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Official websites use. Share sensitive information only on official, secure websites. This article was submitted to Systems Microbiology, a section of the journal Frontiers in Microbiology. The use, distribution or reproduction in other forums is permitted, provided the original author s or licensor are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms. Information on the diversity of fungal spores in air is limited, and also the content of airborne spores of fungal plant pathogens is understudied. In the present study, a total of air samples were taken from rooftops at urban settings in Slagelse, DK, Wageningen NL, and Rothamsted, UK together with 41 samples from above oilseed rape fields in Rothamsted. Samples were taken during day periods in spring and autumn, each sample representing 1 day of sampling. The fungal content of samples was analyzed by metabarcoding of the fungal internal transcribed sequence 1 ITS1 and by qPCR for specific fungi. The metabarcoding results demonstrated that season had significant effects on airborne fungal communities. In contrast, location did not have strong effects on the communities, even though locations were separated by up to km. Also, a number of plant pathogens had strikingly similar patterns of abundance at the three locations. Rooftop samples were more diverse than samples taken above fields, probably reflecting greater mixing of air from a range of microenvironments for the rooftop sites. Pathogens that were known to be present in the crop were also found in air samples taken above the field. This paper is one of the first detailed studies of fungal composition in air with the focus on plant pathogens and shows that it is possible to detect a range of pathogens in rooftop air samplers using metabarcoding. Aerial dispersal of spores over short or long distances affects the epidemiology of many fungal plant pathogens, and long-distance dispersal is an important strategy for a number of pathogens which may lead to invasion into new areas or spread of aggressive races of pathogens on the global scale Brown and Hovmoller, The amount and timing of air dispersal of spores of individual fungal plant pathogens has been studied with the aim to model disease pressures and in the end to be able to predict disease risks in decision support systems. However, the mechanisms of how air mass is mixed, the origins and release of spores, and finally deposition of spores on plant leaves are not very well-studied Schmale and Ross, Previously, airborne spores were identified by microscopy which is a lengthy process that can only identify relatively large spores with visual characteristics. The introduction of immunological and DNA based methods have largely facilitated the detection and quantification of specific fungal species in air samples. Kennedy et al. Ramularia beticola in air samples could be detected by qPCR 14 to 16 days prior to first visible symptoms on sugar beet and the assay was suggested as part of an early warning system Wieczorek et al. Carisse et al. In another study, periods of high risk of grape powdery mildew could be established using measurements of conidia in air Carisse et al. Despite that temporal and spatial dispersal of airborne spores of a few plant pathogens has been studied in detail Brown and Hovmoller, ; Rogers et al. Novel sequencing technologies have enabled insights into microbial communities with an unprecedented resolution Caporaso et al. Previous studies of airborne microbial diversity using next generation sequencing technology have focused on allergenic or human pathogenic organisms whereas plant pathogens have received comparatively little attention Adams et al. Similarly, pyrosequencing of air samples from an urban setting resulted in the identification of more than fungal OTUs operational taxonomic units of which most showed seasonal variation Yamamoto et al. In the present study, we sampled spores from air during day periods in spring and autumn from three locations in Northwestern Europe Denmark, England, and The Netherlands , from rooftops remote of agricultural fields. Those three locations have approximately similar climates. The spore traps were placed on top of tall buildings in urban surroundings in order to sample well-mixed air and to avoid sampling bias from single close-by fields. The aim was to obtain air samples which were representative of the fungal species composition in air at a regional scale West and Kimber, For reference, a spore trap was operated at ground level in experimental oilseed rape fields at Rothamsted. Autumn and early spring were chosen as sampling periods to allow for detection of plant pathogens in periods where we assume that spores would be important in initiating new infections in fields with either autumn or spring-sown crops. The content of fungal spores in the collected samples was analyzed using metabarcoding of the fungal ITS1 region and by qPCR for selected pathogens. By doing this, we wanted to answer the following questions: what is the level of diversity of fungi in air and what are the proportions of plant pathogenic fungi, and finally, what are the drivers of variation in those communities? Slagelse is a city with a population of 30, and is located in a rural area with cereals and rape as the main crops. Wageningen has a population of 40, and is surrounded by arable land and woodland. Rothamsted is located on the edge of a small town 30, inhabitants surrounded by primarily arable farmland with additional areas of permanent grassland and woodland. Furthermore, sampling at ground level took place in experimental fields at Rothamsted. The air sampler was raised to the same height as the crop canopy approximately 1 m. Sampling was performed using a Burkard 7-day recording volumetric spore trap Burkard Manufacturing, Co. Weather data mean temperature and precipitation for the respective locations and periods can be found in Supplementary Table S2. One of the two DNA extractions representing a daily section was used for sequencing analysis; the other was stored as a back-up. To each tube 0. Primers were synthesized by Eurofins MWG. The amount of amplicons was estimated by visual inspection after gel electrophoresis. Tagged PCR amplicons were pooled in equimolar amounts and resolved in 1. Distribution of samples in sequencing runs is shown in Supplementary Table S1. The primers that were used for pyrosequencing were not able to efficiently amplify DNA from the genus Puccinia as also observed in previous studies Sapkota et al. As Puccinia contains important plant pathogens, we quantified the amount of Puccinia striiformis , P. The concentration of the samples was automatically scored on the basis of the dilution series of the PCR products generated from the reference material. Fungal gene copy numbers were calculated using estimated genome sizes of the species, and the measured DNA quantities. Flowgrams were subjected to Ampliconnoise to remove reads with mismatching primers and MID sequences, PCR and sequencing errors, and chimeras Quince et al. All singletons were removed before constructing OTU tables. Sub-sampling to a minimum sequencing depth of reads per sample was used for analysis of the entire dataset and samples having fewer reads were removed. Non-phylogenetic diversity was calculated separately for year, season and location. In order to compare fungal community composition in different categories and to partition the variance in different categories, Bray—Curtis distance matrices were subjected to Permutational MANOVA Anderson, using the adonis function with a permutation number of available in the vegan package of R Oksanen et al. In total DNA samples each representing 24 h of air sampling from rooftops at three locations and from different seasonal periods, and 41 samples from above agricultural fields in Rothamsted were subjected to pyrosequencing of the fungal ITS1 region. Sequencing resulted in a total of , reads after quality filtering and ITS extraction. A species accumulation curve indicated that sequencing and sampling depths did not cover the full diversity in air as the curve did not reach a plateau Supplementary Figure S1. The composition of the communities in each sample is shown at class level in Figure 1 , and Figure 2 shows the overall composition of fungal communities at Phylum, Class, Order, Family, and Genus levels. Most of the detected fungi were Ascomycota The proportion of Basidiomycota was highest in autumn , which was primarily caused by a high abundance of Agaricomycetes gilled mushrooms in the samples Figure 1. The dominant classes in Ascomycota were Dothideomycetes The proportion of classes within sampling periods was generally constant, whereas variation was observed between seasons Figure 1. Barchart showing the relative taxonomic distribution of fungal classes in air samples each representing 1 day of sampling at rooftops in Rothamsted, UK, Slagelse, DK and Wageningen, NL, and above oilseed rape fields in Rothamsted during five periods in and early spring , late spring , autumn , early spring , late spring Upper, middle and lower lines represent first quartiles, medians and third quartiles. The whiskers represent a 1. Generally, samples taken from above fields had lower richness The effect of season at individual locations was tested using the Kruskal—Wallis rank sum test after separating data based on location. Boxplots showing the number of observed operational taxonomic units OTUs for the different sampling periods. Each point represents samples, and upper, middle and lower lines represent first quartiles, medians and third quartiles. A principal coordinates analysis PCoA did not show any distinct clustering with regard to the three different rooftop locations in Rothamsted, Slagelse, and Wageningen Figure 4A. For example, the genus Fomes a bracket fungus was found in almost all samples from Slagelse and Wageningen at a relatively high abundance, but was almost absent in samples from Rothamsted Supplementary Table S1. Bray—Curtis matrices visualized using principal coordinates analysis PCoA axes 1, 2, and 3 showing A distribution of samples according to location Rothamsted, Slagelse, and Wageningen in the dataset from rooftop samples, B distribution of samples according to season early spring , late spring , autumn , early spring , late spring in the dataset from rooftop samples. In contrast, season and year were more important in shaping community structures and explained As shown in the PCoA plot Figure 4B , fungal communities clustered according to both year and also season of the year. Samples from autumn were most distinctly separated, but also separation between early and late spring could be observed. The following taxa, which are known to contain mainly plant pathogens, were identified species identifications by BLAST matches in NCBI are shown in brackets : Sclerotiniaceae several species, blast hits including both Botrytis cinerea and S. Sclerotiniaceae reads , Mycosphaerellaceae reads , Blumeria reads , and Microdochium reads were found in relatively high abundance, whereas reads from the other genera were found in much lower abundance. There was a remarkably high abundance of the class Exobasidiomycetes in the Rothamsted field samples from late spring Figure 1 , a closer inspection by BLAST matches of representative reads revealed that they belonged to the genus Entyloma , a genus consisting of plant pathogenic smut fungi. The genus Leptosphaeria , containing the oilseed rape pathogen L. The relative abundance of taxa containing plant pathogens varied greatly over the sampling periods in and as exemplified in Figure 5 by the four most abundant taxa. Read distributions were strikingly similar at the three locations for many genera including Blumeria and Mycosphaerellaceae which were both present in higher quantities in spring compared to spring and were almost absent in autumn Figures 5A,B. In contrast, Monographella was more evenly distributed throughout the different periods Figure 5C , although significant day-to-day variation could be observed. Sclerotiniaceae was highly abundant in samples from above the oilseed rape fields in the late spring Figure 5D , which was confirmed by qPCR analysis Supplementary Table S1. The most abundant genera with mainly plant pathogenic during five periods in spring and and autumn Note that the graph does not represent a continuous sampling but five temporally separated periods. The amount of the plant pathogens P. This revealed peaks of P. Graph showing the abundance of Puccinia graminis and P. This is one of the first studies to examine fungal diversity in air samples using metabarcoding. On the basis of relative quantities of reads we studied the composition of fungal taxa in air sampled at three locations representing different Northwestern European regions. To dilute effects from single close-by fields, spore traps were placed on top of tall buildings in urban surroundings. For comparison, we also included a few samples taken from the air just above oilseed rape fields in Rothamsted, UK. The study clearly demonstrated that the composition of fungal communities in air was similar over a large geographical area Northwestern Europe in a region with similar climates. As expected, season had a marked influence on fungal composition probably reflecting the different climatic conditions, phenological patterns, and different life cycles of the fungal taxa and the varying availability of fungal growth substrates during the year. Although sampling sites were separated by up to km between Slagelse and Rothamsted , location did not have significant effects on observed species richness between the three locations. Based on variance partitioning on community distances by the adonis test, location explained 8. Likewise, a PCoA plot did not show any distinctive clustering based on sampling site again confirming that location within this climatic region is not an important driver of the diversity of airborne fungal spores. This observation is supported by Bowers et al. The three locations used in this study are all in the Northwestern part of Europe with approximately identical climates mild winters, cool summers with an average yearly rainfall between and mm , and with similar plant and crop covers. In addition, rooftop sample locations at heights around 10—15 m are expected to sample air well-mixed by the turbulent boundary layer and representing particles released from many sources over a relatively large local area compared to ground locations, which bias sampling toward close local sources rather than the background air stream Lacey and West, This may explain the little variation observed between the three sampling sites, as the majority of airborne spores originate from local plant and soil sources and only a minority originates from distant sources transported by strong winds Behzad et al. The species present in the air spora at the three sites appears to be similar at each sample period when generally mobile patterns of wind circulation direction in Northwestern Europe delivered similar weather differing only in timing of passing weather systems. Differences between sites could be more apparent on certain individual days, because as weather systems pass over NW Europe, the wind direction either side of the weather front is different Schmale and Ross, and also due to local active dispersal of spores after a rain front has delivered rain compared to dry conditions locally ahead of the front. Finally, DNA markers with a finer resolution might have revealed subtle differences in the read abundances between closely related strains that were not discernible using the ITS1 region as a marker. There was generally a lower amount of PCR product from samples taken in autumn than from samples taken in the spring data not shown , which may be caused by lower amounts of airborne fungal spores in autumn, although other explanations may exist such as differences in PCR inhibition, differences in the lysis of spores, or differences in trapping efficiency in samples between the seasons. Despite this, species richness was highest in autumn compared to early and late spring. This could be caused by the higher amounts of decaying plant material after the growth season, a more diverse plant cover after harvest of monoculture crops, or by the abundance of sporulating mushrooms in the autumn. The higher proportion of Basidiomycota during autumn was mainly caused by Agaricomycetes including many mushroom-forming fungi that are dominant in autumn in the Northwestern European area. The finding that species richness is higher in the autumn is partly supported by Yamamoto et al. These different observations may be caused by local differences such as variations in plant-covered areas and diversity of plant species in surroundings. The species richness in field samples was low compared to rooftop samples, probably caused by dominance of spores from a few fungal species coming from the crop just below the spore sampler. Lower diversity is expected at ground level than at rooftop height because the air is less-well mixed and the sample is heavily weighted toward sources of spores close to the sampler because less dilution will have occurred into the atmosphere. This suggests that the rooftop site is actually a better location for assessing fungal content in air representative of the region and to detect more exotic airborne particles than at ground level. The rooftop samples represent smoothed samples of mixed air comprising spore releases from many different microclimates and habitats within the region. In field samples, Exobasidiomycetes were highly dominant at single days or at short intervals of days in late spring Sequence comparisons showed that reads from Exobasidiomycetes belonged to Entyloma , a genus in which the plant pathogenic smuts belong. We were not able to identify reads to species level, however, there were fields of grass nearby and long uncut grass margins around the field that had not been fungicide treated, these may have been infected with smuts providing a link to observations in the air sample data. The Sclerotiniaceae dominated a few samples during late spring This indicates massive spore release from the crop just below the sampler, which was oilseed rape that had been artificially inoculated with S. The oilseed rape crop was also affected by L. This corresponds well with the presence of reads of this species in the autumn samples, as well as our qPCR data. Based on variance partitioning on community distances, season explained A PCoA plot illustrated clustering of samples according to both year and season. Early spring and late spring samples showed some clustering but not as clear as between spring and autumn or between the two years. Early spring was sampled in the end of April or beginning of May and late spring was sampled at the beginning of June both years meaning that the two sampling periods were only separated by approximately 1 month, which may explain the similarity between fungal communities in the two sampling periods. The two years and were clearly separated. This may be explained by differences in the weather conditions during the different periods or by differences in plant cover between the 2 years. Generally spring was wet, autumn was slightly wetter than normal, and spring was relatively dry and was warmer than during sampling periods Supplementary Table S2. Different fungal genera containing important plant pathogens showed different patterns of relative read abundances during the season, but were strikingly similar across the three locations and in many cases peaking on approximately the same days as shown for Blumeria , Mycosphaerellaceae, Monographella and Sclerotiniaceae. Blumeria causes powdery mildew in grasses including cereals and is an obligate parasite depending on living host tissue. It overwinters as chasmothecia in plant debris or as mycelium and conidia in living plant tissue. In early spring airborne ascospores from chasmothecia is the primary inoculum but also conidia from overwintering mycelium is released. Blumeria reads showed the highest peaks in in all three locations with an initial peak in early spring and a later peak in late spring. Interestingly, many of the peaks coincided on the same day at the three locations. However, our data set is too limited to predict which factors have provoked the massive spore releases. The wet spring of was not conducive to a strong epidemic, while relatively dry and warmer conditions in but still with some rain occasionally probably facilitated better sporulation and dispersal events. Blumeria was almost absent from autumn samples, which is explained by the fact that very little green plant substrate is available at that time. Blumeria peaks from samples taken from rooftops coincided with peaks from air samples taken from above crops, indicating dispersal of Blumeria spores from the surrounding rural areas at the regional scale. Mycosphaerellaceae peaked in early spring at all three locations. The majority of reads assigned to this family were identified as belonging to Ramularia and some could be even further identified to species such as R. These are species that infect trees such as alder, oak and beech, which are grown in many urban areas. The peak in early spring was probably originating from an early onset of Ramularia in one or more tree species in the urban surroundings caused by the warm and dry conditions in spring Infection by Ramularia is initiated by air-borne ascospores and splash-dispersed conidia produced on leaf residues from the previous season. Surprisingly, we did not detect any Zymoseptoria tritici reads in our dataset. The high peak of Sclerotiniaceae in the Rothamsted field samples coincided with data from the Rothamsted rooftop samples in late spring This field was artificially inoculated with S. It is interesting that the rooftop site had a similar pattern of S. This suggests that the rooftop site was sampling spores from natural sources in the region which responded to the same weather events to release ascospores. Monographella identified by BLAST in NCBI to Microdochium nivale did not show a marked seasonal variation, although there was a high day-to-day variation and the abundance was higher in spring This could reflect the fact that M. Furthermore, M. The presence of Puccinia sp. Generally, our results show that air samples may be an important source for monitoring movements of Puccinia spores on a regional scale. Monitoring air-borne inoculum of plant pathogens is relevant for developing decision support systems for disease management and also for understanding fundamental questions in epidemiology of plant pathogens, even more so in view of climate change which is predicted to increase severity of many plant diseases. Until recently, monitoring was done by microscopy and in some cases by culturing of the organisms, or more recently, by PCR-based methods able to monitor individual pathogens of interest at a high sensitivity and specificity. Using next generation sequencing based metabarcoding, it is now possible to analyze the composition of fungal communities in air samples at a very high resolution and in practice all pathogens in one analysis, including unculturable organisms. This opens new opportunities to study the temporal and spatial dynamics of spore concentrations, the factors that shape these communities, and finally how these concentrations influence disease development of crops. However, there are still many challenges for the full exploitation of metabarcoding in epidemiological studies of plant pathogens: i as most plant pathogens have a narrow host range it is necessary to identify reads at species level or even below this. This represents a challenge, as only a fraction of reads can be assigned to species level when using the ITS region as the barcode; ii as disease may be initiated from small numbers of spores, a very high sensitivity is required in a high background of other material. It has not yet been fully investigated whether metabarcoding has sufficient sensitivity for detection of primary inoculum concentrations; iii PCR procedures may introduce biases in read abundance as shown in the present experiment, in which no Puccinia was detected using metabarcoding, although spores of Puccinia were present, as evidenced by qPCR; iv method and location of sampling may have impact on data. Generally, qPCR approaches have shown very high sensitivity and will be the preferred method for detection of single species of pathogens because of both sensitivity and specificity whereas metabarcoding has higher potential for a systems-based understanding of microbial diversity in air. In this study we have found that the relative abundance of fungal spores does not vary much over relatively large areas with similar climates, and that some species of pathogens peak at the same days even at long distances apart. The explanation for this could be due to the sampling locations having similar climates and land-use surrounding them. However, further work is needed as our data were too limited to link weather observations and land-use for the three locations to metabarcoding data. All authors approved the manuscript for submission. The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest. The authors want to thank Ard Nieuwenhuizen and Jean-Marie Michielsen for valuable inputs in experimental design and spore sampling. Species accumulation curve showing the number of detected OTUs as a function of number of samples. Operational taxonomic unit OTU table including taxonomic classification, sequencing run, barcode used, location, date of sampling and relative abundance of reads. Daily precipitation and mean temperatures are given. Observed species at the different locations. Primer and probes: a developed probe sequence Kim and Knudsen, was modified for the reporter dye, b—d developed probe sequences Barnes and Szabo, were modified with a ZEN component and quenching IABkFQ dye, e primers and probe Waalwijk et al. This section collects any data citations, data availability statements, or supplementary materials included in this article. As a library, NLM provides access to scientific literature. Front Microbiol. Find articles by Mogens Nicolaisen. Find articles by Jonathan S West. Find articles by Rumakanta Sapkota. Find articles by Gail G M Canning. Find articles by Cor Schoen. Find articles by Annemarie F Justesen. Edited by: Jessy L. Received Jun 28; Accepted Aug 24; Collection date Open in a new tab. Click here for additional data file. TABLE S1 Operational taxonomic unit OTU table including taxonomic classification, sequencing run, barcode used, location, date of sampling and relative abundance of reads. Similar articles. Add to Collections. 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