Review
Evolution of the indoor biome
NESCent Working Group on the Evolutionary Biology of the Built Environment,
Laura J. Martin1, Rachel I. Adams2, Ashley Bateman3, Holly M. Bik4, John Hawks5,
Sarah M. Hird4, David Hughes6, Steven W. Kembel7, Kerry Kinney8,
Sergios-Orestis Kolokotronis9, Gabriel Levy10, Craig McClain11, James F. Meadow12,
Raul F. Medina13, Gwynne Mhuireach14, Corrie S. Moreau15,
Jason Munshi-South9,16, Lauren M. Nichols17, Clare Palmer18, Laura Popova19,
Coby Schal17,20, Martin Täubel21, Michelle Trautwein22,
Juan A. Ugalde23, and Robert R. Dunn17,24
1
Department of Natural Resources, Cornell University, Ithaca, NY 14853, USA
Department of Plant and Microbial Biology, University of California Berkeley, Berkeley, CA 94720, USA
3
Department of Biology, Institute of Ecology and Evolution, University of Oregon, Eugene, OR 97403, USA
4
UC Davis Genome Center, University of California Davis, Davis, CA 95616, USA
5
Department of Anthropology, University of Wisconsin–Madison, Madison, WI 53706, USA
6
Department of Entomology, Penn State University, University Park, PA 16802, USA
7
Département des Sciences Biologiques, Université du Québec à Montréal, Montréal, QC H3C 3P8, Canada
8
Department of Civil, Architectural, and Environmental Engineering, University of Texas at Austin, Austin, TX 78712, USA
9
Department of Biological Sciences, Fordham University, Bronx, NY 10458, USA
10
Department of Philosophy and Religious Studies, Norwegian University of Science and Technology, NO-7491 Trondheim,
Norway
11
National Evolutionary Synthesis Center, Durham, NC, 27705, USA
12
Biology and the Built Environment Center, Institute of Ecology and Evolution, University of Oregon, Eugene, OR 97403, USA
13
Department of Entomology, Texas A&M University, College Station, TX 77843, USA
14
Department of Architecture, University of Oregon, Eugene, OR 97403, USA
15
Department of Science and Education, Field Museum of Natural History, Chicago, IL 60605, USA
16
Louis Calder Center–Biological Field Station, Fordham University, Armonk, NY 10504, USA
17
Department of Biological Sciences, North Carolina State University, Raleigh, NC 27695, USA
18
Department of Philosophy, Texas A&M University, College Station, TX 77843, USA
19
Barrett Honors College, Arizona State University, Tempe, AZ 85287, USA
20
Department of Entomology, North Carolina State University, Raleigh, NC 27695, USA
21
National Institute for Health and Welfare, Department of Health Protection, 70210 Kuopio, Finland
22
California Academy of Sciences, San Francisco, CA 94118, USA
23
Centro de Genómica y Bioinformática, Facultad de Ciencias, Universidad Mayor, Santiago, Chile
24
Center for Macroecology, Evolution and Climate, Natural History Museum of Denmark, University of Copenhagen,
Universitetsparken 15, DK-2100 Copenhagen Ø, Denmark
2
Few biologists have studied the evolutionary processes
at work in indoor environments. Yet indoor environments comprise approximately 0.5% of ice-free land area
– an area as large as the subtropical coniferous forest
biome. Here we review the emerging subfield of ‘indoor
biome’ studies. After defining the indoor biome and
tracing its deep history, we discuss some of its evolutionary dimensions. We restrict our examples to the
species found in human houses – a subset of the environments constituting the indoor biome – and offer preliminary hypotheses to advance the study of indoor
evolution. Studies of the indoor biome are situated at
the intersection of evolutionary ecology, anthropology,
Corresponding author: Martin, L.J. (LJM222@cornell.edu).
Keywords: urban ecology; anthrome; microbiome; phylogeography; built environment.
0169-5347/
ß 2015 Elsevier Ltd. All rights reserved. http://dx.doi.org/10.1016/j.tree.2015.02.001
architecture, and human ecology and are well suited for
citizen science projects, public outreach, and large-scale
international collaborations.
Glossary
Biome: Robert H. Whittaker first developed the biome concept to classify the
different realms of life found on Earth. His classification scheme was based on
two abiotic factors – precipitation and temperature – that he viewed to have the
largest impact on the distribution of species and their traits and function.
Subsequent biome classification systems have considered the biomes found in
the absence of human agency and so exclude much of Earth’s terrestrial area.
One exception is the anthrome framework, which includes biomes engendered
by humans [2]. However, even anthromes deal only with outdoor environments.
Indoor biome: the ecological realm comprising species that reside and can
(although do not necessarily always) reproduce in enclosed and semi-enclosed
built structures.
Indoor environment: the space enclosed by walled and roofed structures built
by organisms to shelter themselves, their symbiotic partners, or stored goods.
For the purposes of this review we focus on the indoor environments created
by humans.
Trends in Ecology & Evolution, April 2015, Vol. 30, No. 4
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The indoor biome
Evolution occurs everywhere, even in the most densely
settled places. Indeed, Darwin based his arguments for
natural selection on domesticated plants and animals.
Recent work in the fields of evolutionary biology, ecology,
anthropology, and building sciences turns our attention
back to species that coexist with humans. Much of this
work is conducted in outdoor spaces [1], but a growing
body of work addresses evolution in the indoor biome (see
Glossary).
The indoor biome is expansive. Estimates of the extent
of residential and commercial buildings range between
1.3% [3] and 6% [4] of global ice-free land area, an area
as extensive as other small biomes such as flooded grasslands and tropical coniferous forests (Figure 1). In addition, whereas the area of flooded grasslands and tropical
coniferous forests is shrinking, that of the indoor biome is
rapidly growing [5], as is our ability to study indoor species
thanks to citizen science, new approaches in genetics, and
calls to integrate humans into the ecosystem concept [6–
10] (Figure 2).
Here we review the rich but fragmented literature on
evolution in the indoor biome. For the purpose of brevity we
restrict our examples to one type of built structure –
human dwellings – although the indoor biome encompasses all built structures (Box 1, Table 1).
A brief history of the indoor biome
The nests of birds, termites, and ants are part of the
extended phenotype of those organisms, as are those of
our closest living relatives, the great apes, which construct
nests across a broad range of environments. Our common
ancestors would probably also have used regular sleeping
places with constructed nests [11]. Primate nests, like
Box 1. Built structures other than houses
In this review we have focused on houses, but many other buildings
constitute the indoor biome. These include places of worship, food
storage areas, commercial spaces, factories, offices, and restaurants
[2]. In addition, houses are not closed systems; many materials flow
into and out of them. For instance, a diverse range of microorganisms is present in municipal water supply and piping biofilms that
enter homes via water lines, so mapping the inflow and outflow of
organisms into the indoor biome may be a nontrivial challenge.
Furthermore, it should be recognized that studies of indoor biomes
cannot avoid intersecting questions of politics and justice. It should
not be taken for granted that humans live in houses. An estimated
100 million people were homeless in 2005 [United Nations
Commission on Human Rights (2005) Press briefing by special
rapporteur on right to adequate housing (http://www.un.org/News/
briefings/docs/2005/kotharibrf050511.doc.htm)], while human structures are sometimes abandoned and may persist as indoor
environments without a human presence. It should also not escape
notice that structures also vary widely by place. For example,
approximately 50% of Canadians live in houses with seven or more
rooms, while only 9% of people from Burkina-Faso do so [United
Nations Department of Economic and Social Affairs (2012)
Table 21. In Compendium of Housing Statistics (http://unstats.un.
org/unsd/demographic/sconcerns/)]. It is therefore important, as
with all biological studies, to be context specific [75].
modern built environments, are places where bodies habitually rest and thus suitable places for organisms that
depend on access to bodies to reproduce. How the nest is
constructed thus influences the species to which the builder is exposed. Chimpanzees choose nesting sites and construction methods that reduce arthropod parasites [12],
suggesting that, in the past, parasites imposed selection on
primate nesting behavior. Meanwhile, the evolutionary
history of many human ectoparasites and commensals,
including body lice, Demodex mites, and bacterial symbionts, predates the origin of apes (and hence almost
Tropical & subtropical coniferous forests
Indoor
Flooded grasslands & savannas
Tropical & subtropical dry broadleaf forests
Mediterranean forests, woodlands & shrub
Biome
Temperate coniferous forests
Montane grasslands & shrublands
Tundra
Temperate grasslands, savannas & shrublands
Temperate broadleaf & mixed forests
Boreal forests
Tropical & subtropical moist broadleaf forests
Tropical & subtropical grasslands, savannas & shrublands
Deserts & xeric shrublands
0%
5%
10%
15%
20%
Proporon of earth’s terrestrial area
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Figure 1. The relative areas of 13 outdoor biomes and the indoor biome.
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Manhaan
Indoor biome
Land area
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59 km2
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Figure 2. The trajectory of the indoor biome in one exemplar area, the island of Manhattan. The indoor biome in Manhattan is now nearly three times as large, in terms of
its floor space, as is the geographical area of the island itself. Historically Manhattan was an outlier, but as urban populations grow much, perhaps most, of the world’s
population will soon be living in areas with more floor space than dirt. Included on this figure are key changes in the development of the indoor biome, as manifested in
Manhattan. These changes are neither universal in the indoor biome nor necessarily unidirectional (the population, for instance, in Manhattan declined in the early 1900s),
yet, as emphasized in the text, when they occur have the potential to have large but poorly studied consequences on evolution indoors.
certainly the first ape nest) [13,14]. Other species that
inhabit contemporary houses, including dust mites, some
beetles, and webbing clothes moths – many of which are
found in contemporary nests of mammals or birds – may
have first become associated with our ancestors subsequent to their construction of nests (e.g., [15]).
With time, some primates began to use caves as sleeping
sites [16]. Caves share more similarities with human
houses than do nests, as they are less variable in terms
of climate than the outdoor environment and represent
places where ectoparasites and other associates of hominids could reliably find bodies and food. Bed bugs (Cimex
lectularius), for example, are speculated to have moved
from bats onto humans during a time when humans occupied cave environments [17].
The first human houses emerged approximately
20 000 years ago [18]. Before the origin of agriculture,
houses were places where humans slept, mated, and ate
and where refuse accumulated. After the origin of agriculture, trajectories differed among regions. In some regions,
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people shifted from sedentary to nomadic lifestyles or from
high- to low-density settlements [19]. Eventually, however,
in virtually all inhabited regions, urbanism arose, and with
it higher-density living.
Initially, humans designed houses to take into account
the climatic conditions of specific places [20]. Increasingly,
however, technological and political developments have
changed the relationship between house design and the
outdoor environment in affluent countries, cities, and
neighborhoods. As a result, apartments in Finland and
Singapore may now be very similar, independent of their
very different settings. These developments include: the
adoption of indoor plumbing in the late 1800s; electrification and air conditioning of residences in the 1920s; electrification of farms in the USA in the 1930s; and new
standards for ventilation and insulation following energy
crises in the 1970s (Figure 3).
Nevertheless, modern analogs of many historic indoor
biomes still exist (and in some regions predominate). As a
result, the global diversity of conditions within the indoor
biome is likely to be as great as it has ever been. For the
purposes of this review we attempt to consider the evolution of the indoor biome in light of the great modern and
historical variation in homes, but note that most studies of
indoor evolution are done in relatively new, relatively large
houses in North America and Europe.
Species of the indoor biome
Thousands of species – perhaps hundreds of thousands –
live in the indoor biome, many of them preferentially or
even obligately. A study of just nine habitats (e.g., kitchen,
bedroom) in each of 40 houses in North Carolina, USA,
documented more than 8000 bacterial and archaeal taxa
through molecular detection [21], while a study of 50 houses in North Carolina, USA noted more than 750 arthropod
species, with often more than 100 species of arthropod per
house (M. Trautwein, unpublished). Similarly, a molecular-based survey of 11 houses in California, USA, found
hundreds of fungal taxa [22], and dozens of fungal species
have been cultured from showers and drains alone
[23]. Strong biogeographical patterns have been identified
for bacteria in residential kitchens [24] and inhabitants in
a new home can drastically influence the home microbiome
within a matter of days [25]. Molecular surveys have also
identified a suite of microscopic species in treated drinking
water [26].
What we know today about the natural history of the
indoor biome derives from the relatively small proportion
of indoor species that have been studied in any detail
(Box 2), a group biased toward species that humans attempt to exclude from the indoor biome. It is from these
species that we begin to derive a more general story of the
evolution of the indoor biome.
Selection pressures in the indoor biome
Perhaps the only intentional actions humans take to alter
evolution in the indoor biome are attempts to extinguish
disliked species, whether through cleaning practices, the
use of biocides, or attempts to prevent species from colonizing in the first place. The organisms subject to biocide
differ across regions and cultures as a function of which
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animals are feared or disliked. What does not seem to vary
is a dislike or fear of at least a few organisms that live in the
home [27]. In many instances, the use of biocides has led to
the local extinction of susceptible genotypes and the increase of less susceptible ones. Many insect species have
evolved resistance to insecticides [28], for example, and
multiple rodent species have evolved resistance to rodenticides [29]. Such species have evolved both the ability to
tolerate biocides and the behavior of avoiding biocide
ingestion. German cockroaches (Blattella germanica) have
evolved an adaptive behavioral aversion to glucose in
poison baits [30]. Many bacteria have evolved resistance
in response to the use of antibiotics in living facilities and
hospitals (e.g., [31]) and in the production of domestic food
animals (e.g., [32]). The antimicrobial triclosan has been
suggested to disfavor some microbial lineages in sink
drains while, like most biocides, favoring others [33].
Other selective pressures in houses remain unstudied.
These selective pressures result from choices humans
make as a result of their preference for living conditions,
design, or indoor climate. Globally, the distribution of
indoor climatic conditions and resources varies widely
because of both variation in outdoor climate and differences in the extent to which different types of home buffer
that climate. Many of the Western houses that have been
the focus of studies on indoor taxa are relatively decoupled
in terms of their climate from outdoor conditions (e.g.,
Figure 3A), such that many species of the indoor biome
are likely to have experienced recent selection favoring
lineages able to tolerate dry, warm habitats (Figure 3A,B)
relative to those that prefer moist, cool habitats [34]. While
seasonal patterns in temperature and humidity are buffered by houses, the extremes at smaller scales (centimeters
and minutes rather than kilometers and days) can be as
great as those outdoors. Even within a single house, temperature, humidity, salinity, pH, and other environmental
variables can span nearly the full range observed globally
outside. Bathroom showerheads, for instance, can go from
completely dry to saturated within hours (which favors
microorganisms able to take advantage of moisture-pulse
events, including pathogens) [23].
In the following sections, we outline three questions for
future research. (i) How did species come to populate the
indoor biome? (ii) Which traits does the indoor biome select
for? (iii) How will changes in human culture affect indoor
evolution?
On the origin of indoor species
Little research explores how species come to populate the
indoor biome. We hypothesize that, in many cases, preadaptations allow species to colonize built structures and
then, having colonized, these species respond to local
selection pressures. The grain weevil (Sitophilus granarius) appears to have evolved to feed on grains stored by
ants and rodents and thus was preadapted to make the
transition to grains stored by humans [35]. However, since
colonizing human-stored grains, S. granarius is likely to
have experienced strong selection for traits that facilitate
survival in the very different conditions of granaries. Similarly, rodents of the genus Rattus appear to have been
predisposed to success as human commensals, with 14 of
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TRENDS in Ecology & Evolution
Figure 3. Ambient conditions in the indoor biome can differ substantially from outdoor conditions. (A) Paired outdoor (light gray) and indoor (black) values of mean relative
humidity and mean temperature recorded in 47 US states and the District of Columbia across a 4-month period. During this part of the year, most houses tend to be warmer
and less humid than adjacent outdoor environments, but some states, particularly in the southwest USA, do not follow this trend. (B) Localities within the USA differ in their
relative differences between indoor and outdoor ambient conditions. Orange bars show the difference between mean indoor and outdoor temperatures. Gray bars show
the same difference for relative humidity. (C) Three examples from across the USA demonstrate the difference in temporal variability depending on locality. Hourly point
temperature (8C) and percentage relative humidity measurements outdoors (gray) and indoors (black) across three states. Data recorded by iButton1 data loggers
(Hydrochron iButton model DS1923; Maxim/Dallas Semiconductor, Dallas, TX) between February 24, 2013 and June 24, 2013.
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Box 2. Categorizing species of the indoor biome
The species of the indoor biome can be separated into ‘intended
introductions’ and ‘unintended introductions’.
Intended introductions are species that humans intentionally
bring into indoor environments, often supporting their metabolism
and sometimes reproduction. These species include pets, houseplants, and species used for food fermentation. Such species
possess traits that increase their probability of being indoors; these
traits and species evolve as humans select some lineages over
others, either intentionally or otherwise. While some intended
introductions may be true mutualists of humans, the fitness
advantage of living with humans for some other organisms, such
as domestic cats or flowering plants, is less clear (but see [76]).
Unintended introductions constitute the other species found in
the indoor biome – species that have long been associated with
humans but have been ignored by humans or deterred from
occupying human dwellings. These species include human commensals, pathogens, and parasites as well as mammals, arthropods,
fungi, and other species that use indoor environments opportunistically. Many of these species, such as rats (Rattus spp.) and the
house mouse (Mus musculus), have ancient relationships with
humans and have spread with humans and particular human
cultures.
The above framework excludes species that passively drift into
houses from surrounding environments but are not metabolically or
reproductively active inside houses. For these species, houses are
essentially restaurants, hotels, or cemeteries (ecological sinks or
traps). ‘Peridomestic’ species, for example, feed indoors and
reproduce outdoors [77].
61 species found inside the indoor biome in at least some
region [36]. We speculate that fungal and bacterial species
in the home may also include taxa that were preadapted for
colonization, but in most cases too little is known about
indoor microbes to identify their colonization history. For
example, Abe and Hamada found that Scolecobasidium
fungus isolated from bathrooms and washing machines
formed a distinct clade most closely related to Scolecobasidium humicola isolated from plant litter [37]. It is possible that fungal isolates from bathrooms represent a
recently evolved lineage adapted to indoor, soapy environments ([38] suggested as much). However, it is also possible
that the lineage from which these indoor populations
derive has simply not yet been sampled. As another example, the bacterium Thermus aquaticus, which is often found
in water heaters, was originally hypothesized to have
evolved from ancestors from hot springs [39] but no one
has yet studied how this colonization event might have
occurred.
Phylogeographical and phylogenomic advances promise
to elucidate the stories of both indoor species and the
humans with whom they have traveled. Studies of the
black rat (Rattus rattus) reveal a complex history in which
rats colonized human built environments multiple times
independently in different regions [40]. The subsequent
history of evolution in these lineages illuminates patterns
of human migration and trade. The phylogeography of
insular populations of black rats reveals that many distinct
lineages have evolved since the human colonization of
Indian Ocean islands and these lineages reflect the individual colonization histories of different islands
[41,42]. The spread of the Norway rat (Rattus norvegicus)
was later than that of the black rat (although also out of
Asia) and as it spread the Norway rat displaced the black
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rat in many regions [43], setting the stage for the possibility of evolution in both species in response not only to
climatic gradients and isolation but also to each other’s
presence. Given that R. rattus has colonized most of the
world and, in doing so, now experiences great variation in
human living conditions, the species represents a potential
model organism for the indoor biome.
Most indoor taxa, despite being encountered every day,
have evolutionary histories that are poorly resolved. The
case of roaches is emblematic of the huge gaps that exist
even for species that are considered well studied. For
decades, it has been known that the center of species
diversity of the cockroach genus Blattella is Southeast
Asia, but only one of the 51 species, the German cockroach
(B. germanica), has become so specialized in the built
environment that it is not known to occur anywhere else
[44]. Although several studies have considered local population dynamics in B. germanica, none has considered its
evolution relative to its likely sister taxa or wild populations in the region in which it is putatively native. The
situation is similar for most indoor species, be they animals, plants, fungi, bacteria, or others.
Our knowledge of the indoor biome would benefit from
phylogeographical and phylogenomic comparisons that
include both indoor taxa and outdoor congeners (e.g.,
[46]). The common bed bug (C. lectularius), for example,
occurs only in the built environment and has congeners in
nature – bat bugs – that could inform us about evolution in
the indoor biome [45]. The challenge in many cases will be
identifying potential sister lineages to include in analyses.
Exophiala, for example, is a black yeast commonly found in
sinks and dishwashers in houses and on steam-bath walls.
Its known counterparts in outdoor areas are found on the
skins of tropical fruits and, because of its occurrence
patterns, thermotolerance, acid tolerance, osmotolerance,
and melanization, its natural life cycle is thought to be tied
to that of frugivorous animals in the tropical rain forest
[47]. However, closer relatives might live in other habitats
but have not yet been studied.
Which traits does the indoor biome select for?
Many household organisms share phenotypes and behaviors with cave-dwelling organisms. Many indoor arthropods have flattened bodies (e.g., bed bugs, cockroaches,
silverfish), presumably because this body type better fits in
crevices within houses. Some arthropods in houses, like
those that live in caves, have less acute vision but longer
antennae, which are often used to orient to edges (e.g.,
cockroaches, silverfish, crickets). Cave-dwelling microbes
are relatively unstudied but, based on the similarity of food
sources, substrates, and climates in caves and homes, some
species of house-dwelling microbes may have evolved in
caves.
In caves, animals tend either to lose their ability to
disperse (because dispersal is costly and the odds of finding
a new cave are low) or to evolve the ability to disperse
passively with animals able to travel to new caves, such as
bats. We predict a similar pattern in the indoor biome,
particularly in regions in which indoor and outdoor conditions are very different. Urban populations of the weed
Crepis sancta that inhabit tree pits surrounded by concrete
Review
have adapted to produce non-dispersing seed types at a
higher frequency than rural populations [48] because it is
better to stay in a crowded pit than to die on the cement.
Wingless and blind invertebrates are common in barns,
where stored products are predictably transported, and are
patchily distributed at geographical scales that are large
relative to the ability of most invertebrates to actively
disperse [49]. Similarly, many indoor species appear to
have reduced dispersal ability. Camel crickets, some roach
species, bed bugs, silverfish, and booklice lack flight, although flightlessness is relatively rare among insects
[50,51]. Even winged animals found indoors, such as webbing clothes moths, are often poor flyers [15].
Many bacteria in homes and human-dominated environments appear to be sufficiently ubiquitous in the air that
they are neither dispersal limited [52] nor able to prevent
dispersal into bad habitats. For these taxa, selection may
favor tolerance of indoor conditions (and their fluctuation)
rather than particular dispersal traits. Other taxa of bacteria and other microbes are able to reliably enter houses
on humans and their pets [21,25] or arthropods [53] and
some food-borne taxa arrive in houses within food.
In all organisms in homes, except those able to easily
move in and out, the fluctuating conditions experienced at
small scales in homes, such as on showerheads, should
favor tolerance of fluctuating stresses [23]. For arthropods,
this often involves reduction in metabolic activity. Indoor
ectoparasites (e.g., fleas, bed bugs) have evolved metabolic
strategies to withstand long periods without their human
or pet host (e.g., lower metabolic rate, delayed molting,
ability to engorge to several times their body mass)
[54]. Indoor silverfish (Lepisma saccharina) and firebrats
(Thermobia domestica) can survive long periods of starvation and firebrats can actively absorb water from the
atmosphere [55]. Meanwhile, one of the most common
fungi in houses, Aspergillus fumigatus, can grow across
a broader range of temperature conditions than other
related taxa – an ability that may facilitate its survival
in varied indoor habitats [56]. Additionally, the bacterium
Deinococcus radiodurans, known for its extreme desiccation and UV tolerance, appears to accumulate in building
dust over time indoors [57]. The adaptations that allow
microbes to survive in episodically stressful conditions,
such as those present in dishwashers, showers, and sinks,
may also favor pathogenic species and perhaps even the
evolution of pathogenecity [58] – a worrisome hypothesis,
given that we have recreated these conditions in houses
across the world.
Interestingly, the dependence of many indoor species on
passive or facilitated dispersal means that the composition
of species in a particular built structure is likely to be
stochastic (with the stochasticity being greater where the
amount of movement into the home is lower and for taxa
with poorer dispersal abilities). Both roaches and bed bugs
in apartments seem often to derive from single introduction events [59]. Until relatively recently, Norway rats
were unable to colonize Phoenix, AZ due to the relatively
inhospitable climate around the city [36]. As a consequence
of the stochasticity of colonization, parthenogenetic reproduction may be favored indoors. At least some species that
thrive indoors are facultatively parthenogenetic [e.g., the
Trends in Ecology & Evolution April 2015, Vol. 30, No. 4
American cockroach (Periplaneta americana), the Surinam
cockroach (Pycnoscelus surinamensis)] [60]. Whether the
incidence of parthenogenesis in indoor species is unusually
high has not been formally tested. A priori, animal species
that reproduce indoors may also have evolved the ability to
tolerate extensive inbreeding. Whether particular reproductive strategies might also be favored in microbes in
indoor environments does not appear to have been considered.
How will changes in human culture affect indoor
evolution?
Subtle features of human culture have the potential to
have large impacts on evolution indoors. The spread of
parasites and other infectious agents often depends on
intimacy among humans and between humans and other
animals. For example, genital lice (Pthirus pubis) moved
from the ancestor of gorillas to humans in a moment of
some form of intimacy [61]. Close interaction has allowed
new microbes to enter human habitats through meat, milk,
dung, and common vectors (like flies, fleas, and ticks).
Classic epidemic viral diseases of humans have their origins in the animals that were domesticated early
[62,63]. In some cases, intimate interactions with nonhuman animals lead to the colonization of humans and homes
with species that spread globally; in others, they seem
likely to lead to more local populations.
A related aspect of human culture that may affect the
evolutionary trajectories of indoor species is a preoccupation with purity and pollution [64]. Many of the visible
organisms found in houses have a ‘disgust-evoking status’.
However, the organisms that elicit these responses vary
from place to place (although see [27]), as do the social
stigmas related to these organisms. Cultural conceptions of
what is clean or dirty ultimately drive how we behave
toward indoor species, especially those that we label ‘pest
species’, and consequently how we shape the indoor biome
[65]. One could argue, for example, that the widespread
presence of antibiotic resistance in the USA is due to an
industry-driven response to a cultural construct: the idea
of ‘germs’ [66]. The study of the influence of culture on
indoor evolution offers rich potential for new discoveries
and important case examples of rapid evolution.
Ecological theory suggests that the spatial arrangement
and density of indoor spaces within a region may also have
an impact on the evolution of indoor species, particularly
for those whose fitness is higher indoors than outdoors
[67]. Species–area relationships, island biogeographical
models, and even metabolic theory predict that, as the
habitat and resources available in a particular biome
increase, so too should its total (gamma) diversity. To
the extent that houses vary within and among cities, we
might predict that beta diversity is also likely to remain
high. We hypothesize that urbanization will increase the
number of species that evolve to persist indoors, with the
differences among homes, settlements, and regions being a
more complex function of the relative differences among
them in culture and connectedness.
A trend toward sustainable building practices may also
influence indoor evolution. Strategies to improve energy
efficiency and control of the indoor biome include tighter
229
Review
Box 3. Outstanding questions
Are houses similar enough to consider them a single biome or are
they more akin to remote islands (multiple biomes)? Would one
expect convergent or divergent evolution to appear across
habitats in the indoor biome?
How will climate change affect both building design and the
outdoor environment and, subsequently, determine which species thrive indoors?
Was there an adaptive evolutionary syndrome of phenotypic or
genomic changes that accompanied the evolution of house living
in many species in many regions?
Has evolution of indoor microbes (or colonization by preadapted
microbes) influenced our own microbiome health? Can we design
buildings to function as healthier human/microbe habitats?
Are ecological interactions specific or unique in any way indoors
or are they analogous to outdoor interactions?
How many and which species are found exclusively in the biome?
Have any species moved from the indoor biome to other, outdoor
biomes? Is there speciation indoors?
What is the role of horizontal gene transfer in the indoor biome?
How frequent is it and are there indoor hotspots where microbes
are more likely to exchange information?
Are populations of some indoor species genetically distinct within
or among different types of structure (e.g., public kitchens versus
private kitchens, bedrooms versus movie theaters)? In other
words, what is the population structure of the inhabitants of the
indoor biome? Does scale matter? Would we be more likely to find
structured populations of, say, bacteria than mice?
What are the primary producers in the indoor biome?
What can the indoor biome tell us about the origins and formation
of other biomes that have existed on Earth?
sealing of building envelopes [68], which has the potential
to influence all selection pressures indoors, favoring the
subset of lineages that are best able to enter sealed environments and deal with self-contained climate systems [69]
and the novel chemistry of new building materials. Although the impacts of sustainable building and new building materials remains to be fully explored, they seem likely
to have lasting influences on evolution in the indoor environment – effects we are likely to experience long before
they are well studied.
Concluding remarks and future directions
Although many biologists have studied the evolutionary
processes at work in indoor environments, such studies
focus disproportionately on pest organisms. As a result,
most taxa of the indoor biome remain to be considered in an
evolutionary ecological framework. As a research field, the
evolutionary biology of the indoor biome is interdisciplinary, situated at the intersections of evolutionary biology,
ecology, anthropology, archaeology, engineering, architecture and design, human ecology, urban planning, environmental history, and political ecology. There are many
avenues open for future research on the ecology and evolution of the indoor biome (Box 3).
Arguably, the indoor biome is one of the realms in which
the field of evolution offers the most to humanity. The
study of the indoor biome intersects with the field of public
health and medicine. Houses with increased levels of
fungal, cockroach, and mouse allergens are associated with
higher rates of asthma in children, for example, and the
absence of beneficial species indoors has been linked to
autoimmune and allergic disorders [70]. Evolutionary biol230
Trends in Ecology & Evolution April 2015, Vol. 30, No. 4
Table 1. Categories of species of the indoor biome and
references that describe their evolution or ecology in indoor
environments
Category
Intended introduction
Unintended introduction
Examples
Pets
Microbes for fermentation
Houseplants
Humans
Human pathogens
and parasites
Arthropods
Human-associated microbes
Other microbes
Rodents
Birds
Bats
Other mammals
Reptiles
Refs
[78,79]
[80,81]
–
[18,82]
[83,84]
[30,59,85]
[57,86,87]
[22,88–90]
[40,67,91]
–
[92]
–
–
ogists have the opportunity to engage with these basic and
applied research topics through the study of indoor biomes.
Perhaps more than any other evolutionary examples,
the stories of the species that evolve indoors are accessible
to students and other members of the public [71]. Already
conservation biologists are engaged in a parallel movement
to bring conservation stories to inhabited places
[9,72]. Study of the indoor biome could bring evolution
to our doorsteps. One framework in which this could occur
is through citizen science. Citizen science offers an approach to the study of indoor species that simultaneously
engages the public, allows scientists to sample many houses, and generates stories about ecology and evolution of
which the public is intricately a part [73]. Recent studies
engaging citizens in the study of their own homes have
revealed the spread of two species of giant invasive camel
cricket among North American basements and crawlspaces [50], patterns of bacterial composition within and
among houses [21], and the distribution and composition of
ants in backyards [74]. Given that our understanding of the
indoor biome remains heavily weighted toward North
America and parts of Europe, it will be important to our
understanding of indoor evolution to distribute projects
more evenly across geographical regions [75].
Acknowledgments
This review emerged from a catalysis meeting at the National
Evolutionary Synthesis Center [National Science Foundation (NSF) EF0905606] supported by the Sloan Foundation (2012-5-47 IE). R.R.D. was
supported by NSF grant 551819-0654 and by the Southeast Climate
Science Center while writing this review and L.J.M. by an NSF Graduate
Research Fellowship Program. The authors thank S. Crane, L. Fellman,
C.E. Kraft, H. Menninger, M. Siva-Jothy, J. Siegel, W. Wilson, and two
anonymous reviewers for their helpful feedback.
References
1 Martin, L.J. et al. (2012) Mapping where ecologists work: biases in the
global distribution of terrestrial ecological observations. Front. Ecol.
Environ. 10, 195–201
2 Ellis, E.C. and Ramankutty, N. (2008) Putting people in the map:
anthropogenic biomes of the world. Front. Ecol. Environ. 6, 439–447
3 Kitzes, J. et al. (2007) Current methods for calculating national
ecological footprint accounts. Sci. Environ. Sustain. Soc. 4, 1–9
Review
4 Hooke, R.L. and Martı́n-Duque, J.F. (2012) Land transformation by
humans: a review. GSA Today 22, 4–10
5 United Nations (2012) World Urbanization Prospects: The
2011 Revision (Vol. I), United Nations
6 Costello, E.K. et al. (2012) The application of ecological theory toward
an understanding of the human microbiome. Science 336, 1255–1261
7 Turnbaugh, P.J. et al. (2007) The human microbiome project: exploring
the microbial part of ourselves in a changing world. Nature 449, 804–
810
8 Savard, J.L. et al. (2000) Biodiversity concepts and urban ecosystems.
Land. Urban Plan. 48, 131–142
9 Martin, L.J. et al. (2014) Conservation opportunities across the world’s
anthromes. Divers. Distrib. 20, 745–755
10 Burnside, W.R. et al. (2012) Human macroecology: linking pattern and
process in big-picture human ecology. Biol. Rev. 87, 194–208
11 Prado-Martinez, J. et al. (2013) Great ape genetic diversity and
population history. Nature 499, 471–475
12 Samson, D.R. et al. (2013) Do chimpanzees (Pan troglodytes
schweinfurthii) exhibit sleep related behaviors that minimize
exposure to parasitic arthropods? A preliminary report on the
possible anti-vector function of chimpanzee sleeping platforms.
Primates 54, 73–80
13 Thoemmes, M.S. et al. (2014) Ubiquity and diversity of humanassociated Demodex mites. PLoS ONE 9, e106265
14 Nutting, W. (1976) Hair follicle mites (Demodex spp.) of medical and
veterinary concern. Cornell Vet. 66, 214–231
15 Plarre, R. and Krüger-Carstensen, B. (2012) An attempt to reconstruct
the natural and cultural history of the webbing clothes moth Tineola
bisselliella Hummel (Lepidoptera: Tineidae). J. Entomol. Acarol. Res.
43, 83–93
16 Hamilton, W.J. (1982) Baboon sleeping site preferences and
relationships to primate grouping patterns. Am. J. Primatol. 3, 41–53
17 Balvı́n, O. et al. (2012) Mitochondrial DNA and morphology show
independent evolutionary histories of bedbug Cimex lectularius
(Heteroptera: Cimicidae) on bats and humans. Parasitol. Res. 111, 457–469
18 Moore, J.D. (2012) The Prehistory of Home, University of California
Press
19 Yoffee, N. (2005) Myths of the Archaic State: Evolution of the Earliest
Cities, States, and Civilizations, Cambridge University Press
20 Hay, F.S. (1924) The house and geography. J. Geogr. 23, 225–233
21 Dunn, R.R. et al. (2013) Home life: factors structuring the bacterial
diversity found within and between homes. PLoS ONE 8, e64133
22 Adams, R.I. et al. (2013) Dispersal in microbes: fungi in indoor air are
dominated by outdoor air and show dispersal limitation at short
distances. ISME J. 7, 1262–1273
23 Feazel, L.M. et al. (2009) Opportunistic pathogens enriched in
showerhead biofilms. Proc. Natl. Acad. Sci. U.S.A. 106, 16393–16399
24 Flores, G.E. et al. (2011) Microbial biogeography of public restroom
surfaces. PLoS ONE 6, e28132
25 Lax, S. et al. (2014) Longitudinal analysis of microbial interaction
between humans and the indoor environment. Science 345, 1048–1052
26 Hwang, C. et al. (2012) Microbial community dynamics of an urban
drinking water distribution system subjected to phases of
chloramination and chlorination treatments. Appl. Environ.
Microbiol. 78, 7856–7865
27 Davey, G.C. (1994) Self-reported fears to common indigenous animals
in an adult UK population: the role of disgust sensitivity. Br. J. Psychol.
85, 541–554
28 Cochran, D. (1995) . In Insecticide resistance. Understanding and
Controlling the German Cockroach (Rust, M.K. et al., eds), Oxford
University Press
29 Rost, S. et al. (2009) Novel mutations in the VKORC1 gene of wild rats
and mice – a response to 50 years of selection pressure by warfarin?
BMC Genet. 10, 4
30 Wada-Katsumata, A. et al. (2013) Changes in taste neurons support the
emergence of an adaptive behavior in cockroaches. Science 340, 972–
975
31 Murphy, C.R. et al. (2013) Predicting high prevalence of community
methicillin-resistant Staphylococcus aureus strains in nursing homes.
Infect. Control Hosp. Epidemiol. 34, 325–326
32 van Cleef, B.A. et al. (2014) Dynamics of MRSA and MSSA carriage in
pig farmers: a prospective cohort study. Clin. Microbiol. Infect. 20,
O764–O771
Trends in Ecology & Evolution April 2015, Vol. 30, No. 4
33 Kim, Y-M. et al. (2011) Triclosan susceptibility and co-metabolism – a
comparison for three aerobic pollutant-degrading bacteria. Bioresour.
Technol. 102, 2206–2212
34 Brimblecombe, P. and Lankester, P. (2012) Long-term changes in
climate and insect damage in historic houses. Stud. Conserv. 58, 13–22
35 King,
G.A.
et
al.
(2014)
Six-legged
hitchhikers:
an
archaeobiogeographical account of the early dispersal of grain
beetles. J. North Atlantic 23, 1–18
36 Singleton, G.R. et al. (2003) Rats, Mice and People: Rodent Biology and
Management, Australian Centre for International Agricultural
Research
37 Abe, N. and Hamada, N. (2011) Molecular characterization and
surfactant utilization of Scolecobasidium isolates from detergentrich indoor environments. Biocontrol Sci. 16, 139–147
38 Gostinčar, C. et al. (2011) Evolution of fungal pathogens in domestic
environments? Fungal Biol. 115, 1008–1018
39 Brock, T.D. and Boylen, K.L. (1973) Presence of thermophilic bacteria
in laundry and domestic hot-water heaters. Appl. Microbiol. 25, 72–76
40 Wilmshurst, J.M. et al. (2008) Dating the late prehistoric dispersal of
Polynesians to New Zealand using the commensal Pacific rat. Proc.
Natl. Acad. Sci. U.S.A. 105, 7676–7680
41 Gibbs, R.A. et al. (2004) Genome sequence of the Brown Norway rat
yields insights into mammalian evolution. Nature 428, 493–521
42 Audoin-Rouzeau, F. and Vigne, J.D. (1994) La colonization de l’Europe
par le rat noir (Rattus rattus). Rev. Paleobiol. 13, 125–145 (in French)
43 Meehan, A.P. (1984) Rats and Mice: Their Biology and Control,
Rentokil
44 Roth, L.M. (1995) New species of Blattella and Neoloboptera from India
and Burma (Dictyoptera: Blattaria: Blattellidae). Orient. Insects 29,
23–31
45 Saenz, V.L. et al. (2012) Genetic analysis of bed bug populations reveals
small propagule size within individual infestations but high genetic
diversity across infestations from the eastern United States. J. Med.
Entomol. 49, 865–875
46 Amend, A.S. et al. (2010) Indoor fungal composition is geographically
patterned and more diverse in temperate zones than in the tropics.
Proc. Natl. Acad. Sci. U.S.A. 107, 13748–13753
47 Sudhadham, M. et al. (2008) The neurotropic black yeast Exophiala
dermatitidis has a possible origin in the tropical rain forest. Stud.
Mycol. 61, 145–155
48 Cheptou, P.O. et al. (2008) Rapid evolution of seed dispersal in an
urban environment in the weed Crepis sancta. Proc. Natl. Acad. Sci.
U.S.A. 105, 3796–3799
49 Kenward, H.K. (1975) The biological and archaeological implications of
the beetle Aglenus brunneus (Gyllenhal) in ancient faunas. J. Archaeol.
Sci. 2, 63–69
50 Epps, M.J. et al. (2014) Too big to be noticed: cryptic invasion of Asian
camel crickets in North American houses. PeerJ 2, e523
51 Thoms, E.M. and Robinson, W.H. (1987) Distribution and movement of
the oriental cockroach (Orthoptera: Blattidae) around apartment
buildings. Environ. Entomol. 16, 731–737
52 Ramirez, K.S. et al. (2014) Biogeographic patterns in below-ground
diversity in New York City’s Central Park are similar to those observed
globally. Proc. Biol. Soc. Published online November 22, 2014. (http://
dx.doi.org/10.1098/rspb.2014.1988)
53 Elgderi, R.M. et al. (2006) Carriage by the German cockroach (Blattella
germanica) of multiple-antibiotic-resistant bacteria that are
potentially pathogenic to humans, in hospitals and households in
Tripoli, Libya. Ann. Trop. Med. Parasitol. 100, 55–62
54 Silverman, J. and Rust, M.K. (1985) Extended longevity of the preemerged adult cat flea (Siphonaptera: Pulicidae) and factors
stimulating emergence from the pupal cocoon. Ann. Entomol. Soc.
Am. 78, 763–768
55 Sweetman, H.L. (1938) Physical ecology of the firebrat, Thermobia
domestica (Packard). Ecol. Monogr. 8, 285–311
56 Low, S.Y. et al. (2011) The allergenicity of Aspergillus fumigatus
conidia is influenced by growth temperature. Fungal Biol. 115, 625–
632
57 Kembel, S.W. et al. (2014) Architectural design drives the biogeography
of indoor bacterial communities. PLoS ONE 9, e87093
58 Zalar, P. et al. (2011) Dishwashers – a man-made ecological niche
accommodating human opportunistic fungal pathogens. Fungal Biol.
115, 997–1007
231
Review
59 Crissman, J.R. et al. (2010) Population genetic structure of the German
cockroach (Blattodea: Blattellidae) in apartment buildings. J. Med.
Entomol. 47, 553–564
60 Roth, L.M. and Willis, E.R. (1956) Parthenogenesis in cockroaches.
Ann. Entomol. Soc. Am. 49, 195–204
61 Weiss, R.A. (2007) Lessons from naked apes and their infections. J.
Med. Primatol. 36, 172–179
62 Torrey, E.F. and Yolken, R.H. (2005) Beasts of the Earth: Animals,
Humans, and Disease, Rutgers University Press
63 Furuse, Y. et al. (2010) Origin of measles virus: divergence from
rinderpest virus between the 11th and 12th centuries. Virol. J. 7, 52
64 Douglas, M. (2003) Purity and Danger: An Analysis of Concepts of
Pollution and Taboo, Routledge
65 Biehler, D. (2014) Pests in the City: Flies, Bedbugs, Cockroaches, and
Rats, University of Washington Press
66 Tomes, N. (1999) The Gospel of Germs, Harvard University Press
67 Munshi-South, J. (2012) Urban landscape genetics: canopy cover
predicts gene flow between white-footed mouse (Peromyscus
leucopus) populations in New York City. Mol. Ecol. 21, 1360–1378
68 Wolverton, B.C. and Wolverton, J.D. (1996) Interior plants: their
influence on airborne microbes inside energy-efficient buildings. J.
Miss. Acad. Sci. 41, 99–105
69 Institute of Medicine (2011) Climate Change, the Indoor Environment
and Health, National Academy Press
70 Olmedo, O. et al. (2011) Neighborhood differences in exposure and
sensitization to cockroach, mouse, dust mite, cat, and dog allergens in
New York City. J. Allergy Clin. Immunol. 128, 284–292
71 Ordish, G. (1985) The Living House, Bodley Head
72 Dunn, R.R. et al. (2006) The pigeon paradox: dependence of global
conservation on urban nature. Conserv. Biol. 20, 1814–1816
73 Cooper, C.B. et al. (2007) Citizen science as a tool for conservation in
residential ecosystems. Ecol. Soc. 12, 11
74 Savage, A.M. et al. (2014) Fine-scale heterogeneity across Manhattan’s
urban habitat mosaic is associated with variation in ant composition
and richness. Insect Cons. Divers. Published online November 4, 2014.
(http://dx.doi.org/10.1111/icad.12098)
75 Karl, J.W. et al. (2013) Geo-semantic searching: discovering
ecologically relevant knowledge from published studies. Bioscience
63, 674–682
76 Berg, G. et al. (2014) Beneficial effects of plant-associated microbes on
indoor microbiomes and human health? Front. Microbiol. 5, 15
232
Trends in Ecology & Evolution April 2015, Vol. 30, No. 4
77 Frankie, G.W. and Ehler, L.E. (1978) Ecology of insects in urban
environments. Annu. Rev. Entomol. 23, 367–387
78 vonHoldt, B.M. et al. (2010) Genome-wide SNP and haplotype analyses
reveal a rich history underlying dog domestication. Nature 464, 898–
902
79 Rochlitz, I. (2005) A review of the housing requirements of domestic
cats (Felis silvestris catus) kept in the home. Appl. Anim. Behav. Sci. 93,
97–109
80 Rokas, A. (2009) The effect of domestication on the fungal proteome.
Trends Genet. 25, 60–63
81 Makarova, K. et al. (2006) Comparative genomics of the lactic acid
bacteria. Proc. Natl. Acad. Sci. U.S.A. 103, 15611–15616
82 Biehler, D.D. and Simon, G.L. (2010) The great indoors: research
frontiers on indoor environments as active political–ecological
spaces. Prog. Hum. Geogr. 35, 172–192
83 Azad, A.F. and Beard, C.B. (1998) Rickettsial pathogens and their
arthropod vectors. Emerg. Infect. Dis. 4, 179–186
84 Yadon, Z.E. et al. (2003) Transmission of American cutaneous
leishmaniasis in northwestern Argentina: a retrospective casecontrol study. Am. J. Trop. Med. Hyg. 68, 519–526
85 Booth, W. et al. (2011) Population genetic structure in German
cockroaches (Blattella germanica): differentiated islands in an
agricultural landscape. J. Hered. 102, 175–183
86 Hospodsky, D. et al. (2012) Human occupancy as a source of indoor
airborne bacteria. PLoS ONE 7, e34867
87 Meadow, J.F. et al. (2013) Indoor airborne bacterial communities are
influenced by ventilation, occupancy, and outdoor air source. Indoor Air
24, 41–48
88 Adams, R.I. et al. (2014) Airborne bacterial communities in residences:
similarities and differences with fungi. PLoS ONE 9, e91283
89 Kelley, S.T. et al. (2004) Molecular analysis of shower curtain biofilm
microbes. Appl. Environ. Microbiol. 70, 4187–4192
90 Remold, S.K. et al. (2011) Differential habitat use and niche
partitioning by Pseudomonas species in human homes. Microb. Ecol.
62, 505–517
91 Tollenaere, C. et al. (2010) Phylogeography of the introduced
species Rattus rattus in the western Indian Ocean, with special
emphasis on the colonization history of Madagascar. J. Biogeogr.
37, 398–410
92 Gehrt, S.D. and Chelsvig, J.E. (2004) Species-specific patterns of bat
activity in an urban landscape. Ecol. Appl. 14, 625–635