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them to alter their behaviours and interactions, therefore resetting the so-called "behavioral space race". The way in which fragmentation changes and re-shapes these interactions can occur in many different forms. Most prey species have patches of land that are a refuge from their predators, allowing them the safety to reproduce and raise their young. Human introduced structures such as roads and pipelines alter these areas by facilitating predator activity in these refuges, increasing predator-prey overlap. The opposite could also occur in the favour of prey, increasing prey refuge and subsequently decreasing predation rates. Fragmentation may also increase predator abundance or predator efficiency and therefore increase predation rates in this manner. Several other factors can also increase or decrease the extent to which the shifting predator-prey dynamics affect certain species, including how diverse a predators diet is and how flexible habitat requirements are for predators and prey. Depending on which species are affected and these other factors, fragmentation and its effects on predator-prey dynamics may contribute to species extinction. In response to these new environmental pressures, new adaptive behaviours may be developed. Prey species may adapt to increased risk of predation with strategies such as altering mating tactics or changing behaviours and activities related to food and foraging.
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vocalizations, the song, and the territorial call. The territorial call is used by males to defend and signal territory from other male Larks and is shared between neighbouring territories when males respond to a rivals song. Occasionally it is used as a threat signal to signify an impending attack on territory. A large song repertoire can enhance a male's ability to survive and reproduce as he has a greater ability to defend his territory from other males, and a larger number of males in the species means a larger variety of songs being transmitted. Fragmentation of the Dupont's Lark territory from agriculture, forestry and urbanization appears to have a large effect on their communication structures. Males only perceive territories of a certain distance to be rivals and so isolation of territory from others due to fragmentation leads to a decrease in territorial calls as the males no longer have any reason to use it or have any songs to match.
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fragmentation per se), has been suggested to be small. A review of empirical studies found that, of the 381 reported significant effect of habitat fragmentation per se on species occurrences, abundances or diversity in the scientific literature, 76% were positive whereas 24% were negative. Despite these results, the scientific literature tends to emphasize negative effects more than positive effects. Positive effects of habitat fragmentation per se imply that several small patches of habitat can have higher conservation value than a single large patch of equivalent size. Land sharing strategies could therefore have more positive impacts on species than land sparing strategies. Although the negative effects of habitat loss are generally viewed to be much larger than that of habitat fragmentation, the two events are heavily connected and observations are not usually independent of one another.
541:. Genetic drift is random changes to the genetic makeup of populations and leads to reductions in genetic diversity. The smaller the population is, the more likely genetic drift will be a driving force of evolution rather than natural selection. Because genetic drift is a random process, it does not allow species to become more adapted to their environment. Habitat fragmentation is associated with increases to genetic drift in small populations which can have negative consequences for the genetic diversity of the populations. However, research suggests that some tree species may be resilient to the negative consequences of genetic drift until population size is as small as ten individuals or less.
66:
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fitness and survival. Habitat fragmentation alters the resources available and the structure of habitats, as a result, alters the behaviours of species and the dynamics between differing species. Behaviours affected can be within a species such as reproduction, mating, foraging, species dispersal, communication and movement patterns or can be behaviours between species such as predator-prey relationships. In addition, when animals happen to venture into unknown areas in between fragmented forests or landscapes, they can supposedly come into contact with humans which puts them at a great risk and further decreases their chances of survival.
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Endogenous threats can result in changes to breeding patterns or migration patterns and are often triggered by exogenous processes. Exogenous processes are independent of species biology and can include habitat degradation, habitat subdivision or habitat isolation. These processes can have a substantial impact on endogenous processes by fundamentally altering species behavior. Habitat subdivision or isolation can lead to changes in dispersal or movement of species including changes to seasonal migration. These changes can lead to a decrease in a density of species, increased competition or even increased predation.
51:
513:. When a habitat becomes fragmented and reduced in area, gene flow and migration are typically reduced. Fewer individuals will migrate into the remaining fragments, and small disconnected populations that may have once been part of a single large population will become reproductively isolated. Scientific evidence that gene flow is reduced due to fragmentation depends on the study species. While trees that have long-range pollination and dispersal mechanisms may not experience reduced gene flow following fragmentation, most species are at risk of reduced gene flow following habitat fragmentation.
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Planted forests become increasingly important as they supply approximately a quarter of global industrial roundwood production and are predicted to account for 50% of global output within two decades (Brown, 1998; Jaakko Poyry, 1999). Although there have been many difficulties, the implementation of forest certification has been quite prominent in being able to raise effective awareness and disseminating knowledge on a holistic concept, embracing economic, environmental and social issues, worldwide. While also providing a tool for a range of other applications than assessment of
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electricity transmission ROWs, gas pipeline and telecommunication ROWs. Electricity transmission ROWs are created to prevent vegetation interference with transmission lines. Some studies have shown that electricity transmission ROWs harbor more plant species than adjoining forest areas, due to alterations in the microclimate in and around the corridor. Discontinuities in forest areas associated with utility right-of-ways can serve as biodiversity havens for native bees and grassland species, as the right-of-ways are preserved in an early successional stage.
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442:. The existence of viable habitat is critical to the survival of any species, and in many cases, the fragmentation of any remaining habitat can lead to difficult decisions for conservation biologists. Given a limited amount of resources available for conservation is it preferable to protect the existing isolated patches of habitat or to buy back land to get the largest possible contiguous piece of land. In rare cases, a
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162:, or whether the term primarily applies to the phenomenon of habitat being cut into smaller pieces without significant reduction in habitat area. Scientists who use the stricter definition of "habitat fragmentation" per se would refer to the loss of habitat area as "habitat loss" and explicitly mention both terms if describing a situation where the habitat becomes less connected and there is less overall habitat.
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that is denoted by isolated patches of habitat surrounded by unsuitable landscape environments, the variegation model applies to landscapes modified by agriculture where small patches of habitat remain near the remnant original habitat. In between these patches are a matrix of grassland that is often modified versions of the original habitat. These areas do not present as much of a barrier to native species.
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155:"fragmentation ... not only causes loss of the amount of habitat but by creating small, isolated patches it also changes the properties of the remaining habitat" (van den Berg et al. 2001). Habitat fragmentation is the landscape level of the phenomenon, and patch level process. Thus meaning, it covers; the patch areas, edge effects, and patch shape complexity.
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different climate and favours different species from the interior habitat. Small fragments are therefore unfavourable for species that require interior habitat. The percentage preservation of contiguous habitats is closely related to both genetic and species biodiversity preservation. Generally a 10% remnant contiguous habitat will result in a 50%
498:, have a smaller pool of fitness-maintaining alleles to survive in the face of environmental change. However, in some scenarios, where subsets of genetic diversity are partitioned among multiple habitat fragments, almost all original genetic diversity can be maintained despite each individual fragment displaying a reduced subset of diversity.
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organisms are disproportionately affected by some types of habitat fragmentation because they cannot respond quickly to the altered spatial configuration of the habitat. Habitat fragmentation consistently reduces biodiversity by 13 to 75% and impairs key ecosystem functions by decreasing biomass and
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The other model is the variegation model. Variegated landscapes retain much of their natural vegetation but are intermixed with gradients of modified habitat This model of habitat fragmentation typically applies to landscapes that are modified by agriculture. In contrast to the fragmentation model
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Forest patches that are smaller or more isolated will lose species faster than those that are larger or less isolated. A large number of small forest "islands" typically cannot support the same biodiversity that a single contiguous forest would hold, even if their combined area is much greater than
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In the boreal woodland caribous of
British Columbia, the effects of fragmentation are demonstrated. The species refuge area is peatland bog which has been interrupted by linear features such as roads and pipelines. These features have allowed their natural predators, the wolf, and the black bear to
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Habitat fragmentation due to anthropogenic activities has been shown to greatly affect the predator-prey dynamics of many species by altering the number of species and the members of those species. This affects the natural predator-prey relationships between animals in a given community and forces
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The best solution is generally dependent on the particular species or ecosystem that is being considered. More mobile species, like most birds, do not need connected habitat while some smaller animals, like rodents, may be more exposed to predation in open land. These questions generally fall under
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The effects of current fragmentation will continue to emerge for decades. Extinction debts are likely to come due, although the counteracting immigration debts may never fully be paid. Indeed, the experiments here reveal ongoing losses of biodiversity and ecosystem functioning two decades or longer
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than nearby protected areas, and forest fires only affected 0.1 percent of certified land area, compared to 10.4 percent of protected areas. However, it must be duly noted that short term decisions regarding forest sector employment and harvest practices can have long-term effects on biodiversity.
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Forest fragmentation also includes less subtle forms of discontinuities such as utility right-of-ways (ROWs). Utility ROWs are of ecological interest because they have become pervasive in many forest communities, spanning areas as large as 5 million acres in the United States. Utility ROWs include
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of an environment. Increased fragmentation has been linked to reduced populations and diversity of fungi responsible for decomposition, as well as the insects they are host to. This has been linked to simplified food webs in highly fragmented areas compared to old growth forests. Furthermore, edge
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As the remaining habitat patches are smaller, they tend to support smaller populations of fewer species. Small populations are at an increased risk of a variety of genetic consequences that influence their long-term survival. Remnant populations often contain only a subset of the genetic diversity
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Reduced fragment area, increased isolation, and increased edge initiate changes that percolate through all ecosystems. Habitat fragmentation is able to formulate persistent outcomes which can also become unexpected such as an abundance of some species and the pattern that long temporal scales are
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may gain some measure of disease protection by being distributed in isolated habitats, and when controlled for overall habitat loss some studies have shown a positive relationship between species richness and fragmentation; this phenomenon has been called the habitat amount hypothesis, though the
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Fletcher, Robert J.; Didham, Raphael K.; Banks-Leite, Cristina; Barlow, Jos; Ewers, Robert M.; Rosindell, James; Holt, Robert D.; Gonzalez, Andrew; Pardini, Renata; Damschen, Ellen I.; Melo, Felipe P.L.; Ries, Leslie; Prevedello, Jayme A.; Tscharntke, Teja; Laurance, William F.; Lovejoy, Thomas;
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Although the way habitat fragmentation affects the genetics and extinction rates of species has been heavily studied, fragmentation has also been shown to affect species' behaviours and cultures as well. This is important because social interactions can determine and have an effect on a species'
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and reducing gene flow within plant species. While genetic variation may decrease with remnant population size, not all fragmentation events lead to genetic losses and different types of genetic variation. Rarely, fragmentation can also increase gene flow among remnant populations, breaking down
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is found in the fossil record.Studies have demonstrated the impacts of individual species at the landscape level For example, From research the results show that the impact of deer herbivory on forest plant communities can be observed at the landscape level at the
Rondeau Provincial park for the
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Forest fragmentation is a form of habitat fragmentation where forests are reduced (either naturally or man-made) to relatively small, isolated patches of forest known as forest fragments or forest remnants. The intervening matrix that separates the remaining woodland patches can be natural open
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become more likely in the area as humidity drops and temperature and wind levels rise. Exotic and pest species may establish themselves easily in such disturbed environments, and the proximity of domestic animals often upsets the natural ecology. Also, habitat along the edge of a fragment has a
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There are two types of processes that can lead to habitat fragmentation. There are exogenous processes and endogenous processes. Endogenous is a process that develops as a part of species biology so they typically include changes in biology, behavior, and interactions within or between species.
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reservoirs. Habitats which were once continuous become divided into separate fragments. Due to human activities, many tropical and temperate habitats have already been severely fragmented, and in the near future, the degree of fragmentation will significantly rise. After intensive clearing, the
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In order for populations to evolve in response to natural selection, they must be large enough that natural selection is a stronger evolutionary force than genetic drift. Recent studies on the impacts of habitat fragmentation on adaptation in some plant species have suggested that organisms in
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Area is the primary determinant of the number of species in a fragment and the relative contributions of demographic and genetic processes to the risk of global population extinction depend on habitat configuration, stochastic environmental variation and species features. Minor fluctuations in
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Additionally, forest fragmentation affects the native plant species present within the area by dividing large populations into smaller ones. In turn, smaller populations are more inclined to be affected by genetic drift and population performance, as well as experience increases in inbreeding
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of native vegetation. In some cases, a bridge or underpass may be enough to join two fragments. This has the potential to mitigate the problem of isolation but not the loss of interior habitat. Wildlife corridors can help animals to move and occupy new areas when food sources or other natural
371:. In an unfragmented landscape a declining population can be "rescued" by immigration from a nearby expanding population. In fragmented landscapes, the distance between fragments may prevent this from happening. Additionally, unoccupied fragments of habitat that are separated from a source of
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Habitat loss, which can occur through the process of habitat fragmentation, is considered to be the greatest threat to species. But, the effect of the configuration of habitat patches within the landscape, independent of the effect of the amount of habitat within the landscape (referred to as
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Fragmentation affecting the communication behaviours of birds has been well studied in Dupont's Lark. The Larks primarily reside in regions of Spain and are a small passerine bird which uses songs as a means of cultural transmission between members of the species. The Larks have two distinct
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climate, resources, or other factors that would be unremarkable and quickly corrected in large populations can be catastrophic in small, isolated populations. Thus fragmentation of habitat is an important cause of species extinction. Population dynamics of subdivided populations tend to vary
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The species-oriented approach focuses specifically on individual species and how they each respond to their environment and habitat changes with in it. This approach can be limited because it does only focus on individual species and does not allow for a broad view of the impacts of habitat
422:. These fragments of habitat may not be large or connected enough to support species that need a large territory where they can find mates and food. The loss and fragmentation of habitats makes it difficult for migratory species to find places to rest and feed along their migration routes.
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Haddad, Nick M.; Brudvig, Lars A.; Clobert, Jean; Davies, Kendi F.; Gonzalez, Andrew; Holt, Robert D.; Lovejoy, Thomas E.; Sexton, Joseph O.; Austin, Mike P.; Collins, Cathy D.; Cook, William M.; Damschen, Ellen I.; Ewers, Robert M.; Foster, Bryan L.; Jenkins, Clinton N. (2015-03-06).
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Haddad, Nick M.; Brudvig, Lars A.; Clobert, Jean; Davies, Kendi F.; Gonzalez, Andrew; Holt, Robert D.; Lovejoy, Thomas E.; Sexton, Joseph O.; Austin, Mike P.; Collins, Cathy D.; Cook, William M.; Damschen, Ellen I.; Ewers, Robert M.; Foster, Bryan L.; Jenkins, Clinton N. (2015-03-06).
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Pavlova, Alexandra; Beheregaray, Luciano B.; Coleman, Rhys; Gilligan, Dean; Harrisson, Katherine A.; Ingram, Brett A.; Kearns, Joanne; Lamb, Annika M.; Lintermans, Mark; Lyon, Jarod; Nguyen, Thuy T. T.; Sasaki, Minami; Tonkin, Zeb; Yen, Jian D. L.; Sunnucks, Paul (July 2017).
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Bogaert, Jan; Barima, Yao S. S.; Mongo, LĂ©on Iyongo Waya; Bamba, Issouf; Mama, Adi; Toyi, Mireille; Lafortezza, Raffaele (2011), Li, Chao; Lafortezza, Raffaele; Chen, Jiquan (eds.), "Forest
Fragmentation: Causes, Ecological Impacts and Implications for Landscape Management",
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and tries to infer causal relationships between the defined landscapes and the occurrence of species or groups of species within them. The approach has limitations in its collective assumptions across species or landscapes which may not account for variations amongst them.
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increases, facilitating the expression of deleterious alleles that reduce the fitness. Habitat fragmentation can lead to inbreeding depression for many species due to reduced gene flow. Inbreeding depression is associated with conservation risks, like local extinction.
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Wilson, Maxwell C.; Chen, Xiao-Yong; Corlett, Richard T.; Didham, Raphael K.; Ding, Ping; Holt, Robert D.; Holyoak, Marcel; Hu, Guang; Hughes, Alice C.; Jiang, Lin; Laurance, William F.; Liu, Jiajia; Pimm, Stuart L.; Robinson, Scott K.; Russo, Sabrina E. (2016-02-01).
451:(Single Large or Several Small). Habitat loss in a biodiversity hotspot can result in a localized extinction crisis, generally speaking habitat loss in a hotspot location can be a good indicator or predictor of the number of threatened and extinct endemic species.
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have also brought on varying implications into ecosystems which in turn affect animal behaviour and responses generated. Although there are some species which are able to survive these kinds of harsh conditions, such as, cutting down wood in the forests for
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more efficiently travel over landscapes and between patches of land. Since their predators can more easily access the caribous' refuge, the females of the species attempt to avoid the area, affecting their reproductive behaviours and offspring produced.
31:
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compared to interior forest due to variations in light availability, presence of wind, changes in precipitation, and overall moisture content of leaf litter. These microenvironments are often not conducive to overall forest health as they enable
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after fragmentation occurred. Understanding the relationship between transient and long-term dynamics is a substantial challenge that ecologists must tackle, and fragmentation experiments will be central for relating observation to theory.
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released a university based newspaper statement stating that 70% of the world's remaining forest stands within one kilometre of a forest edge putting biodiversity at an immense risk based on research conducted by international scientists.
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Brooks, Thomas M.; Mittermeier, Russell A.; Mittermeier, Cristina G.; da
Fonseca, Gustavo A. B.; Rylands, Anthony B.; Konstant, William R.; Flick, Penny; Pilgrim, John; Oldfield, Sara; Magin, Georgina; Hilton-Taylor, Craig (August 2002).
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van den Berg LJL, Bullock JM, Clarke RT, Langsten RHW, Rose RJ. 2001. Territory selection by the
Dartford warbler (Sylvia undata) in Dorset, England: the role of vegetation type, habitat fragmentation, and population size. Biol. Conserv.
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Another mitigation measure is the enlargement of small remnants to increase the amount of interior habitat. This may be impractical since developed land is often more expensive and could require significant time and effort to restore.
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of a forest patch depends on a) the size of the patch, and b) its degree of isolation. Isolation depends on the distance to the nearest similar patch, and the contrast with the surrounding areas. For example, if a cleared area is
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in unfragmented forests verses fragmented forests. As for an example of an antagonistic relationship of nest predation, a study found that there is no increase in nest predation on fragmented forests - thus not supporting the
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will lessen the isolation of the forest fragments. However, when formerly forested lands are converted permanently to pastures, agricultural fields, or human-inhabited developed areas, the remaining forest fragments, and the
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Dixo, Marianna; Metzger, Jean Paul; Morgante, JoĂŁo S.; Zamudio, Kelly R. (August 2009). "Habitat fragmentation reduces genetic diversity and connectivity among toad populations in the
Brazilian Atlantic Coastal Forest".
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While habitat fragmentation is often associated with its effects on large plant and animal populations and biodiversity, due to the interconnectedness of ecosystems there are also significant effects that it has on the
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Wagner, David L.; Metzler, Kenneth J.; Leicht-Young, Stacey A.; Motzkin, Glenn (2014-09-01). "Vegetation composition along a New
England transmission line corridor and its implications for other trophic levels".
1039:(beyond simple provisioning), through government compensation schemes, and through effective regulation and legal frameworks. The only realistic method of conserving forests is to apply and practice sustainable
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levels, resulting in decreased nutrient retention. Furthermore, habitat fragmentation alters relationships between biodiversity and ecosystem functioning across multiple scales, affecting both the local loss of
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Haddad, Nick M.; Brudvig, Lars A.; Clobert, Jean; Davies, Kendi F.; Gonzalez, Andrew; Holt, Robert D.; Lovejoy, Thomas E.; Sexton, Joseph O.; Austin, Mike P.; Collins, Cathy D.; Cook, William M. (2015-03-01).
2015:
Fahrig, L. (2018) Forty years of biais in habitat fragmentation research, In: Effective
Conservation Science: Data Not Dogma (Edited by Kareiva, Marvier and Silliman), Oxford University Press, United Kingdom
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The pattern-oriented approach is based on land cover and its patterning in correlation with species occurrences. One model of study for landscape patterning is the patch-matrix-corridor model developed by
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Peacock, Mary M.; Smith, Andrew T. (24 November 1997). "The effect of habitat fragmentation on dispersal patterns, mating behavior, and genetic variation in a pika ( Ochotona princeps ) metapopulation".
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Banks, Sam C; Piggott, Maxine P; Stow, Adam J; Taylor, Andrea C (2007). "Sex and sociality in a disconnected world: a review of the impacts of habitat fragmentation on animal social interactions".
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Fischer, Joern & B. Lindenmayer, David. (2007). Landscape modification and habitat fragmentation: a synthesis. Global
Ecology and Biogeography. 16. 265-280. 10.1111/j.1466-8238.2007.00287.
3858:"Effects of forest fragmentation on pollination of Mesogyne insignis (Moraceae) in Amani Nature Reserve forests, Tanzania: Effects of forest fragmentation on pollination of Mesogyne insignis"
383:. Studies showed 25% of juveniles travel a distance over 200m compared to 4% of adults. Of these, 95% remain in their new locale, demonstrating that this journey is necessary for survival.
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The technical report from 2006 - the result of a collaboration between the Swiss
Federal Office for the Environment (FOEN) and the European Environment Agency (EEA). Accessed: Feb 22, 2016
4869:, an ongoing programme to map the past, current and future impacts of human activities on the natural environment, specifically highlighting larger wilderness areas and their fragmentation
828:. Overall, habitat fragmentation significantly disrupts ecosystem services by altering nutrient retention, biodiversity, and ecosystem functioning at various spatial and temporal scales.
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activities. Moreover, fragmentation can affect the relationship present between animals and plants, such as the relationships regarding seed-dispersal or pollinator-plant relationship.
1031:, and water quality regulation in soybean fields through separate distances by nearby forest fragments which all varied in isolation and size across an agricultural landscape in
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fragmented landscapes may be able to adapt to fragmentation. However, there are also many cases where fragmentation reduces adaptation capacity because of small population size.
470:
being possible vectors of habitat corridors. A recent study has found that green roofs are beneficial in connecting the habitats of arthropods, specifically bees and weevils.
878:, remnant woodlands act like islands of forest in a sea of pastures, fields, subdivisions, shopping malls, etc. These fragments will then begin to undergo the process of
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Komonen, Atte; Penttila, Reijo; Lindgren, Mariko; Hanski, Ilkka (July 2000). "Forest fragmentation truncates a food chain based on an old-growth forest bracket fungus".
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A few approaches and measures which can be taken in order to conserve forests are methods by which erosion can be minimized, waste is properly disposed, conserve native
344:. This underscores the severe and lasting ecological impacts of fragmentation, which could be highlighted in the sections discussing the consequences of fragmentation.
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between related individuals. Inbreeding does not always result in negative fitness consequences, but when inbreeding is associated with fitness reduction it is called
2829:"Low genetic diversity and strong population structure shaped by anthropogenic habitat fragmentation in a critically endangered primate, Trachypithecus leucocephalus"
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Legrand, Delphine; Cote, Julien; Fronhofer, Emanuel A.; Holt, Robert D.; Ronce, Ophélie; Schtickzelle, Nicolas; Travis, Justin M. J.; Clobert, Jean (January 2017).
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separate fragments tend to be very small islands isolated from each other by cropland, pasture, pavement, or even barren land. The latter is often the result of
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modifications caused by humans they are led onto artificial structures which emit artificial light which are induced by dry asphalt dry roads for an example.
390:. Microclimatic changes in light, temperature, and wind can alter the ecology around the fragment, and in the interior and exterior portions of the fragment.
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of Chile fragmentation appear to not affect overall plant diversity much, and tree diversity is indeed higher in fragments than in large continuous forests.
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803:, impacting nutrient retention, species richness, and local biophysical conditions. Fragmentation-mediated processes cause generalizable responses at the
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300 million years ago led to a great loss of amphibian diversity, but simultaneously the drier climate spurred on a burst of diversity among reptiles.
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Crooks, Kevin R.; Burdett, Christopher L.; Theobald, David M.; King, Sarah R. B.; Di Marco, Moreno; Rondinini, Carlo; Boitani, Luigi (2017-07-18).
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Magnago, Luiz Fernando Silva; Rocha, Mariana Ferreira; Meyer, Leila; Martins, Sebastião Venâncio; Meira-Neto, João Augusto Alves (September 2015).
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occurs when individuals of the same species exchange genetic information through reproduction. Populations can maintain genetic diversity through
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can increase. Species that relocate seasonally can do so more safely and effectively when it does not interfere with human development barriers.
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Siry, Jacek P.; Cubbage, Frederick W.; Ahmed, Miyan Rukunuddin (2005-05-01). "Sustainable forest management: global trends and opportunities".
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validity of this claim has been disputed. The ongoing debate of what size fragments are most relevant for conservation is often referred to as
2772:"Severe consequences of habitat fragmentation on genetic diversity of an endangered Australian freshwater fish: A call for assisted gene flow"
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has efficiently been able to put into place an approach to sustainable forest management, and they established this in the late 1980s. Their
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2674:"Consequences of plant population size and density for plant-pollinator interactions and plant performance: Plant-pollinator interactions"
3811:"Meta-Analysis of the Effects of Forest Fragmentation on Interspecific Interactions: Forest Fragmentation and Interspecific Interactions"
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impacts which can increase species survival in those environments. Overall, habitat fragmentation results in habitat disintegration and
65:
5502:
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Laiolo, Paola; Tella, José L (2005). "Habitat fragmentation affects culture transmission: patterns of song matching in Dupont's lark".
2956:"Habitat Fragmentation Differentially Affects Genetic Variation, Phenotypic Plasticity and Survival in Populations of a Gypsum Endemic"
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Kramer, Andrea T.; Ison, Jennifer L.; Ashley, Mary V.; Howe, Henry F. (August 2008). "The Paradox of Forest Fragmentation Genetics".
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Russell, K. N.; Ikerd, H.; Droege, S. (2005-07-01). "The potential conservation value of unmowed powerline strips for native bees".
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243:
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Rametsteiner, Ewald; Simula, Markku (2003-01-01). "Forest certification—an instrument to promote sustainable forest management?".
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4496:"Native and exotic plant species diversity in forest fragments and forestry plantations of a coastal landscape of central Chile"
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3286:"A Rapid, Strong, and Convergent Genetic Response to Urban Habitat Fragmentation in Four Divergent and Widespread Vertebrates"
2220:"Microclimatic conditions at forest edges have significant impacts on vegetation structure in large Atlantic forest fragments"
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sources for animals thus splitting these species apart. Thus, making these animals become much more susceptible to effects of
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to the next, especially for species living in smaller population sizes. Whereas, for species of larger populations have more
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fields (Mitchell et al. 2014). Mitchell et al. (2014), researched on six varying ecosystem factors such as crop production,
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and GRASP projects in 2002. Areas shown in black and red delineate areas of severe and moderate habitat loss, respectively.
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Young, Andrew; Boyle, Tim; Brown, Tony (1996). "The population genetic consequences of habitat fragmentation for plants".
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that alter the conditions of the outer areas of the fragment, greatly reducing the amount of true forest interior habitat.
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found in the previously continuous habitat. In these cases, processes that act upon underlying genetic diversity, such as
123:
fragmentation is a process by which large and contiguous habitats get divided into smaller, isolated patches of habitats.
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can also occur frequently and measures can also be taken to further prevent forest fires from occurring. For example, in
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Matlack, Glenn R. (1993). "Microenvironment variation within and among forest edge sites in the eastern United States".
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The pattern-oriented approach focuses on land cover defined by human means and activities. This model has stemmed from
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Wildlife passages – De-Fragmentation in the Netherlands – How to evaluate their effectiveness? Accessed: Jan 22, 2009
3889:"Tropical forest fragmentation and nest predation – an experimental study in an Eastern Arc montane forest, Tanzania"
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can provide with, thus businesses which will want more access to the cutting of forests to gain those resources. The
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2103:"Find the weakest link. A comparison between demographic, genetic and demo-genetic metapopulation extinction times"
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Nordén, Jenni; Penttilä, Reijo; Siitonen, Juha; Tomppo, Erkki; Ovaskainen, Otso (May 2013). Thrall, Peter (ed.).
1354:"Genetic effects of anthropogenic habitat fragmentation on remnant animal and plant populations: a meta-analysis"
708:
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is by reducing the amount of suitable habitat available for organisms. Habitat fragmentation often involves both
84:
6142:
4875:– Simulations of habitat fragmentation and population genetics online at Monash University's Virtual Laboratory.
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industries, there are animals which can survive this change but some that cannot. An example includes, varying
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4461:[Fragmentation and regeneration dynamics of the Maulino forest: present status and future prospects]
4163:"Urban Power Line Corridors as Novel Habitats for Grassland and Alien Plant Species in South-Western Finland"
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3629:"Specialist species of wood-inhabiting fungi struggle while generalists thrive in fragmented boreal forests"
3541:
2876:
Hedrick, Philip W.; Kalinowski, Steven T. (November 2000). "Inbreeding Depression in Conservation Biology".
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resources are lacking in their core habitat, and animals can find new mates in neighbouring regions so that
158:
In scientific literature, there is some debate whether the term "habitat fragmentation" applies in cases of
4447:, Banaszak J. (ed.) 2000. Ecology of Forest Islands. Bydgoszcz University Press, Bydgoszcz, Poland, 313 pp.
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the single forest. However, forest islands in rural landscapes greatly increase their biodiversity. In the
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the inability of individual forest fragments to support viable populations, especially of large vertebrates
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by some barrier are less likely to be repopulated than adjoining fragments. Even small species such as the
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Lampinen, Jussi; Ruokolainen, Kalle; Huhta, Ari-Pekka; Chapman, Maura (Gee) Geraldine (13 November 2015).
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Delaney, Kathleen Semple; Riley, Seth P. D.; Fisher, Robert N.; Fleischer, Robert C. (16 September 2010).
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4459:"Fragmentación y dinámica de regeneración del bosque Maulino: diagnóstico actual y perspectivas futuras"
1798:
Lienert, Judit (July 2004). "Habitat fragmentation effects on fitness of plant populations – a review".
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Some species that have experienced genetic consequences due to habitat fragmentation are listed below:
521:
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One solution to the problem of habitat fragmentation is to link the fragments by preserving or planting
376:
354:
205:
104:
3857:
4895:
Kinver, Mark. (2013, September 26). "Forest fragmentation triggers 'ecological Armageddon'", BBC News.
2954:
Matesanz, Silvia; Rubio Teso, MarĂa Luisa; GarcĂa-Fernández, Alfredo; Escudero, Adrián (26 May 2017).
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Quammen, David (1997), "The Song of the Dodo: Island Biogeography in an Age of Extinction" (Scribner)
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Defragmentation in Belgium (Flanders) – Connecting nature, connecting people. Accessed: Jan 22, 2009
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at both local and regional scales, influencing biodiversity through interactions with anthropogenic
61:. France is the most deforested country in Europe, with only 15% of the native vegetation remaining.
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Landscape Ecology in Forest Management and Conservation: Challenges and Solutions for Global Change
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2625:"Genetic diversity maintained among fragmented populations of a tree undergoing range contraction"
1121:
Two approaches are typically used to understand habitat fragmentation and its ecological impacts.
1035:. Sustainable forest management can be achieved in several ways including by managing forests for
549:
Habitat fragmentation decreases the size and increases plant populations' spatial isolation. With
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was deemed successful as it has saved over nearly half a billion acres of land around the world.
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5912:
3928:"Exploring the influences of different processes of habitat fragmentation on ecosystem services"
3436:"Nowhere to hide: Effects of linear features on predator-prey dynamics in a large mammal system"
2376:
Hanski, Ilkka (May 2015). Triantis, Kostas (ed.). "Habitat fragmentation and species richness".
1352:
Schlaepfer, Daniel R.; Braschler, Brigitte; Rusterholz, Hans-Peter; Baur, Bruno (October 2018).
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habitat in many third world countries has experienced fragmentation through the development of
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88:
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McIntyre, S.; Barrett, G. W. (1992). "Habitat Variegation, An Alternative to Fragmentation".
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192:, to be able to effectively adapt to their changing environments. Ultimately, this prevents
178:
174:
2623:
Borrell, James S.; Wang, Nian; Nichols, Richard A.; Buggs, Richard J. A. (15 August 2018).
932:
of species that do not have at least one fragment capable of supporting a viable population
188:
Additionally, the effects of habitat fragmentation damage the ability for species, such as
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The Fragmented Forest: Island Biogeography Theory and the Preservation of Biotic Diversity
2166:
2162:"High dispersal in a frog species suggests that it is vulnerable to habitat fragmentation"
2002:
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969:
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284:
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4042:"Habitat fragmentation and biodiversity conservation: key findings and future challenges"
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processes that slowly alter the layout of the physical environment (suspected of being
39:
4841:
4716:
3951:
3752:
2499:"Habitat connectivity shapes urban arthropod communities: the key role of green roofs"
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83:
describes the emergence of discontinuities (fragmentation) in an organism's preferred
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69:
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1412:"Rainforest collapse triggered Pennsylvanian tetrapod diversification in Euramerica"
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Habitat Fragmentation and Landscape Change: An Ecological and Conservation Synthesis
466:
Due to the continuous expansion of urban landscapes, current research is looking at
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6423:
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5863:
5828:
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1635:"Outcomes of longterm deciduous forest restoration in southwestern Ontario, Canada"
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Li, Dehuan; Yang, Yixuan; Xia, Fan; Sun, Wei; Li, Xiao; Xie, Yujing (2022-11-01).
4673:
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4147:
4111:
3686:"Fragmentation disrupts microbial effects on native plant community productivity"
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1016:
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139:
4313:"The diverse effects of habitat fragmentation on plant–pollinator interactions"
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region, researchers were able to find over a 20-year period, actively managed
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Discontinuities in an organism's environment causing population fragmentation.
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3156:
3132:"Genetic effects of chronic habitat fragmentation in a wind-pollinated tree"
2972:
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Mustajärvi, Kaisa; Siikamäki, Pirkko; Rytkönen, Saara; Lammi, Antti (2001).
2335:
1945:"Rethinking patch size and isolation effects: the habitat amount hypothesis"
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4362:
Lessons from Amazonia: The Ecology and Conservation of a Fragmented Forest
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Kiesewetter, Kasey N.; Otano, Leydiana; Afkhami, Michelle E. (June 2023).
3247:
1989:
Fahrig, L (2017). "Ecological Responses to Habitat Fragmentation Per Se".
165:
Furthermore, habitat fragmentation is considered as an invasive threat to
6838:
6565:
6388:
6317:
5848:
5355:
5267:
5214:
5169:
1452:
Fahrig, Lenore (2019). "Habitat fragmentation: A long and tangled tale".
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are able to identify appropriate ponds to lay their eggs with the aid of
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Simberloff, Daniel (1 January 1998). "Small and Declining Populations".
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Templeton, Alan R.; Shaw, Kerry; Routman, Eric; Davis, Scott K. (1990).
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and the local loss of function. Moreover, fragmentation can change the
335:
and the subdivision of previously continuous habitat. Plants and other
170:
120:
73:
3856:
Olotu, Moses I.; Ndangalasi, Henry J.; Nyundo, Bruno A. (March 2012).
3011:
Philosophical Transactions of the Royal Society B: Biological Sciences
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1969:
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1473:
1378:
1353:
766:, to a less degree. For example, the mutualistic relationship between
6823:
3092:
1438:
1059:
1032:
995:
991:
58:
3976:"Habitat fragmentation and its lasting impact on Earth's ecosystems"
3607:"polarized Light Pollution: a new kind of ecological photopollution"
3367:
3007:"Effects of fragmentation on plant adaptation to urban environments"
1917:
1900:
1836:"Habitat fragmentation and its lasting impact on Earth's ecosystems"
1697:
1555:"Habitat fragmentation and its lasting impact on Earth's ecosystems"
291:, 90% of the native vegetation has been cleared and over 99% of the
4467:
Historia, biodiversidad y ecologĂa de los bosques costeros de Chile
2497:
Braaker, S.; Ghazoul, J.; Obrist, M. K.; Moretti, M. (April 2014).
921:
that caused the fragmentation in the first place is compounded by:
545:
Genetic consequences of habitat fragmentation for plant populations
2593:
Frankham, Richard; Ballou, Jonathan D.; Briscoe, David A. (2009).
1055:
1011:
The presence of forest fragments influences the supply of various
947:
943:
758:
relationships while affecting antagonistic relationships, such as
695:
585:
353:
29:
4258:"Habitat fragmentation, climate change, and inbreeding in plants"
1410:
Sahney, S.; Benton, M. J.; Falcon-Lang, H. J. (1 December 2010).
131:
The term habitat fragmentation includes five discrete phenomena:
4311:
Xiao, Yian; Li, Xiaohong; Cao, Yusong; Dong, Ming (2016-07-01).
1074:
1047:
148:
Breaking up of one patch of habitat into several smaller patches
6467:
5650:
4903:
4748:"Landscape Modification and Habitat Fragmentation: A synthesis"
4601:
4599:
4597:
1901:"Quantifying Threats to Imperiled Species in the United States"
1729:"Landscape Modification and Habitat Fragmentation: A synthesis"
2476:"Wildlife Crossings: Animals survive with bridges and tunnels"
1081:, and setting aside forestland (provides habitat for critical
835:
754:
analysis has found that habitat fragmentation greatly affects
415:
299:
has been cleared, resulting in extreme habitat fragmentation.
3005:
Dubois, Jonathan; Cheptou, Pierre-Olivier (5 December 2016).
2422:"Habitat Loss and Extinction in the Hotspots of Biodiversity"
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Isolation of one habitat fragment from other areas of habitat
115:, which can alter the environment much faster and causes the
2827:
Wang, W; Qiao, Y; Li, S; Pan, W; Yao, M (15 February 2017).
1101:-certified forests experienced substantially lower rates of
516:
Reduced gene flow, and reproductive isolation can result in
524:. Inbreeding becomes of increasing concern as the level of
434:
Habitat fragmentation is often a cause of species becoming
244:
habitat fragmentation of tropical rainforests in Euramerica
4746:
Fischer, Joern; Lindenmayer, David B. (February 7, 2007).
2160:
Funk W.C.; Greene A.E.; Corn P.S.; Allendorf F.W. (2005).
1727:
Fischer, Joern; Lindenmayer, David B. (February 7, 2007).
729:
effects have been shown to result in significantly varied
254:
Habitat fragmentation is frequently caused by humans when
4866:
4557:
Campanhola, Clayton; Pandey, Shivaji, eds. (2019-01-01),
327:
One of the major ways that habitat fragmentation affects
3542:
10.1890/1540-9295(2007)5[68:eoacif]2.0.co;2
2597:(2nd ed.). Cambridge: Cambridge University Press.
913:
Forest fragmentation is one of the greatest threats to
169:, due to its implications of affecting large number of
917:
in forests, especially in the tropics. The problem of
151:
Decrease in the average size of each patch of habitat
4465:. In Smith, C.; Armesto, J.; Valdovinos, C. (eds.).
3056:"Eco-evolutionary dynamics in fragmented landscapes"
1991:
Annual Review of Ecology, Evolution, and Systematics
1770:
Annual Review of Ecology, Evolution, and Systematics
1510:
Annual Review of Ecology, Evolution, and Systematics
746:
Effect on mutualistic and antagonistic relationships
414:. Aquatic species’ habitats have been fragmented by
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5052:
4946:
3434:DeMars, Craig A; Boutin, Stan (September 4, 2017).
1682:"The Genetic Consequences of Habitat Fragmentation"
4388:
4359:
1003:required to discern many strong system responses.
874:, or developed areas. Following the principles of
2028:"Is habitat fragmentation good for biodiversity?"
1117:Approaches to understanding habitat fragmentation
6734:Other effective area-based conservation measures
4494:Becerra, Pablo I.; Simonetti, Javier A. (2020).
889:Forest fragmentation reduces food resources and
6729:Integrated Conservation and Development Project
3557:"Behavioral responses to changing environments"
3381:
3379:
3377:
3136:Proceedings of the National Academy of Sciences
2315:Proceedings of the National Academy of Sciences
2280:
2278:
4632:"Strategies for Sustainable Forest Management"
4469:(in Spanish). pp. 529–539. Archived from
4085:
4083:
2764:
2762:
2760:
2618:
2616:
2614:
1793:
1791:
799:Habitat fragmentation has profound effects on
358:Habitat fragmented by numerous roads near the
6479:
5662:
4915:
4534:"Forest fragmentation threatens biodiversity"
3622:
3620:
3523:
3521:
3519:
3473:
3471:
3429:
3427:
3425:
3423:
3279:
3277:
3275:
3273:
2074:
2072:
1984:
1982:
1980:
1938:
1936:
386:Additionally, habitat fragmentation leads to
8:
4559:"Chapter 23 - Sustainable Forest Management"
4420:, John Wiley & Sons, pp. a0021904,
3349:
3347:
3345:
3343:
3341:
3339:
1633:McLachlan, S.M; Bazely, D.R (October 2003).
1547:
1545:
1543:
1541:
1503:
1501:
1499:
3555:Wong, B. B. M.; Candolin, U. (2015-05-01).
1093:’s culturally and ecologically significant
849:It has been suggested that this section be
34:Predicted fragmentation and destruction of
6486:
6472:
6464:
5883:Latitudinal gradients in species diversity
5669:
5655:
5647:
4922:
4908:
4900:
4262:Annals of the New York Academy of Sciences
553:and increased methods of inter-population
537:Small populations are more susceptible to
135:Reduction in the total area of the habitat
99:. Causes of habitat fragmentation include
4771:
4517:
4196:
4186:
4015:
3652:
3582:
3572:
3507:
3451:
3411:
3319:
3309:
3165:
3155:
3130:Jump, A. S.; Penuelas, J. (12 May 2006).
3082:
3030:
2981:
2971:
2852:
2803:
2689:
2648:
2352:
2334:
2194:
2136:
2126:
1968:
1916:
1875:
1752:
1594:
1377:
258:are cleared for human activities such as
5781:Predator–prey (Lotka–Volterra) equations
5420:Tritrophic interactions in plant defense
4797:"Landscape Ecology and Landscape Change"
3530:Frontiers in Ecology and the Environment
2878:Annual Review of Ecology and Systematics
1782:10.1146/annurev.ecolsys.34.011802.132419
1522:10.1146/annurev.ecolsys.34.011802.132419
972:within them, are often highly isolated.
283:. In the wheat belt of central-western
64:
49:
5813:Random generalized Lotka–Volterra model
3887:Carlson, Allan; Hartman, Göran (2001).
1899:Wilcove, David S.; et al. (1998).
1686:Annals of the Missouri Botanical Garden
1322:
1308:Lindenmayer D.B & Fischer J (2013)
897:and making them less likely to perform
5621:Herbivore adaptations to plant defense
1628:
1626:
1046:There is a high industrial demand for
742:that depend on specific environments.
4251:
4249:
2595:Introduction to conservation genetics
2003:10.1146/annurev-ecolsys-110316-022612
7:
5636:Predator avoidance in schooling fish
738:species to thrive at the expense of
119:of many species. More specifically,
6086:Intermediate disturbance hypothesis
4699:. Maintaining Forest Biodiversity.
4697:Journal of Environmental Management
4395:. The University of Chicago Press.
2084:Species diversity in space and time
942:The effect of fragmentation on the
5839:Ecological effects of biodiversity
4571:10.1016/B978-0-12-812134-4.00023-6
782:and increased fruit production of
402:Much of the remaining terrestrial
233:through natural processes such as
25:
6606:Conservation biology of parasites
5175:Generalist and specialist species
4889:Landscape Fragmentation in Europe
4842:10.1046/j.1523-1739.1992.610146.x
3952:10.1016/j.landurbplan.2022.104544
3753:10.1034/j.1600-0706.2000.900112.x
2913:Trends in Ecology & Evolution
7309:
7308:
6722:Tropical rainforest conservation
6626:Vulnerability and susceptibility
5898:Occupancy–abundance relationship
4773:10.1111/j.1466-8238.2007.00287.x
4563:Sustainable Food and Agriculture
4282:10.1111/j.1749-6632.2010.05450.x
3874:10.1111/j.1365-2028.2011.01302.x
3500:10.1111/j.1365-2664.2005.01093.x
3413:10.1046/j.1365-2664.2001.00642.x
2890:10.1146/annurev.ecolsys.31.1.139
2735:10.1111/j.1523-1739.2008.00944.x
2691:10.1046/j.1365-2745.2001.00521.x
2446:10.1046/j.1523-1739.2002.00530.x
1754:10.1111/j.1466-8238.2007.00287.x
1610:
1209:
1195:
1181:
1167:
1058:, and other resources which the
840:
212:which both tie into destructing
7271:NatureServe conservation status
6556:Conservation-induced extinction
5918:Relative abundance distribution
5631:Plant defense against herbivory
5498:Competitive exclusion principle
5210:Mesopredator release hypothesis
4752:Global Ecology and Biogeography
4607:"What is Sustainable Forestry?"
4519:10.4067/S0717-92002020000200125
2562:Conservation Science and Action
1800:Journal for Nature Conservation
1733:Global Ecology and Biogeography
1454:Global Ecology and Biogeography
711:to guide them, however, due to
410:such as roads interfering with
18:Causes of habitat fragmentation
6662:Conservation management system
6546:Conservation-dependent species
6506:Index of conservation articles
5503:Consumer–resource interactions
4426:10.1002/9780470015902.a0021904
4225:, Springer, pp. 273–296,
1130:fragmentation across species.
901:- lowering genetic diversity.
242:period of 1955-1978and also,
111:), and human activity such as
1:
7360:Sustainable forest management
6888:Assisted natural regeneration
6692:Ecoregion conservation status
6349:Biological data visualization
6176:Environmental niche modelling
5903:Population viability analysis
4717:10.1016/S0301-4797(02)00191-3
4418:Encyclopedia of Life Sciences
4128:Forest Ecology and Management
3893:Biodiversity and Conservation
2224:Biodiversity and Conservation
1659:10.1016/s0006-3207(02)00248-3
1007:Sustainable forest management
317:Habitat and biodiversity loss
7276:Special Area of Conservation
6814:Landscape-scale conservation
6809:High conservation value area
6687:Community-based conservation
5834:Density-dependent inhibition
4674:10.1016/j.forpol.2003.09.003
4231:10.1007/978-3-642-12754-0_12
4188:10.1371/journal.pone.0142236
4148:10.1016/j.foreco.2014.04.026
4112:10.1016/j.biocon.2005.01.022
3932:Landscape and Urban Planning
3796:10.1016/0006-3207(93)90004-K
3386:Shneider, Michael F (2001).
3311:10.1371/journal.pone.0012767
3212:10.1016/j.biocon.2008.11.016
2933:10.1016/0169-5347(96)10045-8
2478:. Wilder Eutopia. 2013-05-19
2290:National Wildlife Federation
2055:10.1016/j.biocon.2018.07.022
853:out into another article. (
795:Effect on ecosystem services
778:. A study has found greater
579:Examples of impacted species
557:due to increased effects of
444:conservation reliant species
7294:List of conservation issues
6702:Evidence-based conservation
6596:Mutualisms and conservation
6303:Liebig's law of the minimum
6138:Resource selection function
5029:Metabolic theory of ecology
4654:Forest Policy and Economics
4565:, Academic Press: 233–236,
4510:Austral University of Chile
3356:Canadian Journal of Zoology
660:Effect on animal behaviours
360:Indiana Dunes National Park
7376:
7355:Environmental conservation
6744:Roadless area conservation
6536:Compassionate conservation
6203:Niche apportionment models
5923:Relative species abundance
5127:Primary nutritional groups
5024:List of feeding behaviours
3862:African Journal of Ecology
3480:Journal of Applied Ecology
3392:Journal of Applied Ecology
2960:Frontiers in Plant Science
2088:Cambridge University Press
320:
138:Decrease of the interior:
7289:
6501:
6452:
6384:Ecosystem based fisheries
5996:Interspecific competition
5888:Minimum viable population
5746:Maximum sustainable yield
5731:Intraspecific competition
5726:Effective population size
5606:Anti-predator adaptations
5117:Photosynthetic efficiency
4873:Monash Virtual Laboratory
4387:Harris, Larry D. (1984).
4366:. Yale University Press.
4337:10.1007/s11258-016-0608-7
4066:10.1007/s10980-015-0312-3
3440:Journal of Animal Ecology
2776:Evolutionary Applications
2641:10.1038/s41437-018-0132-8
2570:10.1002/9781444313499.ch6
2244:10.1007/s10531-015-0961-1
1820:10.1016/j.jnc.2003.07.002
1134:Pattern-oriented approach
1125:Species-oriented approach
1110:, such as e.g. verifying
566:local genetic structure.
7131:Central African Republic
6779:Conservation designation
6697:Environmental protection
6682:Conspicuous conservation
6672:Conservation photography
6647:Conservation development
6642:Conservation agriculture
6374:Ecological stoichiometry
6339:Alternative stable state
3111:fishesofaustralia.net.au
3107:"Macquaria australasica"
2128:10.1186/1471-2148-11-260
2107:BMC Evolutionary Biology
2026:Haddad, Nick M. (2018).
719:Effect on microorganisms
687:Communication behaviours
678:Boreal woodland caribous
502:Gene Flow and Inbreeding
303:Endogenous vs. exogenous
93:population fragmentation
7345:Ecological connectivity
6870:Human–wildlife conflict
6754:Site-based conservation
6677:Conservation psychology
6495:Conservation of species
6218:Ontogenetic niche shift
6081:Ideal free distribution
5991:Ecological facilitation
5741:Malthusian growth model
5711:Consumer-resource model
5568:Paradox of the plankton
5533:Energy systems language
5253:Chemoorganoheterotrophy
5220:Optimal foraging theory
5195:Heterotrophic nutrition
4092:Biological Conservation
3905:10.1023/A:1016649731062
3776:Biological Conservation
3710:10.1111/1365-2745.14097
3654:10.1111/1365-2745.12085
3453:10.1111/1365-2656.12760
3192:Biological Conservation
3157:10.1073/pnas.0510127103
2973:10.3389/fpls.2017.00843
2378:Journal of Biogeography
2336:10.1073/pnas.1705769114
2035:Biological Conservation
1639:Biological Conservation
646:Sceloporus occidentalis
639:Plestiodon skiltonianus
196:from one generation of
105:one of the major causes
6927:Species reintroduction
6586:Latent extinction risk
6364:Ecological forecasting
6308:Marginal value theorem
6106:Landscape epidemiology
6041:Cross-boundary subsidy
5976:Biological interaction
5326:Microbial intelligence
5014:Green world hypothesis
4000:10.1126/sciadv.1500052
3023:10.1098/rstb.2016.0038
2187:10.1098/rsbl.2004.0270
2080:Rosenzweig, Michael L.
1860:10.1126/sciadv.1500052
1579:10.1126/sciadv.1500052
1276:Reproductive isolation
1261:Landscape connectivity
1043:to risk further loss.
597:Macquaria australasica
591:
363:
77:
62:
47:
7299:List of organisations
6953:Hawaiian honeycreeper
6893:Ecosystem restoration
6865:Habitat fragmentation
6860:Fortress conservation
6819:Marine protected area
6789:Conservation easement
6784:Conservation district
6749:Roadside conservation
6667:Conservation movement
6611:Species translocation
6551:Conservation genetics
6541:Conservation behavior
6369:Ecological humanities
6268:Ecological energetics
6213:Niche differentiation
6076:Habitat fragmentation
5844:Ecological extinction
5791:Small population size
5543:Feed conversion ratio
5523:Ecological succession
5455:San Francisco Estuary
5369:Ecological efficiency
5311:Microbial cooperation
3584:10.1093/beheco/aru183
3574:10.1093/beheco/aru183
3248:10.1007/s004420050341
1203:Earth sciences portal
589:
522:inbreeding depression
430:Informed conservation
377:Columbia spotted frog
357:
206:genetic recombination
81:Habitat fragmentation
68:
53:
33:
7350:Conservation biology
7261:Planetary boundaries
7251:Conservation officer
6855:Conservation refugee
6804:Habitat conservation
6794:Conservation reserve
6759:Wetland conservation
6657:Conservation grazing
6652:Conservation finance
6616:Conservation welfare
6581:In-situ conservation
6576:Extinction threshold
6571:Ex-situ conservation
6394:Evolutionary ecology
6359:Ecological footprint
6354:Ecological economics
6278:Ecological threshold
6273:Ecological indicator
6143:Source–sink dynamics
6096:Land change modeling
6091:Insular biogeography
5943:Species distribution
5682:Modelling ecosystems
5341:Microbial metabolism
5180:Intraguild predation
4969:Biogeochemical cycle
4935:Modelling ecosystems
4822:Conservation Biology
3815:Conservation Biology
2715:Conservation Biology
2564:. pp. 116–134.
2426:Conservation Biology
1246:Habitat conservation
1077:species to maintain
1025:pesticide regulation
961:structural diversity
832:Forest fragmentation
669:Predation behaviours
559:random genetic drift
270:and the creation of
204:which can arise and
175:biological invasions
6601:Nature conservation
6591:Marine conservation
6561:Conservation status
6444:Theoretical ecology
6419:Natural environment
6283:Ecosystem diversity
6253:Ecological collapse
6243:Bateman's principle
6198:Limiting similarity
6111:Landscape limnology
5933:Species homogeneity
5771:Population modeling
5766:Population dynamics
5583:Trophic state index
4834:1992ConBi...6..146M
4764:2007GloEB..16..265F
4709:2003JEnvM..67...87R
4666:2005ForPE...7..551S
4611:Rainforest Alliance
4329:2016PlEco.217..857X
4274:2010NYASA1195...84L
4179:2015PLoSO..1042236L
4140:2014ForEM.327..231W
4104:2005BCons.124..133R
4058:2016LaEco..31..219W
3992:2015SciA....1E0052H
3944:2022LUrbP.22704544L
3788:1993BCons..66..185M
3745:2000Oikos..90..119K
3702:2023JEcol.111.1292K
3645:2013JEcol.101..701N
3492:2005JApEc..42.1183L
3404:2001JApEc..38..720S
3302:2010PLoSO...512767D
3240:1997Oecol.112..524P
3204:2009BCons.142.1560D
3148:2006PNAS..103.8096J
3075:2017Ecogr..40....9L
2925:1996TEcoE..11..413Y
2788:2017EvApp..10..531P
2727:2008ConBi..22..878K
2515:2014Ecol...95.1010B
2438:2002ConBi..16..909B
2390:2015JBiog..42..989H
2327:2017PNAS..114.7635C
2236:2015BiCon..24.2305M
2179:2005BiLet...1...13F
2119:2011BMCEE..11..260R
2047:2018BCons.226....9F
1961:2013JBiog..40.1649F
1852:2015SciA....1E0052H
1812:2004JNatC..12...53L
1745:2007GloEB..16..265F
1651:2003BCons.113..159M
1571:2015SciA....1E0052H
1466:2019GloEB..28...33F
1431:2010Geo....38.1079S
1370:2018Ecosp...9E2488S
1281:Restoration ecology
1256:Habitat destruction
1145:island biogeography
1064:rainforest alliance
919:habitat destruction
876:island biogeography
483:island biogeography
379:are reliant on the
333:habitat destruction
231:habitat destruction
6898:Island restoration
6829:Open space reserve
6621:Threatened species
6455:Outline of ecology
6404:Industrial ecology
6399:Functional ecology
6263:Ecological deficit
6208:Niche construction
6171:Ecosystem engineer
5948:Species–area curve
5869:Introduced species
5684:: Other components
5616:Deimatic behaviour
5518:Ecological network
5450:North Pacific Gyre
5435:hydrothermal vents
5374:Ecological pyramid
5321:Microbial food web
5132:Primary production
5077:Foundation species
3827:10.1111/cobi.12304
3690:Journal of Ecology
3633:Journal of Ecology
3561:Behavioral Ecology
3084:10.1111/ecog.02537
3017:(1712): 20160038.
2845:10.1038/hdy.2017.2
2678:Journal of Ecology
2101:Robert, A (2011).
1943:Fahrig, L (2013).
1175:Environment portal
1037:ecosystem services
1027:, carbon storage,
801:ecosystem services
592:
555:genetic divergence
364:
293:tall grass prairie
78:
63:
48:
7322:
7321:
7281:Soil conservation
6834:Wildlife corridor
6717:Forest protection
6712:Forest management
6461:
6460:
6344:Balance of nature
6101:Landscape ecology
5986:Community ecology
5928:Species diversity
5864:Indicator species
5859:Gradient analysis
5736:Logistic function
5644:
5643:
5601:Animal coloration
5578:Trophic mutualism
5316:Microbial ecology
5107:Photoheterotrophs
5092:Myco-heterotrophy
5004:Ecosystem ecology
4989:Carrying capacity
4954:Abiotic component
4580:978-0-12-812134-4
4435:978-0-470-01617-6
4402:978-0-226-31763-2
4373:978-0-300-08483-2
4240:978-3-642-12754-0
4046:Landscape Ecology
3362:(10): 1065–1079.
3142:(21): 8096–8100.
2796:10.1111/eva.12484
2604:978-0-521-70271-3
2579:978-1-4443-1349-9
2523:10.1890/13-0705.1
2398:10.1111/jbi.12478
2321:(29): 7635–7640.
1970:10.1111/jbi.12130
1474:10.1111/geb.12839
1425:(12): 1079–1082.
1379:10.1002/ecs2.2488
1296:Wildlife crossing
1291:Wildlife corridor
1266:Landscape ecology
1231:Extinction vortex
1152:Variegation model
1085:). Additionally,
1079:genetic diversity
1041:forest management
984:McGill University
959:, the increasing
867:
866:
862:
769:Mesogyne insignis
731:microenvironments
625:Ochotona princeps
551:genetic variation
461:genetic diversity
397:biodiversity loss
323:biodiversity loss
264:rural development
202:genetic mutations
16:(Redirected from
7367:
7312:
7311:
7196:Papua New Guinea
7088:Cryopreservation
7053:Gray nurse shark
6707:Flagship species
6531:Captive breeding
6488:
6481:
6474:
6465:
6161:Ecological niche
6133:selection theory
5953:Umbrella species
5938:Species richness
5874:Invasive species
5854:Flagship species
5761:Population cycle
5756:Overexploitation
5721:Ecological yield
5671:
5664:
5657:
5648:
5553:Mesotrophic soil
5493:Climax community
5425:Marine food webs
5364:Biomagnification
5165:Chemoorganotroph
5019:Keystone species
4979:Biotic component
4924:
4917:
4910:
4901:
4854:
4853:
4817:
4811:
4810:
4808:
4806:
4801:
4793:
4787:
4784:
4778:
4777:
4775:
4743:
4737:
4736:
4692:
4686:
4685:
4649:
4643:
4642:
4636:
4628:
4622:
4621:
4619:
4618:
4603:
4592:
4591:
4554:
4548:
4547:
4545:
4544:
4530:
4524:
4523:
4521:
4491:
4485:
4484:
4482:
4481:
4475:
4464:
4454:
4448:
4445:
4439:
4438:
4413:
4407:
4406:
4394:
4384:
4378:
4377:
4365:
4355:
4349:
4348:
4308:
4302:
4301:
4253:
4244:
4243:
4217:
4211:
4210:
4200:
4190:
4173:(11): e0142236.
4158:
4152:
4151:
4122:
4116:
4115:
4087:
4078:
4077:
4036:
4030:
4029:
4019:
3980:Science Advances
3970:
3964:
3963:
3923:
3917:
3916:
3899:(7): 1077–1085.
3884:
3878:
3877:
3853:
3847:
3846:
3821:(5): 1342–1348.
3806:
3800:
3799:
3771:
3765:
3764:
3728:
3722:
3721:
3696:(6): 1292–1307.
3681:
3675:
3674:
3656:
3624:
3615:
3614:
3603:
3597:
3596:
3586:
3576:
3552:
3546:
3545:
3525:
3514:
3513:
3511:
3486:(6): 1183–1193.
3475:
3466:
3465:
3455:
3431:
3418:
3417:
3415:
3383:
3372:
3371:
3351:
3334:
3333:
3323:
3313:
3281:
3268:
3267:
3222:
3216:
3215:
3198:(8): 1560–1569.
3186:
3180:
3179:
3169:
3159:
3127:
3121:
3120:
3118:
3117:
3103:
3097:
3096:
3086:
3060:
3051:
3045:
3044:
3034:
3002:
2996:
2995:
2985:
2975:
2951:
2945:
2944:
2908:
2902:
2901:
2873:
2867:
2866:
2856:
2824:
2818:
2817:
2807:
2766:
2755:
2754:
2710:
2704:
2703:
2693:
2669:
2663:
2662:
2652:
2620:
2609:
2608:
2590:
2584:
2583:
2557:
2551:
2550:
2509:(4): 1010–1021.
2494:
2488:
2487:
2485:
2483:
2472:
2466:
2465:
2416:
2410:
2409:
2373:
2367:
2366:
2356:
2338:
2306:
2300:
2299:
2297:
2296:
2282:
2273:
2270:
2264:
2263:
2230:(9): 2305–2318.
2215:
2209:
2208:
2198:
2157:
2151:
2150:
2140:
2130:
2098:
2092:
2091:
2076:
2067:
2066:
2032:
2022:
2016:
2013:
2007:
2006:
1986:
1975:
1974:
1972:
1955:(9): 1649–1663.
1940:
1931:
1930:
1920:
1896:
1890:
1889:
1879:
1840:Science Advances
1830:
1824:
1823:
1795:
1786:
1785:
1765:
1759:
1758:
1756:
1724:
1718:
1717:
1677:
1671:
1670:
1630:
1621:
1614:
1608:
1598:
1559:Science Advances
1549:
1536:
1532:
1526:
1525:
1505:
1494:
1493:
1449:
1443:
1442:
1439:10.1130/G31182.1
1416:
1407:
1392:
1391:
1381:
1349:
1343:
1342:
1337:. Archived from
1331:"GLOBIO: Africa"
1327:
1251:Habitat corridor
1219:
1214:
1213:
1205:
1200:
1199:
1198:
1191:
1186:
1185:
1184:
1177:
1172:
1171:
1083:wildlife species
858:
844:
843:
836:
653:Chamaea fasciata
632:Uta stansburiana
478:the headings of
420:water diversions
281:tropical forests
179:overexploitation
21:
7375:
7374:
7370:
7369:
7368:
7366:
7365:
7364:
7325:
7324:
7323:
7318:
7285:
7239:
7094:
7012:Indian elephant
6931:
6874:
6843:
6839:30 by 30 target
6770:
6763:
6739:Riparian buffer
6630:
6517:
6510:
6497:
6492:
6462:
6457:
6448:
6434:Systems ecology
6322:
6293:Extinction debt
6258:Ecological debt
6248:Bioluminescence
6229:
6222:
6191:marine habitats
6166:Ecological trap
6147:
6027:
6020:
5963:
5957:
5913:Rapoport's rule
5908:Priority effect
5849:Endemic species
5817:
5776:Population size
5692:
5685:
5675:
5645:
5640:
5593:
5587:
5573:Trophic cascade
5483:Bioaccumulation
5466:
5393:
5350:
5272:
5239:
5136:
5048:
5009:Ecosystem model
4942:
4928:
4863:
4858:
4857:
4819:
4818:
4814:
4804:
4802:
4799:
4795:
4794:
4790:
4785:
4781:
4745:
4744:
4740:
4694:
4693:
4689:
4651:
4650:
4646:
4634:
4630:
4629:
4625:
4616:
4614:
4605:
4604:
4595:
4581:
4556:
4555:
4551:
4542:
4540:
4532:
4531:
4527:
4493:
4492:
4488:
4479:
4477:
4473:
4462:
4456:
4455:
4451:
4446:
4442:
4436:
4415:
4414:
4410:
4403:
4386:
4385:
4381:
4374:
4357:
4356:
4352:
4310:
4309:
4305:
4255:
4254:
4247:
4241:
4219:
4218:
4214:
4160:
4159:
4155:
4124:
4123:
4119:
4089:
4088:
4081:
4038:
4037:
4033:
3986:(2): e1500052.
3972:
3971:
3967:
3925:
3924:
3920:
3886:
3885:
3881:
3855:
3854:
3850:
3808:
3807:
3803:
3773:
3772:
3768:
3730:
3729:
3725:
3683:
3682:
3678:
3626:
3625:
3618:
3605:
3604:
3600:
3554:
3553:
3549:
3527:
3526:
3517:
3477:
3476:
3469:
3433:
3432:
3421:
3385:
3384:
3375:
3368:10.1139/Z07-094
3353:
3352:
3337:
3283:
3282:
3271:
3224:
3223:
3219:
3188:
3187:
3183:
3129:
3128:
3124:
3115:
3113:
3105:
3104:
3100:
3058:
3053:
3052:
3048:
3004:
3003:
2999:
2953:
2952:
2948:
2919:(10): 413–418.
2910:
2909:
2905:
2875:
2874:
2870:
2826:
2825:
2821:
2768:
2767:
2758:
2712:
2711:
2707:
2671:
2670:
2666:
2622:
2621:
2612:
2605:
2592:
2591:
2587:
2580:
2559:
2558:
2554:
2496:
2495:
2491:
2481:
2479:
2474:
2473:
2469:
2418:
2417:
2413:
2375:
2374:
2370:
2308:
2307:
2303:
2294:
2292:
2284:
2283:
2276:
2271:
2267:
2217:
2216:
2212:
2159:
2158:
2154:
2100:
2099:
2095:
2078:
2077:
2070:
2030:
2024:
2023:
2019:
2014:
2010:
1988:
1987:
1978:
1942:
1941:
1934:
1918:10.2307/1313420
1898:
1897:
1893:
1846:(2): e1500052.
1832:
1831:
1827:
1797:
1796:
1789:
1767:
1766:
1762:
1726:
1725:
1721:
1698:10.2307/2399621
1679:
1678:
1674:
1632:
1631:
1624:
1565:(2): e1500052.
1551:
1550:
1539:
1533:
1529:
1507:
1506:
1497:
1451:
1450:
1446:
1414:
1409:
1408:
1395:
1351:
1350:
1346:
1341:on 30 Oct 2005.
1329:
1328:
1324:
1319:
1305:
1300:
1241:Genetic erosion
1215:
1208:
1201:
1196:
1194:
1187:
1182:
1180:
1173:
1166:
1163:
1154:
1136:
1127:
1119:
1009:
911:
880:ecosystem decay
863:
860:(November 2022)
845:
841:
834:
797:
748:
721:
709:polarized light
705:aquatic insects
689:
680:
671:
662:
618:Rhinella ornata
604:Fagus sylvatica
590:Macquarie perch
581:
572:
547:
535:
504:
491:
480:metapopulations
432:
408:urban expansion
347:
342:nutrient cycles
325:
319:
314:
305:
285:New South Wales
252:
227:
222:
129:
113:land conversion
97:ecosystem decay
28:
23:
22:
15:
12:
11:
5:
7373:
7371:
7363:
7362:
7357:
7352:
7347:
7342:
7337:
7327:
7326:
7320:
7319:
7317:
7316:
7306:
7304:List of people
7301:
7296:
7290:
7287:
7286:
7284:
7283:
7278:
7273:
7268:
7263:
7258:
7253:
7247:
7245:
7241:
7240:
7238:
7237:
7236:
7235:
7225:
7224:
7223:
7216:United Kingdom
7213:
7208:
7203:
7198:
7193:
7188:
7183:
7178:
7173:
7168:
7163:
7158:
7153:
7148:
7143:
7138:
7133:
7128:
7123:
7118:
7113:
7108:
7102:
7100:
7096:
7095:
7093:
7092:
7091:
7090:
7085:
7077:
7076:
7075:
7070:
7065:
7063:Painted turtle
7060:
7055:
7050:
7040:
7039:
7038:
7033:
7032:
7031:
7021:
7016:
7015:
7014:
7004:
6999:
6998:
6997:
6987:
6982:
6980:American bison
6974:
6969:
6968:
6967:
6966:
6965:
6955:
6945:
6939:
6937:
6933:
6932:
6930:
6929:
6924:
6923:
6922:
6912:
6911:
6910:
6900:
6895:
6890:
6884:
6882:
6876:
6875:
6873:
6872:
6867:
6862:
6857:
6851:
6849:
6845:
6844:
6842:
6841:
6836:
6831:
6826:
6821:
6816:
6811:
6806:
6801:
6796:
6791:
6786:
6781:
6775:
6773:
6765:
6764:
6762:
6761:
6756:
6751:
6746:
6741:
6736:
6731:
6726:
6725:
6724:
6719:
6709:
6704:
6699:
6694:
6689:
6684:
6679:
6674:
6669:
6664:
6659:
6654:
6649:
6644:
6638:
6636:
6632:
6631:
6629:
6628:
6623:
6618:
6613:
6608:
6603:
6598:
6593:
6588:
6583:
6578:
6573:
6568:
6563:
6558:
6553:
6548:
6543:
6538:
6533:
6528:
6522:
6520:
6512:
6511:
6509:
6508:
6502:
6499:
6498:
6493:
6491:
6490:
6483:
6476:
6468:
6459:
6458:
6453:
6450:
6449:
6447:
6446:
6441:
6436:
6431:
6426:
6421:
6416:
6414:Microecosystem
6411:
6406:
6401:
6396:
6391:
6386:
6381:
6376:
6371:
6366:
6361:
6356:
6351:
6346:
6341:
6336:
6330:
6328:
6324:
6323:
6321:
6320:
6315:
6313:Thorson's rule
6310:
6305:
6300:
6295:
6290:
6285:
6280:
6275:
6270:
6265:
6260:
6255:
6250:
6245:
6240:
6238:Assembly rules
6234:
6232:
6224:
6223:
6221:
6220:
6215:
6210:
6205:
6200:
6195:
6194:
6193:
6183:
6178:
6173:
6168:
6163:
6157:
6155:
6149:
6148:
6146:
6145:
6140:
6135:
6123:
6121:Patch dynamics
6118:
6116:Metapopulation
6113:
6108:
6103:
6098:
6093:
6088:
6083:
6078:
6073:
6068:
6063:
6058:
6053:
6048:
6043:
6038:
6032:
6030:
6022:
6021:
6019:
6018:
6013:
6011:Storage effect
6008:
6003:
5998:
5993:
5988:
5983:
5978:
5973:
5967:
5965:
5959:
5958:
5956:
5955:
5950:
5945:
5940:
5935:
5930:
5925:
5920:
5915:
5910:
5905:
5900:
5895:
5893:Neutral theory
5890:
5885:
5880:
5878:Native species
5871:
5866:
5861:
5856:
5851:
5846:
5841:
5836:
5831:
5825:
5823:
5819:
5818:
5816:
5815:
5810:
5809:
5808:
5803:
5793:
5788:
5783:
5778:
5773:
5768:
5763:
5758:
5753:
5751:Overpopulation
5748:
5743:
5738:
5733:
5728:
5723:
5718:
5713:
5708:
5703:
5697:
5695:
5687:
5686:
5676:
5674:
5673:
5666:
5659:
5651:
5642:
5641:
5639:
5638:
5633:
5628:
5623:
5618:
5613:
5608:
5603:
5597:
5595:
5589:
5588:
5586:
5585:
5580:
5575:
5570:
5565:
5560:
5558:Nutrient cycle
5555:
5550:
5548:Feeding frenzy
5545:
5540:
5535:
5530:
5528:Energy quality
5525:
5520:
5515:
5510:
5505:
5500:
5495:
5490:
5488:Cascade effect
5485:
5480:
5474:
5472:
5468:
5467:
5465:
5464:
5463:
5462:
5457:
5452:
5447:
5442:
5437:
5432:
5422:
5417:
5412:
5407:
5401:
5399:
5395:
5394:
5392:
5391:
5386:
5381:
5376:
5371:
5366:
5360:
5358:
5352:
5351:
5349:
5348:
5343:
5338:
5333:
5331:Microbial loop
5328:
5323:
5318:
5313:
5308:
5303:
5298:
5296:Lithoautotroph
5293:
5288:
5282:
5280:
5278:Microorganisms
5274:
5273:
5271:
5270:
5265:
5260:
5255:
5249:
5247:
5241:
5240:
5238:
5237:
5235:Prey switching
5232:
5227:
5222:
5217:
5212:
5207:
5202:
5197:
5192:
5187:
5182:
5177:
5172:
5167:
5162:
5157:
5152:
5146:
5144:
5138:
5137:
5135:
5134:
5129:
5124:
5119:
5114:
5112:Photosynthesis
5109:
5104:
5099:
5094:
5089:
5084:
5079:
5074:
5069:
5067:Chemosynthesis
5064:
5058:
5056:
5050:
5049:
5047:
5046:
5041:
5036:
5031:
5026:
5021:
5016:
5011:
5006:
5001:
4996:
4991:
4986:
4981:
4976:
4971:
4966:
4961:
4959:Abiotic stress
4956:
4950:
4948:
4944:
4943:
4929:
4927:
4926:
4919:
4912:
4904:
4898:
4897:
4892:
4886:
4881:
4876:
4870:
4862:
4861:External links
4859:
4856:
4855:
4828:(1): 146–147.
4812:
4788:
4779:
4758:(3): 265–280.
4738:
4687:
4660:(4): 551–561.
4644:
4623:
4613:. 28 July 2016
4593:
4579:
4549:
4525:
4486:
4449:
4440:
4434:
4408:
4401:
4379:
4372:
4350:
4323:(7): 857–868.
4303:
4245:
4239:
4212:
4153:
4117:
4098:(1): 133–148.
4079:
4052:(2): 219–227.
4031:
3965:
3918:
3879:
3868:(1): 109–116.
3848:
3801:
3782:(3): 185–194.
3766:
3739:(1): 119–126.
3723:
3676:
3639:(3): 701–712.
3616:
3598:
3567:(3): 665–673.
3547:
3515:
3467:
3446:(1): 274–284.
3419:
3398:(4): 720–735.
3373:
3335:
3269:
3234:(4): 524–533.
3217:
3181:
3122:
3098:
3046:
2997:
2946:
2903:
2884:(1): 139–162.
2868:
2839:(6): 542–553.
2819:
2782:(6): 531–550.
2756:
2721:(4): 878–885.
2705:
2664:
2635:(4): 304–318.
2610:
2603:
2585:
2578:
2552:
2489:
2467:
2432:(4): 909–923.
2411:
2384:(5): 989–993.
2368:
2301:
2286:"Habitat Loss"
2274:
2265:
2210:
2152:
2093:
2068:
2017:
2008:
1976:
1932:
1911:(8): 607–615.
1891:
1825:
1787:
1776:(1): 487–515.
1760:
1739:(3): 265–280.
1719:
1672:
1645:(2): 159–169.
1622:
1537:
1527:
1495:
1444:
1393:
1344:
1321:
1320:
1318:
1315:
1314:
1313:
1312:(Island Press)
1304:
1301:
1299:
1298:
1293:
1288:
1283:
1278:
1273:
1271:Patch dynamics
1268:
1263:
1258:
1253:
1248:
1243:
1238:
1233:
1228:
1222:
1221:
1220:
1217:Biology portal
1206:
1192:
1189:Ecology portal
1178:
1162:
1159:
1153:
1150:
1141:Richard Forman
1135:
1132:
1126:
1123:
1118:
1115:
1108:sustainability
1033:Quebec, Canada
1029:soil fertility
1008:
1005:
978:Maulino forest
955:or allowed to
940:
939:
933:
926:
910:
907:
865:
864:
848:
846:
839:
833:
830:
826:climate change
796:
793:
747:
744:
720:
717:
701:pulp and paper
688:
685:
679:
676:
670:
667:
661:
658:
657:
656:
649:
642:
635:
628:
621:
614:
607:
600:
580:
577:
571:
568:
546:
543:
534:
531:
503:
500:
490:
487:
431:
428:
369:asynchronously
321:Main article:
318:
315:
313:
310:
304:
301:
277:slash and burn
251:
248:
239:climate change
226:
225:Natural causes
223:
221:
218:
153:
152:
149:
146:
143:
136:
128:
125:
40:Central Africa
26:
24:
14:
13:
10:
9:
6:
4:
3:
2:
7372:
7361:
7358:
7356:
7353:
7351:
7348:
7346:
7343:
7341:
7338:
7336:
7333:
7332:
7330:
7315:
7307:
7305:
7302:
7300:
7297:
7295:
7292:
7291:
7288:
7282:
7279:
7277:
7274:
7272:
7269:
7267:
7266:IUCN Red List
7264:
7262:
7259:
7257:
7256:De-extinction
7254:
7252:
7249:
7248:
7246:
7242:
7234:
7231:
7230:
7229:
7228:United States
7226:
7222:
7219:
7218:
7217:
7214:
7212:
7209:
7207:
7204:
7202:
7199:
7197:
7194:
7192:
7189:
7187:
7184:
7182:
7179:
7177:
7174:
7172:
7169:
7167:
7164:
7162:
7159:
7157:
7154:
7152:
7149:
7147:
7144:
7142:
7139:
7137:
7134:
7132:
7129:
7127:
7124:
7122:
7119:
7117:
7114:
7112:
7109:
7107:
7104:
7103:
7101:
7097:
7089:
7086:
7084:
7081:
7080:
7078:
7074:
7071:
7069:
7066:
7064:
7061:
7059:
7056:
7054:
7051:
7049:
7046:
7045:
7044:
7041:
7037:
7034:
7030:
7027:
7026:
7025:
7022:
7020:
7017:
7013:
7010:
7009:
7008:
7005:
7003:
7000:
6996:
6993:
6992:
6991:
6988:
6986:
6983:
6981:
6978:
6977:
6975:
6973:
6970:
6964:
6961:
6960:
6959:
6956:
6954:
6951:
6950:
6949:
6946:
6944:
6941:
6940:
6938:
6934:
6928:
6925:
6921:
6918:
6917:
6916:
6913:
6909:
6908:afforestation
6906:
6905:
6904:
6903:Reforestation
6901:
6899:
6896:
6894:
6891:
6889:
6886:
6885:
6883:
6881:
6877:
6871:
6868:
6866:
6863:
6861:
6858:
6856:
6853:
6852:
6850:
6846:
6840:
6837:
6835:
6832:
6830:
6827:
6825:
6822:
6820:
6817:
6815:
6812:
6810:
6807:
6805:
6802:
6800:
6797:
6795:
6792:
6790:
6787:
6785:
6782:
6780:
6777:
6776:
6774:
6772:
6766:
6760:
6757:
6755:
6752:
6750:
6747:
6745:
6742:
6740:
6737:
6735:
6732:
6730:
6727:
6723:
6720:
6718:
6715:
6714:
6713:
6710:
6708:
6705:
6703:
6700:
6698:
6695:
6693:
6690:
6688:
6685:
6683:
6680:
6678:
6675:
6673:
6670:
6668:
6665:
6663:
6660:
6658:
6655:
6653:
6650:
6648:
6645:
6643:
6640:
6639:
6637:
6633:
6627:
6624:
6622:
6619:
6617:
6614:
6612:
6609:
6607:
6604:
6602:
6599:
6597:
6594:
6592:
6589:
6587:
6584:
6582:
6579:
6577:
6574:
6572:
6569:
6567:
6564:
6562:
6559:
6557:
6554:
6552:
6549:
6547:
6544:
6542:
6539:
6537:
6534:
6532:
6529:
6527:
6524:
6523:
6521:
6519:
6513:
6507:
6504:
6503:
6500:
6496:
6489:
6484:
6482:
6477:
6475:
6470:
6469:
6466:
6456:
6451:
6445:
6442:
6440:
6439:Urban ecology
6437:
6435:
6432:
6430:
6427:
6425:
6422:
6420:
6417:
6415:
6412:
6410:
6407:
6405:
6402:
6400:
6397:
6395:
6392:
6390:
6387:
6385:
6382:
6380:
6377:
6375:
6372:
6370:
6367:
6365:
6362:
6360:
6357:
6355:
6352:
6350:
6347:
6345:
6342:
6340:
6337:
6335:
6332:
6331:
6329:
6325:
6319:
6316:
6314:
6311:
6309:
6306:
6304:
6301:
6299:
6298:Kleiber's law
6296:
6294:
6291:
6289:
6286:
6284:
6281:
6279:
6276:
6274:
6271:
6269:
6266:
6264:
6261:
6259:
6256:
6254:
6251:
6249:
6246:
6244:
6241:
6239:
6236:
6235:
6233:
6231:
6225:
6219:
6216:
6214:
6211:
6209:
6206:
6204:
6201:
6199:
6196:
6192:
6189:
6188:
6187:
6184:
6182:
6179:
6177:
6174:
6172:
6169:
6167:
6164:
6162:
6159:
6158:
6156:
6154:
6150:
6144:
6141:
6139:
6136:
6134:
6132:
6128:
6124:
6122:
6119:
6117:
6114:
6112:
6109:
6107:
6104:
6102:
6099:
6097:
6094:
6092:
6089:
6087:
6084:
6082:
6079:
6077:
6074:
6072:
6071:Foster's rule
6069:
6067:
6064:
6062:
6059:
6057:
6054:
6052:
6049:
6047:
6044:
6042:
6039:
6037:
6034:
6033:
6031:
6029:
6023:
6017:
6014:
6012:
6009:
6007:
6004:
6002:
5999:
5997:
5994:
5992:
5989:
5987:
5984:
5982:
5979:
5977:
5974:
5972:
5969:
5968:
5966:
5960:
5954:
5951:
5949:
5946:
5944:
5941:
5939:
5936:
5934:
5931:
5929:
5926:
5924:
5921:
5919:
5916:
5914:
5911:
5909:
5906:
5904:
5901:
5899:
5896:
5894:
5891:
5889:
5886:
5884:
5881:
5879:
5875:
5872:
5870:
5867:
5865:
5862:
5860:
5857:
5855:
5852:
5850:
5847:
5845:
5842:
5840:
5837:
5835:
5832:
5830:
5827:
5826:
5824:
5820:
5814:
5811:
5807:
5804:
5802:
5799:
5798:
5797:
5794:
5792:
5789:
5787:
5784:
5782:
5779:
5777:
5774:
5772:
5769:
5767:
5764:
5762:
5759:
5757:
5754:
5752:
5749:
5747:
5744:
5742:
5739:
5737:
5734:
5732:
5729:
5727:
5724:
5722:
5719:
5717:
5714:
5712:
5709:
5707:
5704:
5702:
5699:
5698:
5696:
5694:
5688:
5683:
5679:
5672:
5667:
5665:
5660:
5658:
5653:
5652:
5649:
5637:
5634:
5632:
5629:
5627:
5624:
5622:
5619:
5617:
5614:
5612:
5609:
5607:
5604:
5602:
5599:
5598:
5596:
5590:
5584:
5581:
5579:
5576:
5574:
5571:
5569:
5566:
5564:
5561:
5559:
5556:
5554:
5551:
5549:
5546:
5544:
5541:
5539:
5536:
5534:
5531:
5529:
5526:
5524:
5521:
5519:
5516:
5514:
5511:
5509:
5506:
5504:
5501:
5499:
5496:
5494:
5491:
5489:
5486:
5484:
5481:
5479:
5476:
5475:
5473:
5469:
5461:
5458:
5456:
5453:
5451:
5448:
5446:
5443:
5441:
5438:
5436:
5433:
5431:
5428:
5427:
5426:
5423:
5421:
5418:
5416:
5413:
5411:
5408:
5406:
5403:
5402:
5400:
5396:
5390:
5389:Trophic level
5387:
5385:
5382:
5380:
5377:
5375:
5372:
5370:
5367:
5365:
5362:
5361:
5359:
5357:
5353:
5347:
5346:Phage ecology
5344:
5342:
5339:
5337:
5336:Microbial mat
5334:
5332:
5329:
5327:
5324:
5322:
5319:
5317:
5314:
5312:
5309:
5307:
5304:
5302:
5299:
5297:
5294:
5292:
5291:Bacteriophage
5289:
5287:
5284:
5283:
5281:
5279:
5275:
5269:
5266:
5264:
5261:
5259:
5258:Decomposition
5256:
5254:
5251:
5250:
5248:
5246:
5242:
5236:
5233:
5231:
5228:
5226:
5223:
5221:
5218:
5216:
5213:
5211:
5208:
5206:
5205:Mesopredators
5203:
5201:
5198:
5196:
5193:
5191:
5188:
5186:
5183:
5181:
5178:
5176:
5173:
5171:
5168:
5166:
5163:
5161:
5158:
5156:
5153:
5151:
5150:Apex predator
5148:
5147:
5145:
5143:
5139:
5133:
5130:
5128:
5125:
5123:
5120:
5118:
5115:
5113:
5110:
5108:
5105:
5103:
5100:
5098:
5095:
5093:
5090:
5088:
5085:
5083:
5080:
5078:
5075:
5073:
5070:
5068:
5065:
5063:
5060:
5059:
5057:
5055:
5051:
5045:
5042:
5040:
5037:
5035:
5032:
5030:
5027:
5025:
5022:
5020:
5017:
5015:
5012:
5010:
5007:
5005:
5002:
5000:
4997:
4995:
4992:
4990:
4987:
4985:
4984:Biotic stress
4982:
4980:
4977:
4975:
4972:
4970:
4967:
4965:
4962:
4960:
4957:
4955:
4952:
4951:
4949:
4945:
4940:
4936:
4932:
4925:
4920:
4918:
4913:
4911:
4906:
4905:
4902:
4896:
4893:
4890:
4887:
4885:
4882:
4880:
4877:
4874:
4871:
4868:
4865:
4864:
4860:
4851:
4847:
4843:
4839:
4835:
4831:
4827:
4823:
4816:
4813:
4798:
4792:
4789:
4783:
4780:
4774:
4769:
4765:
4761:
4757:
4753:
4749:
4742:
4739:
4734:
4730:
4726:
4722:
4718:
4714:
4710:
4706:
4702:
4698:
4691:
4688:
4683:
4679:
4675:
4671:
4667:
4663:
4659:
4655:
4648:
4645:
4640:
4633:
4627:
4624:
4612:
4608:
4602:
4600:
4598:
4594:
4590:
4586:
4582:
4576:
4572:
4568:
4564:
4560:
4553:
4550:
4539:
4535:
4529:
4526:
4520:
4515:
4511:
4507:
4503:
4502:
4497:
4490:
4487:
4476:on 2022-06-22
4472:
4468:
4460:
4453:
4450:
4444:
4441:
4437:
4431:
4427:
4423:
4419:
4412:
4409:
4404:
4398:
4393:
4392:
4383:
4380:
4375:
4369:
4364:
4363:
4354:
4351:
4346:
4342:
4338:
4334:
4330:
4326:
4322:
4318:
4317:Plant Ecology
4314:
4307:
4304:
4299:
4295:
4291:
4287:
4283:
4279:
4275:
4271:
4267:
4263:
4259:
4252:
4250:
4246:
4242:
4236:
4232:
4228:
4224:
4216:
4213:
4208:
4204:
4199:
4194:
4189:
4184:
4180:
4176:
4172:
4168:
4164:
4157:
4154:
4149:
4145:
4141:
4137:
4133:
4129:
4121:
4118:
4113:
4109:
4105:
4101:
4097:
4093:
4086:
4084:
4080:
4075:
4071:
4067:
4063:
4059:
4055:
4051:
4047:
4043:
4035:
4032:
4027:
4023:
4018:
4013:
4009:
4005:
4001:
3997:
3993:
3989:
3985:
3981:
3977:
3969:
3966:
3961:
3957:
3953:
3949:
3945:
3941:
3937:
3933:
3929:
3922:
3919:
3914:
3910:
3906:
3902:
3898:
3894:
3890:
3883:
3880:
3875:
3871:
3867:
3863:
3859:
3852:
3849:
3844:
3840:
3836:
3832:
3828:
3824:
3820:
3816:
3812:
3805:
3802:
3797:
3793:
3789:
3785:
3781:
3777:
3770:
3767:
3762:
3758:
3754:
3750:
3746:
3742:
3738:
3734:
3727:
3724:
3719:
3715:
3711:
3707:
3703:
3699:
3695:
3691:
3687:
3680:
3677:
3672:
3668:
3664:
3660:
3655:
3650:
3646:
3642:
3638:
3634:
3630:
3623:
3621:
3617:
3612:
3611:Research Gate
3608:
3602:
3599:
3594:
3590:
3585:
3580:
3575:
3570:
3566:
3562:
3558:
3551:
3548:
3543:
3539:
3535:
3531:
3524:
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3516:
3510:
3505:
3501:
3497:
3493:
3489:
3485:
3481:
3474:
3472:
3468:
3463:
3459:
3454:
3449:
3445:
3441:
3437:
3430:
3428:
3426:
3424:
3420:
3414:
3409:
3405:
3401:
3397:
3393:
3389:
3382:
3380:
3378:
3374:
3369:
3365:
3361:
3357:
3350:
3348:
3346:
3344:
3342:
3340:
3336:
3331:
3327:
3322:
3317:
3312:
3307:
3303:
3299:
3296:(9): e12767.
3295:
3291:
3287:
3280:
3278:
3276:
3274:
3270:
3265:
3261:
3257:
3253:
3249:
3245:
3241:
3237:
3233:
3229:
3221:
3218:
3213:
3209:
3205:
3201:
3197:
3193:
3185:
3182:
3177:
3173:
3168:
3163:
3158:
3153:
3149:
3145:
3141:
3137:
3133:
3126:
3123:
3112:
3108:
3102:
3099:
3094:
3090:
3085:
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3076:
3072:
3068:
3064:
3057:
3050:
3047:
3042:
3038:
3033:
3028:
3024:
3020:
3016:
3012:
3008:
3001:
2998:
2993:
2989:
2984:
2979:
2974:
2969:
2965:
2961:
2957:
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2947:
2942:
2938:
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2883:
2879:
2872:
2869:
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2524:
2520:
2516:
2512:
2508:
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2500:
2493:
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2477:
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2468:
2463:
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2423:
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2407:
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2399:
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2291:
2287:
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2261:
2257:
2253:
2249:
2245:
2241:
2237:
2233:
2229:
2225:
2221:
2214:
2211:
2206:
2202:
2197:
2192:
2188:
2184:
2180:
2176:
2172:
2169:
2168:
2163:
2156:
2153:
2148:
2144:
2139:
2134:
2129:
2124:
2120:
2116:
2112:
2108:
2104:
2097:
2094:
2089:
2086:. Cambridge:
2085:
2081:
2075:
2073:
2069:
2064:
2060:
2056:
2052:
2048:
2044:
2040:
2036:
2029:
2021:
2018:
2012:
2009:
2004:
2000:
1996:
1992:
1985:
1983:
1981:
1977:
1971:
1966:
1962:
1958:
1954:
1950:
1946:
1939:
1937:
1933:
1928:
1924:
1919:
1914:
1910:
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1158:
1151:
1149:
1146:
1142:
1133:
1131:
1124:
1122:
1116:
1114:
1113:
1112:carbon sinks.
1109:
1104:
1103:deforestation
1100:
1096:
1092:
1088:
1084:
1080:
1076:
1071:
1069:
1065:
1061:
1057:
1053:
1049:
1044:
1042:
1038:
1034:
1030:
1026:
1022:
1021:decomposition
1018:
1014:
1006:
1004:
1000:
997:
993:
989:
985:
981:
979:
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971:
966:
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934:
931:
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906:
902:
900:
899:interbreeding
896:
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831:
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539:genetic drift
533:Genetic drift
532:
530:
527:
523:
519:
514:
512:
508:
501:
499:
497:
489:Genetic risks
488:
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382:
381:rescue effect
378:
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334:
330:
324:
316:
311:
309:
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300:
298:
297:North America
294:
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286:
282:
278:
273:
272:hydroelectric
269:
265:
261:
257:
256:native plants
249:
247:
245:
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224:
219:
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215:
211:
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199:
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191:
190:native plants
186:
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82:
75:
71:
70:Deforestation
67:
60:
56:
55:Deforestation
52:
45:
41:
37:
32:
19:
7029:Bengal Tiger
6985:Arabian oryx
6976:Land mammal
6963:Golden eagle
6864:
6799:Gap analysis
6526:Biodiversity
6516:Conservation
6424:Regime shift
6409:Macroecology
6130:
6126:
6075:
6066:Edge effects
6036:Biogeography
5981:Commensalism
5829:Biodiversity
5706:Allee effect
5445:kelp forests
5398:Example webs
5263:Detritivores
5102:Organotrophs
5082:Kinetotrophs
5034:Productivity
4825:
4821:
4815:
4803:. Retrieved
4791:
4782:
4755:
4751:
4741:
4703:(1): 87–98.
4700:
4696:
4690:
4657:
4653:
4647:
4638:
4626:
4615:. Retrieved
4610:
4562:
4552:
4541:. Retrieved
4537:
4528:
4505:
4499:
4489:
4478:. Retrieved
4471:the original
4466:
4452:
4443:
4417:
4411:
4390:
4382:
4361:
4353:
4320:
4316:
4306:
4268:(1): 84–98.
4265:
4261:
4222:
4215:
4170:
4166:
4156:
4131:
4127:
4120:
4095:
4091:
4049:
4045:
4034:
3983:
3979:
3968:
3935:
3931:
3921:
3896:
3892:
3882:
3865:
3861:
3851:
3818:
3814:
3804:
3779:
3775:
3769:
3736:
3732:
3726:
3693:
3689:
3679:
3636:
3632:
3610:
3601:
3564:
3560:
3550:
3536:(2): 68–72.
3533:
3529:
3483:
3479:
3443:
3439:
3395:
3391:
3359:
3355:
3293:
3289:
3231:
3227:
3220:
3195:
3191:
3184:
3139:
3135:
3125:
3114:. Retrieved
3110:
3101:
3066:
3062:
3049:
3014:
3010:
3000:
2963:
2959:
2949:
2916:
2912:
2906:
2881:
2877:
2871:
2836:
2832:
2822:
2779:
2775:
2718:
2714:
2708:
2684:(1): 80–87.
2681:
2677:
2667:
2632:
2628:
2594:
2588:
2561:
2555:
2506:
2502:
2492:
2480:. Retrieved
2470:
2429:
2425:
2414:
2381:
2377:
2371:
2318:
2314:
2304:
2293:. Retrieved
2289:
2268:
2227:
2223:
2213:
2170:
2165:
2155:
2110:
2106:
2096:
2083:
2038:
2034:
2020:
2011:
1994:
1990:
1952:
1948:
1908:
1904:
1894:
1843:
1839:
1828:
1806:(1): 53–72.
1803:
1799:
1773:
1769:
1763:
1736:
1732:
1722:
1692:(1): 13–27.
1689:
1685:
1675:
1642:
1638:
1609:
1562:
1558:
1530:
1513:
1509:
1460:(1): 33–41.
1457:
1453:
1447:
1422:
1418:
1361:
1357:
1347:
1339:the original
1334:
1325:
1309:
1303:Bibliography
1226:Empty forest
1155:
1137:
1128:
1120:
1087:forest fires
1072:
1068:conservation
1045:
1017:agricultural
1015:in adjacent
1010:
1001:
982:
974:
941:
936:edge effects
915:biodiversity
912:
909:Implications
903:
888:
884:
868:
859:
822:microclimate
818:biodiversity
798:
791:hypothesis.
783:
773:
767:
749:
722:
694:
690:
681:
672:
663:
651:
644:
637:
630:
623:
616:
609:
602:
595:
582:
573:
561:, elevating
548:
536:
526:homozygosity
515:
505:
492:
476:
472:
465:
453:
433:
424:
412:habitat loss
401:
388:edge effects
385:
365:
349:
346:
329:biodiversity
326:
312:Implications
306:
268:urbanization
253:
250:Human causes
237:, fire, and
229:Evidence of
228:
216:as a whole.
214:biodiversity
210:habitat loss
187:
167:biodiversity
164:
160:habitat loss
157:
154:
130:
80:
79:
7201:South Sudan
7186:New Zealand
6880:Restoration
6061:Disturbance
5964:interaction
5786:Recruitment
5716:Depensation
5508:Copiotrophs
5379:Energy flow
5301:Lithotrophy
5245:Decomposers
5225:Planktivore
5200:Insectivore
5190:Heterotroph
5155:Bacterivore
5122:Phototrophs
5072:Chemotrophs
5044:Restoration
4994:Competition
4512:: 125–136.
4134:: 231–239.
3509:10261/57878
3069:(1): 9–25.
2482:19 December
2173:(1): 13–6.
2167:Biol. Lett.
1949:J. Biogeogr
1516:: 487–515.
789:edge effect
784:M. insignis
780:pollination
756:mutualistic
740:specialists
611:Betula nana
468:green roofs
279:farming in
260:agriculture
91:), causing
85:environment
42:, from the
38:habitat in
7329:Categories
7136:Costa Rica
7099:By country
7019:Slow loris
6995:Polar bear
6848:Key issues
6635:Approaches
6429:Sexecology
6006:Parasitism
5971:Antibiosis
5806:Resistance
5801:Resilience
5691:Population
5611:Camouflage
5563:Oligotroph
5478:Ascendency
5440:intertidal
5430:cold seeps
5384:Food chain
5185:Herbivores
5160:Carnivores
5087:Mixotrophs
5062:Autotrophs
4941:components
4617:2020-03-06
4543:2020-03-06
4480:2021-03-08
3938:: 104544.
3116:2018-06-06
2295:2020-03-06
2113:(1): 260.
1905:BioScience
1535:101:217-28
1317:References
1013:ecosystems
965:vegetation
957:regenerate
953:reforested
930:extinction
928:the local
805:population
736:generalist
726:microbiota
570:Adaptation
563:inbreeding
518:inbreeding
496:adaptation
440:endangered
436:threatened
373:immigrants
198:population
127:Definition
117:extinction
109:speciation
101:geological
7176:Mauritius
7156:Indonesia
7141:Hong Kong
7111:Australia
7083:Seed bank
7073:Sea otter
6943:Arthropod
6915:Rewilding
6769:Protected
6334:Allometry
6288:Emergence
6016:Symbiosis
6001:Mutualism
5796:Stability
5701:Abundance
5513:Dominance
5471:Processes
5460:tide pool
5356:Food webs
5230:Predation
5215:Omnivores
5142:Consumers
5097:Mycotroph
5054:Producers
4999:Ecosystem
4964:Behaviour
4805:March 22,
4725:0301-4797
4682:1389-9341
4589:128938268
4345:1573-5052
4290:0077-8923
4074:1572-9761
4008:2375-2548
3960:0169-2046
3761:0030-1299
3718:0022-0477
3663:0022-0477
3593:1045-2249
3228:Oecologia
3093:2164/9606
3063:Ecography
2898:0066-4162
2531:0012-9658
2454:0888-8892
2345:0027-8424
2252:0960-3115
1868:2375-2548
1706:0026-6493
1667:0006-3207
1617:CC BY 4.0
1587:2375-2548
1482:1466-8238
1388:2150-8925
1358:Ecosphere
1286:Road kill
1236:Gene pool
1091:Guatemala
895:predation
813:ecosystem
809:community
775:Megachile
764:herbivory
760:predation
713:ecosystem
511:migration
507:Gene flow
456:corridors
340:altering
289:Australia
235:volcanism
194:gene flow
183:pollution
36:Great Ape
7335:Habitats
7314:Category
7221:Scotland
7191:Pakistan
7171:Malaysia
7007:Elephant
6936:By taxon
6566:Endemism
6389:Endolith
6318:Xerosere
6230:networks
6046:Ecocline
5592:Defense,
5268:Detritus
5170:Foraging
5039:Resource
4733:12659807
4538:Newsroom
4298:20536818
4207:26565700
4167:PLOS ONE
4026:26601154
3913:20971928
3835:24725007
3671:85037421
3462:28940254
3330:20862274
3290:PLOS ONE
3256:28307630
3176:16698935
3041:27920383
2992:28603529
2941:21237900
2863:28198816
2833:Heredity
2814:28616062
2743:18544089
2700:84923092
2659:30111882
2629:Heredity
2547:41070926
2539:24933819
2462:44009934
2406:84220990
2363:28673992
2260:16927557
2205:17148116
2147:21929788
2082:(1995).
2063:52839843
2041:: 9–15.
1997:: 1–23.
1886:26601154
1619:license.
1605:26601154
1490:91260144
1161:See also
988:Montreal
872:farmland
752:metadata
404:wildlife
7340:Habitat
7244:Related
7233:forests
7181:Namibia
7161:Ireland
7146:Iceland
7058:Manatee
7048:Dolphin
7002:Cheetah
6518:biology
6379:Ecopath
6186:Habitat
6056:Ecotype
6051:Ecotone
6028:ecology
6026:Spatial
5962:Species
5822:Species
5693:ecology
5678:Ecology
5626:Mimicry
5594:counter
5538:f-ratio
5286:Archaea
4974:Biomass
4947:General
4939:Trophic
4931:Ecology
4850:2385863
4830:Bibcode
4760:Bibcode
4705:Bibcode
4662:Bibcode
4325:Bibcode
4270:Bibcode
4198:4643934
4175:Bibcode
4136:Bibcode
4100:Bibcode
4054:Bibcode
4017:4643828
3988:Bibcode
3940:Bibcode
3843:5526322
3784:Bibcode
3741:Bibcode
3698:Bibcode
3641:Bibcode
3488:Bibcode
3400:Bibcode
3321:2940822
3298:Bibcode
3264:2446276
3236:Bibcode
3200:Bibcode
3167:1472435
3144:Bibcode
3071:Bibcode
3032:5182434
2983:5445106
2966:: 843.
2921:Bibcode
2854:5436025
2805:5469170
2784:Bibcode
2751:1665248
2723:Bibcode
2650:6134035
2511:Bibcode
2503:Ecology
2434:Bibcode
2386:Bibcode
2354:5530695
2323:Bibcode
2232:Bibcode
2196:1629065
2175:Bibcode
2138:3185286
2115:Bibcode
2043:Bibcode
1957:Bibcode
1927:1313420
1877:4643828
1848:Bibcode
1808:Bibcode
1741:Bibcode
1714:2399621
1647:Bibcode
1596:4643828
1567:Bibcode
1462:Bibcode
1427:Bibcode
1419:Geology
1366:Bibcode
963:of the
891:habitat
870:areas,
855:Discuss
337:sessile
171:species
121:habitat
89:habitat
76:, 2016.
74:Bolivia
7211:Uganda
7206:Sweden
7126:Canada
7121:Brazil
7116:Belize
7106:Angola
7079:Plant
7068:Salmon
7043:Marine
6958:Raptor
6920:marine
6824:Marxan
5410:Rivers
5306:Marine
4867:GLOBIO
4848:
4731:
4723:
4680:
4639:fed.us
4587:
4577:
4501:Bosque
4432:
4399:
4370:
4343:
4296:
4288:
4237:
4205:
4195:
4072:
4024:
4014:
4006:
3958:
3911:
3841:
3833:
3759:
3716:
3669:
3661:
3591:
3460:
3328:
3318:
3262:
3254:
3174:
3164:
3039:
3029:
2990:
2980:
2939:
2896:
2861:
2851:
2812:
2802:
2749:
2741:
2698:
2657:
2647:
2601:
2576:
2545:
2537:
2529:
2460:
2452:
2404:
2361:
2351:
2343:
2258:
2250:
2203:
2193:
2145:
2135:
2061:
1925:
1884:
1874:
1866:
1712:
1704:
1665:
1603:
1593:
1585:
1488:
1480:
1386:
1364:(10).
1335:GLOBIO
1060:forest
996:Canada
992:Quebec
811:, and
696:Humans
220:Causes
59:Europe
44:GLOBIO
7166:Italy
7151:India
7024:Tiger
6972:Fungi
6771:areas
6327:Other
6228:Other
6181:Guild
6153:Niche
5405:Lakes
4846:JSTOR
4800:(PDF)
4635:(PDF)
4585:S2CID
4508:(2).
4474:(PDF)
4463:(PDF)
3909:S2CID
3839:S2CID
3733:Oikos
3667:S2CID
3260:S2CID
3059:(PDF)
2747:S2CID
2696:S2CID
2543:S2CID
2458:S2CID
2402:S2CID
2256:S2CID
2059:S2CID
2031:(PDF)
1923:JSTOR
1710:JSTOR
1486:S2CID
1415:(PDF)
1095:Petén
1056:paper
970:biota
948:fauna
944:flora
851:split
449:SLOSS
392:Fires
181:, or
173:than
142:ratio
95:and
7036:Wolf
6990:Bear
6948:Bird
5415:Soil
4807:2018
4729:PMID
4721:ISSN
4678:ISSN
4575:ISBN
4430:ISBN
4397:ISBN
4368:ISBN
4341:ISSN
4294:PMID
4286:ISSN
4266:1195
4235:ISBN
4203:PMID
4070:ISSN
4022:PMID
4004:ISSN
3956:ISSN
3831:PMID
3757:ISSN
3714:ISSN
3659:ISSN
3589:ISSN
3458:PMID
3326:PMID
3252:PMID
3172:PMID
3037:PMID
2988:PMID
2937:PMID
2894:ISSN
2859:PMID
2810:PMID
2739:PMID
2655:PMID
2599:ISBN
2574:ISBN
2535:PMID
2527:ISSN
2484:2017
2450:ISSN
2359:PMID
2341:ISSN
2248:ISSN
2201:PMID
2143:PMID
1882:PMID
1864:ISSN
1702:ISSN
1663:ISSN
1601:PMID
1583:ISSN
1478:ISSN
1384:ISSN
1075:tree
1052:pulp
1048:wood
946:and
772:and
762:and
418:and
416:dams
140:edge
4838:doi
4768:doi
4713:doi
4670:doi
4567:doi
4514:doi
4422:doi
4333:doi
4321:217
4278:doi
4227:doi
4193:PMC
4183:doi
4144:doi
4132:327
4108:doi
4096:124
4062:doi
4012:PMC
3996:doi
3948:doi
3936:227
3901:doi
3870:doi
3823:doi
3792:doi
3749:doi
3706:doi
3694:111
3649:doi
3637:101
3579:hdl
3569:doi
3538:doi
3504:hdl
3496:doi
3448:doi
3408:doi
3364:doi
3316:PMC
3306:doi
3244:doi
3232:112
3208:doi
3196:142
3162:PMC
3152:doi
3140:103
3089:hdl
3079:doi
3027:PMC
3019:doi
3015:372
2978:PMC
2968:doi
2929:doi
2886:doi
2849:PMC
2841:doi
2837:118
2800:PMC
2792:doi
2731:doi
2686:doi
2645:PMC
2637:doi
2633:121
2566:doi
2519:doi
2442:doi
2394:doi
2349:PMC
2331:doi
2319:114
2240:doi
2191:PMC
2183:doi
2133:PMC
2123:doi
2051:doi
2039:226
1999:doi
1965:doi
1913:doi
1872:PMC
1856:doi
1816:doi
1778:doi
1749:doi
1694:doi
1655:doi
1643:113
1591:PMC
1575:doi
1518:doi
1470:doi
1435:doi
1374:doi
1099:FSC
986:in
438:or
295:of
107:of
72:in
57:in
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