- Open Access
Bacterial communities on classroom surfaces vary with human contact
Microbiome volume 2, Article number: 7 (2014)
Humans can spend the majority of their time indoors, but little is known about the interactions between the human and built-environment microbiomes or the forces that drive microbial community assembly in the built environment. We sampled 16S rRNA genes from four different surface types throughout a university classroom to determine whether bacterial assemblages on each surface were best predicted by routine human interactions or by proximity to other surfaces within the classroom. We then analyzed our data with publicly-available datasets representing potential source environments.
Bacterial assemblages from the four surface types, as well as individual taxa, were indicative of different source pools related to the type of human contact each surface routinely encounters. Spatial proximity to other surfaces in the classroom did not predict community composition.
Our results indicate that human-associated microbial communities can be transferred to indoor surfaces following contact, and that such transmission is possible even when contact is indirect, but that proximity to other surfaces in the classroom does not influence community composition.
In the developed world, humans spend a majority of their lives indoors. While indoors we encounter microorganisms on virtually every surface we touch, and this frequent exposure to indoor microbes carries with it the potential for disease transmission, as well as interactions with our own commensal microbiome [1–3]. Yet we have very little knowledge regarding the ecological processes that drive microbial community assembly indoors, nor do we understand the degree to which humans share microbes with indoor surfaces.
For any given indoor surface, microbial community composition is likely shaped by habitat-specific environmental constraints (such as the type of surface material), and dispersal sources (which include humans, bioaerosols and other surfaces within a space). If dispersal among surfaces is a primary determinant of community structure, then adjacent surfaces should be more similar in community composition than surfaces further apart. If dispersal from humans is a major determinant, then community structure should vary with frequency and nature of human contact.
Because humans harbor distinguishably different microbial assemblages on different parts of their bodies [4–6], it is reasonable to assume that different indoor surface types could harbor different microbial communities due to frequent contact with specific body parts. Several studies suggest that this may be the case. In a recent survey of public restroom surfaces, Flores and colleagues  found that microbes on restroom surfaces were similar to those found on specific human body parts, with the strongest association observed between toilet surfaces and gut and vaginal communities. These associations are to be expected given the direct contact common in this environment between surfaces and the human body. Associations between human use and bacterial community composition have also been found on residential kitchen surfaces , with bacterial taxa commonly found on human skin predominating on kitchen surfaces, consistent with frequent skin-to-surface contact. It is not known whether more indirect skin-to-surface contact, such as sitting fully clothed on a chair, might result in similar bacterial transmission.
Here we test: (a) if different types of surfaces in a classroom vary in microbial community composition; (b) if their composition varies predictably with the type of human contact; and (c) whether these associations are stronger than the association between community similarity and spatial distance. We sampled desktops, floors, walls and chair seats in a classroom to determine whether these groups of surfaces harbored distinct bacterial assemblages related to their differing types of human contact.
All samples were collected in the same classroom at the Lillis Business Complex, University of Oregon, Eugene, OR, USA, during 4–5 August 2011. During the week prior to the sampling period, the classroom was occupied by classes daily, including on the first day of sampling. Desks, floors, chair seats and walls were sampled (n = 18, 18, 18 and 16, respectively) following identical protocols. Samples were distributed throughout the classroom (9.2 m × 15.2 m). Pairwise spatial distance between samples ranged from 0 to 16 m, with sets of chair, desk and floor samples generally taken within 1 m2 of one another. Figure 1 displays the spatial distribution of samples within the classroom. Surfaces were sampled using a nylon flocked swab (copanusa.com; #552C) moistened with sterile buffer solution (0.15 M NaCl, 0.1 Tween20). A 289 cm2 (17 cm × 17 cm) area was swabbed from each surface. Chairs were sampled in the center of their upholstered seat surfaces; desks (plastic laminate surface) and floors (linoleum) were sampled directly above and below chair seats; and walls (latex paint) were sampled around the perimeter of the room (Figure 1). We were not able to ascertain the cleaning schedule prior to sampling, but all surfaces were visibly devoid of standing dust. All samples were frozen (−80°C) until DNA extraction.
DNA extraction, amplification and Illumina library preparation followed methods described previously [9, 10]. DNA was extracted from swabs using a PowerWater DNA extraction kit (MoBio Laboratories, Inc., Carlsbad, CA, USA) with the following modifications: samples were frozen and thawed for two cycles; bead beating length was extended to 10 minutes; and samples were eluted in 50 μL Solution PW6.
The V4 region of the 16S rRNA gene was amplified using the F515/R806 primer combination (5′-GTGCCAGCMGCCGCGG-3′, 5′-TACNVGGGTATCTAATCC-3′; ). Amplification proceeded in two steps using a custom Illumina preparation protocol where PCR1 was performed with forward primers that contained partial unique barcodes and partial Illumina adapters. The remaining ends of the Illumina adapters were attached during PCR2, and barcodes were recombined in silico using paired-end reads. Adapter sequences are detailed in Additional file 1. All extracted samples were amplified in triplicate for PCR1 and triplicates were pooled before PCR2. PCR1 (25 μL total volume per reaction) consisted of the following steps: 5 μL 5× HF buffer (Thermo Fisher Scientific, Waltham, MA, USA), 0.5 μL deoxyribonucleotide triphosphates (10 mM, Invitrogen, Life Technologies, Grand Island, NY, USA), 0.25 μL Phusion Hotstart II polymerase (0.5 units; Thermo Fisher Scientific), 13.25 μL certified nucleic-acid free water, 0.5 μL (10 μM) forward primer, 0.5 μL (10 μM) reverse primer, and 5 μL template DNA. The PCR1 conditions were as follows: initial denaturation for 2 minutes at 98°C; 22 cycles of 20 seconds at 98°C, 30 seconds at 50°C and 20 seconds at 72°C; and 72°C for 2 minutes for final extension. After PCR1, the triplicate reactions were pooled and cleaned with the Qiagen MinElute PCR Purification Kit according to the manufacturer’s protocol (Qiagen, Germantown, MD, USA). Samples were eluted in 11.5 μL Buffer EB (10 mM Tris-Cl, pH 8.5, Qiagen). For PCR2, a single primer pair was used to add the remaining Illumina adapter segments to the ends of the concentrated amplicons of PCR1. The PCR2 (25 μL volume per reaction) consisted of the same combination of reagents that was used in PCR1, along with 5 μL concentrated PCR1 product as a template. The PCR2 conditions were as follows: 2 minutes denaturation at 98°C; 12 cycles of 20 seconds at 98°C, 30 seconds at 66°C and 20 seconds at 72°C; and 2 minutes at 72°C for final extension.
Amplicons were size selected by gel electrophoresis, extracted, quantified on a Qubit 2.0 Fluorometer (Life Technologies, Carlsbad, CA, USA), concentrated, combined in equimolar concentrations and sequenced on the Illumina MiSeq platform at the Dana-Farber/Harvard Cancer Center DNA Resource Core (Boston, MA; dnaseq.med.harvard.edu).
Sequence processing was performed using the FastX Toolkit (http://hannonlab.cshl.edu/fastx_toolkit) and QIIME . Quality filtering settings were as follows: a minimum 30 quality score over at least 75% of the sequence read, no ambiguous bases, and 1 primer mismatch allowed. After quality control and barcode assignment, the remaining high-quality sequences (mean 13,786 sequences per sample ± 4,735 SD) were binned into operational taxonomic units (OTUs) at a 97% sequence similarity cutoff using uclust . High-quality sequences from each OTU cluster were taxonomically identified using reference sequences from the Greengenes database (2011 release; [14, 15]), and plant-chloroplast OTUs were removed by name (“Streptophyta”) based on Greengenes taxonomic classifications (mean = 8% of sequences in each sample ± 10% SD). All samples retaining more than 4,000 sequences (n = 15, 14, 15 and 14 for desks, walls, floors, and chairs, respectively) were rarefied to that level for even sampling depth. Sequence files and metadata for all samples used in this study have been deposited in Figshare (http://dx.doi.org/10.6084/m9.figshare.687155). Metadata, the unrarefied OTU table, and corresponding taxonomic classifications have all been included as Additional files 2, 3 and 4, respectively.
All statistical analyses were performed in R , primarily utilizing multivariate community ecology procedures in the labdsv and vegan packages [17, 18]. A full record of all statistical analysis is included as Additional file 5, and was created using the knitr package in R . Community distance between samples was calculated using the Canberra distance, implemented in the vegan package. Given that the four surface types we sampled represent potentially similar microbial habitats, we did not expect to see major phylogenetic differences among the communities. Thus, we used the Canberra taxonomic metric as a way to emphasize community differences driven by relatively rare taxa with a decreased emphasis on total abundance and phylogenetic community distance. Distance-based redundancy analysis (DB-RDA) was performed with the capscale function in vegan. Individual OTUs exert varying degrees of influence, or weight, on DB-RDA clustering patterns, and we selectively tested the strength of association between the strongest weighted individual bacterial OTUs and relative surface types (that is, indicator value, as defined in ) with the indval function in labdsv. Mantel tests, using the mantel function in vegan, were used to test for a community dissimilarity correlation with spatial distance within the classroom for each of the four surface types, as well as all sites regardless of surface type. To assess community similarity to various potential source habitats (soil, aquatic, phyllosphere, human skin and human gut), we compared all samples at the class level to publicly-available datasets from representative potential source environments [4, 21–24] using principal components analysis. Positions of each point in relation to source environments along the first principal component are used to compare their similarity to either human skin or phyllosphere bacterial communities.
Results and discussion
After rarefaction to 4,000 sequences per sample, 58 surface samples were represented by a total of 3,745 bacterial OTUs. Approximately half (51.4%) of OTUs were found only once or twice, and these were included in analysis. The most commonly detected OTU (Sphingomonas sp.) accounted for 1.9% of all sequences. The four surface types harbored significantly different communities (P = 0.001; F = 2.34; from permutational multivariate analysis of variation on Canberra distances; Figure 2). Within each surface type, bacterial community composition was not significantly predicted by spatial distance among samples (all four P values >0.1; from Mantel tests). Even when all surfaces were considered together, spatial distance was not a significant predictor of bacterial community composition (P = 0.4). These results suggest that site-specific factors (for example, habitat selection or dispersal from specific body sites) are more important than dispersal among sites for bacterial community assembly in the built environment.
We found that surface communities were significantly associated with taxa specific to distinct microbial sources (Table 1). Bacterial OTUs labeled in Figure 2b are the most strongly weighted OTUs for each surface type that are also significant (P < 0.05) indicator OTUs. Three of the strongest indicators for chair seats were Lactobacillus OTUs closely related to taxa commonly found in the human gut and vagina, in addition to other human-associated Corynebacterium and Staphylococcus species. Desk surfaces were significantly associated with several indicator taxa from human body habitats; two of the strongest desk surface indicator OTUs were Streptococcus species commonly found in human skin and oral samples, as well as another Streptococcus originally isolated from purulent infections. Floors in the classroom also harbored skin-associated OTUs, but were more strongly indicated by a cyanobacterial OTU, presumably from a non-human environmental source. Walls are likely the surfaces in this study that have the least contact with humans; this was consistent with our observation that these surfaces were associated with indicator taxa related to Sphingomonas and Alicyclobacillus species that are commonly abundant in airborne bacterial assemblages [10, 25]. Both walls and floors held larger relative proportions of Cyanobacteria than seats and desktops, likely reflecting soil and bioaerosols as microbial sources. Few other major phylogenetic differences are evident at a broad taxonomic level (Figure 3).
The community variation we observed among surface types could be the result of either surface-specific environmental filtering or dispersal. Evidence to date suggests that microbial communities on indoor surfaces, with a few exceptions, are likely primarily dispersal-driven given the well-documented inputs from dust, settled airborne particles, outdoor air and surface contact [7–9, 25–27]. The relative importance of in situ community dynamics and habitat filtering remain to be fully understood in the built environment.
Dispersal between human skin and contacted surfaces is well documented, primarily in a medical context using known pathogenic strains [1, 28, 29]. However, the vast majority of bacteria on and in the human body are not pathogens, but rather appear to be commensal components of our own microbiome . Recent evidence has suggested that the unique microbial assemblages detected on different human body parts can be transferred to indoor surfaces following contact [26, 31], and that these bacterial traces of human contact are evident in places such as restrooms . Our results suggest that this transmission is possible even when that contact is indirect, and that such contact has a greater impact on microbial community structure indoors than dispersal among surfaces.
We are constantly surrounded by diverse microbial communities indoors, and we are just beginning to understand how our interactions in the built environment shape those communities and our own human microbiome. Our results indicate that human-associated microbial communities can be transferred to indoor surfaces following contact, and that such transmission is possible even when contact is indirect, but that proximity to other surfaces in the classroom does not influence community composition.
Availability of supporting data
Sequence files and metadata for all samples used in this study have been deposited in Figshare (http://dx.doi.org/10.6084/m9.figshare.687155). A full record of all statistical analysis is included as Additional file 5, and was created using the knitr package in R . Original R scripts are available in GitHub (https://github.com/jfmeadow/Meadow_etal_Surfaces). Metadata, the unrarefied OTU table, and corresponding taxonomic classifications have all been included as Additional files 2, 3 and 4, respectively.
distance-based redundancy analysis
operational taxonomic unit
polymerase chain reaction.
Pessoa-Silva CL, Dharan S, Hugonnet S, Touveneau S, Posfay-Barbe K, Pfister R, Pittet D: Dynamics of bacterial hand contamination during routine neonatal care. Infect Control Hosp Epidemiol. 2004, 25: 192-197. 10.1086/502376.
Fujimura KE, Demoor T, Rauch M, Faruqi AA, Jang S, Johnson CC, Boushey HA, Zoratti E, Ownby D: Lukacs NW. 2013, House dust exposure mediates gut microbiome Lactobacillus enrichment and airway immune defense against allergens and virus infection. Proc Natl Acad Sci: Lynch SV, doi:10.1073/pnas.1310750111
Davis MF, Iverson SA, Baron P, Vasse A, Silbergeld EK, Lautenbach E, Morris DO: Household transmission of meticillin-resistant Staphylococcus aureus and other staphylococci. Lancet Infect Dis. 2012, 12: 703-716. 10.1016/S1473-3099(12)70156-1.
Costello EK, Lauber CL, Hamady M, Fierer N, Gordon JI, Knight R: Bacterial community variation in human body habitats across space and time. Science. 2009, 326: 1694-1697. 10.1126/science.1177486.
Fierer N, Hamady M, Lauber CL, Knight R: The influence of sex, handedness, and washing on the diversity of hand surface bacteria. Proc Natl Acad Sci USA. 2008, 105: 17994-17999. 10.1073/pnas.0807920105.
Grice EA, Kong HH, Conlan S, Deming CB, Davis J, Young AC, Bouffard GG, Blakesley RW, Murray PR, Green ED, Turner ML, Segre JA: Topographical and temporal diversity of the human skin microbiome. Science. 2009, 324: 1190-1192. 10.1126/science.1171700.
Flores GE, Bates ST, Knights D, Lauber CL, Stombaugh J, Knight R, Fierer N: Microbial biogeography of public restroom surfaces. PLoS One. 2011, 6: e28132-10.1371/journal.pone.0028132.
Flores GE, Bates ST, Caporaso JG, Lauber CL, Leff JW, Knight R, Fierer N: Diversity, distribution and sources of bacteria in residential kitchens. Environ Microbiol. 2013, 15: 588-596. 10.1111/1462-2920.12036.
Meadow JF, Bateman AC, Herkert KM, O’Connor TK, Green JL: Significant changes in the skin microbiome mediated by the sport of roller derby. PeerJ. 2013, 1: e53-
Meadow JF, Altrichter AE, Kembel SW, Kline J, Mhuireach G, Moriyama M, Northcutt D, O’Connor TK, Womack AM, Brown GZ, Green JL, Bohannan BJM: Indoor airborne bacterial communities are influenced by ventilation, occupancy, and outdoor air source. Indoor Air. 2013, 24: 41-48.
Liu Z, Lozupone CA, Hamady M, Bushman FD, Knight R: Short pyrosequencing reads suffice for accurate microbial community analysis. Nucleic Acids Res. 2007, 35: e120-10.1093/nar/gkm541.
Caporaso JG, Kuczynski J, Stombaugh J, Bittinger K, Bushman FD, Costello EK, Fierer N, Pena AG, Goodrich JK, Gordon JI, Huttley GA, Kelley ST, Knights D, Koenig JE, Ley RE, Lozupone CA, McDonald D, Muegge BD, Pirrung M, Reeder J, Sevinsky JR, Tumbaugh PJ, Walters WA, Widmann J, Yatsunenko T, Zaneveld J, Knight R: QIIME allows analysis of high-throughput community sequencing data. Nat Methods. 2010, 7: 335-336. 10.1038/nmeth.f.303.
Edgar RC: Search and clustering orders of magnitude faster than BLAST. Bioinformatics. 2010, 26: 2460-2461. 10.1093/bioinformatics/btq461.
DeSantis TZ, Hugenholtz P, Larsen N, Rojas M, Brodie EL, Keller K, Huber T, Dalevi D, Hu P, Andersen GL: Greengenes, a chimera-checked 16S rRNA gene database and workbench compatible with ARB. Appl Environ Microbiol. 2006, 72: 5069-5072. 10.1128/AEM.03006-05.
Cole JR, Wang Q, Cardenas E, Fish J, Chai B, Farris RJ, Kulam-Syed-Mohideen AS, McGarrell DM, Marsh T, Garrity GM, Tiedje JM: The Ribosomal Database Project: improved alignments and new tools for rRNA analysis. Nucleic Acids Res. 2009, 37: 141-145.
R Development Core Team: R: A Language and Environment for Statistical Computing. 2010, [http://cran.r-project.org]
Roberts DW: labdsv. 2010, Ordination and Multivariate Analysis for Ecology, [http://cran.r-project.org/web/packages/labdsv/index.html]
Oksanen J, Blanchet FG, Kindt R, Legendre P, O’Hara RB, Simpson GL, Solymos P, Stevens MHH, Wagner H: vegan. 2011, Community Ecology Package, [http://cran.r-project.org/web/packages/vegan/index.html]
Xie Y: knitr: a comprehensive tool for reproducible research in R. In Implementing Reprodcible Compututational Research. 2013, Chapman and Hall/CRC: Stodden V, Leisch F, Peng RD
Dufrene M, Legendre P: Species assemblages and indicator species: the need for a flexible asymmetrical approach. Ecol Monogr. 1997, 67: 345-366.
Redford AJ, Fierer N: Bacterial succession on the leaf surface: a novel system for studying successional dynamics. Microb Ecol. 2009, 58: 189-198. 10.1007/s00248-009-9495-y.
Nemergut DR, Townsend AR, Sattin SR, Freeman KR, Fierer N, Neff JC, Bowman WD, Schadt CW, Weintraub MN, Schmidt SK: The effects of chronic nitrogen fertilization on alpine tundra soil microbial communities: implications for carbon and nitrogen cycling. Environ Microbiol. 2008, 10: 3093-3105. 10.1111/j.1462-2920.2008.01735.x.
Hansel CM, Fendorf S, Jardine PM, Francis CA: Changes in bacterial and archaeal community structure and functional diversity along a geochemically variable soil profile. Appl Environ Microbiol. 2008, 74: 1620-1633. 10.1128/AEM.01787-07.
Crump BC, Peterson BJ, Raymond PA, Amon RMW, Rinehart A, McClelland JW, Holmes RM: Circumpolar synchrony in big river bacterioplankton. Proc Natl Acad Sci USA. 2009, 106: 21208-21212. 10.1073/pnas.0906149106.
Qian J, Hospodsky D, Yamamoto N, Nazaroff WW, Peccia J: Size-resolved emission rates of airborne bacteria and fungi in an occupied classroom. Indoor Air. 2012, 22: 339-351. 10.1111/j.1600-0668.2012.00769.x.
Fierer N, Lauber CL, Zhou N, McDonald D, Costello EK, Knight R: Forensic identification using skin bacterial communities. Proc Natl Acad Sci USA. 2010, 107: 6477-6481. 10.1073/pnas.1000162107.
Kembel SW, Meadow JF, O’Connor TK, Mhuireach G, Northcutt D, Kline J, Moriyama M, Brown GZ, Bohannan BJM, Green JL: Architectural design drives the biogeography of indoor bacterial communities. PLoS One. 2014, 9: e87093-10.1371/journal.pone.0087093.
Noble WC, Habbema JDF, van Furth R, Smith I, de Raay C: Quantitative studies on the dispersal of skin bacteria into the air. J Med Microbiol. 1976, 9: 53-61. 10.1099/00222615-9-1-53.
Pittet D, Dharan S, Touveneau S, Sauvan V, Perneger TV: Bacterial contamination of the hands of hospital staff during routine patient care. Arch Intern Med. 1999, 159: 821-826. 10.1001/archinte.159.8.821.
The Human Microbiome Project Consortium: Structure, function and diversity of the healthy human microbiome. Nature. 2012, 486: 207-214. 10.1038/nature11234.
Hübner N-O, Hübner C, Kramer A, Assadian O: Survival of bacterial pathogens on paper and bacterial retrieval from paper to hands: preliminary results. Am J Nurs. 2011, 111: 30-34.
This research was funded by a grant from the Alfred P. Sloan Foundation to the Biology and the Built Environment Center. We would like to thank Daniel Aughenbaugh, Laura Cavin, Jeff Kline, Kate Laue, Gwynne Mhuireach, Maxwell Moriyama, Dale Northcutt, and Iman Rajaie for their help during sampling. Cornelis de Kluyver, Stephanie Bosnyk, Gordon Burke, Greg Haider, George Hecht, Don Neet, Pete Rocksvold, Frank Sharpy and Del Smith were instrumental in assisting with building operations and access during the study.
The authors declare that they have no competing interests.
JFM analyzed the data and wrote the manuscript. AEA performed laboratory assays. SWK conceived the study and collected samples. MM conceived the study, prepared figures and collected samples. TKO conceived the study, performed laboratory assays and collected samples. AMW conceived the study and collected samples. GZB contributed resources. JLG conceived the study, contributed resources and collected samples. BJMB conceived the study, contributed resources and collected samples. All authors edited the manuscript and approved the final draft.
Electronic supplementary material
Additional file 1: Explanation of partial adapter sequences used in Illumina amplicon library preparation.(TXT 532 bytes)
Additional file 4: Taxonomic assignments for all operational taxonomic units in Additional file 3 .(CSV 426 KB)
About this article
Cite this article
Meadow, J.F., Altrichter, A.E., Kembel, S.W. et al. Bacterial communities on classroom surfaces vary with human contact. Microbiome 2, 7 (2014). https://doi.org/10.1186/2049-2618-2-7
- Built environment
- Microbial ecology
- Indoor microbiology