment, and early removal of diseased plant material. General sanitation should be a matter of routine good agricultural practices. Because it is so important to do a thorough job, key sanitation practices should be selected that control the pathogens that routinely affect plants at a facility and those that are prevalent and would severely impact production if introduced. Good records are an important tool to select which pathosystems are problems, to determine cost benefit decisions, and to select subject matter for worker training modules. The information in this chapter represents an overview of methods known to be effective.