A critical aspect regarding the global dispersion of pathogenic microorganisms is associated with atmospheric movement of soil particles. Especially, desert dust storms can transport alien microorganisms over continental scales and can deposit them in sensitive sink habitats. In winter 2014, the largest ever recorded Saharan dust event in Italy was efficiently deposited on the Dolomite Alps and was sealed between dust-free snow. This provided us the unique opportunity to overcome difficulties in separating dust associated from “domestic” microbes and thus, to determine with high precision microorganisms transported exclusively by desert dust.
Our metagenomic analysis revealed that sandstorms can move not only fractions but rather large parts of entire microbial communities far away from their area of origin and that this microbiota contains several of the most stress-resistant organisms on Earth, including highly destructive fungal and bacterial pathogens. In particular, we provide first evidence that winter-occurring dust depositions can favor a rapid microbial contamination of sensitive sink habitats after snowmelt.
Airborne microbial depositions accompanying extreme meteorological events represent a realistic threat for ecosystem and public health. Therefore, monitoring the spread and persistence of storm-travelling alien microbes is a priority while considering future trajectories of climatic anomalies as well as anthropogenically driven changes in land use in the source regions.
Many microorganisms use Aeolian dispersal as a key strategy for colonization of new habitats, and here especially, the global dispersal of microbial pathogens constitutes a threat to environmental health [1, 2]. Dust particles can facilitate intercontinental movement by acting as vehicles for viable microorganisms . West African soils, primary the Saharan desert, are major sources of airborne dust that is frequently transported at high altitude over the Atlantic and the European continent . Both the Sahara and the atmosphere are characterized by harsh conditions with limited availability of nutrients, high radiation, and extreme temperatures . Therefore, microorganisms that are able to survive in these environments represent potential invaders of sites with comparable challenging conditions such as high-elevated alpine regions . Further, recent knowledge suggests that the transported mineral and biological particles of large-scale dust storms affect cloud ice formation and precipitation processes, creating novel climate system feedbacks . In particular, during winter, alien biological particles associated with large dust events may be deposited in vast numbers leaving persistent dust layers in the snowpack  that, at the highest elevations are preserved in the ice of glaciers. Such permanently frozen environments harbour a variety of viable microorganisms  that have been deposited over centuries , but it was rarely shown that they can persist in the new habitat after the snowpack was melted . Previous studies revealed that microorganisms transported with Saharan dust can provoke several severe plant diseases . Moreover, increasing incidences of pulmonary and cardiovascular diseases , as well as meningitis epidemics , have been attributed to dust storms either caused by the dust itself or due to plant-derived constituents or endotoxins of microbial dust “passengers” . Hence, the characterization of alien microorganisms that are currently sequestered in the cryosphere is a priority while considering global warming and future trajectories of climatic anomalies as well as anthropogenically driven changes in land use in the source regions [4, 15, 16]. An increasing frequency of dust storms may intensify the global dispersal, the deposition, and consequently the rapid contamination of new habitats by alien microbes. Yet difficulties in separating dust associated from “domestic” microbes have complicated a precise description of the deposited airborne desert dust microbiota. To efficiently study the long-distance dispersal of microbes by large-scale desert dust events and their impact on distant ecosystems, a collaborating effort of geologists, atmospheric chemists, and microbiologists was strongly requested .
In winter 2014, a massive amount of Saharan dust particles was mobilized and transported towards the Western Mediterranean Basin (Fig. 1) resulting in the largest Saharan winter dust event that was recorded at the Italian Climate Observatory  up to that time. This massive event was then efficiently deposited in the Alpine region, covered by successive snowfalls and thus remained sealed between two dust-free snow layers (Fig. 1), preventing windblown contamination by material from the local environment .The clear separation of snow layers associated with the dust event and with the dust-free snowfall events gave us the unique opportunity to determine with high precision the bacterial and fungal communities that were transported in the troposphere from the Sahara to the Alps (Fig. 1). Additionally, we tested the contamination potential of these airborne communities by comparing them to the Alpine soil microbiota after snowmelt.
Our detailed metagenomic analysis unveiled that extreme meteorological events can move not only fractions but also large parts of entire microbial communities over continental scales, that this microbiota contains highly destructive environmental and important human pathogens, and that winter occurring dust depositions bear a great potential for a rapid microbial contamination of sensitive sink habitats after snowmelt.
During the wetter than normal winter 2014 over the Alpine region by the end of January, a positive snow anomaly was present in the central sector 1500–1700 masl . In this area, between the end of January and the first half of February abundant precipitation events provided a thick snow coverage even at low altitudes starting from 800 masl. . On 14th of February, a cyclonic depression generated over the southern Morocco moved rapidly eastward to Mauritania, north Mali and south Algeria, mobilizing a massive amount of Saharan dust particles until 17th of February. Then, on 19–20 February 2014, a north–northwest displacement of the sub-tropical Azores high-pressure system over the Atlantic Ocean, and a large anticyclone circulation centered over Libya provided the favorable conditions for a north-to-south elongated trough, associated with an extratropical cyclone over the British Islands, that was extended from Senegal/Niger to Great Britain and Western Europe. It generated a vigorous southerly flow towards the Western Mediterranean Basin from February 14th to 20th (Fig. 1, Additional file 1: Figure S1) resulting in the largest Saharan winter dust event ever recorded at the Italian Climate Observatory . This massive aerosol plume was then efficiently deposited during a moderate snowing event at altitudes above 1800 masl. in the Alpine region on 19th of February. The Saharan dust-rich snow layer was covered by successive snowfalls, starting 2 days later due to Atlantic air masses and thus remained sealed between two dust-free snow layers (Fig. 1). Backward trajectories, based on a high-resolution non-hydrostatic mesoscale model simulation , revealed that the most likely emission source was located along the path covering Mali, Mauritania, Morocco, and Algeria (Fig. 1).
The major ion composition of deposited mineral dust validated the back trajectories (Fig. 1) for the identification of the potential source areas (Table 1, Additional file 1: Table S1). Geochemical characterizations clearly showed that the chemical composition of the snow containing Saharan dust differed from dust-free snow for higher concentrations of trace, major, and rare earth elements, in particular regarding the very high concentrations of crustal elements such as Na, Mg, K, Ca, and Fe (Additional file 1: Figure S2). Elemental ratios are one of the best tools to reveal regional potential source areas of Saharan dust particles . In this case, the elemental mass ratios of snow samples containing dust (MA289 and MAJ025) are within the intervals reported for the Saharan desert  (Table 1).
The pyrosequencing produced a total of 310.994 reads of the V3-V5 variable region of the 16S rRNA gene (average read length 649 nt) and 582.811 reads of the variable ITS1 region (average read length 443 nt). After pre-processing and rarefaction, a total of 1282 operational taxonomic units (OTUs) for the 16S rRNA gene (with a depth of 2879 reads per sample) and 1095 OTUs for ITS data (with a depth of 5264 reads per sample) were considered.
Both the targeted 16S rRNA gene and ITS1 sequencing revealed clear differences between the bacterial and fungal communities present in snow containing Saharan sand (layer B) and snow that fell before (layer C) and after (layer A) the deposition event (Fig. 1; Fig. 2, unweighted UniFrac distance PERMANOVA P < 0.0001). Layer B showed a significantly higher diversity of its microbial community than layers A and C (Fig. 2, P = 5.5 × 10−4 and P = 7.3 × 10−4 for the 16S rRNA gene and ITS, respectively, Wilcoxon rank-sum test, FDR corrected; Additional file 1: Figure S3). Layers A and C were characterized by a higher fraction of the bacterial classes Alpha-, Gammaproteo-, and Cyanobacteria (Fig. 1), with Pseudomonas as the most abundant genus (Additional file 1: Figure S4). We could additionally identify with high precision other microorganisms significantly enriched in dust-free snow, these are Acinetobacter, Caulobacter, Acquabacterium, Beijerinckia, Novosphingobium, Granullicella, Terriglobus, Pelomonas, Ralstonia, and Phenylobacterium (Additional file 1: Figure S4). Regarding fungi, layers A and C were especially rich in molds of the genus Penicillium (Additional file 1: Figure S5).
Snow containing Saharan dust (layer B) was mainly represented by Actinobacteria and Bacilli (Fig. 1). Strikingly, layer B was significantly enriched in the most abundant bacterial families previously described for Saharan sand samples taken in Chad  (Fig. 3), and we found that 85% of the principal Saharan bacterial genera  (Additional file 1: Figure S4) arrived in the European Alps in a single meteorological event. The genus Geodermatophilus was frequent in all layer B samples.
As seen for the long-range transport of bacterial communities, also the three most abundant fungal classes described for the Saharan desert , namely, Dothideomycetes, Agaricomycetes, and Sordariomycetes, were significantly enriched in layer B when compared to sand-free snow layers (FDR adjusted Wilcoxon rank-sum test P = 7.7.0 × 10−4, 2.5 × 10−3, and 2.0 × 10−3). Additionally, layer B snow could be easily distinguished from sand-free snow, as 79% of the significantly enriched fungal genera were almost exclusively present in layer B samples (Additional file 1: Figure S5). Like the mycobiota described for hot deserts, fungal microbes specific for dusty snow were dominated by imperfect ascomycetes, teleomorph genera, and dematiaceous fungi with darkly pigmented, thick-walled, and strongly melanized spores . A closer look on these fungal genera unveiled that mainly so-called “black fungi” especially of the orders Pleosporales, Capnodiales, and Dothideales were dominant in almost all layer B samples as reflected in the genera, Aurebasidium, Periconia, Pleosporaceae, Montagnulaceae, Embellisia, and Davidiella (Fig. 4).
To uncover if alien dust storm microbes remained in the Alpine soil after snowmelt, we compared operational taxonomic units (OTUs) of species exclusively present in layer B with those present in soil samples. Out of these identical OTUs, 82 bacterial and 36 fungal OTUs matched the criterion (Additional file 2: Table S2). This is equivalent to approximately 10% of the bacterial and fungal layer B OTUs. Members of the fungal class Dothideomycetes seem to be predesignated for the survival in new challenging environments as half of the fungal species belonged to them with Pleosporales as the dominant order and Phoma as the most abundant genus (Additional file 2: Table S2). Regarding bacteria, Actinobacteria was the prevalent class (39%), followed by Alphaproteobacteria (22%), and Bacilli (9%) (Additional file 2: Table S2).
During last decades, an overall increase in quantity of African dust depositon was noted . This phenomenon has been so far considered relevant for nutrient deposition and soil development [25, 26], yet the recent knowledge on the microbial world suggests that dust deposition may introduce exotic microorganisms, including pathogens, into sensitive ecosystems [3, 4]. First insights on the immigration potential of Saharan dust microbes has been gained from studies on high alpine remote lakes, highlighting microorganisms that might have the capability to be successful colonizers under favourable conditions [4, 27–29]. Here, we analyzed the microbial load of the largest ever recorded winter-occurring Saharan dust event in Italy and, for the first time, we provide evidence on the potential contamination of alpine soils by desert dust microorganisms after snowmelt.
The clear demarcation of the deposited dust allowed us to precisely determine microorganisms associated with this massive dust event. The role of desert storm sand deposition in moving entire microbial communities is mirrored by the result that layer B (dust-containing snow) has a significantly higher alpha diversity than layers A and C (dust-free snow). The African origin of these microbial communities is reflected in the high conformity of principal bacterial and fungal genera described for the Saharan desert  with those present in layer B. It is especially noteworthy that extremely stress-resistant bacteria and fungi were among the most abundant microbes present in the snow containing Saharan sand. They are known for their ability to adapt to environmental stressors including desiccation and extreme γ radiation, like in the case of the genus Geodermatophilus . Several members of these black and thick-walled bacteria were isolated from arid soils , from Mont Blanc snow containing Saharan sand , and directly from sand sampled in the Saharan desert .
Further, endospore-forming Bacillus species are highly present in Saharan sand , and this genus was also frequently detected in our layer B samples. Similarly, viable Bacillus species originating from Chinese deserts were shown to be distributed via the atmosphere to long distance habitats in Japan [32, 33]. The ability to form spores provides resistance to extreme environments  and indicates that these genera have a high probability of surviving years of enclosure in the snowpack , while for the survival in the troposphere pigmentation seems to be an important factor [4, 8]. Regarding the latter case, the pigmented Deinococcus-Thermus and Gemmatimonadetes were recently considered as bio-indicators for Saharan dust events  which is supported by our observations (Additional file 1: Table S4). The genera Deinococcus and Gemmatimonas were significantly enriched in layer B, but Gemmatimonas was also enriched in soil samples. Gemmatimonadetes are normally not present in the Southern European air, but are prevailing bacteria in soils of recently deglaciated glacier forefields [8, 36], therefore they might represent a suitable example for Saharan immigrants of alpine soils.
The so-called black fungi were characteristic for the fugal dust-borne community. They are among the most stress-resistant organisms on Earth and colonize rock surfaces even in the most arid zones of the world . The remarkable survival capacity of black fungi has been further highlighted by a recent study in which Saharan dust samples collected by Charles Darwin in 1838 were successfully cultured and here, next to spore-forming bacteria (e.g., Bacillus), a member of Dothideomycetes (Davidiella tassiana, Capnodiales) was isolated among cultivable fungi . More important Capnodiales and Pleosporales contain several highly destructive and important pathogens of cereal crops, vegetables fruits, dicots, and trees as well as the most important fungal allergens .
Taken together, Saharan sand microbes that arrived with the dust event showed the potential to overcome all challenges posed, such as long-distance transport in the troposphere, long quiescence state in snow at sub-zero temperature, low nutrient availability, and persistence in the Alpine soil after snowmelt. Representatives of black thick-walled fungi and bacteria seem to have the best armamentarium, which allows them to survive harsh conditions. This high adaptation potential to challenging environments in a changing climate might be a possible prerequisite for the evolution of pathogenicity . Moreover, pathogens cannot solely survive in foreign environments but some can still germinate as it is the case for some ancient viruses recovered from melted permafrost in which it has been stored for more than 30,000 years . The “European Respiratory Society Environment and Health Committee” recommended attention and control of wind-blown dust from, for example, the Sahara, as they may have adverse health effects . Hence, together with fine inorganic dust particles, dust-associated microbes represent a serious health risk as several layer B genera include species that are known to cause allergic reactions, pulmonary infections, skin infections, or fatal brain infections in humans as well as leaf disease, inhibition of growth, branch and stem canker, blight, rot, scab, and mildew in plants. On the other hand, it has to be noted that some of these microbes are, albeit their potential pathogenicity, known as beneficial organisms like members of the genus Aurebasidium [41, 42].
The dust-free snow (layers A and C) was significantly enriched on genera containing known ice nucleators such as Pseudomonas, that were missing from layer B. The high relative abundance of Pseudomonas in dust-free snow samples might be related to the ability of some Pseudomonas species to initiate ice formation by special ice nucleation active proteins present in their outer membrane . Next to Pseudomonas, dust-free snow was significantly enriched in Acinetobacter and molds of the genera Penicillium. Acinetobacter genera were frequently found in atmospheric water, and Penicillium strains were discussed to impact the atmospheric multiphase chemistry . Additionally, we could identify other microorganisms significantly enriched in dust-free snow, and it will be interesting to study whether they have ice nucleation activities similar to Pseudomonas or be hitchhiking on ice nucleators. Our data supports the hypothesis that Saharan dust and biological aerosols have ice nucleation activity and are important for precipitation processes ; it further suggests that dust-driven snowfalls seem to be events that are microbiologically much more complex and well separated from dust-free snowfalls, bearing the potential ability of the former to bring down to the ground species that normally are not airborne, at least on such big distances.
Overall, there is evidence that large dust storms can move quasi-entire microbial communities far away from their area of origin and thus subsequently exposing them to novel environmental niches. The inoculum size is crucial as it determines the ability of a microbial community to survive, colonize, and eventually take over in a new environment. When dust events occur during the warm seasons, in form of rain, these are likely buffered by the robustness of the recipient microbial communities, and the inoculum is likely to be diluted and dispersed by surface runoff and infiltration. But when these events occur during winter, the microbes are accumulated in the snow, reaching a high titer upon rise of temperature during spring and summer. In those cases, masses of microbes are released in high concentrations on a limited surface during the melting of the snowpack. This effect might be further multiplied by the release of similar alien microbes that have been transported with desert dust over centuries and that were stored in the now ever retrieving glacial ice . The quantification of the overall load of microorganisms currently sequestered in melting glaciers should be assessed by means of ice cores sampling. Awareness of this realistic microbial contamination together with the increasing availability of next generation sequencing resources for metagenomic analysis, require the development of up-to-date monitoring capabilities targeted to melting snow and glacier effluents for the effective implementation of early warning systems.
A full non-hydrostatic regional model (Regional Atmospheric Modeling System (RAMS)) has been forced by atmospheric fields from NCEP/NCAR Reanalysis dataset and sea surface temperature field obtained from the Optimal Interpolation Sea Surface Temperature dataset. The model simulation was run over a wide domain covering North Atlantic basin, Africa, Europe, and Middle East, from February 1s to March 1st 2014, with a horizontal grid spacing of 50 km, a vertical extent of about 21 km above sea level, and a temporal resolution of 1 h. Backward trajectories calculation has been computed by using the full 3D wind field modelled by the RAMS and with a centred difference in time computation in Grid Analysis and Display System (GrADS) (http://cola.gmu.edu/grads/grads.php). This regional reanalysis approach guarantees a coherent description of the three-dimensional flow dynamics. Furthermore, the non-hydrostatic formulation of model, along with the fine time resolution (1 h) ensures a reliable representation of backward trajectories .
Samples were collected on two mountains located in the Trentino region of the Italian Alps: Marmolada (Punta Rocca, collection site at 3054 m) and Latemar (collection site at 2080 m) (Fig. 1). To maximize sampling efficiency, we collected at an altitude for which the maximum deposition of Saharan dust (approx. 2000–3000 m) was reported . Further, the air temperature at the collection sides rarely, if at all (Marmolada), exceeds freezing during winter. Snow samples were collected based on established sampling methods [18, 48]. Briefly, samples were taken wearing protective suits (coveralls), facemasks, and vinyl gloves. Surface snow was removed using a clean sterilized shovel. The snowpit was carefully dug in order to maintain the stratigraphy of the snow layers and consisted of layer A: snow that fell after the Saharan dust event; layer B: Saharan sand-containing snow, clearly distinguishable by its light brown color, and layer C: snow that fell before the Saharan dust event (Fig. 1).The compacted snow of the layers indicated that no snowmelt took place after dust deposition. Samples were collected in sterile plastic containers or plastic bags, were transported on dry ice, and were stored at−80 °C.
Two snow samples with clearly visible dust layers and four sample of “clean” snow were collected at different depths from the entire pit profile at the Marmolada collection site. In the laboratory, samples were melted under a clean bench and acidified with HNO3 (ultrapure grade, Romil, Cambridge, UK) to obtain 2% solutions (v/v). CRC-ICP-MS measurements were performed using an Agilent 7500cx collision/reaction cell inductively coupled plasma mass spectrometer (CRC-ICP-MS) equipped with a CETAC ASX-520 auto-sampler. Measurements of selected major and trace elements were carried out with and without the collision cell in both helium and in hydrogen mode to reduce potential interferences. Instrumental drift and plasma fluctuations were corrected by online addition of a Rhodium internal standard solution (0.1 mg L−1, Ultra Scientific, Milano, Italy, 1000 mg L−1 stock solution).
The elemental suite was quantified using an external calibration. Five calibration standards ranging from 0.1 to 100 μg L−1 were prepared from the 10 mg L−1 multi-elemental standards CLM-2AN and IMS-101 (Ultra Scientific, Milano, Italy). Three additional calibrations points were prepared for the major crustal elements (Fe, Al, Na, K, Ca, Mg, Ti) from single standard solutions (ULTRA Scientific, 1000 mg L−1). The concentrations of these ranged from 200 to 2000 μg L−1.
For quality control purposes a certified reference material (CRM TMRAIN-04, lot 0913, Envir. Canada) was analyzed. The measured values are in good agreement with the certified and information values for this CRM (Additional file 1: Table S3).
Per collection site, five snow samples were taken. A snow sample set consists of three samples: layer A—fresh snow above the Saharan sand; layer B—snow containing Saharan sand; and layer C—snow below the Saharan sand layer (Fig. 1). Depending on snow height on the two mountains, layer A was collected from 30 to 60 cm, layer B from 70 to 100 cm, and layer C from 120 to 180 m under the snow surface. Additional six soil samples were taken at the Latemar collection site after snowmelt in a depth of approximately 10 to 20 cm under the surface.
All samples were gently melted and opened inside a clean bench. Melted snow (approx. 30 ml) was filtered (MO BIO Water filter; 0,22 μm), and genomic DNA was extracted using the PowerWater® DNA Isolation Kit (MO BIO Laboratories Inc., Carlsbad, USA) according to the manufacturer’s instructions. Soil samples were extracted using the FastDNA Spin Kit for Soil (MP Biomedicals, Santa Ana, USA) according to the manufacturer’s instructions. DNA quality was assessed by gel electrophoresis and UV-Vis spectroscopy. High-throughput metagenomics sequencing of the variable V3-V5 region of the bacterial 16S rRNA gene and of the fungal ITS1 region was performed on a GS FLX+ system using the XL+ chemistry following the manufacture’s protocols.
Raw 454 files were demultiplexed using the Roche’s sff file software. Reads were pre-processed using the MICCA pipeline . Operational taxonomic units (OTUs) were assigned by clustering the sequences with a threshold of 97% pair-wise identity, and their representative sequences were classified using the RDP  software version 2.8.
Alpha (within-sample richness) and beta diversity (between-sample dissimilarity) estimates were computed using the phyloseq R package . Permutational MANOVA (PERMANOVA) statistical tests were performed using the R package vegan  (adonis function) with 9999 permutations. See supplementary information for full detailed methods.
Griffin DW. Atmospheric movement of microorganisms in clouds of desert dust and implications for human health. Clin Microbiol Rev. 2007;20:459–77.
Brown JK, Hovmoller MS. Aerial dispersal of pathogens on the global and continental scales and its impact on plant disease. Science. 2002;297:537–41.
Kellogg CA, Griffin DW. Aerobiology and the global transport of desert dust. Trends Ecol Evol. 2006;21:638–44. Available from: http://dx.doi.org/10.1016/j.tree.2006.07.004.
Barberán A, Henley J, Fierer N, Casamayor EO. Structure, inter-annual recurrence, and global-scale connectivity of airborne microbial communities. Sci Total Environ. 2014;487:187–95. Elsevier B.V, Available from: http://dx.doi.org/10.1016/j.scitotenv.2014.04.030.
Smith DJ, Griffin DW, Mcpeters RD, Ward PD, Schuerger AC. Microbial survival in the stratosphere and implications for global dispersal. Aerobiologia (Bologna). 2011;27:319–32.
Chuvochina MS, Marie D, Chevallier S, Petit J-R, Normand P, Alekhina IA, et al. Community variability of bacteria in Alpine snow (Mont Blanc) containing Saharan dust deposition and their snow colonisation potential. Microbes Environ. 2011;26:237–47.
Pratt KA, DeMott PJ, French JR, Wang Z, Westphal DL, Heymsfield AJ, et al. In situ detection of biological particles in cloud ice-crystals. Nat Geosci. 2009;2:398–401. Nat Publ Group, Available from: http://dx.doi.org/10.1038/ngeo521.
Meola M, Lazzaro A, Zeyer J. Bacterial composition and survival on Sahara dust particles transported to the European Alps. Front Microbiol. 2015;6:1–17.
Simon C, Wiezer A, Strittmatter AW, Daniel R. Phylogenetic diversity and metabolic potential revealed in a glacier ice metagenome. Appl Environ Microbiol. 2009;75:7519–26. http://dx.doi.org/10.1128/AEM.00946-09.
Rogers SO, Starmer WT, Castello JD. Recycling of pathogenic microbes through survival in ice. Med Hypotheses. 2004;63:773–7. Available from: http://dx.doi.org/10.1016/j.mehy.2004.04.004.
Costello EK, Schmidt SK. Microbial diversity in alpine tundra wet meadow soil: novel Chloroflexi from a cold, water-saturated environment. Environ Microbiol. 2006;8:1471–86.
Kellogg CA, Shinn EA. Dust in the wind: long range transport of dust in the atmosphere and its implications for global public and ecosystem health. Glob Chang Hum Heal. 2001;2:20–33.
Goudie AS. Desert dust and human health disorders. Environ Int. 2014;63:101–13. Elsevier Ltd, Available from: http://dx.doi.org/10.1016/j.envint.2013.10.011.
García-Pando CP, Stanton MC, Diggle PJ, Trzaska S, Miller RL. Soil dust aerosols and wind as predictors of seasonal meningitis incidence. Environ Health Perspect. 2014;122:679–86.
Lee S-K, Park W, Baringer MO, Gordon AL, Huber B, Liu Y. Pacific origin of the abrupt increase in Indian Ocean heat content during the warming hiatus. Nat Geosci. 2015;8:445–9. Nature Publishing Group, Available from: http://dx.doi.org/10.1038/ngeo2438.
Ji Z, Wang G, Yu M, Pal JS. Potential climate effect of mineral aerosols over West Africa. Part II- contribution of dust and land cover to future climate change. Clim. Dyn. 2015;1–19. Springer Berlin Heidelberg. Available from: http://dx.doi.org/10.1007/s00382-015-2792-x.
Bonasoni P, Cristofanelli P, Marinoni A, Duchi R, Calzolari F, Roccato F, et al. Italian Climate Observatory “O. Vittori” at Mt.Cimone. GAW-WMO Global Station-WINTER 2013/2014 REPORT [Internet]. 2014. Available from: http://www.isac.cnr.it/cimone/sites/default/files/ICOVCimoneReport_3.pdf. Accessed 1 Mar 2017.
Maki T, Aoki K, Kobayashi F, Kakikawa M, Tobo Y, Matsuki A, et al. Characterization of halotolerant and oligotrophic bacterial communities in Asian desert dust (KOSA) bioaerosol accumulated in layers of snow on Mount Tateyama, Central Japan. Aerobiologia (Bologna). 2011;27:277–90.
METEOTRENTINO. MeteoTrentino snow event records, station data and season summary bulletins (in Italian) [Internet]. [cited 2017 Jan 20]. Available from: http://www.meteotrentino.it/neve-ghiacci/neve/calendario.aspx?id=216.
Scheuvens D, Schütz L, Kandler K, Ebert M, Weinbruch S. Bulk composition of northern African dust and its source sediments - a compilation. Earth Sci Rev. 2013;116:170–94. Elsevier B.V, Available from: http://dx.doi.org/10.1016/j.earscirev.2012.08.005.
Abed AM, Al Kuisi M, Khair HA. Characterization of the Khamaseen (spring) dust in Jordan. Atmos Environ. 2009;43:2868–76. Elsevier Ltd, Available from: http://dx.doi.org/10.1016/j.atmosenv.2009.03.015.
Favet J, Lapanje A, Giongo A, Kennedy S, Aung Y, Cattaneo A, et al. Microbial hitchhikers on intercontinental dust : catching a lift in Chad. ISME J. 2013;7:850–67.
Sterflinger K, Tesei D, Zakharova K. Fungi in hot and cold deserts with particular reference to microcolonial fungi. Fungal Ecol. 2012;5:453–62. Elsevier Ltd, Available from: http://dx.doi.org/10.1016/j.funeco.2011.12.007.
Goudie AS. Dust storms: recent developments. J Environ Manage. 2009;90:89–94. Elsevier Ltd, Available from: http://dx.doi.org/10.1016/j.jenvman.2008.07.007.
Swap R, Garstang M, Greco S. Saharan dust in the Amazon Basin. Tellus. 1992;44B:133–49.
Gallisai R, Peters F, Volpe G, Basart S, Baldasano JM. Saharan dust deposition may affect phytoplankton growth in the mediterranean sea at ecological time scales. PLoS One. 2014;9:e110762.
Hervàs A, Camarero L, Reche I, Casamayor EO. Viability and potential for immigration of airborne bacteria from Africa that reach high mountain lakes in Europe. Environ Microbiol. 2009;11:1612–23. Available from: http://dx.doi.org/10.1111/j.1462-2920.2009.01926.x.
Peter H, Hörtnagl P, Reche I, Sommaruga R. Bacterial diversity and composition during rain events with and without Saharan dust influence reaching a high mountain lake in the Alps. Environ Microbiol Rep. 2014;6:618–24. Available from: http://dx.doi.org/10.1111/1758-2229.12175.
Reche I, Ortega-retuerta E, Romera O, Pulido-villena E, Morales-baquero R, Casamayor EO. Effect of Saharan dust inputs on bacterial activity and community composition in Mediterranean lakes and reservoirs. Limnol Ocean. 2009;54:869–79.
Rainey FA, Ray K, Ferreira M, Gatz BZ, Nobre MF, Bagaley D, et al. Extensive diversity of ionizing-radiation-resistant bacteria recovered from Sonoran desert soil and description of nine new species of the genus deinococcus obtained from a single soil sample. Appl Environ Microbiol. 2005;71:5225–35.
Markus CM, Rohde M, Spro C, Klenk H. Geodermatophilus africanus sp.nov., a halotolerant actinomycete isolated from Saharan desert sand. Antonie Van Leeuwenhoek. 2013;104:207–16.
Maki T, Susuki S, Kobayashi F, Kakikawa M, Tobo Y, Yamada M, et al. Phylogenetic analysis of atmospheric halotolerant bacterial communities at high altitude in an Asian dust (KOSA) arrival region, Suzu City. Sci Total Environ. 2010;408:4556–62. Elsevier B.V, Available from: http://dx.doi.org/10.1016/j.scitotenv.2010.04.002.
Maki T, Hara K, Kobayashi F, Kurosaki Y, Kakikawa M, Matsuki A, et al. Vertical distribution of airborne bacterial communities in an Asian-dust downwind area, Noto Peninsula. Atmos Environ. 2015;119:282–93. Elsevier Ltd, Available from: http://dx.doi.org/10.1016/j.atmosenv.2015.08.052.
Nicholson WL, Munakata N, Horneck G, Melosh HJ, Setlow P. Resistance of Bacillus endospores to extreme terrestrial and extraterrestrial environments. Microbiol Mol Biol Rev. 2000;64:548–72. Available from: http://dx.doi.org/10.1128/MMBR.64.3.548-572.2000.
Yung PT, Shafaat HS, Connon SA, Ponce A. Quantification of viable endospores from a Greenland ice core. FEMS Microbiol Ecol. 2007;59:300–6. Available from: https://doi.org/10.1111/j.1574-6941.2006.00218.x.
Rime T, Hartmann M, Brunner I, Widmer F, Zeyer J, Frey B. Vertical distribution of the soil microbiota along a successional gradient in a glacier forefield. Mol Ecol. 2015;24:1091–108.
Gorbushina AA, Kort R, Schulte A, Lazarus D, Schnetger B, Brumsack H, et al. Life in Darwin’s dust: intercontinental transport and survival of microbes in the nineteenth century. Environ Microbiol. 2007;9:2911–22.
Ohm RA, Feau N, Henrissat B, Schoch CL, Horwitz BA, Barry KW, et al. Diverse lifestyles and strategies of plant pathogenesis encoded in the genomes of eighteen Dothideomycetes fungi. PLoS Pathog. 2012;8:e1003037. Available from: http://dx.doi.org/10.1371/journal.ppat.1003037.
Legendre M, Bartoli J, Shmakova L, Jeudy S, Labadie K, Adrait A. Thirty-thousand-year-old distant relative of giant icosahedral DNA viruses with a pandoravirus morphology. Proc Natl Acad Sci. 2014;111:4274–9.
Brunekreef B, Ayres JG, Forastiere F, Forsberg B, Ku N, Pekkanen J, et al. Ten principles for clean air. Eur Respir J. 2013;39:525–8.
Gostincar C, Ohm RA, Kogej T, Sonjak S, Turk M, Zajc J, et al. Genome sequencing of four Aureobasidium pullulans varieties: biotechnological potential, stress tolerance, and description of new species. BMC Genomics. 2014;15:549. Available from: http://dx.doi.org/10.1186/1471-2164-15-549.
Hawkes M, Rennie R, Sand C, Vaudry W. Aureobasidium pullulans infection : fungemia in an infant and a review of human cases. Diagn Microbiol Infect Dis. 2005;51:209–13.
Monteil CL, Bardin M, Morris CE. Features of air masses associated with the deposition of Pseudomonas syringae and Botrytis cinerea by rain and snowfall. ISME. 2014;8:2290–304. Nature Publishing Group, Available from: http://dx.doi.org/10.1038/ismej.2014.55.
Delort AM, Vaïtilingom M, Amato P, Sancelme M, Parazols M, Mailhot G, et al. A short overview of the microbial population in clouds: Potential roles in atmospheric chemistry and nucleation processes. Atmos Res. 2010;98:249–60. Elsevier B.V, Available from: http://dx.doi.org/10.1016/j.atmosres.2010.07.004.
Creamean JM, Suski KJ, Rosenfeld D, Cazorla A, Demott PJ, Sullivan RC, et al. Dust and biological aerosols from the Sahara and Asia influence percipitation in the western U.S. Science. 2013;339:1572–8. http://dx.doi.org/10.1126/science.1227279
Calastrini F, Guarnieri F, Becagli S, Busillo C, Chiari M, Dayan U, et al. Desert dust outbreaks over mediterranean basin: A modeling, observational, and synoptic analysis approach. Adv. Meteorol. 2012; 2012. Available from: http://dx.doi.org/10.1155/2012/246874
Psenner R. Living in a dusty world: airborne dust as a key factor for alpine lakes. Water, Air Soil Polution. 1999;112:217–27.
Tanaka D, Tokuyama Y, Terada Y, Kunimochi K, Mizumaki C, Tamura S, et al. Bacterial communities in Asian dust-containing snow layers on Mt. Tateyama, Japan. Bull Glaciol Res. 2011;29:31–9.
Albanese D, Fontana P, De Filippo C, Cavalieri D, Donati C. MICCA: a complete and accurate software for taxonomic profiling of metagenomic data. Sci Rep. 2015;5:9743. Available from: http://dx.doi.org/10.1038/srep09743.
Wang Q, Garrity GM, Tiedje JM, Cole JR. Naive Bayesian classifier for rapid assignment of rRNA sequences into the new bacterial taxonomy. Appl Environ Microbiol. 2007;73:5261–7. Available from: http://dx.doi.org/10.1128/AEM.00062-07.
McMurdie PJ, Holmes S. Phyloseq: an R package for reproducible interactive analysis and graphics of microbiome census data. PLoS One. 2013;8:e61217.
Oksanen AJ, Blanchet FG, Kindt R, Minchin PR, Hara RBO, Simpson GL, et al. R Package “vegan” [Internet]. Community Ecol. Packag. version 2.3-1. 2015. Available from: https://cran.r-project.org/web/packages/vegan/vegan.pdf.
Katra I, Arotsker L, Krasnov H, Zaritsky A, Kushmaro A, Ben-Dov E. Richness and diversity in dust stormborne biomes at the southeast mediterranean. Sci Rep. 2014;4:5265. Available from: http://dx.doi.org/10.1038/srep05265.
Wilhelm RC, Niederberger TD, Greer C, Whyte LG. Microbial diversity of active layer and permafrost in an acidic wetland from the Canadian High Arctic. Can J Microbiol. 2011;57:303–15. Available from: http://dx.doi.org/10.1139/w11-004. Accessed 1 Mar 2017.
Franca L, Sannino C, Turchetti B, Buzzini P, Margesin R. Seasonal and altitudinal changes of culturable bacterial and yeast diversity in Alpine forest soils. Extremophiles. 2016;20:855–73 Springer Japan.
Xu Z, Hansen MA, Hansen LH, Jacquiod S, Sørensen SJ. Bioinformatic Approaches Reveal Metagenomic Characterization of Soil Microbial Community. PLoS One. 2014;9:e93445. Available from: http://dx.doi.org/10.1371/journal.pone.0093445.
We thank the Centro Valanghe di Arabba for their support during snow sampling.
Financial support for this research was provided by the Transnational Access to Research Infrastructures activity in the 7th Framework Programme of the EC under the Trees4Future project (no. 284181), the METAFOODLABS grant from the Provincia Autonoma di Trento (PAT Prot. S116/2012/537723), the Tawani Foundation and the European Union’s Seventh Framework Programme (FP7/2007-2013)/ERC, Grant agreement no. 267696-EARLYhumanIMPACT.
Availability of data and materials
The sequence data supporting the results of this article are available at the European Nucleotide Archive (www.ebi.ac.uk/ena) under the study accession number PRJEB11741. Sample accessions and metadata are available in Additional file 3: Table S5.
DC and FM led the study. TW, MPa, CB, DC, and FM conceived the initial study design. TW, JG, MPi, and DC collected the samples. TW, JG, and MPi performed the experiments. DA, JG, CD, MPa, and CB analyzed the data. TW, DA, JG, CD, MPa, BS, CB, DC, and FM interpreted the data. TW, BS, CB, DC, and FM wrote the paper with significant input from all other authors. All authors read and approved the final manuscript.
The authors declare that they have no competing interests.
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Weil, T., De Filippo, C., Albanese, D. et al. Legal immigrants: invasion of alien microbial communities during winter occurring desert dust storms. Microbiome 5, 32 (2017). https://doi.org/10.1186/s40168-017-0249-7