Earth:Assisted colonization

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Short description: Intentional transport of species to a different habitat

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The Western Larch (Larix occidentalis) was selected by the government of British Columbia for an assisted colonization program that saw the tree being seeded 1000 km north of its historical range.

Assisted colonization (sometimes referred to as assisted migration or managed relocation) is the act of moving plants or animals to a different habitat. The destination habitat may or may not have once previously held the species; the only requirement is the destination habitat must provide the bioclimatic requirements to support the species. The goal of assisted colonization is to remove the species from a threatening environment and give them a chance to survive and reproduce in an environment that does not pose an existential threat to the species.[1]

In recent years, assisted colonization has been presented as a potential solution to the climate change crisis that has changed environments faster than natural selection can adapt to.[2][3] While assisted colonization has the potential to allow species that have poor natural dispersal abilities to avoid extinction, it has also sparked intense debate over the possibility of the introduction of invasive species and diseases into previously healthy ecosystems. Despite these debates, scientists and land managers have already begun the process of assisted colonization for certain species.[4]

Background

Climate change is expected to drive many species out of parts of their current ranges while creating new suitable habitats elsewhere.[5] In order to avoid climate change-caused population declines and extinction, many species will need to either adapt or colonize newly suitable areas. Using a niche modeling approach, scientists have predicted that a failure to migrate or adapt will result in about a quarter of the world's species dying out this century under moderate climate change.[5] The natural dispersal rates for many species are far slower than those needed to keep pace with projected habitat shifts in many regions of the world.[3][6][7][8][9] Prehistoric climatic changes have resulted in massive global extinctions, and the rate of warming projected for the near future is many times faster than changes in the past 10,000 years,[10] Prehistoric climate change events resulted in massive global extinctions, and the rate of global warming that is projected for the near future is significantly higher than the rate of global warming that occurred in the past 10,000 years. The inability of species to migrate in response to human-caused climate change has led to some scientists and land managers to consider exploring assisted colonization as a means for preventing extinction of species.[1]

Assisted colonization v. species introduction

Assisted colonization is a specific type of species introduction. Species introduction is any act of establishing a species in a habitat it does not currently occupy. It often refers to a long-distance relocation, such as the accidental introduction of an invasive species from one continent to another, or the intentional relocation of a species in decline to a habitat where it can persist. By contrast, assisted colonization acknowledges that the natural dispersal rate of many species may be too low to naturally respond to rapid human-caused climate change and instead focuses on where the species would be able to disperse fast enough via natural selection to keep pace with the changing environment. Assisted colonization practitioners consider helping the species disperse into such sites, which are often immediately adjacent to the species’ historical range.[11] In their eyes, assisted colonization represents a small artificial boost to an otherwise natural process. [12]

Terminology

Assisted colonization was initially referred to as "assisted migration" when it was first proposed.[1] The terminology was later criticized for being reminiscent of natural, cyclic animal migrations in response to changing seasons.[11] The term "assisted migration" was met with criticism, as it incorrectly inferred human assistance with natural cyclic animal migrations in response to changing seasons. It was renamed "assisted colonization", as colonization more accurately describes the natural phenomenon humans were seeking. Others have sought to further distinguish assisted colonization from any natural connotation by referring to it as "managed relocation".[13][14] No specific name has been unanimously adopted. Within the scientific and conservation communities the terms "assisted migration", "managed relocation", and "assisted colonization" are often used interchangeably and are understood to refer to the same idea.

Alternatives

Even under rapid climate change, dispersal into new areas may not be necessary for some species to persist. Instead of tracking climate shifts through space, some species may be able to survive in their present locations by developing tolerance to new conditions through acclimatization and adaptation.[15][16] The potential for acclimatization or adaptation to allow persistence in the face of climate change varies by species and is generally poorly understood. One study determined that evolution of higher temperature tolerances in some species of amphibians and reptiles will likely occur fast enough to allow these species to survive a 3 °C temperature increase over 100 years, consistent with low- to mid-range projections of global warming.[16] By contrast, many species, such as most temperate trees, have longer generation times and therefore may adapt more slowly; they may take thousands of years to evolve a similar increase in temperature tolerance.[15][16] Adaptation this slow would be insufficient for keeping up with expected future global warming if colonization of new habitats is not an option. In addition to acclimatization and adaption, assisted evolution is an alternative to assisted colonization that has been growing in popularity recently due to the worldwide coral reef crisis. Assisted evolution is the practice of using human intervention to accelerate the rate of natural evolutionary processes.[17] There are three main types of assisted evolution.

Stress conditioning

Stress conditioning consists of exposing organisms to sublethal stress, with the goal of inducing physiological changes that increase tolerance to future stress events. There has been documented evidence that some changes can be passed throughout generations in both plants and animals. Stress conditioning can be artificially induced in a laboratory environment to create desired responses based on their environments. Notable examples include a 1989 experiment which used stress conditioning via heat shock on rat kidneys to extend their safe cold storage time to 48 hours.[18] More recently, stress conditioning is being studied as a potential solution for the preservation of coral reefs as they are continually exposed to ocean warming and acidification.

Assisted gene flow

Assisted gene flow (AGF) works to increase the presence of desired naturally-occurring genes in offspring. AGF relies on pre-existing genes within the species' genome, rather than the artificial creation and insertion of genetic code within the genome of the species. Assisted gene flow can also introduce related species' genomes into the gene pool to allow for the introduction of previously impossible behaviors into the new species. AGF identifies genes that produce desired behaviors or tolerance to environmental conditions, and works to increase the chance that parental transmission of the gene in question occurs (also known as heritability). Determining which genes within the genome produce desired behaviors or environmental tolerance consist of experiments which measure the growth, survival, and behavior exhibition of offspring with varying genotypes. AGF is one possible strategy to preserve species that are threatened by climate change,[19] and can be applied to both plants (e.g. forest restoration) or animal populations. Currently, different coral colonies of the Great Barrier Reef are being interbred to test whether offspring display increased resistance to warmer living conditions. Increased resistance to warmer living conditions allow for the preservation of the Great Barrier Reef even as water temperatures continue to rise.

Hybridization

Hybridization refers to the process where an egg and sperm from two different species can fertilize and produce young. Hybridization was studied in the 1800s by Johann Gregor Mendel, who posthumously has been credited with the discovery of genes and alleles and their impact on an offspring's genotype. Benefits of hybridization include the increase in genetic diversity and the potential for genetic combinations which are able to adapt to, and reproduce in, increasingly difficult environments. Hybridization of coral reefs during the annual coral spawning is being experimented with to create hybrid offspring that will hopefully have higher survival and growth rates in a variety of climate change related conditions.

Types

Generally speaking, there are three accepted ways that assisted colonization can take place, each one of them with specific benefits and situations in which it applies. They can be defined as reintroduction, introduction and augmentation processes.[20]

Augmentation

In augmentation, a population is identified with a small number of mating individuals. This can lead to many problems, including inbreeding depression, and often leads to a dwindling number of individuals. Further complicating matters, with such a small population and consistent inbreeding depression, genetic drift is of worry as well, leading to high levels of homozygosity. To combat these problems, individuals are reintroduced to the population. This can be done via ex situ breeding of individuals or by physically relocating a separate population to join the identified, problematic population.

Introduction

In introduction, a species is brought to a habitat in which it has never before existed. This can be done for a number of reasons, ranging from climate change associated habitat loss to the introduction of predator species that cannot be controlled. Generally speaking, this is the type of assisted colonization that contains the most potential for harmful effects, like those described elsewhere in this article. Currently, a number of introductions of endangered populations from Australia have been made with varying degrees of success to small islands near the mainland where the only reason that the population had not dispersed before was due to the physical waterway.

Reintroduction

Reintroductions involve restoring a species to its native range. The species may no longer be found there due to any number of reasons, though most common is often the introduction of predators or habitat loss due to either climate change or other human factors. This is generally done to broaden the range of threatened populations and to reconnect fragmented populations.

Controversy

Significant controversy has developed around the idea of assisted colonization since it was first put forth in the scientific literature in 2007.[1] The two sides can be separated roughly as follows. Supporters generally believe that the expected benefits of assisted colonization, including saving and strengthening species, outweigh the potential harm of any project. Detractors generally believe that other conservation techniques which do not include the high risk of invasive species are not only better suited but are also more likely to succeed. This debate continues throughout the literature, generally due to a lack of real-world applications and follow-ups. Though these conservation efforts are becoming increasingly common, few long term looks at their success have been conducted.[4]

Invasive species risk

Perhaps the principal concern scientists have expressed over assisted colonization is the potential for relocated species to be invasive in their new habitats, driving out native species.[21] The fear that assisted colonization will facilitate invasions stems mostly from observations of the vast numbers of species that have become invasive outside their native ranges by (often inadvertent) introduction by humans. Although most agree that assisted colonization efforts, unlike accidental introductions, should involve detailed planning and risk assessment, for some, any threat of introducing invasive species, no matter how small, disqualifies assisted colonization as a viable management response to climate change.[21]

Those who wish to keep assisted colonization on the table often note that the vast majority of historical species invasions have resulted from continent-to-continent or continent-to-island transportation of species and that very few invasions have resulted from the comparatively short-distance, within-continent movement of species proposed for assisted colonization.[12][13][22] For example, Mueller and Hellman reviewed 468 documented species invasions and found that only 14.7% occurred on the same continent where the species originated.[12] Of the 14.7%, the vast majority were fish and crustaceans. Terrestrial species that became invasive on the same continent where they originated were often transported across large biogeographic barriers, such as mountain ranges. These long-distance, within-continent translocations are unlike expected uses of assisted colonization, which generally involve helping species colonize habitats immediately adjacent to their current ranges.[11]

Uncertainty in the planning process

To identify populations at risk and locate new potential habitats, conservationists often use niche models. These models predict the suitability of habitats in the future based on how closely their climates resemble the climate currently inhabited by the species. Though useful for describing broad trends, these models make a number of unrealistic assumptions that restrict the usefulness of their predictions.[23] For instance, they do not consider the possibility that species may be able to develop tolerance of new climates through acclimatization or adaptation.[24] Further, they do not account for the fact that a given species may perform better (e.g., become invasive) or worse (e.g., fail to establish) in a new habitat than in its current range if the community of competitor, predator, and mutualist species is different there.[24][25] Additionally, because different climate variables (e.g., minimum January temperature, average annual precipitation) rarely shift in unison, it is possible that few areas will exactly match the historical climates of species threatened by climate change.[26] Such multi-directional climate shifts will make it especially difficult to determine the species that are at greatest risk of habitat loss due to climate change and to predict future suitable habitat. The uncertainties in predictions of future suitable habitat limits confidence in assisted colonization decisions and has led some to reject assisted colonization entirely.[21]

Despite the uncertainty inherent in predictions of future suitable habitat, some studies have demonstrated that predictions can be quite accurate. A study of Hesperia comma butterflies in Britain identified unoccupied habitat sites that were likely to support the species under a warmer climate based on their similarity to occupied sites.[27] As the climate warmed, the butterfly colonized many of the sites; most of the sites it did not colonize were located far from existing populations, suggesting they were uncolonized because the butterfly could not reach them on its own. The data suggested that the suitable, uncolonized sites could be good targets for assisted colonization. The results suggested that if investigators can demonstrate their model makes reliable predictions with real-world data, models might be trusted for informing assisted colonization decisions.

Risks and benefits

The science is clear that climate change will drive many species extinct, and a traditional, land-preservation ethic will not prevent extinctions.[1] Those wary of moving species instead suggest expanding networks of habitat corridors, allowing species to naturally migrate into newly suitable areas.[28] Under the rates of climate change projected for the coming decades, however, even perfectly connected habitats will probably be insufficient.[29] Species that cannot naturally keep pace with shifting climates will be at risk regardless of habitat connectivity. Evidence suggests that slowly evolving and slowly dispersing species (including species that are dispersal-limited due to habitat fragmentation) will decline or go extinct in the absence of assisted colonization programs.[22]

In their rejection of assisted colonization, Ricciardi and Simberloff cite the precautionary principle, stating that any unknown risk, no matter how small, of assisted colonization resulting in the creation of new invasive species is enough to require that it not be undertaken.[21] Many scientists reject this position, however, noting that in many cases where extinctions due to climate change are likely, the risks of extinction from not facilitating colonization are probably far worse than the risks of facilitating colonization.[13][14] They argue that the precautionary principle cuts both ways, and the risks of inaction must be compared against the risks of action. Others note that the ethics of assisting colonization will depend on the values of the stakeholders involved in a specific decision rather than the position of scientists on assisted colonization in general.[30] At the very least, some note, scientists should conduct further research into assisted colonization and improve our capacity to predict specific outcomes instead of outright rejecting it.[14]

Because confidence in expected outcomes is often greater in the short-term (e.g., 20 years) than the long-term future, it may be more reasonable to use short-term projections to guide actions.[31] However, it is also important to consider whether the climate will remain suitable long enough for colonizing species to mature and reproduce, if that is the management goal.[32]

Due to climate change, accidental species introductions, and other global changes, there is nowhere on the planet free of human disturbance.[33] Thus, the idea that land managers should refrain from creating human-altered communities through assisted colonization may be moot given that all communities have been altered by humans to some degree whether managers undertake assisted colonization or not.[34][35][36] Given the reality of global change, it will be impossible to maintain past ecological communities indefinitely. Many therefore believe we should strive to maintain biodiversity and functioning ecosystems in the face of climate change, even if it means actively moving species beyond their native ranges.[35] In the absence of assisted colonization, climate change is already causing many highly mobile species, such as butterflies, to colonize areas they have not previously inhabited.[35] Through assisted colonization, managers could help rare or less-mobile species keep pace, possibly preventing future extinctions due to a their inability to colonize new areas fast enough. Though some argue that nature often responds to challenges more effectively in the absence of human intervention, others note that current climate change, itself, is a human intervention.[35] Many species that would have been effective dispersers under slower, natural climate change may be left behind by more mobile species under current rates of human-caused climate change. Thus, through changing the climate, humans may already be artificially segregating species even without actively relocating them.[35]

Critics may also have major concerns about different genetic issues when considering assisted colonization such as maladaptation to novel environmental conditions and hybridization with similar species. These often depend on the genetic structure and level of genetic variation in the source populations. The environmental conditions in which these populations are being introduced must also be taken into account. In order to enhance genetic variation, and thus adaptive potential, material could be sourced from multiple populations. This is known as composite provenancing.[37] However, if the environmental gradient is well known, such as predictable changes in elevation or aridity, source populations should be ‘genetically matched’ to recipient sites as best as possible to ensure that the translocated individuals ae not maladapted. This strategy of moving species beyond their current range has been suggested for those that are severely threatened or endangered. By moving them outside their native range, hopefully the immediate threats of predation, disease, and habitat loss can be avoided. However, these species are usually already suffering from some sort of genetic issue resulting from low effective population size such as inbreeding depression, loss in genetic diversity, or maladaptation. Therefore, caution must be taken with what few individuals remain and rapid population growth must be the primary goal. In the case of some species, this can be accomplished with a captive breeding program [38]

Examples

Forestry in North America

This section is an excerpt from Assisted migration of forests in North America[ edit ]

Dixon National Tallgrass Prairie Seed Bank, US

Although not actively engaging in assisted colonization, the Dixon National Tallgrass Prairie Seed Bank seeks to collect seeds from populations of species expected to decline or disappear due to climate change.[39] They prioritize collections from populations at greatest risk of disappearance and for which suitable habitat is projected to occur elsewhere in the general region, keeping open the possibility of using collected seeds for assisted colonization projects in the future.

Great Barrier Reef

The Great Barrier Reef's health has been in jeopardy in recent years due to rising sea temperatures caused by climate change. The Australian Institute of Marine Science has been at the forefront of attempting to save the reefs using various forms of assisted evolution and assisted colonization. Assisted evolution is believed to be a temporary solution to save many threatened species from global warming and other climate change related environmental changes.[40]

Stitchbird (hihi)

The stitchbird, also known as the Hihi, is a bird endemic to New Zealand. Changes in climate have shown to have a profound effect on the hihi's ability to thrive and reproduce. As a result, human caused climate change is an existential threat to the species. The hihi's current native habitat is becoming unstable due to rising temperatures, and suitable temperatures are shifting further south. Assisted colonization is being considered as a means of ensuring the hihi can remain in its current natural habitat. Critics, however, argue the risks that are presented to the new host environments are not worth the potential benefits assisted colonization may present.[41]

Florida torreya, US

The Florida torreya (Torreya taxifolia) is an critically endangered tree of the yew family, Taxaceae,[42] found in the Southeastern United States, at the state border region of northern Florida and southwestern Georgia. A self-organized group of conservationists called the Torreya Guardians was created in 2004 to facilitate the assisted colonization of the endangered tree by rewilding it in more northern parts of the United States .[43]

See also

References

  1. ↑ 1.0 1.1 1.2 1.3 1.4 McLachlan, J. S.; Hellmann, J. J.; Schwartz, M. W. (2007). "A Framework for Debate of Assisted Migration in an Era of Climate Change". Conservation Biology 21 (2): 297–302. doi:10.1111/j.1523-1739.2007.00676.x. PMID 17391179. 
  2. ↑ Allen, C. D.; MacAlady, A. K.; Chenchouni, H.; Bachelet, D.; McDowell, N.; Vennetier, M.; Kitzberger, T.; Rigling, A. et al. (2010). "A global overview of drought and heat-induced tree mortality reveals emerging climate change risks for forests". Forest Ecology and Management 259 (4): 660. doi:10.1016/j.foreco.2009.09.001. https://hal.archives-ouvertes.fr/hal-00457602/file/AX2010-PUB00027818.pdf. 
  3. ↑ 3.0 3.1 Zhu, K.; Woodall, C. W.; Clark, J. S. (2012). "Failure to migrate: Lack of tree range expansion in response to climate change". Global Change Biology 18 (3): 1042. doi:10.1111/j.1365-2486.2011.02571.x. Bibcode: 2012GCBio..18.1042Z. 
  4. ↑ 4.0 4.1 Heller, N. E.; Zavaleta, E. S. (2009). "Biodiversity management in the face of climate change: A review of 22 years of recommendations". Biological Conservation 142: 14–32. doi:10.1016/j.biocon.2008.10.006. 
  5. ↑ 5.0 5.1 Thomas, C. D.; Cameron, A.; Green, R. E.; Bakkenes, M.; Beaumont, L. J.; Collingham, Y. C.; Erasmus, B. F. N.; De Siqueira, M. F. D. et al. (Jan 2004). "Extinction risk from climate change" (Full free text). Nature 427 (6970): 145–148. doi:10.1038/nature02121. PMID 14712274. Bibcode: 2004Natur.427..145T. http://www.geog.umd.edu/resac/outgoing/GEOG442%20Fall%202005/Lecture%20materials/extinctions%20and%20climate%20change.pdf. 
  6. ↑ Davis, M. B.; Shaw, R. G. (2001). "Range Shifts and Adaptive Responses to Quaternary Climate Change". Science 292 (5517): 673–679. doi:10.1126/science.292.5517.673. PMID 11326089. Bibcode: 2001Sci...292..673D. 
  7. ↑ Warren, M. S.; Hill, J. K.; Thomas, J. A.; Asher, J.; Fox, R.; Huntley, B.; Roy, D. B.; Telfer, M. G. et al. (2001). "Rapid responses of British butterflies to opposing forces of climate and habitat change". Nature 414 (6859): 65–69. doi:10.1038/35102054. PMID 11689943. Bibcode: 2001Natur.414...65W. http://eprints.whiterose.ac.uk/119/1/thomascd4.pdf. 
  8. ↑ McLachlan, J. S.; Clark, J. S.; Manos, P. S. (2005). "Molecular Indicators of Tree Migration Capacity Under Rapid Climate Change". Ecology 86 (8): 2088. doi:10.1890/04-1036. 
  9. ↑ Menendez, R.; Megias, A. G.; Hill, J. K.; Braschler, B.; Willis, S. G.; Collingham, Y.; Fox, R.; Roy, D. B. et al. (2006). "Species richness changes lag behind climate change". Proceedings of the Royal Society B: Biological Sciences 273 (1593): 1465–70. doi:10.1098/rspb.2006.3484. PMID 16777739. 
  10. ↑ Karl, T. R.; Trenberth, K. E. (2003). "Modern Global Climate Change". Science 302 (5651): 1719–1723. doi:10.1126/science.1090228. PMID 14657489. Bibcode: 2003Sci...302.1719K. https://zenodo.org/record/1230878. 
  11. ↑ 11.0 11.1 11.2 Hunter, M. L. (2007). "Climate Change and Moving Species: Furthering the Debate on Assisted Colonization". Conservation Biology 21 (5): 1356–1358. doi:10.1111/j.1523-1739.2007.00780.x. PMID 17883502. 
  12. ↑ 12.0 12.1 12.2 Mueller, J. M.; Hellmann, J. J. (2008). "An Assessment of Invasion Risk from Assisted Migration". Conservation Biology 22 (3): 562–567. doi:10.1111/j.1523-1739.2008.00952.x. PMID 18577085. 
  13. ↑ 13.0 13.1 13.2 Sax, D. F.; Smith, K. F.; Thompson, A. R. (2009). "Managed relocation: A nuanced evaluation is needed". Trends in Ecology & Evolution 24 (9): 472–3; author reply 476–7. doi:10.1016/j.tree.2009.05.004. PMID 19577321. 
  14. ↑ 14.0 14.1 14.2 Schwartz, M. W.; Hellmann, J. J.; McLachlan, J. S. (2009). "The precautionary principle in managed relocation is misguided advice". Trends in Ecology & Evolution 24 (9): 474; author reply 476–7. doi:10.1016/j.tree.2009.05.006. PMID 19595477. 
  15. ↑ 15.0 15.1 Rice, Kevin J.; Emery, Nancy C. (2003). "Managing microevolution: Restoration in the face of global change". Frontiers in Ecology and the Environment 1 (9): 469–478. doi:10.2307/3868114. 
  16. ↑ 16.0 16.1 16.2 Skelly, D. K.; Joseph, L. N.; Possingham, H. P.; Freidenburg, L. K.; Farrugia, T. J.; Kinnison, M. T.; Hendry, A. P. (2007). "Evolutionary Responses to Climate Change". Conservation Biology 21 (5): 1353–1355. doi:10.1111/j.1523-1739.2007.00764.x. PMID 17883501. 
  17. ↑ "Assisted Evolution". ”Australian Institute of Marine Science”. https://www.aims.gov.au/reef-recovery/assisted-evolution. 
  18. ↑ Perdrizet, George (1989). "Stress conditioning: a novel approach to organ preservation". ”Europe PMC” 46 (1): pp. 23–6. PMID 2656107. 
  19. ↑ Aitken, Sally N.; Whitlock, Michael C. (2013). "Assisted Gene Flow to Facilitate Local Adaptation to Climate Change". Annual Review of Ecology, Evolution, and Systematics 44 (1): 367–388. doi:10.1146/annurev-ecolsys-110512-135747. 
  20. ↑ Weeks, Andrew R; Sgro, Carla M; Young, Andrew G; Frankham, Richard; Mitchell, Nicki J; Miller, Kim A; Byrne, Margaret; Coates, David J et al. (2011-11-01). "Assessing the benefits and risks of translocations in changing environments: a genetic perspective". Evolutionary Applications 4 (6): 709–725. doi:10.1111/j.1752-4571.2011.00192.x. ISSN 1752-4571. PMID 22287981. 
  21. ↑ 21.0 21.1 21.2 21.3 Ricciardi, A.; Simberloff, D. (2009). "Assisted colonization is not a viable conservation strategy". Trends in Ecology & Evolution 24 (5): 248–53. doi:10.1016/j.tree.2008.12.006. PMID 19324453. 
  22. ↑ 22.0 22.1 Hoegh-Guldberg, O.; Hughes, L.; McIntyre, S.; Lindenmayer, D. B.; Parmesan, C.; Possingham, H. P.; Thomas, C. D. (2008). "ECOLOGY: Assisted Colonization and Rapid Climate Change". Science 321 (5887): 345–346. doi:10.1126/science.1157897. PMID 18635780. 
  23. ↑ Dawson, T. P.; Jackson, S. T.; House, J. I.; Prentice, I. C.; Mace, G. M. (2011). "Beyond Predictions: Biodiversity Conservation in a Changing Climate". Science 332 (6025): 53–58. doi:10.1126/science.1200303. PMID 21454781. Bibcode: 2011Sci...332...53D. 
  24. ↑ 24.0 24.1 Guisan, A.; Thuiller, W. (2005). "Predicting species distribution: Offering more than simple habitat models". Ecology Letters 8 (9): 993. doi:10.1111/j.1461-0248.2005.00792.x. 
  25. ↑ Leathwick, J.R.; Austin, M.P. (2001). "Competitive interactions between tree species in New Zealand's old-growth indigenous forests". Ecology 82 (9): 2560–2573. doi:10.1890/0012-9658(2001)082[2560:cibtsi2.0.co;2]. 
  26. ↑ Williams, J. W.; Jackson, S. T.; Kutzbach, J. E. (2007). "Projected distributions of novel and disappearing climates by 2100 AD". Proceedings of the National Academy of Sciences 104 (14): 5738–42. doi:10.1073/pnas.0606292104. PMID 17389402. Bibcode: 2007PNAS..104.5738W. 
  27. ↑ Lawson, C. R.; Bennie, J. J.; Thomas, C. D.; Hodgson, J. A.; Wilson, R. J. (2012). "Local and landscape management of an expanding range margin under climate change". Journal of Applied Ecology: no. doi:10.1111/j.1365-2664.2011.02098.x. 
  28. ↑ Krosby, M.; Tewksbury, J.; Haddad, N. M.; Hoekstra, J. (2010). "Ecological Connectivity for a Changing Climate". Conservation Biology 24 (6): 1686–1689. doi:10.1111/j.1523-1739.2010.01585.x. PMID 20961330. 
  29. ↑ Galatowitsch, S.; Frelich, L.; Phillips-Mao, L. (2009). "Regional climate change adaptation strategies for biodiversity conservation in a midcontinental region of North America". Biological Conservation 142 (10): 2012. doi:10.1016/j.biocon.2009.03.030. 
  30. ↑ Schlaepfer, M. A.; Helenbrook, W. D.; Searing, K. B.; Shoemaker, K. T. (2009). "Assisted colonization: Evaluating contrasting management actions (and values) in the face of uncertainty". Trends in Ecology & Evolution 24 (9): 471–2; author reply 476–7. doi:10.1016/j.tree.2009.05.008. PMID 19595475. 
  31. ↑ Gray, L. K.; Gylander, T.; Mbogga, M. S.; Chen, P. Y.; Hamann, A. (2011). "Assisted migration to address climate change: Recommendations for aspen reforestation in western Canada". Ecological Applications 21 (5): 1591–1603. doi:10.1890/10-1054.1. PMID 21830704. 
  32. ↑ McDonald-Madden, E.; Runge, M. C.; Possingham, H. P.; Martin, T. G. (2011). "Optimal timing for managed relocation of species faced with climate change". Nature Climate Change 1 (5): 261. doi:10.1038/nclimate1170. Bibcode: 2011NatCC...1..261M. http://espace.library.uq.edu.au/view/UQ:246908/UQ246908_OA.pdf. 
  33. ↑ Vitousek, P. M. (1997). "Human Domination of Earth's Ecosystems". Science 277 (5325): 494–499. doi:10.1126/science.277.5325.494. https://izvestia.igras.ru/jour/article/view/743. 
  34. ↑ Seddon, P. J. (2010). "From Reintroduction to Assisted Colonization: Moving along the Conservation Translocation Spectrum". Restoration Ecology 18 (6): 796–802. doi:10.1111/j.1526-100X.2010.00724.x. https://zenodo.org/record/998241. 
  35. ↑ 35.0 35.1 35.2 35.3 35.4 Thomas, C. D. (2011). "Translocation of species, climate change, and the end of trying to recreate past ecological communities". Trends in Ecology & Evolution 26 (5): 216–221. doi:10.1016/j.tree.2011.02.006. PMID 21411178. 
  36. ↑ Hobbs, R. J.; Hallett, L. M.; Ehrlich, P. R.; Mooney, H. A. (2011). "Intervention Ecology: Applying Ecological Science in the Twenty-first Century". BioScience 61 (6): 442. doi:10.1525/bio.2011.61.6.6. 
  37. ↑ Broadhurst, Linda (4 September 2008). "Seed supply for broadscale restoration: maximizing evolutionary potential". Evolutionary Applications 1 (4): 587–597. doi:10.1111/j.1752-4571.2008.00045.x. PMID 25567799. 
  38. ↑ Weeks, Andrew; Sgro, Carla; Young, Andrew; Frankham, Richard; Mitchell, Nicki; Byrne, Margaret; Coates, David; Eldridge, Mark et al. (18 June 2011). "Assessing the benefits and risks of translocations in changing environments: a genetic perspective". Evolutionary Applications 4 (6): 709–725. doi:10.1111/j.1752-4571.2011.00192.x. PMID 22287981. 
  39. ↑ Vitt, P.; Havens, K.; Kramer, A. T.; Sollenberger, D.; Yates, E. (2010). "Assisted migration of plants: Changes in latitudes, changes in attitudes". Biological Conservation 143: 18–27. doi:10.1016/j.biocon.2009.08.015. 
  40. ↑ Johnston, Ian. ""Climate change is changing nature so much it may need "human-assisted evolution", scientists say"". ”Independent”. https://www.independent.co.uk/environment/climate-change-global-warming-changing-nature-human-assisted-evolution-a7410286.html. 
  41. ↑ L. M. Chauvenet, Aliénor. "EDITOR'S CHOICE: Saving the hihi under climate change: a case for assisted colonization". ”British Ecological Society”. doi:10.1111/1365-2664.12150. 
  42. ↑ Esser, Lora L. (1993). Torreya taxifolia. In: Fire Effects Information System (Report). U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. https://www.fs.fed.us/database/feis/plants/tree/tortax/all.html. Retrieved 15 March 2020. 
  43. ↑ Berdik, Chris (12 October 2008). "Driving Mr. Lynx". The Boston Globe. http://archive.boston.com/bostonglobe/ideas/articles/2008/10/12/driving_mr_lynx/?page=1. 




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