627:
100:
818:
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One method is the comparison of differences between nuclear and mitochondrial markers among populations. Markers showing higher levels of differentiation indicate the more philopatric sex; that is, the more a sex remains at natal grounds, the more their markers will take on a unique I.D, due to lack of gene flow with respect to that marker. Researchers can also quantify male-male and female-female pair relatedness within populations to understand which sex is more likely to disperse. Pairs with values consistently lower in one sex indicate the dispersing sex. This is because there is more gene flow in the dispersing sex and their markers are less similar than individuals of the same sex in the same population, which produces a low relatedness value.
380:
469:) values. If both of these values are similar and Fst is based on neutral markers then it can be assumed that the QTLs were based on neutral markers (markers not under selection or locally adapted) as well. However, in the case of the barn owls the Qst value was much higher than the Fst value. This means that high gene flow was present allowing the neutral markers to be similar, indicated by the low Fst value. But, local adaptation due to selection was present as well, in the form of varying plumage coloration since the Qst value was high, indicating differences in these non-neutral loci. In other words, this cline of plumage coloration has some sort of adaptive value to the birds.
814:
which describes a species as the smallest identifiable monophyletic group of organisms within which there is a parental pattern of ancestry and descent. This concept defines species on the identifiable. It would also suggest that until two identifiable groups actually produce offspring, they remain separate species. In 1999, John Avise and Glenn Johns suggested a standardized method for defining species based on past speciation and measuring biological classifications as time dependent. Their method used temporal banding to make genus, family and order based on how many tens of millions of years ago the speciation event that resulted in each species took place.
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159:
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emphasizes interactions between loci rather than within them. Inbreeding and outbreeding depression can occur at the same time. Risks of outbreeding depression increase with increased distance between populations. The risk of outbreeding depression during genetic rescue often limits the ability to increase a small or fragmented gene pool's genetic diversity. The spawn of an intermediate of two or more adapted traits can render the adaptation less effective than either of the parental adaptations. Three main mechanisms influence outbreeding depression;
355:
689:, and set chromosomal dissimilarities resulting in sterile offspring. If outbreeding is limited and the population is large enough, selective pressure acting on each generation may be able to restore fitness. However, the population is likely to experience a multi-generational decline of overall fitness as selection for traits takes multiple generations. Selection acts on outbred generations using increased diversity to adapt to the environment. This may result in greater fitness among offspring than the original parental type.
237:
data. Currently, there is no consensus on preferred methods for clustering, and clustering and sequence processing methods can significantly affect results, especially for the variable-length ITS region. In addition, fungal species vary in intra-specific sequence similarity of the ITS region. Recent research has been devoted to the development of flexible clustering protocols that allow sequence similarity thresholds to vary by taxonomic groups, which are supported by well-annotated sequences in public sequence databases.
444:
number of individuals of a certain sex dispersing to other populations. A more mathematical approach to quantifying sex-biased dispersal on the molecular level is the use of spatial autocorrelation. This correlation analyzes the relationship between geographic distance and spatial distance. A correlation coefficient, or r value, is calculated and the plot of r against distance provides an indication of individuals more related to or less related to one another than expected.
376:
regions. Another drawback to using molecular clocks is that they ideally need to be calibrated from an independent source of data other than the molecular data. This poses a problem for taxa that don't fossilize/preserve easily, making it almost impossible to calibrate their molecular clock. Despite these inconveniences, the molecular clock hypothesis is still used today. The molecular clock has been successful in dating events happening up to 65 million years ago.
825:
342:, and deplete genetic variation. However, dispersal between populations in the metapopulation can reverse or halt these processes over the long term. Therefore, in order for individual sub-populations to remain healthy, they must either have a large population size or have a relatively high rate of dispersal with other subpopulations. Molecular ecology focuses on using tests to determine the rates of dispersal between populations and can use
800:
and composition of a community. There are three primary approaches to integrating phylogenetic information into studies of community organizations. The first approach focuses on examining the phylogenetic structure of community assemblages. The second approach focuses on exploring the phylogenetic basis of community niche structures. The final way zones in on adding a community context to studies of trait evolution and biogeography.
282:(IBD), like reproductive isolation, is the effect of physical barriers to populations that limit migration and lower gene flow. The shorter the distance between populations the more likely individuals are to disperse and mate and thus, increase gene flow. The use of molecular data, specifically allele frequencies of individuals among populations in relation to their geographic distance help to explain concepts such as, sex-biased
371:
lineages studied diverged. The sources usually used to calibrate the molecular clocks are fossils or known geological events in the past. After calibrating the clock the next step is to calculate divergence time by dividing the estimated time since the sequences diverged by the amount of sequence divergence. The resulting number is the estimated rate at which
849:
travel from point A to point B. Least cost path analysis uses geographic data to determine the most efficient path from one point to another. Circuit scape analysis predicts all the possible paths and the probability of each path's use between point A and point B. These analyses are used to determine the route a dispersing individual is likely to travel.
653:. The rate of inbreeding is based on decreased heterozygosity. In other words, the rate at which heterozygosity is lost from a population due to genetic drift is equal to the rate of accumulating inbreeding in a population. In the absence of migration, inbreeding will accumulate at a rate that is inversely proportional to the size of the population.
257:
have found that males will adjust their parental care in response to changes in their paternity. Other studies have shown that in socially monogamous species, some individuals will employ an alternative strategy to be reproductively successful since a social bond does not always equal reproductive success.
456:(QTL) refers to a suite of genes that controls a quantitative trait. A quantitative trait is one that is influenced by several different genes as opposed to just one or two. QTLs are analyzed using Qst. Qst looks at the relatedness of the traits in focus. In the case of QTLs, clines are analyzed by Qst. A
852:
Landscape genetics is becoming an increasingly important tool in wildlife conservation efforts. It is being used to determine how habitat loss and fragmentation affects the movement of species. It is also used to determine which species need to be managed and whether to manage subpopulations the same
256:
While most bird species are socially monogamous, molecular data has revealed that less than 25% of these species are genetically monogamous. EPFs complicate matters, especially for male individuals, because it does not make sense for an individual to care for offspring that are not their own. Studies
232:
sequencing technologies. Porras-Alfaro et al. showed that the accuracy of classification of either ITS or D1-D3 region sequences was largely based on the sequence composition and quality of databases used for comparison, and poor-quality sequences and sequence misidentification in public databases is
813:
which defines a species as groups of actually or potentially interbreeding natural populations, which are reproductively isolated from other such groups (Mayr, 1942). This concept is not always useful, particularly when it comes to hybrids. Other species concepts include phylogenetic species concept
326:
changes in population sizes which may lead to extinction at the population level. Once this has occurred, dispersing individuals from other populations will immigrate and "rescue" the population at that site. Other metapopulation models include the source-sink model (island-mainland model) where one
840:
is a rapidly emerging interdisciplinary field within molecular ecology. Landscape genetics relates genetics to landscape characteristics, such as land-cover use (forests, agriculture, roads, etc.), presence of barriers, and corridors, rivers, elevation, etc. Landscape genetics answers how landscape
438:
Studying these hypotheses can be arduous since it is nearly impossible to keep track of every individual and their whereabouts within and between populations. To combat this time-consuming method, scientists have recruited several molecular ecology techniques in order to study sex-biased dispersal.
848:
Geographic data used for landscape genetics can include data collected by radars in planes, land satellite data, marine data collected by NOAA, as well as any other ecological data. In landscape genetics researchers often use different analyses to attempt to determine the best way for a species to
808:
Species concepts are the subject of debate in the field of molecular ecology. Since the beginning of taxonomy, scientists have wanted to standardize and perfect the way species are defined. There are many species concepts that dictate how ecologists determine a good species. The most commonly used
799:
emerged from natural history and population biology. Not only does it include the study of the interactions between species, but it also focuses on ecological concepts such as mutualism, predation, and competition within communities. It is used to explicate properties such as diversity, dominance,
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Phylogenies confer important historical processes that shape current distributions of genes and species. When two species become isolated from each other they retain some of the same ancestral alleles also known as allele sharing. Alleles can be shared because of lineage sorting and hybridization.
407:
the females will search out for the most suitable males and re-mate until they have found the best sperm to fertilize their eggs. Genetic compatibility is where mates are choosing their partner based on the compatibility of their genotypes. The mate which is doing the selecting must know their own
370:
hypothesis states that DNA sequences roughly evolve at the same rate and because of this the dissimilarity between two sequences can be used to tell how long ago they diverged from one another. The first step in using a molecular clock is it must be calibrated based on the approximate time the two
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Barriers are any landscape features that prevents dispersal. Barriers for terrestrial species can include mountains, rivers, roads, and unsuitable terrain, such as agriculture fields. Barriers for aquatic species can include islands or dams. Barriers are species specific; for example a river is a
741:
were given evolutionary significance based on the differences in genetic sequences found among different populations. This detection of evolutionary significance can allow each population of salmon to receive customized conservation and protection based on their adaptive uniqueness in response to
460:
is a change in allele frequency across a geographical distance. This change in allele frequency causes a series of intermediate varying phenotypes that when associated with certain environmental conditions can indicate selection. This selection causes local adaptation, but high gene flow is still
443:
are also used to understand dispersing behaviors by calculating an FST value for each sex. The sex that disperses more displays a lower FST value, which measures levels of inbreeding between the subpopulation and the total population. Additionally, assignment tests can be utilized to quantify the
236:
Next-generation sequencing technologies generate large amounts of data, and analysis of fungal marker-gene data is an active area of research. Two primary areas of concern are methods for clustering sequences into operational taxonomic units by sequence similarity and quality control of sequence
464:
For example, barn owls in Europe exhibit a cline in reference to their plumage coloration. Their feathers range in coloration from white to reddish-brown across the geological range of the southwest to the northeast. This study sought to find if this phenotypic variation was due to selection by
95:
sequences. This approach has been enhanced over a number of years to allow researchers to sequence thousands of genes from a small amount of starting DNA. Allele sizes are another way researchers are able to compare individuals and populations which allows them to quantify the genetic diversity
375:
is occurring. The most widely cited molecular clock is a ‘universal’ mtDNA clock of approximately two percent sequence divergence every million years. Although referred to as a universal clock, this idea of the "universal" clock is not possible considering rates of evolution differ within DNA
321:
theory dictates that a metapopulation consists of spatially distinct populations that interact with one another on some level and move through a cycle of extinctions and recolonizations (i.e. through dispersal). The most common metapopulation model is the extinction-recolonization model which
768:
is a tree that shows evolutionary relationships between different species based on similarities/differences among genetic or physical traits. Community ecology is based on knowledge of evolutionary relationships among coexisting species. Phylogenies embrace aspects of both time (evolutionary
656:
There are two ways in which inbreeding depression can occur. The first of these is through dominance, where beneficial alleles are usually dominant and harmful alleles are usually recessive. The increased homozygosity resulting from inbreeding means that harmful alleles are more likely to be
676:
Outbreeding depression is the reduced biological fitness in the offspring of distantly related parents. The decline in fitness due to outbreeding is attributed to a breakup of coadapted gene complexes or favorable epistatic relationships. Unlike inbreeding depression, outbreeding depression
574:
is the expected heterozygosity of a sub-populations. Both measures of heterozygosity are measured at one loci. In the equation, heterozygosity values expected from the total population are compared to observed heterozygosity values of the sub-populations within this total population. Larger
430:
sex (the sex more likely to remain at its natal grounds) benefits during reproduction simply by having familiarity with natal ground resources. A second proposal for sex-biased dispersal is the local mate competition hypothesis, which introduces the idea that individuals encounter less mate
425:
Sex-biased dispersal, or the tendency of one sex to disperse between populations more frequently than the other, is a common behavior studied by researchers. Three major hypotheses currently exist to help explain sex-biased dispersal. The resource-competition hypothesis infers that the more
297:
is an assessment that compares genetic distance with geographic distance and is most appropriate because it doesn't assume that the comparisons are independent of each other. There are three main factors that influence the chances of finding a correlation of IBD, which include sample size,
728:
and time since reproductive isolation within and among species and populations, while using non-neutral markers can provide more accurate estimations of adaptive evolutionary divergence, which can help determine the potential for a conservation unit to adapt within a certain habitat.
465:
calculating the Qst values across the owl populations. Because high gene flow was still anticipated along this cline, selection was only expected to act upon the QTLs that incur locally adaptive phenotypic traits. This can be determined by comparing the Qst values to Fst (
346:
to determine when historic bottlenecks occurred. As habitat becomes more fragmented, dispersal between populations will become increasingly rare. Therefore, subpopulations that may have historically been preserved by a metapopulation structure may start to decline. Using
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relationships) and space (geographic distribution). Typically phylogeny trees include tips, which represent groups of descendent species, and nodes, which represent the common ancestors of those descendants. If two descendants split from the same node, they are called
264:) extra-pair males had significantly longer tarsi than within-pair males, and all of the extra-pair offspring were males, supporting the prediction that females will bias their clutch towards males when they mate with an "attractive" male. In house wrens (
732:
Because of conservation units, populations and species that have high or differing levels of genetic variation can be distinguished in order to manage each individually, which can ultimately differ based on a number of factors. In one instance,
845:
barrier to a field mouse, while a hawk can fly over a river. Corridors are areas over which dispersal is possible. Corridors are stretches of suitable habitat and can also be man-made, such as overpasses over roads and fish ladders on dams.
215:
genes due to its utility in identifying fungi to genus or species taxonomic levels, and its high representation in public sequence databases. A second widely used locus (e.g. Amend et al. 2010, Weber et al. 2013), the D1-D3 region of
180:
community since the first publication of their use in the field in 2009. Similar to the exploration of bacterial diversity, these techniques have allowed high-resolution studies of fundamental questions in fungal ecology such as
1978:
Conrad KF, Johnston PV, Crossman C, Kempenaers B, Robertson RJ, Wheelwright NT, Boag PT (May 2001). "High levels of extra-pair paternity in an isolated, low-density, island population of tree swallows (Tachycineta bicolor)".
591:
can also be viewed as a way of comparing the amount of inbreeding within sub-populations to the amount of inbreeding for the total population and is sometimes referred to as an inbreeding coefficient. In these cases, higher
138:
leads to a mix of genetic material, requiring sorting before sequencing and identification. The classic technique to achieve this is through cloning, which involves incorporating the amplified DNA fragments into bacterial
412:
in mammals, because of complex genetic interactions. This behavior is potentially seen in humans. A study looking at women's choice in men based on body odors concluded that the scent of the odors were influenced by the
661:, or heterozygote advantage. Individuals that are heterozygous at a particular locus have a higher fitness than homozygotes at that locus. Inbreeding leads to decreased heterozygosity, and therefore decreased fitness.
723:
Conservation units are often identified using both neutral and non-neutral genetic markers, with each having its own advantages. Using neutral markers during unit identification can provide unbiased assumptions of
327:(or multiple) large central population(s) produces disperses to smaller satellite populations that have a population growth rate of less than one and could not persist without the influx from the main population.
253:. These are mating events that occur outside of a social bond, like monogamy and are hard to observe. Molecular data has been key to understanding the prevalence of and the individuals participating in EPFs.
249:, the study of animal behavior in relation to its ecology and evolutionary history. One behavior that molecular data has helped scientists better understand is extra-pair fertilizations (EPFs), also known as
705:, and molecular ecology in order to separate and group different species or populations based on genetic variance and significance for protection. Two of the most common types of conservation units are:
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Vandersteen
Tymchuk W, O'Reilly P, Bittman J, Macdonald D, Schulte P (May 2010). "Conservation genomics of Atlantic salmon: variation in gene expression between and within regions of the Bay of Fundy".
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Lineage sorting is driven by genetic drift and must occur before alleles become species specific. Some of these alleles over time will simply be lost, or they may proliferate. Hybridization leads to
641:
is the reduced fitness and survival of offspring from closely related parents. Inbreeding is commonly seen in small populations because of the greater chance of mating with a relative due to limited
351:
or nuclear markers to monitor dispersal coupled with population Fst values and allelic richness can provide insight into how well a population is performing and how it will perform into the future.
626:
557:
1892:
Hunt J, Simmons LW (2002-09-01). "Confidence of paternity and paternal care: covariation revealed through the experimental manipulation of the mating system in the beetle
Onthophagus taurus".
91:
Molecular ecology uses molecular genetic data to answer ecological question related to biogeography, genomics, conservation genetics, and behavioral ecology. Studies mostly use data based on
579:
values imply that the level of genetic differentiation between sub-populations within a total population is more significant. The level of differentiation is the result of a balance between
57:, and others. These fields are united in their attempt to study genetic-based questions "out in the field" as opposed to the laboratory. Molecular ecology is related to the fields of
41:
techniques to ecological questions (e.g., population structure, phylogeography, conservation, speciation, hybridization, biodiversity). It is virtually synonymous with the field of "
2030:
Kempenaers B, Everding S, Bishop C, Boag P, Robertson RJ (2001-01-18). "Extra-pair paternity and the reproductive role of male floaters in the tree swallow (Tachycineta bicolor)".
408:
genotype as well as the genotypes of potential mates in order to select the appropriate partner. Genetic compatibility in most instances is limited to specific traits, such as the
657:
expressed as homozygotes, and the deleterious effects cannot be masked by the beneficial dominant allele. The second method through which inbreeding depression occurs is through
2856:
Antoniazza S, Burri R, Fumagalli L, Goudet J, Roulin A (July 2010). "Local adaptation maintains clinal variation in melanin-based coloration of
European barn owls (Tyto alba)".
998:
Větrovský T, Baldrian P (2013). "Analysis of soil fungal communities by amplicon pyrosequencing: current approaches to data analysis and the introduction of the pipeline SEED".
330:
Metapopulation structure and the repeated extinctions and recolonizations can significantly affect a population's genetic structure. Recolonization by a few dispersers leads to
395:
explains how organisms select their mates based on two main methods; The Good Genes
Hypothesis and Genetic Compatibility. The Good Genes Hypothesis, also referred to as the
155:
platforms, has allowed exploration of bacterial ecology concerning continental-scale environmental gradients such as pH that was not feasible with traditional technology.
233:
a major concern. The construction of sequence databases that have broad representation across fungi, and that are curated by taxonomic experts is a critical next step.
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587:
within these sub-populations (increasing differentiation); however, some molecular ecologists note that it cannot be assumed that these factors are at equilibrium. F
1802:"Intraspecific ITS variability in the kingdom fungi as expressed in the international sequence databases and its implications for molecular species identification"
1461:"From genus to phylum: large-subunit and internal transcribed spacer rRNA operon regions show similar classification accuracies influenced by database composition"
403:. Therefore, the mates that are more 'attractive" are more likely to be chosen for mating and pass on their genes to the next generation. In species which exhibit
2115:
Schwarzová L, Šimek J, Coppack T, Tryjanowski P (2008-06-01). "Male-Biased Sex of Extra Pair Young in the
Socially Monogamous Red-Backed Shrike Lanius collurio".
176:
has also benefited from next-generation DNA sequencing technologies. The use of high-throughput sequencing techniques has been widely adopted by the fungal
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3488:
719:(ESU): Evolutionarily significant units are populations that show enough genetic differentiation to warrant their management as distinct units.
207:(e.g. Baldrian et al. 2012). The locus of choice for a description of the taxonomic structure of fungal communities has traditionally been the
1849:
Griffith SC, Owens IP, Thuman KA (November 2002). "Extra pair paternity in birds: a review of interspecific variation and adaptive function".
3721:
3196:
Fenster CB, Galloway LF (2000-10-18). "Inbreeding and
Outbreeding Depression in Natural Populations of Chamaecrista fasciculata (Fabaceae)".
668:. As homozygosity increases, less fit individuals will be selected against and thus those harmful alleles will be lost from the population.
2717:"Genetic variation in nuclear and mitochondrial markers supports a large sex difference in lifetime reproductive skew in a lekking species"
596:
values typically imply higher amounts of inbreeding within the sub-populations. Other factors such as selection pressures may also affect F
271:
Without molecular ecology, identifying individuals that participate in EPFs and the offspring that result from EPFs would be impossible.
1348:"Changes in Fungal Community Composition in Response to Elevated Atmospheric CO2 and Nitrogen Fertilization Varies with Soil Horizon"
147:, allow for a faster result. More recently, the advent of relatively low-cost, next-generation DNA sequencing technologies, such as
144:
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2902:
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934:"Pyrosequencing-based assessment of soil pH as a predictor of soil bacterial community structure at the continental scale"
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399:, suggests that the females will choose a male that produce an offspring that will have increased fitness advantages and
99:
1151:"Active and total microbial communities in forest soil are largely different and highly stratified during decomposition"
817:
3714:
2297:
Levins R (1969). "Some demographic and genetic consequences of environmental heterogeneity for biological control".
1654:"Five simple guidelines for establishing basic authenticity and reliability of newly generated fungal ITS sequences"
123:
in the laboratory, which would allow for identification and characterization. It also stems from the development of
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Movement: Mechanisms and Consequences : Proceedings of the Royal Entomological Society's 20th Symposium
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are used when determining the level of genetic differentiation between sub-populations within a total population. F
409:
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genes, may not allow the low taxonomic level classification of the ITS, but demonstrates superior performance in
192:
The majority of fungal ecology research leveraging next-generation sequencing approaches involves sequencing of
3453:
Harrison, Larson, Richard, Erica (2014). "Hybridization, introgression, and the nature of species boundaries".
1048:"Indoor fungal composition is geographically patterned and more diverse in temperate zones than in the tropics"
379:
88:
as a result of changes in environmental conditions or different responses by differently adapted individuals.
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2443:
Yasui Y (March 1997). "A "Good-Sperm" model can explain the evolution of costly multiple mating by females".
3689:
3707:
1399:"Limits of nuclear ribosomal DNA internal transcribed spacer (ITS) sequences as species barcodes for Fungi"
203:
in the fungal community in question, though more recent research has focused on sequencing functional gene
3161:
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1521:"UNITE: a database providing web-based methods for the molecular identification of ectomycorrhizal fungi"
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20:
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185:, fungal diversity in forest soils, stratification of fungal communities in soil horizons, and fungal
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335:
193:
124:
69:
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Kõljalg U, Larsson KH, Abarenkov K, Nilsson RH, Alexander IJ, Eberhardt U, et al. (June 2005).
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In recent years, molecular data and analyses have been able to supplement traditional approaches of
781:, which is a group of organisms that include an ancestor and all descendants of that ancestor. The
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3370:
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1684:
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It appears that EPFs in some species is driven by the good genes hypothesis, In red-back shrikes (
4022:
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2936:
225:
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Lindahl BD, Nilsson RH, Tedersoo L, Abarenkov K, Carlsen T, Kjøller R, et al. (July 2013).
80:, which allows for the simultaneous analysis of the expression of thousands of different genes.
76:
between populations. The development of molecular ecology is also closely related to the use of
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2258:"A meta-analysis of isolation by distance: relic or reference standard for landscape genetics?"
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Nilsson RH, Tedersoo L, Abarenkov K, Ryberg M, Kristiansson E, Hartmann M, et al. (2012).
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3587:"Proposal for a standardized temporal scheme of biological classification for extant species"
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of conserved regions of DNA (i.e. marker genes) to identify and describe the distribution of
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645:. Inbreeding, especially in small populations, is more likely to result in higher rates of
432:
283:
2622:
1927:
Neff BD (April 2003). "Decisions about parental care in response to perceived paternity".
1107:"454 Pyrosequencing analyses of forest soils reveal an unexpectedly high fungal diversity"
649:, which leads to higher rates of homozygosity at all loci in the population and decreased
158:
8:
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4009:
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Frankham R, Ballou JD, Eldridge MD, Lacy RC, Ralls K, Dudash MR, Fenster CB (June 2011).
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Deleterious alleles can be scrubbed by natural selection from inbred populations through
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Jenkins DG, Carey M, Czerniewska J, Fletcher J, Hether T, Jones A, et al. (2010).
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competition with relatives the farther from their natal grounds they disperse. And the
268:, extra-pair offspring were also found to be male-biased compared to within-offspring.
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1630:
1599:
1542:
1537:
1520:
1498:
1438:
1379:
1328:
1323:
1298:
1279:
1275:
1245:
1188:
1128:
1123:
1106:
1087:
971:
912:
782:
765:
709:
Management Units (MU): Management units are populations that have very low levels of
400:
348:
217:
148:
3502:
3233:
3147:
3003:
Charlesworth D, Willis JH (November 2009). "The genetics of inbreeding depression".
2701:
2623:"Sex allocation in response to local resource competition over breeding territories"
2550:
2464:
2378:
2144:
2059:
2016:
1913:
1027:
354:
3934:
3906:
3667:
3657:
3616:
3606:
3557:
3547:
3462:
3379:
3353:
3333:
3213:
3170:
3125:
3059:
3012:
2959:
2865:
2801:
2793:
2744:
2736:
2681:
2634:
2593:
2585:
2530:
2487:
2452:
2409:
2392:
Kumar S, Hedges SB (April 1998). "A molecular timescale for vertebrate evolution".
2356:
2348:
2306:
2277:
2228:
2220:
2179:
2171:
2124:
2039:
1996:
1964:
1944:
1901:
1866:
1821:
1813:
1772:
1764:
1718:
1708:
1661:
1626:
1589:
1581:
1532:
1488:
1480:
1428:
1418:
1369:
1359:
1318:
1271:
1235:
1227:
1178:
1170:
1118:
1077:
1067:
1015:
961:
953:
904:
343:
120:
81:
73:
3399:
3087:
3032:
1208:"Fungal community on decomposing leaf litter undergoes rapid successional changes"
4085:
4068:
4042:
3999:
3994:
3969:
3939:
2892:
2685:
1299:"The molecular revolution in ectomycorrhizal ecology: peeking into the black-box"
734:
665:
457:
367:
85:
2224:
1105:
Buée M, Reich M, Murat C, Morin E, Nilsson RH, Uroz S, Martin F (October 2009).
3896:
3891:
3884:
3852:
3746:
3591:
Proceedings of the
National Academy of Sciences of the United States of America
3532:
Proceedings of the National Academy of Sciences of the United States of America
3528:"Community ecology in a changing environment: Perspectives from the Quaternary"
3314:
2963:
2491:
1403:
Proceedings of the National Academy of Sciences of the United States of America
1052:
Proceedings of the National Academy of Sciences of the United States of America
761:
650:
567:
477:
466:
440:
318:
182:
116:
54:
2160:"Extra-pair young in house wren broods are more likely to be male than female"
1019:
4105:
3949:
3944:
3921:
3911:
3879:
3871:
3857:
3847:
3766:
3391:
3266:
3225:
3071:
2774:"Genetic diversity and sex-bias dispersal of plateau pika in Tibetan plateau"
2646:
2136:
2128:
2051:
1562:"Accurate, rapid taxonomic classification of fungal large-subunit rRNA genes"
1364:
790:
770:
757:
725:
678:
658:
646:
584:
339:
299:
212:
30:
3611:
3552:
3466:
2638:
2621:
Hjernquist MB, Thuman Hjernquist KA, Forsman JT, Gustafsson L (2009-03-01).
2620:
2310:
1666:
1653:
1423:
1072:
4090:
3984:
3959:
3901:
3779:
3774:
3630:
3571:
3474:
3345:
3139:
3079:
3024:
2971:
2877:
2815:
2758:
2693:
2607:
2566:"Sex-biased breeding dispersal is predicted by social environment in birds"
2534:
2499:
2242:
2193:
2175:
2008:
1956:
1878:
1835:
1800:
Nilsson RH, Kristiansson E, Ryberg M, Hallenberg N, Larsson KH (May 2008).
1786:
1730:
1638:
1603:
1546:
1502:
1442:
1383:
1332:
1283:
1249:
1231:
1192:
1132:
1091:
975:
738:
615:, etc.). These additional measures are interpreted in a similar manner to F
3047:
2542:
2421:
2370:
2043:
1617:
Vilgalys R (2003). "Taxonomic misidentification in public DNA databases".
1174:
4017:
3738:
2361:
1585:
1484:
957:
785:
tree is the simplest tree that has the minimum number of steps possible.
642:
414:
392:
294:
3291:. Chichester, West Sussex, UK: John Wiley & Sons. pp. 332–333.
1948:
1722:
3803:
3798:
3182:
2352:
1686:"Towards a unified paradigm for sequence-based identification of fungi"
713:
and can therefore be genetically differentiated from other populations.
686:
427:
323:
287:
228:. Also, the D1-D3 region may be a better candidate for sequencing with
77:
50:
3699:
3672:
2797:
2740:
2715:
Verkuil YI, Juillet C, Lank DB, Widemo F, Piersma T (September 2014).
2589:
2326:"Mitochondrial DNA sequences of primates: tempo and mode of evolution"
1768:
1713:
824:
1817:
710:
580:
404:
307:
303:
204:
196:
3662:
3645:
3174:
3063:
3016:
1560:
Liu KL, Porras-Alfaro A, Kuske CR, Eichorst SA, Xie G (March 2012).
619:
values; however, they are adjusted to accompany other factors that F
96:
within a population and the genetic similarities among populations.
4080:
2456:
1799:
484:
is the script used to represent this index when using the formula:
3442:. University of California Museum of Paleontology. 22 August 2008.
2413:
1266:
Seifert KA (May 2009). "Progress towards DNA barcoding of fungi".
2114:
322:
explains systems in which spatially distinct populations undergo
177:
172:
140:
34:
1977:
127:, which allows for the rapid amplification of genetic material.
2255:
2157:
1750:
1683:
778:
777:, a species outside of the group of interest. The trees depict
2855:
1651:
1518:
1148:
3867:
3834:
3424:(2nd ed.). Chichester, West Sussex, UK: Wiley-Blackwell.
3246:
1559:
2512:
2094:. West Sussex, UK: John Wiley & Sons, Ltd. p. 295.
2029:
3251:(2nd ed.). Cambridge, UK: Cambridge University Press.
2772:
Zhang L, Qu J, Li K, Li W, Yang M, Zhang Y (October 2017).
2563:
760:
are the evolutionary history of an organism, also known as
134:
from environmental samples using general or group-specific
3694:
3103:
1459:
Porras-Alfaro A, Liu KL, Kuske CR, Xie G (February 2014).
417:
and that they influence mate choice in human populations.
3369:
583:
amongst sub-populations (decreasing differentiation) and
131:
92:
3415:
3413:
3411:
3409:
3046:
Charlesworth, Deborah; Willis, John H. (November 2009).
2714:
1458:
1046:
Amend AS, Seifert KA, Samson R, Bruns TD (August 2010).
931:
3503:"Community ecology - Latest research and news | Nature"
3247:
Frankham R, Ballou JD, Briscoe DA, McInness KH (2010).
1045:
932:
Lauber CL, Hamady M, Knight R, Fierer N (August 2009).
3106:"Predicting the probability of outbreeding depression"
2477:
435:
suggests individuals disperse to decrease inbreeding.
3406:
2937:"Background selection and population differentiation"
2890:
2858:
Evolution; International Journal of Organic Evolution
2323:
697:
Conservation units are classifications often used in
607:
values are accompanied by several analog equations (F
493:
3419:
3286:
2089:
752:
3099:
3097:
1848:
1104:
552:{\displaystyle F_{ST}={\frac {H_{T}-H_{S}}{H_{T}}}}
3045:
3002:
1345:
885:. Alpha Science International Limited. p. 36.
551:
111:Molecular ecological techniques are used to study
3643:
1205:
997:
298:metabolism, and taxa. For example, based on the
4103:
3452:
3094:
2299:Bulletin of the Entomological Society of America
2085:
2083:
2081:
2079:
2077:
2075:
2073:
2071:
2069:
3195:
2324:Brown WM, Prager EM, Wang A, Wilson AC (1982).
894:
892:
623:may not, such as accounting for multiple loci.
3715:
2066:
853:or differently according to their gene flow.
361:
3525:
3487:: CS1 maint: multiple names: authors list (
3160:
889:
240:
2771:
2391:
1891:
1679:
1677:
1296:
3722:
3708:
3584:
2891:Woiwood I, Reynolds DR, Thomas CD (2001).
1746:
1744:
1742:
1740:
447:
3671:
3661:
3620:
3610:
3561:
3551:
3129:
2805:
2748:
2597:
2360:
2281:
2232:
2183:
1825:
1776:
1712:
1665:
1593:
1536:
1492:
1432:
1422:
1373:
1363:
1322:
1239:
1182:
1122:
1081:
1071:
965:
899:Freeland JR (2014). "Molecular Ecology".
671:
386:
3384:10.1146/annurev.ecolsys.33.010802.150448
3372:Annual Review of Ecology and Systematics
1674:
1645:
1616:
898:
823:
816:
793:of alleles from one species to another.
744:
633:
625:
461:expected to be present along the cline.
378:
353:
313:
274:
157:
145:temperature gradient gel electrophoresis
115:questions of bacterial diversity. Many
98:
3729:
3644:Holderegger R, Wagner HH (2008-03-01).
3420:Freeland J, Petersen S, Kirk H (2011).
3287:Freeland J, Kirk H, Petersen S (2011).
3048:"The genetics of inbreeding depression"
2090:Freeland J, Kirk H, Petersen S (2011).
1793:
1737:
1454:
1452:
1346:Weber CF, Vilgalys R, Kuske CR (2013).
1265:
880:
420:
4104:
2296:
2206:
1610:
1566:Applied and Environmental Microbiology
1553:
1514:
1512:
1465:Applied and Environmental Microbiology
1206:Voříšková J, Baldrian P (March 2013).
1144:
1142:
938:Applied and Environmental Microbiology
119:are not easily obtainable as cultured
106:
3703:
3365:
3363:
3310:
3308:
3282:
3280:
3278:
3276:
3249:Introduction to conservation genetics
2919:"Inbreeding and Population Structure"
2851:
2849:
2830:"Spatial autocorrelation — R Spatial"
2659:
2442:
1390:
1290:
1261:
1259:
1041:
1039:
1037:
993:
991:
989:
987:
985:
832:
692:
2934:
1926:
1449:
1396:
1098:
3526:Jackson ST, Blois JL (April 2015).
2662:"Sex ratio adjustment in fig wasps"
2032:Behavioral Ecology and Sociobiology
1509:
1297:Horton TR, Bruns TD (August 2001).
1199:
1139:
909:10.1002/9780470015902.a0003268.pub2
803:
472:
165:
13:
3360:
3305:
3273:
3163:The Journal of Wildlife Management
2846:
1806:Evolutionary Bioinformatics Online
1256:
1034:
982:
14:
4133:
3683:
2480:Trends in Ecology & Evolution
1409:(27): E1811, author reply E1812.
841:affects dispersal and gene flow.
753:Phylogenies and community Ecology
68:Methods frequently include using
3585:Avise JC, Johns GC (June 1999).
3338:10.1111/j.1365-294X.2010.04596.x
3218:10.1046/j.1523-1739.2000.99234.x
3131:10.1111/j.1523-1739.2011.01662.x
2870:10.1111/j.1558-5646.2010.00969.x
2515:Proceedings. Biological Sciences
2283:10.1111/j.1600-0587.2010.06285.x
2164:Proceedings. Biological Sciences
2001:10.1046/j.1365-294X.2001.01263.x
1906:10.1046/j.1420-9101.2002.00442.x
1871:10.1046/j.1365-294X.2002.01613.x
1631:10.1046/j.1469-8137.2003.00894.x
1538:10.1111/j.1469-8137.2005.01376.x
1324:10.1046/j.0962-1083.2001.01333.x
1276:10.1111/j.1755-0998.2009.02635.x
1124:10.1111/j.1469-8137.2009.03003.x
883:Essentials of Molecular Genetics
717:Evolutionarily significant units
410:major histocompatibility complex
170:Exploration of fungal diversity
37:that is concerned with applying
19:For the scientific journal, see
3695:WILEY Molecular Ecology Journal
3637:
3578:
3519:
3495:
3446:
3436:"Reading trees: A quick review"
3428:
3240:
3189:
3154:
3039:
2996:
2978:
2928:
2911:
2884:
2822:
2765:
2708:
2653:
2614:
2557:
2506:
2471:
2436:
2385:
2317:
2290:
2249:
2200:
2151:
2108:
2023:
1971:
1920:
1894:Journal of Evolutionary Biology
1885:
1842:
1339:
433:inbreeding avoidance hypothesis
2944:Journal of Theoretical Biology
2333:Journal of Molecular Evolution
1000:Biology and Fertility of Soils
925:
903:. John Wiley & Sons, Inc.
874:
1:
868:
570:of the total population and H
251:extra-pair copulations (EPCs)
189:on decomposing plant litter.
2686:10.1126/science.228.4701.896
84:may also be used to analyze
7:
1268:Molecular Ecology Resources
856:
773:. They also may include an
209:internal transcribed spacer
72:to determine gene flow and
21:Molecular Ecology (journal)
10:
4138:
2964:10.1016/j.jtbi.2005.01.004
2492:10.1016/j.tree.2005.02.005
811:biological species concept
362:Molecular clock hypothesis
290:, and landscape genetics.
18:
4051:
4008:
3920:
3866:
3829:
3788:
3765:
3737:
2935:Hu XS, He F (July 2005).
2225:10.1093/genetics/28.2.114
1352:Frontiers in Microbiology
1020:10.1007/s00374-013-0801-y
336:effective population size
241:Extra-pair fertilizations
3005:Nature Reviews. Genetics
2924:. University of Vermont.
2129:10.3161/000164508X395379
1365:10.3389/fmicb.2013.00078
683:population bottlenecking
566:represents the expected
454:quantitative trait locus
310:to display greater IBD.
16:Subdiscipline of ecology
4023:Ecological anthropology
3612:10.1073/pnas.96.13.7358
3553:10.1073/pnas.1403664111
3440:Understanding Evolution
3052:Nature Reviews Genetics
2445:The American Naturalist
2209:"Isolation by Distance"
2207:Wright S (March 1943).
1667:10.3897/mycokeys.4.3606
1424:10.1073/pnas.1207508109
1073:10.1073/pnas.1000454107
448:Quantitative trait loci
4033:Ecological engineering
2535:10.1098/rspb.1995.0087
2176:10.1098/rspb.2009.0283
1232:10.1038/ismej.2012.116
829:
821:
749:
672:Outbreeding depression
630:
553:
387:Mate choice hypotheses
383:
358:
334:which will reduce the
332:population bottlenecks
162:
103:
3690:Molecular Ecology UK
3467:10.1093/jhered/esu033
2778:Ecology and Evolution
2721:Ecology and Evolution
2660:Herre EA (May 1985).
2639:10.1093/beheco/arp002
2570:Ecology and Evolution
2311:10.1093/besa/15.3.237
2044:10.1007/s002650000305
1175:10.1038/ismej.2011.95
828:Habitat Fragmentation
827:
820:
748:
742:geographic location.
703:conservation genetics
685:, differentiation of
639:Inbreeding depression
634:Inbreeding depression
629:
554:
382:
357:
314:Metapopulation theory
306:are more likely than
280:Isolation by distance
275:Isolation by distance
161:
143:. Techniques such as
130:The amplification of
102:
63:conservation genetics
47:Theodosius Dobzhansky
4117:Subfields of ecology
4028:Ecological economics
3955:Evolutionary ecology
3922:Ecological phenomena
3752:Quantitative ecology
3646:"Landscape Genetics"
3198:Conservation Biology
3110:Conservation Biology
1586:10.1128/aem.06826-11
1485:10.1128/AEM.02894-13
1397:Kiss L (July 2012).
1270:. 9 Suppl s1: 83–9.
958:10.1128/AEM.00335-09
699:conservation biology
491:
421:Sex-biased dispersal
4074:Restoration ecology
4064:Glossary of ecology
4010:Interdisciplinarity
3757:Theoretical ecology
3731:Branches of ecology
3603:1999PNAS...96.7358A
3544:2015PNAS..112.4915J
3455:Journal of Heredity
3330:2010MolEc..19.1842V
3210:2000ConBi..14.1406F
3122:2011ConBi..25..465F
2956:2005JThBi.235..207H
2790:2017EcoEv...7.7708Z
2733:2014EcoEv...4.3626V
2678:1985Sci...228..896H
2582:2018EcoEv...8.6483V
2527:1995RSPSB.260..245W
2406:1998Natur.392..917K
2345:1982JMolE..18..225B
2274:2010Ecogr..33..315J
1993:2001MolEc..10.1301C
1949:10.1038/nature01528
1941:2003Natur.422..716N
1863:2002MolEc..11.2195G
1757:The New Phytologist
1705:2013MolEc..22.5271K
1578:2012ApEnM..78.1523L
1525:The New Phytologist
1477:2014ApEnM..80..829P
1415:2012PNAS..109E1812S
1315:2001MolEc..10.1855H
1224:2013ISMEJ...7..477V
1167:2012ISMEJ...6..248B
1111:The New Phytologist
1064:2010PNAS..10713748A
1012:2013BioFS..49.1027V
950:2009ApEnM..75.5111L
863:Ecological genetics
737:located within the
562:In this equation, H
397:sexy son hypothesis
373:molecular evolution
107:Bacterial diversity
59:population genetics
43:Ecological Genetics
4059:History of ecology
3965:Functional ecology
3930:Behavioral ecology
3809:Population ecology
2627:Behavioral Ecology
2353:10.1007/bf01734101
2117:Acta Ornithologica
838:Landscape genetics
833:Landscape genetics
830:
822:
750:
693:Conservation units
631:
549:
384:
359:
266:Troglodytes aedon)
247:behavioral ecology
222:sequence alignment
163:
104:
45:" as pioneered by
4122:Molecular biology
4112:Molecular ecology
4099:
4098:
4038:Political ecology
3980:Molecular ecology
3975:Landscape ecology
3843:Microbial ecology
3819:Ecosystem ecology
3814:Community ecology
3422:Molecular Ecology
3318:Molecular Ecology
3298:978-0-470-74833-6
3289:Molecular Ecology
3258:978-0-521-87847-0
2904:978-0-85199-781-0
2798:10.1002/ece3.3289
2784:(19): 7708–7718.
2741:10.1002/ece3.1188
2590:10.1002/ece3.4095
2576:(13): 6483–6491.
2101:978-1-119-99308-7
2092:Molecular Ecology
1981:Molecular Ecology
1851:Molecular Ecology
1769:10.1111/nph.12243
1714:10.1111/mec.12481
1693:Molecular Ecology
1303:Molecular Ecology
918:978-0-470-01590-2
797:Community ecology
783:maximum parsimony
766:phylogenetic tree
547:
401:genetic viability
338:(Ne), accelerate
218:28S ribosomal RNA
55:Godfrey M. Hewitt
39:molecular genetic
27:Molecular ecology
4129:
3935:Chemical ecology
3907:Tropical ecology
3724:
3717:
3710:
3701:
3700:
3678:
3677:
3675:
3665:
3641:
3635:
3634:
3624:
3614:
3582:
3576:
3575:
3565:
3555:
3523:
3517:
3516:
3514:
3513:
3499:
3493:
3492:
3486:
3478:
3450:
3444:
3443:
3432:
3426:
3425:
3417:
3404:
3403:
3367:
3358:
3357:
3312:
3303:
3302:
3284:
3271:
3270:
3244:
3238:
3237:
3204:(5): 1406–1412.
3193:
3187:
3186:
3158:
3152:
3151:
3133:
3101:
3092:
3091:
3043:
3037:
3036:
3000:
2994:
2993:
2982:
2976:
2975:
2941:
2932:
2926:
2925:
2923:
2915:
2909:
2908:
2888:
2882:
2881:
2853:
2844:
2843:
2841:
2840:
2826:
2820:
2819:
2809:
2769:
2763:
2762:
2752:
2712:
2706:
2705:
2657:
2651:
2650:
2618:
2612:
2611:
2601:
2561:
2555:
2554:
2510:
2504:
2503:
2475:
2469:
2468:
2440:
2434:
2433:
2400:(6679): 917–20.
2389:
2383:
2382:
2364:
2330:
2321:
2315:
2314:
2294:
2288:
2287:
2285:
2253:
2247:
2246:
2236:
2204:
2198:
2197:
2187:
2170:(1665): 2285–9.
2155:
2149:
2148:
2112:
2106:
2105:
2087:
2064:
2063:
2027:
2021:
2020:
1975:
1969:
1968:
1924:
1918:
1917:
1889:
1883:
1882:
1857:(11): 2195–212.
1846:
1840:
1839:
1829:
1818:10.4137/EBO.S653
1797:
1791:
1790:
1780:
1748:
1735:
1734:
1716:
1690:
1681:
1672:
1671:
1669:
1649:
1643:
1642:
1614:
1608:
1607:
1597:
1557:
1551:
1550:
1540:
1516:
1507:
1506:
1496:
1456:
1447:
1446:
1436:
1426:
1394:
1388:
1387:
1377:
1367:
1343:
1337:
1336:
1326:
1294:
1288:
1287:
1263:
1254:
1253:
1243:
1212:The ISME Journal
1203:
1197:
1196:
1186:
1155:The ISME Journal
1146:
1137:
1136:
1126:
1102:
1096:
1095:
1085:
1075:
1058:(31): 13748–53.
1043:
1032:
1031:
1006:(8): 1027–1037.
995:
980:
979:
969:
929:
923:
922:
896:
887:
886:
881:Miglani (2015).
878:
804:Species concepts
558:
556:
555:
550:
548:
546:
545:
536:
535:
534:
522:
521:
511:
506:
505:
478:Fixation indices
473:Fixation indices
344:molecular clocks
211:(ITS) region of
201:taxonomic groups
166:Fungal diversity
82:Quantitative PCR
4137:
4136:
4132:
4131:
4130:
4128:
4127:
4126:
4102:
4101:
4100:
4095:
4086:Natural history
4069:Applied ecology
4047:
4043:Systems ecology
4004:
4000:Thermal ecology
3995:Spatial ecology
3970:Genetic ecology
3940:Disease ecology
3916:
3872:biogeographical
3862:
3825:
3784:
3761:
3733:
3728:
3686:
3681:
3663:10.1641/B580306
3642:
3638:
3597:(13): 7358–63.
3583:
3579:
3538:(16): 4915–21.
3524:
3520:
3511:
3509:
3501:
3500:
3496:
3480:
3479:
3451:
3447:
3434:
3433:
3429:
3418:
3407:
3368:
3361:
3313:
3306:
3299:
3285:
3274:
3259:
3245:
3241:
3194:
3190:
3175:10.2307/3796784
3159:
3155:
3102:
3095:
3064:10.1038/nrg2664
3058:(11): 783–796.
3044:
3040:
3017:10.1038/nrg2664
3001:
2997:
2984:
2983:
2979:
2939:
2933:
2929:
2921:
2917:
2916:
2912:
2905:
2889:
2885:
2854:
2847:
2838:
2836:
2828:
2827:
2823:
2770:
2766:
2727:(18): 3626–32.
2713:
2709:
2672:(4701): 896–8.
2658:
2654:
2619:
2615:
2562:
2558:
2521:(1359): 245–9.
2511:
2507:
2476:
2472:
2441:
2437:
2390:
2386:
2328:
2322:
2318:
2295:
2291:
2254:
2250:
2205:
2201:
2156:
2152:
2113:
2109:
2102:
2088:
2067:
2028:
2024:
1976:
1972:
1935:(6933): 716–9.
1925:
1921:
1890:
1886:
1847:
1843:
1798:
1794:
1749:
1738:
1688:
1682:
1675:
1650:
1646:
1615:
1611:
1558:
1554:
1517:
1510:
1457:
1450:
1395:
1391:
1344:
1340:
1295:
1291:
1264:
1257:
1204:
1200:
1147:
1140:
1103:
1099:
1044:
1035:
996:
983:
944:(15): 5111–20.
930:
926:
919:
897:
890:
879:
875:
871:
859:
835:
809:concept is the
806:
755:
735:Atlantic salmon
695:
674:
666:genetic purging
636:
622:
618:
614:
610:
606:
599:
595:
590:
578:
573:
565:
541:
537:
530:
526:
517:
513:
512:
510:
498:
494:
492:
489:
488:
483:
475:
458:cline (biology)
450:
423:
391:The concept of
389:
368:molecular clock
364:
316:
277:
262:Lanius collurio
243:
168:
109:
86:gene expression
78:DNA microarrays
70:microsatellites
24:
17:
12:
11:
5:
4135:
4125:
4124:
4119:
4114:
4097:
4096:
4094:
4093:
4088:
4083:
4078:
4077:
4076:
4066:
4061:
4055:
4053:
4049:
4048:
4046:
4045:
4040:
4035:
4030:
4025:
4020:
4014:
4012:
4006:
4005:
4003:
4002:
3997:
3992:
3990:Social ecology
3987:
3982:
3977:
3972:
3967:
3962:
3957:
3952:
3947:
3942:
3937:
3932:
3926:
3924:
3918:
3917:
3915:
3914:
3909:
3904:
3899:
3897:Forest ecology
3894:
3892:Desert ecology
3889:
3888:
3887:
3885:Arctic ecology
3876:
3874:
3864:
3863:
3861:
3860:
3855:
3853:Insect ecology
3850:
3845:
3839:
3837:
3827:
3826:
3824:
3823:
3822:
3821:
3816:
3811:
3801:
3795:
3793:
3786:
3785:
3783:
3782:
3777:
3771:
3769:
3763:
3762:
3760:
3759:
3754:
3749:
3743:
3741:
3735:
3734:
3727:
3726:
3719:
3712:
3704:
3698:
3697:
3692:
3685:
3684:External links
3682:
3680:
3679:
3656:(3): 199–207.
3636:
3577:
3518:
3507:www.nature.com
3494:
3445:
3427:
3405:
3378:(1): 475–505.
3359:
3324:(9): 1842–59.
3304:
3297:
3272:
3257:
3239:
3188:
3153:
3093:
3038:
3011:(11): 783–96.
2995:
2977:
2927:
2910:
2903:
2883:
2864:(7): 1944–54.
2845:
2821:
2764:
2707:
2652:
2633:(2): 335–339.
2613:
2556:
2505:
2470:
2457:10.1086/286006
2451:(3): 573–584.
2435:
2384:
2316:
2305:(3): 237–240.
2289:
2268:(2): 315–320.
2248:
2199:
2150:
2123:(2): 235–239.
2107:
2100:
2065:
2038:(4): 251–259.
2022:
1970:
1919:
1900:(5): 784–795.
1884:
1841:
1792:
1736:
1699:(21): 5271–7.
1673:
1644:
1609:
1572:(5): 1523–33.
1552:
1508:
1448:
1389:
1338:
1309:(8): 1855–71.
1289:
1255:
1198:
1138:
1097:
1033:
981:
924:
917:
888:
872:
870:
867:
866:
865:
858:
855:
834:
831:
805:
802:
762:phylogeography
754:
751:
721:
720:
714:
694:
691:
673:
670:
651:heterozygosity
635:
632:
620:
616:
612:
608:
604:
597:
593:
588:
576:
571:
568:heterozygosity
563:
560:
559:
544:
540:
533:
529:
525:
520:
516:
509:
504:
501:
497:
481:
474:
471:
467:fixation index
449:
446:
422:
419:
388:
385:
363:
360:
319:Metapopulation
315:
312:
276:
273:
242:
239:
183:phylogeography
167:
164:
117:microorganisms
108:
105:
15:
9:
6:
4:
3:
2:
4134:
4123:
4120:
4118:
4115:
4113:
4110:
4109:
4107:
4092:
4089:
4087:
4084:
4082:
4079:
4075:
4072:
4071:
4070:
4067:
4065:
4062:
4060:
4057:
4056:
4054:
4050:
4044:
4041:
4039:
4036:
4034:
4031:
4029:
4026:
4024:
4021:
4019:
4016:
4015:
4013:
4011:
4007:
4001:
3998:
3996:
3993:
3991:
3988:
3986:
3983:
3981:
3978:
3976:
3973:
3971:
3968:
3966:
3963:
3961:
3958:
3956:
3953:
3951:
3950:Ecotoxicology
3948:
3946:
3945:Ecophysiology
3943:
3941:
3938:
3936:
3933:
3931:
3928:
3927:
3925:
3923:
3919:
3913:
3912:Urban ecology
3910:
3908:
3905:
3903:
3900:
3898:
3895:
3893:
3890:
3886:
3883:
3882:
3881:
3880:Polar ecology
3878:
3877:
3875:
3873:
3869:
3865:
3859:
3858:Human ecology
3856:
3854:
3851:
3849:
3848:Plant ecology
3846:
3844:
3841:
3840:
3838:
3836:
3832:
3828:
3820:
3817:
3815:
3812:
3810:
3807:
3806:
3805:
3802:
3800:
3797:
3796:
3794:
3791:
3787:
3781:
3778:
3776:
3773:
3772:
3770:
3768:
3767:Spatial scale
3764:
3758:
3755:
3753:
3750:
3748:
3747:Field ecology
3745:
3744:
3742:
3740:
3736:
3732:
3725:
3720:
3718:
3713:
3711:
3706:
3705:
3702:
3696:
3693:
3691:
3688:
3687:
3674:
3669:
3664:
3659:
3655:
3651:
3647:
3640:
3632:
3628:
3623:
3618:
3613:
3608:
3604:
3600:
3596:
3592:
3588:
3581:
3573:
3569:
3564:
3559:
3554:
3549:
3545:
3541:
3537:
3533:
3529:
3522:
3508:
3504:
3498:
3490:
3484:
3476:
3472:
3468:
3464:
3460:
3456:
3449:
3441:
3437:
3431:
3423:
3416:
3414:
3412:
3410:
3401:
3397:
3393:
3389:
3385:
3381:
3377:
3373:
3366:
3364:
3355:
3351:
3347:
3343:
3339:
3335:
3331:
3327:
3323:
3319:
3311:
3309:
3300:
3294:
3290:
3283:
3281:
3279:
3277:
3268:
3264:
3260:
3254:
3250:
3243:
3235:
3231:
3227:
3223:
3219:
3215:
3211:
3207:
3203:
3199:
3192:
3184:
3180:
3176:
3172:
3168:
3164:
3157:
3149:
3145:
3141:
3137:
3132:
3127:
3123:
3119:
3116:(3): 465–75.
3115:
3111:
3107:
3100:
3098:
3089:
3085:
3081:
3077:
3073:
3069:
3065:
3061:
3057:
3053:
3049:
3042:
3034:
3030:
3026:
3022:
3018:
3014:
3010:
3006:
2999:
2991:
2987:
2981:
2973:
2969:
2965:
2961:
2957:
2953:
2950:(2): 207–19.
2949:
2945:
2938:
2931:
2920:
2914:
2906:
2900:
2896:
2895:
2887:
2879:
2875:
2871:
2867:
2863:
2859:
2852:
2850:
2835:
2831:
2825:
2817:
2813:
2808:
2803:
2799:
2795:
2791:
2787:
2783:
2779:
2775:
2768:
2760:
2756:
2751:
2746:
2742:
2738:
2734:
2730:
2726:
2722:
2718:
2711:
2703:
2699:
2695:
2691:
2687:
2683:
2679:
2675:
2671:
2667:
2663:
2656:
2648:
2644:
2640:
2636:
2632:
2628:
2624:
2617:
2609:
2605:
2600:
2595:
2591:
2587:
2583:
2579:
2575:
2571:
2567:
2560:
2552:
2548:
2544:
2540:
2536:
2532:
2528:
2524:
2520:
2516:
2509:
2501:
2497:
2493:
2489:
2485:
2481:
2474:
2466:
2462:
2458:
2454:
2450:
2446:
2439:
2431:
2427:
2423:
2419:
2415:
2414:10.1038/31927
2411:
2407:
2403:
2399:
2395:
2388:
2380:
2376:
2372:
2368:
2363:
2362:2027.42/48036
2358:
2354:
2350:
2346:
2342:
2339:(4): 225–39.
2338:
2334:
2327:
2320:
2312:
2308:
2304:
2300:
2293:
2284:
2279:
2275:
2271:
2267:
2263:
2259:
2252:
2244:
2240:
2235:
2230:
2226:
2222:
2219:(2): 114–38.
2218:
2214:
2210:
2203:
2195:
2191:
2186:
2181:
2177:
2173:
2169:
2165:
2161:
2154:
2146:
2142:
2138:
2134:
2130:
2126:
2122:
2118:
2111:
2103:
2097:
2093:
2086:
2084:
2082:
2080:
2078:
2076:
2074:
2072:
2070:
2061:
2057:
2053:
2049:
2045:
2041:
2037:
2033:
2026:
2018:
2014:
2010:
2006:
2002:
1998:
1994:
1990:
1987:(5): 1301–8.
1986:
1982:
1974:
1966:
1962:
1958:
1954:
1950:
1946:
1942:
1938:
1934:
1930:
1923:
1915:
1911:
1907:
1903:
1899:
1895:
1888:
1880:
1876:
1872:
1868:
1864:
1860:
1856:
1852:
1845:
1837:
1833:
1828:
1823:
1819:
1815:
1811:
1807:
1803:
1796:
1788:
1784:
1779:
1774:
1770:
1766:
1763:(1): 288–99.
1762:
1758:
1754:
1747:
1745:
1743:
1741:
1732:
1728:
1724:
1720:
1715:
1710:
1706:
1702:
1698:
1694:
1687:
1680:
1678:
1668:
1663:
1659:
1655:
1648:
1640:
1636:
1632:
1628:
1624:
1620:
1613:
1605:
1601:
1596:
1591:
1587:
1583:
1579:
1575:
1571:
1567:
1563:
1556:
1548:
1544:
1539:
1534:
1531:(3): 1063–8.
1530:
1526:
1522:
1515:
1513:
1504:
1500:
1495:
1490:
1486:
1482:
1478:
1474:
1471:(3): 829–40.
1470:
1466:
1462:
1455:
1453:
1444:
1440:
1435:
1430:
1425:
1420:
1416:
1412:
1408:
1404:
1400:
1393:
1385:
1381:
1376:
1371:
1366:
1361:
1357:
1353:
1349:
1342:
1334:
1330:
1325:
1320:
1316:
1312:
1308:
1304:
1300:
1293:
1285:
1281:
1277:
1273:
1269:
1262:
1260:
1251:
1247:
1242:
1237:
1233:
1229:
1225:
1221:
1218:(3): 477–86.
1217:
1213:
1209:
1202:
1194:
1190:
1185:
1180:
1176:
1172:
1168:
1164:
1161:(2): 248–58.
1160:
1156:
1152:
1145:
1143:
1134:
1130:
1125:
1120:
1117:(2): 449–56.
1116:
1112:
1108:
1101:
1093:
1089:
1084:
1079:
1074:
1069:
1065:
1061:
1057:
1053:
1049:
1042:
1040:
1038:
1029:
1025:
1021:
1017:
1013:
1009:
1005:
1001:
994:
992:
990:
988:
986:
977:
973:
968:
963:
959:
955:
951:
947:
943:
939:
935:
928:
920:
914:
910:
906:
902:
895:
893:
884:
877:
873:
864:
861:
860:
854:
850:
846:
842:
839:
826:
819:
815:
812:
801:
798:
794:
792:
791:introgression
786:
784:
780:
776:
772:
771:sister groups
767:
763:
759:
747:
743:
740:
736:
730:
727:
726:genetic drift
718:
715:
712:
708:
707:
706:
704:
700:
690:
688:
684:
680:
679:genetic drift
669:
667:
662:
660:
659:overdominance
654:
652:
648:
647:genetic drift
644:
640:
628:
624:
601:
586:
585:genetic drift
582:
569:
542:
538:
531:
527:
523:
518:
514:
507:
502:
499:
495:
487:
486:
485:
479:
470:
468:
462:
459:
455:
445:
442:
436:
434:
429:
418:
416:
411:
406:
402:
398:
394:
381:
377:
374:
369:
356:
352:
350:
349:mitochondrial
345:
341:
340:genetic drift
337:
333:
328:
325:
320:
311:
309:
305:
301:
300:meta-analysis
296:
291:
289:
285:
281:
272:
269:
267:
263:
258:
254:
252:
248:
238:
234:
231:
227:
226:phylogenetics
223:
219:
214:
213:ribosomal RNA
210:
206:
202:
198:
195:
190:
188:
184:
179:
175:
174:
160:
156:
154:
150:
146:
142:
137:
133:
128:
126:
125:PCR technique
122:
118:
114:
101:
97:
94:
89:
87:
83:
79:
75:
74:hybridization
71:
66:
64:
60:
56:
52:
48:
44:
40:
36:
32:
31:subdiscipline
28:
22:
4091:Biogeography
3985:Paleoecology
3979:
3960:Fire ecology
3902:Soil ecology
3790:Organisation
3780:Macroecology
3775:Microecology
3653:
3649:
3639:
3594:
3590:
3580:
3535:
3531:
3521:
3510:. Retrieved
3506:
3497:
3483:cite journal
3458:
3454:
3448:
3439:
3430:
3421:
3375:
3371:
3321:
3317:
3288:
3248:
3242:
3201:
3197:
3191:
3166:
3162:
3156:
3113:
3109:
3055:
3051:
3041:
3008:
3004:
2998:
2989:
2980:
2947:
2943:
2930:
2913:
2893:
2886:
2861:
2857:
2837:. Retrieved
2834:rspatial.org
2833:
2824:
2781:
2777:
2767:
2724:
2720:
2710:
2669:
2665:
2655:
2630:
2626:
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4018:Agroecology
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2990:www.nps.gov
1812:: 193–201.
758:Phylogenies
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2017:23317236
2009:11380885
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1914:83253330
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