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Population ecology

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576:(or MSY). Given a population dynamic model, such as any of the ones above, it is possible to calculate the population size that produces the largest harvestable surplus at equilibrium. While the use of population dynamic models along with statistics and optimization to set harvest limits for fish and game is controversial among some scientists, it has been shown to be more effective than the use of human judgment in computer experiments where both incorrect models and natural resource management students competed to maximize yield in two hypothetical fisheries. To give an example of a non-intuitive result, fisheries produce more fish when there is a nearby 569:
the harvest deaths are substituted for the deaths that would have occurred naturally. Harvest above that level is termed "additive" mortality, because it adds to the number of deaths that would have occurred naturally. These terms are not necessarily judged as "good" and "bad," respectively, in population management. For example, a fish & game agency might aim to reduce the size of a deer population through additive mortality. Bucks might be targeted to increase buck competition, or does might be targeted to reduce reproduction and thus overall population size.
625:(the carrying capacity of a population, density dependent). It is important to understand the difference between density-independent factors when selecting the intrinsic rate and density-dependent for the selection of the carrying capacity. Carrying capacity is only found during a density-dependent population. Density-dependent factors influence the carrying capacity are predation, harvest, and genetics, so when selecting the carrying capacity it is important to understand to look at the predation or harvest rates that influence the population (Stewart 2004). An 762:
resources from their habitats. In addition, metapopulation ecology allows for a deeper understanding of the effects of habitat loss, and can help to predict the future of a habitat. To elaborate, metapopulation ecology assumes that, before a habitat becomes uninhabitable, the species in it will emigrate out, or die off. This information is helpful to ecologists in determining what, if anything, can be done to aid a declining habitat. Overall, the information that metapopulation ecology provides is useful to ecologists in many ways (Hanski 1998).
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Parakeets in the United States. Originally from South America, Monk Parakeets were either released or escaped from people who owned them. These birds experienced exponential growth from the years 1975-1994 and grew about 55 times their population size from 1975. This growth is likely due to reproduction within their population, as opposed to the addition of more birds from South America (Van Bael & Prudet-Jones 1996).
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seasonal supply of migrants to other patch locations. Sink patches are unproductive sites that only receive migrants. In metapopulation terminology there are emigrants (individuals that leave a patch) and immigrants (individuals that move into a patch). Metapopulation models examine patch dynamics over time to answer questions about spatial and demographic ecology. An important concept in metapopulation ecology is the
758:, where small patches of lower quality (i.e., sinks) are maintained by a seasonal influx of new immigrants. Metapopulation structure evolves from year to year, where some patches are sinks, such as dry years, and become sources when conditions are more favorable. Ecologists utilize a mixture of computer models and field studies to explain metapopulation structure. 654:
offspring after the initial birth or hatching is the survival of the young, the growth rate, and the birthing success of the offspring. There is found to be no effect of the young being raised by the natural parents or foster parents, the offspring need the proper resources to survive (Kristi 2010).
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Population size can be influenced by the per capita population growth rate (rate at which the population size changes per individual in the population.) Births, deaths, emigration, and immigration rates all play a significant role in growth rate. The maximum per capita growth rate for a population is
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All of these are measured to determine the harvestable surplus, which is the number of individuals that can be harvested from a population without affecting long-term population stability or average population size. The harvest within the harvestable surplus is termed "compensatory" mortality, where
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Metapopulation ecology is a simplified model of the landscape into patches of varying levels of quality. Patches are either occupied or they are not. Migrants moving among the patches are structured into metapopulations either as sources or sinks. Source patches are productive sites that generate a
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theory. For example, if an animal has the choice of producing one or a few offspring, or to put a lot of effort or little effort in offspring—these are all examples of trade-offs. In order for species to thrive, they must choose what is best for them, leading to a clear distinction between r and K
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A Type I survivorship curve is characterized by the fact that death occurs in the later years of an organism's life (mostly mammals). In other words, most organisms reach the maximum expected lifespan and the life expectancy and the age of death go hand-in-hand (Demetrius 1978). Typically, Type I
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A study that was conducted on the egg size and offspring quality in birds found that, in summary, that the egg size contributes to the overall fitness of the offspring. This study shows the direct relationship to the survivorship curve Type I in that if the offspring is cared for during its early
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The offspring fitness is mainly affected by the size and quality of that specific offspring . Factors that contribute to the relative fitness of offspring size is either the resources the parents provide to their young or morphological traits that come from the parents. The overall success of the
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In a population, carrying capacity is known as the maximum population size of the species that the environment can sustain, which is determined by resources available. In many classic population models, r is represented as the intrinsic growth rate, where K is the carrying capacity, and N0 is the
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Metapopulation ecology allows for ecologists to take in a wide range of factors when examining a metapopulation like genetics, the bottle-neck effect, and many more. Metapopulation data is extremely useful in understanding population dynamics as most species are not numerous and require specific
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For example, if plant populations decreased significantly, the herbivore populations would decrease, which would lead to a carnivore population decreasing too. Therefore, if all of the plants disappeared, then the ecosystem would collapse. Another example would be if there were too many plants
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into fewer offspring. K-selected species generally experience stronger competition, where populations generally live near carrying capacity. These species have heavy investment in offspring, resulting in longer lived organisms, and longer period of maturation. Offspring of K-selected species
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When the per capita rate of increase takes the same positive value regardless of population size, the graph shows exponential growth. Exponential growth takes on the assumption that there is unlimited resources and no predation. An example of exponential population growth is that of the Monk
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A population is defined as a group of interacting organisms of the same species. A demographic structure of a population is how populations are often quantified. The total number of individuals in a population is defined as a population size, and how dense these individuals are is defined as
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stages of life by a parent, it will die off later in life. However, if the offspring is not cared for by the parents due to an increase in egg quantity, then the survivorship curve will be similar to Type III, in that the offspring will die off early and will survive later in life.
629:-selected species (e.g., many kinds of insects, such as aphids) is one that has high rates of fecundity, low levels of parental investment in the young, and high rates of mortality before individuals reach maturity. Evolution favors productivity in r-selected species. 680:
For example, the presence of top carnivores keep herbivore populations in check. If there were no top carnivores in the ecosystem, then herbivore populations would rapidly increase, leading to all plants being eaten. This ecosystem would eventually collapse.
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A group of individuals within an investigator-delimited area smaller than the geographic range of the species and often within a population (as defined above). A local population could be a disjunct population as well.
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An ecosystem does not have to be either top-down or bottom-up. There are occasions where an ecosystem could be bottom-up sometimes, such as a marine ecosystem, but then have periods of top-down control due to fishing.
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Survivorship curves are graphs that show the distribution of survivors in a population according to age. Survivorship curves play an important role in comparing generations, populations, or even different species.
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Stewart, Kelley M.; Bowyer, R. Terry.; Dick, Brian L.; Johnson, Bruce K.; Kie, John G. (March 2005). "Density-dependent effects on physical condition and reproduction in North American elk: an experimental test".
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Hubbell, Stephen P. (30 March 1979). "Tree Dispersion, Abundance, and Diversity in a Tropical Dry Forest: That tropical trees are clumped, not spaced, alters conceptions of the organization and dynamics".
416:, the graph shows logistic growth. Environmental and social variables, along with many others, impact the carrying capacity of a population, meaning that it has the ability to change (Schacht 1980). 727:
Type III curves indicate few surviving the younger years, but after a certain age, individuals are much more likely to survive. Type III survivorship typically characterizes r-selected species.
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If we measure these rates over many time intervals, we can determine how a population's density changes over time. Immigration and emigration are present, but are usually not measured.
537: 636:-selected species (such as humans) has low rates of fecundity, high levels of parental investment in the young, and low rates of mortality as individuals mature. Evolution in 724:
Type II survivorship shows that death at any age is equally probable. This means that the chances of death are not dependent on or affected by the age of that organism.
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Bottom-up controls, on the other hand, are driven by producers in the ecosystem. If plant populations change, then the population of all species would be impacted.
604:. It rapidly gets more complicated, but stripping the phenomenon of all its complications, this is the basic principle: two consumers consuming the same resource. 3365: 2618: 2216: 572:
For the management of many fish and other wildlife populations, the goal is often to achieve the largest possible long-run sustainable harvest, also known as
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ecology, renaming autecology as 'species ecology' (Odum regarded "autecology" as an archaic term), thus that there were four subdivisions of ecology.
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Lynam, Christopher Philip; Llope, Marcos; Möllmann, Christian; Helaouët, Pierre; Bayliss-Brown, Georgia Anne; Stenseth, Nils C. (21 February 2017).
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A group of individuals more genetically similar to each other than to other individuals, usually with some degree of spatial isolation as well.
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available, then two herbivore populations may compete for the same food. The competition would lead to an eventual removal of one population.
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population density. There is also a population's geographic range, which has limits that a species can tolerate (such as temperature).
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Holden, Matthew H; Ellner, Stephen P (2016). "Human judgment vs. Quantitative models for the management of ecological resources".
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In some populations, organisms in lower trophic levels are controlled by organisms at the top. This is known as top-down control.
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A group of conspecific individuals that is demographically, genetically, or spatially disjunct from other groups of individuals.
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When describing growth models, there are two main types of models that are most commonly used: exponential and logistic growth.
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Bael, Sunshine Van; Pruett-Jones, Stephen (1996). "Exponential Population Growth of Monk Parakeets in the United States".
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Levins, R. (1969). "Some Demographic and Genetic Consequences of Environmental Heterogeneity for Biological Control".
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In the 1940s, ecology was divided into autecology—the study of individual species in relation to the environment—and
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Whitham, T. G. (1978). "Habitat Selection by Pemphigus Aphids in Response to Response Limitation and Competition".
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When the per capita rate of increase decreases as the population increases towards the maximum limit, or
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which makes it possible to predict the long-term probability of a species persisting in a given patch of
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Kareiva, Peter (1989). "Renewing the Dialogue between Theory and Experiments in Population Ecology".
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An arbitrary spatially delimited subset of individuals from within a population (as defined above).
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At its most elementary level, interspecific competition involves two species utilizing a similar
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Brotz, Lucas; Cheung, William W. L; Kleisner, Kristin; Pakhomov, Evgeny; Pauly, Daniel (2012).
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generally have a higher probability of survival, due to heavy parental care and nurturing.
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Krist, Miloš (August 2011). "Egg size and offspring quality: a meta-analysis in birds".
2069: 2032: 1946: 1855: 1706: 1555: 1316: 1091: 362:. This principle provided the basis for the subsequent predictive theories, such as the 352:. According to Malthus, assuming that the conditions (the environment) remain constant ( 4110: 3934: 3887: 3817: 3812: 3707: 3574: 3447: 3254: 3244: 3224: 3101: 3027: 2992: 2931: 2808: 2763: 2655: 2391: 2386: 2379: 2347: 2241: 1725: 1690: 1407: 1382: 1229: 822: 742: 736: 581: 461: 2019:
Demetrius, Lloyd (September 1978). "Adaptive value, entropy and survivorship curves".
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in the early 19th century, who refined and adjusted the Malthusian demographic model.
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The development of population ecology owes much to the mathematical models known as
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Mathematical bioeconomics : the optimal management of renewable resources
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A set of spatially disjunct populations, among which there is some migration.
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The first journal publication of the Society of Population Ecology, titled
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Terms used to describe natural groups of individuals in ecological studies
942: 923:(Second ed.). Philadelphia and London: W. B. Saunders Co. p. 9, 584:, resulting in higher catches than if the whole area was open to fishing. 4085: 4014: 3545: 3052: 2964: 2911: 2866: 2575: 2048: 749:"as a population of populations which go extinct locally and recolonize." 181: 1691:"Interaction between top-down and bottom-up control in marine food webs" 1383:"An ecological perspective on marine reserves in prey–predator dynamics" 1182: 1158: 4075: 3882: 3752: 3747: 3374: 3322: 2982: 2627: 2098: 1998:
Schacht, Robert M. (December 1980). "Two Models of Population Growth".
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The beginning of population dynamics is widely regarded as the work of
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Scientific articles on population ecology can also be found in the
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Turchin, P. (2001). "Does Population Ecology Have General Laws?".
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Pianka, E. R. (1972). "r and K Selection or b and d Selection?".
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Modeling Nature: Episodes in the History of Population Ecology
640:-selected species favors efficiency in the conversion of more 745:" concept. The metapopulation concept was introduced in 1969: 741:
Populations are also studied and conceptualized through the "
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are covered as special cases of the general formulation. The
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The number of individuals that leave a population over time.
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The number of individuals that join a population over time.
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as adaptations to the environment by individual organisms.
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Map of population trends of native and invasive species of
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Hanski, Ilkka (November 1998). "Metapopulation dynamics".
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Hanski, Ilkka (November 1998). "Metapopulation dynamics".
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Do all ecosystems have to be either top-down or bottom-up?
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are another famous example, as well as the alternative
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Extinction. In: Some Mathematical Questions in Biology
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at the end of the 18th and beginning of 19th century.
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survivorship curves characterize K-selected species.
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the number that emigrated between time 0 and time 1.
481: 385:, in which the models of Gompertz, Verhulst and also 1486: 1484: 1204:"Exponential growth & logistic growth (article)" 4023: 3923: 3848: 3721: 3658: 3518: 3386: 3288: 3167: 3094: 3051: 2973: 2940: 2837: 2749: 2643: 2546: 2503: 2415: 2361: 2324: 2283: 2260: 2232: 1665:"The top-down vs bottom-up control in an ecosystem" 1880:Ecology, genetics and evolution of metapopulations 1521:(4th ed.). Oxford, UK: Blackwell Publishing. 1515:Begon, M.; Townsend, C. R.; Harper, J. L. (2006). 1381:Chakraborty, Kunal; Das, Kunal; Kar, T. K (2013). 1228: 916: 609:An important concept in population ecology is the 531: 1929:Henderson, Kirsten; Loreau, Michel (March 2019). 377:A more general model formulation was proposed by 1790:Bulletin of the Entomological Society of America 1585:Wilson, Edward O.; MacArthur, Robert H. (2016). 1695:Proceedings of the National Academy of Sciences 598: 120:. 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(1838). 1120:Malthus, Thomas Robert. 778:) was released in 1952. 432:Matrix population models 372:Pierre François Verhulst 3915:Ontogenetic niche shift 3778:Ideal free distribution 3688:Ecological facilitation 3438:Malthusian growth model 3408:Consumer-resource model 3265:Paradox of the plankton 3230:Energy systems language 2950:Chemoorganoheterotrophy 2917:Optimal foraging theory 2892:Heterotrophic nutrition 2518:Ecological anthropology 2000:American Anthropologist 1913:10.1002/(ISSN)1438-390X 1716:10.1073/pnas.1621037114 1628:The American Naturalist 1295:Ecological Applications 919:Fundamentals of Ecology 833:Population distribution 350:Malthusian growth model 4061:Ecological forecasting 4005:Marginal value theorem 3803:Landscape epidemiology 3738:Cross-boundary subsidy 3673:Biological interaction 3023:Microbial intelligence 2711:Green world hypothesis 2528:Ecological engineering 1279:10.1093/icesjms/fss192 1124:: Library of Economics 967:Kingsland, S. (1995). 751: 617:The first variable is 606: 554:the number that died, 533: 456:Population growth rate 387:Ludwig von Bertalanffy 68: 4066:Ecological humanities 3965:Ecological energetics 3910:Niche differentiation 3773:Habitat fragmentation 3541:Ecological extinction 3488:Small population size 3240:Feed conversion ratio 3220:Ecological succession 3152:San Francisco Estuary 3066:Ecological efficiency 3008:Microbial cooperation 1802:10.1093/besa/15.3.237 1772:"Survivorship Curves" 1750:"Survivorship Curves" 1227:Clark, Colin (1990). 747: 534: 54: Stable/variable 33: 4091:Evolutionary ecology 4056:Ecological footprint 4051:Ecological economics 3975:Ecological threshold 3970:Ecological indicator 3840:Source–sink dynamics 3793:Land change modeling 3788:Insular biogeography 3640:Species distribution 3379:Modelling ecosystems 3038:Microbial metabolism 2877:Intraguild predation 2666:Biogeochemical cycle 2632:Modelling ecosystems 2523:Ecological economics 2450:Evolutionary ecology 2417:Ecological phenomena 2247:Quantitative ecology 1905:"Population Ecology" 1175:10.1093/jxb/10.2.290 1034:on November 4, 2005. 808:Ecological overshoot 793:and other journals. 479: 348:, formulated as the 110:conservation biology 27:Sub-field of ecology 4141:Theoretical ecology 4116:Natural environment 3980:Ecosystem diversity 3950:Ecological collapse 3940:Bateman's principle 3895:Limiting similarity 3808:Landscape limnology 3630:Species homogeneity 3468:Population modeling 3463:Population dynamics 3280:Trophic state index 2569:Restoration ecology 2559:Glossary of ecology 2505:Interdisciplinarity 2252:Theoretical ecology 2226:Branches of ecology 2172:2005Oecol.143...85S 2115:(4387): 1299–1309. 2087:The Wilson Bulletin 2070:1998Natur.396...41H 2033:1978Natur.275..213D 1947:2019PeoNa...1...31H 1856:1998Natur.396...41H 1707:2017PNAS..114.1952L 1556:1978Ecol...59.1164W 1492:"r and K selection" 1317:2016EcoAp..26.1553H 1235:. New York: Wiley. 1092:2001Oikos..94...17T 858:Theoretical ecology 848:Population genetics 838:Population dynamics 774:(originally called 712:Survivorship curves 706:Survivorship curves 442:wildlife management 335:population dynamics 329:Population dynamics 323:Population dynamics 218: 168:, "household"; and 134:population dynamics 4176:Applied statistics 4171:Population ecology 4152:Outline of ecology 4101:Industrial ecology 4096:Functional ecology 3960:Ecological deficit 3905:Niche construction 3868:Ecosystem engineer 3645:Species–area curve 3566:Introduced species 3381:: Other components 3313:Deimatic behaviour 3215:Ecological network 3147:North Pacific Gyre 3132:hydrothermal vents 3071:Ecological pyramid 3018:Microbial food web 2829:Primary production 2774:Foundation species 2554:History of ecology 2460:Functional ecology 2425:Behavioral ecology 2304:Population ecology 2130:Biological Reviews 1975:. pp. 68–88. 828:Population density 772:Population Ecology 685:Bottom-up controls 614:selected species. 529: 231:Species population 216: 74:is a sub-field of 72:Population ecology 69: 18:Population Ecology 4158: 4157: 4041:Balance of nature 3798:Landscape ecology 3683:Community ecology 3625:Species diversity 3561:Indicator species 3556:Gradient analysis 3433:Logistic function 3341: 3340: 3298:Animal coloration 3275:Trophic mutualism 3013:Microbial ecology 2804:Photoheterotrophs 2789:Myco-heterotrophy 2701:Ecosystem ecology 2686:Carrying capacity 2651:Abiotic component 2594: 2593: 2533:Political ecology 2475:Molecular ecology 2470:Landscape ecology 2338:Microbial ecology 2314:Ecosystem ecology 2309:Community ecology 2027:(5677): 213–214. 1990:978-1-4008-6018-0 1935:People and Nature 1890:978-0-12-323448-3 1828:978-0-8218-1152-8 1609:Project MUSE 1596:978-1-4008-8137-6 1528:978-1-4051-1117-1 1474:978-0-691-11440-8 1061:978-1-118-94757-9 978:978-0-226-43728-6 853:Population growth 673:Top-down controls 649:Offspring Quality 414:carrying capacity 368:Benjamin Gompertz 320: 319: 190:community ecology 16:(Redirected from 4188: 3858:Ecological niche 3830:selection theory 3650:Umbrella species 3635:Species richness 3571:Invasive species 3551:Flagship species 3458:Population cycle 3453:Overexploitation 3418:Ecological yield 3368: 3361: 3354: 3345: 3250:Mesotrophic soil 3190:Climax community 3122:Marine food webs 3061:Biomagnification 2862:Chemoorganotroph 2716:Keystone species 2676:Biotic component 2621: 2614: 2607: 2598: 2430:Chemical ecology 2402:Tropical ecology 2219: 2212: 2205: 2196: 2191: 2153: 2124: 2102: 2081: 2052: 2041:10.1038/275213a0 2015: 1994: 1960: 1958: 1917: 1916: 1901: 1895: 1894: 1874: 1868: 1867: 1839: 1833: 1832: 1812: 1806: 1805: 1785: 1779: 1778: 1776: 1768: 1762: 1761: 1745: 1739: 1738: 1728: 1718: 1701:(8): 1952–1957. 1686: 1680: 1679: 1677: 1676: 1661: 1652: 1651: 1634:(951): 581–588. 1623: 1617: 1616: 1582: 1576: 1575: 1550:(6): 1164–1176. 1539: 1533: 1532: 1512: 1506: 1505: 1503: 1502: 1488: 1479: 1478: 1460: 1454: 1453: 1451: 1427: 1421: 1420: 1410: 1378: 1372: 1371: 1369: 1368: 1361:Pacific Standard 1351: 1345: 1344: 1310: 1301:(5): 1553–1565. 1290: 1284: 1283: 1281: 1253: 1247: 1246: 1234: 1224: 1218: 1217: 1215: 1214: 1200: 1194: 1193: 1191: 1189: 1154: 1148: 1147: 1131: 1125: 1118: 1112: 1111: 1075: 1066: 1065: 1045: 1036: 1035: 1033: 1018: 1009: 1003: 1002: 1000: 999: 989: 983: 982: 964: 958: 953: 947: 946: 922: 909: 900: 899: 897: 873: 813:Irruptive growth 538: 536: 535: 530: 504: 503: 491: 490: 281:Local population 219: 65: 59: 53: 47: 41: 21: 4196: 4195: 4191: 4190: 4189: 4187: 4186: 4185: 4161: 4160: 4159: 4154: 4145: 4131:Systems ecology 4019: 3990:Extinction debt 3955:Ecological debt 3945:Bioluminescence 3926: 3919: 3888:marine habitats 3863:Ecological trap 3844: 3724: 3717: 3660: 3654: 3610:Rapoport's rule 3605:Priority effect 3546:Endemic species 3514: 3473:Population size 3389: 3382: 3372: 3342: 3337: 3290: 3284: 3270:Trophic cascade 3180:Bioaccumulation 3163: 3090: 3047: 2969: 2936: 2833: 2745: 2706:Ecosystem model 2639: 2625: 2595: 2590: 2581:Natural history 2564:Applied ecology 2542: 2538:Systems ecology 2499: 2495:Thermal ecology 2490:Spatial ecology 2465:Genetic ecology 2435:Disease ecology 2411: 2367:biogeographical 2357: 2320: 2279: 2256: 2228: 2223: 2156: 2127: 2105: 2084: 2064:(6706): 41–49. 2055: 2018: 1997: 1991: 1970: 1967: 1928: 1925: 1923:Further reading 1920: 1903: 1902: 1898: 1891: 1876: 1875: 1871: 1850:(6706): 41–49. 1841: 1840: 1836: 1829: 1814: 1813: 1809: 1787: 1786: 1782: 1774: 1770: 1769: 1765: 1747: 1746: 1742: 1688: 1687: 1683: 1674: 1672: 1669:Eco-intelligent 1663: 1662: 1655: 1625: 1624: 1620: 1613:book 44254 1597: 1584: 1583: 1579: 1564:10.2307/1938230 1541: 1540: 1536: 1529: 1514: 1513: 1509: 1500: 1498: 1490: 1489: 1482: 1475: 1462: 1461: 1457: 1429: 1428: 1424: 1380: 1379: 1375: 1366: 1364: 1353: 1352: 1348: 1325:10.1890/15-1295 1292: 1291: 1287: 1255: 1254: 1250: 1243: 1226: 1225: 1221: 1212: 1210: 1202: 1201: 1197: 1187: 1185: 1169:(29): 290–300. 1156: 1155: 1151: 1133: 1132: 1128: 1119: 1115: 1077: 1076: 1069: 1062: 1047: 1046: 1039: 1031: 1016: 1011: 1010: 1006: 997: 995: 991: 990: 986: 979: 966: 965: 961: 954: 950: 935: 913:Odum, Eugene P. 911: 910: 903: 875: 874: 870: 866: 799: 768: 739: 733: 714: 708: 699: 687: 675: 670: 668:Trophic cascade 664: 651: 632:In contrast, a 607: 596: 590: 545: 495: 482: 477: 476: 474: 434: 428: 422: 403: 355:ceteris paribus 331: 325: 202: 142: 67: 63: 61: 57: 55: 51: 49: 45: 43: 39: 28: 23: 22: 15: 12: 11: 5: 4194: 4192: 4184: 4183: 4178: 4173: 4163: 4162: 4156: 4155: 4150: 4147: 4146: 4144: 4143: 4138: 4133: 4128: 4123: 4118: 4113: 4111:Microecosystem 4108: 4103: 4098: 4093: 4088: 4083: 4078: 4073: 4068: 4063: 4058: 4053: 4048: 4043: 4038: 4033: 4027: 4025: 4021: 4020: 4018: 4017: 4012: 4010:Thorson's rule 4007: 4002: 3997: 3992: 3987: 3982: 3977: 3972: 3967: 3962: 3957: 3952: 3947: 3942: 3937: 3935:Assembly rules 3931: 3929: 3921: 3920: 3918: 3917: 3912: 3907: 3902: 3897: 3892: 3891: 3890: 3880: 3875: 3870: 3865: 3860: 3854: 3852: 3846: 3845: 3843: 3842: 3837: 3832: 3820: 3818:Patch dynamics 3815: 3813:Metapopulation 3810: 3805: 3800: 3795: 3790: 3785: 3780: 3775: 3770: 3765: 3760: 3755: 3750: 3745: 3740: 3735: 3729: 3727: 3719: 3718: 3716: 3715: 3710: 3708:Storage effect 3705: 3700: 3695: 3690: 3685: 3680: 3675: 3670: 3664: 3662: 3656: 3655: 3653: 3652: 3647: 3642: 3637: 3632: 3627: 3622: 3617: 3612: 3607: 3602: 3597: 3592: 3590:Neutral theory 3587: 3582: 3577: 3575:Native species 3568: 3563: 3558: 3553: 3548: 3543: 3538: 3533: 3528: 3522: 3520: 3516: 3515: 3513: 3512: 3507: 3506: 3505: 3500: 3490: 3485: 3480: 3475: 3470: 3465: 3460: 3455: 3450: 3448:Overpopulation 3445: 3440: 3435: 3430: 3425: 3420: 3415: 3410: 3405: 3400: 3394: 3392: 3384: 3383: 3373: 3371: 3370: 3363: 3356: 3348: 3339: 3338: 3336: 3335: 3330: 3325: 3320: 3315: 3310: 3305: 3300: 3294: 3292: 3286: 3285: 3283: 3282: 3277: 3272: 3267: 3262: 3257: 3255:Nutrient cycle 3252: 3247: 3245:Feeding frenzy 3242: 3237: 3232: 3227: 3225:Energy quality 3222: 3217: 3212: 3207: 3202: 3197: 3192: 3187: 3185:Cascade effect 3182: 3177: 3171: 3169: 3165: 3164: 3162: 3161: 3160: 3159: 3154: 3149: 3144: 3139: 3134: 3129: 3119: 3114: 3109: 3104: 3098: 3096: 3092: 3091: 3089: 3088: 3083: 3078: 3073: 3068: 3063: 3057: 3055: 3049: 3048: 3046: 3045: 3040: 3035: 3030: 3028:Microbial loop 3025: 3020: 3015: 3010: 3005: 3000: 2995: 2993:Lithoautotroph 2990: 2985: 2979: 2977: 2975:Microorganisms 2971: 2970: 2968: 2967: 2962: 2957: 2952: 2946: 2944: 2938: 2937: 2935: 2934: 2932:Prey switching 2929: 2924: 2919: 2914: 2909: 2904: 2899: 2894: 2889: 2884: 2879: 2874: 2869: 2864: 2859: 2854: 2849: 2843: 2841: 2835: 2834: 2832: 2831: 2826: 2821: 2816: 2811: 2809:Photosynthesis 2806: 2801: 2796: 2791: 2786: 2781: 2776: 2771: 2766: 2764:Chemosynthesis 2761: 2755: 2753: 2747: 2746: 2744: 2743: 2738: 2733: 2728: 2723: 2718: 2713: 2708: 2703: 2698: 2693: 2688: 2683: 2678: 2673: 2668: 2663: 2658: 2656:Abiotic stress 2653: 2647: 2645: 2641: 2640: 2626: 2624: 2623: 2616: 2609: 2601: 2592: 2591: 2589: 2588: 2583: 2578: 2573: 2572: 2571: 2561: 2556: 2550: 2548: 2544: 2543: 2541: 2540: 2535: 2530: 2525: 2520: 2515: 2509: 2507: 2501: 2500: 2498: 2497: 2492: 2487: 2485:Social ecology 2482: 2477: 2472: 2467: 2462: 2457: 2452: 2447: 2442: 2437: 2432: 2427: 2421: 2419: 2413: 2412: 2410: 2409: 2404: 2399: 2394: 2392:Forest ecology 2389: 2387:Desert ecology 2384: 2383: 2382: 2380:Arctic ecology 2371: 2369: 2359: 2358: 2356: 2355: 2350: 2348:Insect ecology 2345: 2340: 2334: 2332: 2322: 2321: 2319: 2318: 2317: 2316: 2311: 2306: 2296: 2290: 2288: 2281: 2280: 2278: 2277: 2272: 2266: 2264: 2258: 2257: 2255: 2254: 2249: 2244: 2238: 2236: 2230: 2229: 2224: 2222: 2221: 2214: 2207: 2199: 2193: 2192: 2154: 2136:(3): 692–716. 2125: 2103: 2093:(3): 584–588. 2082: 2053: 2016: 2006:(4): 782–798. 1995: 1989: 1966: 1963: 1962: 1961: 1956:10.1002/pan3.8 1924: 1921: 1919: 1918: 1896: 1889: 1869: 1834: 1827: 1807: 1796:(3): 237–240. 1780: 1763: 1740: 1681: 1653: 1640:10.1086/282798 1618: 1595: 1577: 1534: 1527: 1507: 1480: 1473: 1455: 1442:(5): 3048–62. 1422: 1373: 1346: 1285: 1248: 1242:978-0471508830 1241: 1219: 1195: 1149: 1126: 1113: 1067: 1060: 1037: 1004: 984: 977: 959: 948: 933: 901: 867: 865: 862: 861: 860: 855: 850: 845: 840: 835: 830: 825: 823:Overpopulation 820: 815: 810: 805: 798: 795: 767: 764: 743:metapopulation 737:Metapopulation 735:Main article: 732: 731:Metapopulation 729: 710:Main article: 707: 704: 698: 695: 686: 683: 674: 671: 666:Main article: 663: 660: 650: 647: 597: 592:Main article: 589: 586: 582:nature reserve 543: 528: 525: 522: 519: 516: 513: 510: 507: 502: 498: 494: 489: 485: 472: 466: 465: 459: 453: 424:Main article: 421: 418: 402: 399: 379:F. J. Richards 327:Main article: 324: 321: 318: 317: 314: 308: 307: 304: 298: 297: 294: 288: 287: 283: 277: 276: 273: 267: 266: 263: 257: 256: 253: 247: 246: 243: 241:Metapopulation 237: 236: 233: 227: 226: 223: 201: 198: 141: 138: 126:mathematicians 62: 60: Decrease 56: 50: 44: 38: 26: 24: 14: 13: 10: 9: 6: 4: 3: 2: 4193: 4182: 4179: 4177: 4174: 4172: 4169: 4168: 4166: 4153: 4148: 4142: 4139: 4137: 4136:Urban ecology 4134: 4132: 4129: 4127: 4124: 4122: 4119: 4117: 4114: 4112: 4109: 4107: 4104: 4102: 4099: 4097: 4094: 4092: 4089: 4087: 4084: 4082: 4079: 4077: 4074: 4072: 4069: 4067: 4064: 4062: 4059: 4057: 4054: 4052: 4049: 4047: 4044: 4042: 4039: 4037: 4034: 4032: 4029: 4028: 4026: 4022: 4016: 4013: 4011: 4008: 4006: 4003: 4001: 3998: 3996: 3995:Kleiber's law 3993: 3991: 3988: 3986: 3983: 3981: 3978: 3976: 3973: 3971: 3968: 3966: 3963: 3961: 3958: 3956: 3953: 3951: 3948: 3946: 3943: 3941: 3938: 3936: 3933: 3932: 3930: 3928: 3922: 3916: 3913: 3911: 3908: 3906: 3903: 3901: 3898: 3896: 3893: 3889: 3886: 3885: 3884: 3881: 3879: 3876: 3874: 3871: 3869: 3866: 3864: 3861: 3859: 3856: 3855: 3853: 3851: 3847: 3841: 3838: 3836: 3833: 3831: 3829: 3825: 3821: 3819: 3816: 3814: 3811: 3809: 3806: 3804: 3801: 3799: 3796: 3794: 3791: 3789: 3786: 3784: 3781: 3779: 3776: 3774: 3771: 3769: 3768:Foster's rule 3766: 3764: 3761: 3759: 3756: 3754: 3751: 3749: 3746: 3744: 3741: 3739: 3736: 3734: 3731: 3730: 3728: 3726: 3720: 3714: 3711: 3709: 3706: 3704: 3701: 3699: 3696: 3694: 3691: 3689: 3686: 3684: 3681: 3679: 3676: 3674: 3671: 3669: 3666: 3665: 3663: 3657: 3651: 3648: 3646: 3643: 3641: 3638: 3636: 3633: 3631: 3628: 3626: 3623: 3621: 3618: 3616: 3613: 3611: 3608: 3606: 3603: 3601: 3598: 3596: 3593: 3591: 3588: 3586: 3583: 3581: 3578: 3576: 3572: 3569: 3567: 3564: 3562: 3559: 3557: 3554: 3552: 3549: 3547: 3544: 3542: 3539: 3537: 3534: 3532: 3529: 3527: 3524: 3523: 3521: 3517: 3511: 3508: 3504: 3501: 3499: 3496: 3495: 3494: 3491: 3489: 3486: 3484: 3481: 3479: 3476: 3474: 3471: 3469: 3466: 3464: 3461: 3459: 3456: 3454: 3451: 3449: 3446: 3444: 3441: 3439: 3436: 3434: 3431: 3429: 3426: 3424: 3421: 3419: 3416: 3414: 3411: 3409: 3406: 3404: 3401: 3399: 3396: 3395: 3393: 3391: 3385: 3380: 3376: 3369: 3364: 3362: 3357: 3355: 3350: 3349: 3346: 3334: 3331: 3329: 3326: 3324: 3321: 3319: 3316: 3314: 3311: 3309: 3306: 3304: 3301: 3299: 3296: 3295: 3293: 3287: 3281: 3278: 3276: 3273: 3271: 3268: 3266: 3263: 3261: 3258: 3256: 3253: 3251: 3248: 3246: 3243: 3241: 3238: 3236: 3233: 3231: 3228: 3226: 3223: 3221: 3218: 3216: 3213: 3211: 3208: 3206: 3203: 3201: 3198: 3196: 3193: 3191: 3188: 3186: 3183: 3181: 3178: 3176: 3173: 3172: 3170: 3166: 3158: 3155: 3153: 3150: 3148: 3145: 3143: 3140: 3138: 3135: 3133: 3130: 3128: 3125: 3124: 3123: 3120: 3118: 3115: 3113: 3110: 3108: 3105: 3103: 3100: 3099: 3097: 3093: 3087: 3086:Trophic level 3084: 3082: 3079: 3077: 3074: 3072: 3069: 3067: 3064: 3062: 3059: 3058: 3056: 3054: 3050: 3044: 3043:Phage ecology 3041: 3039: 3036: 3034: 3033:Microbial mat 3031: 3029: 3026: 3024: 3021: 3019: 3016: 3014: 3011: 3009: 3006: 3004: 3001: 2999: 2996: 2994: 2991: 2989: 2988:Bacteriophage 2986: 2984: 2981: 2980: 2978: 2976: 2972: 2966: 2963: 2961: 2958: 2956: 2955:Decomposition 2953: 2951: 2948: 2947: 2945: 2943: 2939: 2933: 2930: 2928: 2925: 2923: 2920: 2918: 2915: 2913: 2910: 2908: 2905: 2903: 2902:Mesopredators 2900: 2898: 2895: 2893: 2890: 2888: 2885: 2883: 2880: 2878: 2875: 2873: 2870: 2868: 2865: 2863: 2860: 2858: 2855: 2853: 2850: 2848: 2847:Apex predator 2845: 2844: 2842: 2840: 2836: 2830: 2827: 2825: 2822: 2820: 2817: 2815: 2812: 2810: 2807: 2805: 2802: 2800: 2797: 2795: 2792: 2790: 2787: 2785: 2782: 2780: 2777: 2775: 2772: 2770: 2767: 2765: 2762: 2760: 2757: 2756: 2754: 2752: 2748: 2742: 2739: 2737: 2734: 2732: 2729: 2727: 2724: 2722: 2719: 2717: 2714: 2712: 2709: 2707: 2704: 2702: 2699: 2697: 2694: 2692: 2689: 2687: 2684: 2682: 2681:Biotic stress 2679: 2677: 2674: 2672: 2669: 2667: 2664: 2662: 2659: 2657: 2654: 2652: 2649: 2648: 2646: 2642: 2637: 2633: 2629: 2622: 2617: 2615: 2610: 2608: 2603: 2602: 2599: 2587: 2584: 2582: 2579: 2577: 2574: 2570: 2567: 2566: 2565: 2562: 2560: 2557: 2555: 2552: 2551: 2549: 2545: 2539: 2536: 2534: 2531: 2529: 2526: 2524: 2521: 2519: 2516: 2514: 2511: 2510: 2508: 2506: 2502: 2496: 2493: 2491: 2488: 2486: 2483: 2481: 2478: 2476: 2473: 2471: 2468: 2466: 2463: 2461: 2458: 2456: 2453: 2451: 2448: 2446: 2445:Ecotoxicology 2443: 2441: 2440:Ecophysiology 2438: 2436: 2433: 2431: 2428: 2426: 2423: 2422: 2420: 2418: 2414: 2408: 2407:Urban ecology 2405: 2403: 2400: 2398: 2395: 2393: 2390: 2388: 2385: 2381: 2378: 2377: 2376: 2375:Polar ecology 2373: 2372: 2370: 2368: 2364: 2360: 2354: 2353:Human ecology 2351: 2349: 2346: 2344: 2343:Plant ecology 2341: 2339: 2336: 2335: 2333: 2331: 2327: 2323: 2315: 2312: 2310: 2307: 2305: 2302: 2301: 2300: 2297: 2295: 2292: 2291: 2289: 2286: 2282: 2276: 2273: 2271: 2268: 2267: 2265: 2263: 2262:Spatial scale 2259: 2253: 2250: 2248: 2245: 2243: 2242:Field ecology 2240: 2239: 2237: 2235: 2231: 2227: 2220: 2215: 2213: 2208: 2206: 2201: 2200: 2197: 2189: 2185: 2181: 2177: 2173: 2169: 2165: 2161: 2155: 2151: 2147: 2143: 2139: 2135: 2131: 2126: 2122: 2118: 2114: 2110: 2104: 2100: 2096: 2092: 2088: 2083: 2079: 2078:10.1038/23876 2075: 2071: 2067: 2063: 2059: 2054: 2050: 2046: 2042: 2038: 2034: 2030: 2026: 2022: 2017: 2013: 2009: 2005: 2001: 1996: 1992: 1986: 1982: 1978: 1974: 1969: 1968: 1964: 1957: 1952: 1948: 1944: 1940: 1936: 1932: 1927: 1926: 1922: 1914: 1910: 1906: 1900: 1897: 1892: 1886: 1882: 1881: 1873: 1870: 1865: 1864:10.1038/23876 1861: 1857: 1853: 1849: 1845: 1838: 1835: 1830: 1824: 1820: 1819: 1811: 1808: 1803: 1799: 1795: 1791: 1784: 1781: 1773: 1767: 1764: 1759: 1755: 1751: 1744: 1741: 1736: 1732: 1727: 1722: 1717: 1712: 1708: 1704: 1700: 1696: 1692: 1685: 1682: 1670: 1666: 1660: 1658: 1654: 1649: 1645: 1641: 1637: 1633: 1629: 1622: 1619: 1614: 1610: 1606: 1602: 1598: 1592: 1588: 1581: 1578: 1573: 1569: 1565: 1561: 1557: 1553: 1549: 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816: 814: 811: 809: 806: 804: 801: 800: 796: 794: 792: 791: 786: 785: 779: 777: 773: 765: 763: 759: 757: 756:rescue effect 750: 746: 744: 738: 730: 728: 725: 722: 718: 713: 705: 703: 696: 694: 690: 684: 682: 678: 672: 669: 661: 659: 655: 648: 646: 643: 639: 635: 630: 628: 624: 620: 615: 612: 611:r/K selection 605: 603: 595: 594:r/K selection 588:r/K selection 587: 585: 583: 579: 575: 570: 566: 563: 561: 557: 553: 549: 542: 526: 523: 520: 517: 514: 511: 508: 505: 500: 496: 492: 487: 483: 471: 463: 460: 457: 454: 451: 447: 446: 445: 443: 439: 433: 427: 419: 417: 415: 410: 406: 400: 398: 396: 392: 388: 384: 383:Simon Hopkins 380: 375: 373: 369: 365: 361: 360:exponentially 357: 356: 351: 347: 342: 340: 336: 330: 322: 315: 313: 310: 309: 305: 303: 300: 299: 295: 293: 292:Subpopulation 290: 284: 282: 279: 274: 272: 269: 264: 262: 259: 254: 252: 249: 244: 242: 239: 234: 232: 229: 224: 220: 214: 210: 206: 199: 197: 195: 191: 187: 183: 179: 175: 171: 167: 163: 159: 155: 151: 150:Ancient Greek 147: 139: 137: 135: 131: 130:statisticians 127: 123: 119: 115: 111: 106: 104: 100: 96: 92: 88: 84: 81: 77: 73: 66: No data 37: 32: 19: 4121:Regime shift 4106:Macroecology 3827: 3823: 3763:Edge effects 3733:Biogeography 3678:Commensalism 3526:Biodiversity 3403:Allee effect 3387: 3142:kelp forests 3095:Example webs 2960:Detritivores 2799:Organotrophs 2779:Kinetotrophs 2731:Productivity 2586:Biogeography 2480:Paleoecology 2455:Fire ecology 2397:Soil ecology 2303: 2285:Organisation 2275:Macroecology 2270:Microecology 2166:(1): 85–93. 2163: 2159: 2133: 2129: 2112: 2108: 2090: 2086: 2061: 2057: 2024: 2020: 2003: 1999: 1972: 1965:Bibliography 1941:(1): 31–43. 1938: 1934: 1899: 1879: 1872: 1847: 1843: 1837: 1817: 1810: 1793: 1789: 1783: 1766: 1757: 1753: 1743: 1698: 1694: 1684: 1673:. Retrieved 1671:. 2018-04-26 1668: 1631: 1627: 1621: 1605:j.ctt19cc1t2 1586: 1580: 1547: 1543: 1537: 1517: 1510: 1499:. Retrieved 1496:www2.nau.edu 1495: 1464: 1458: 1439: 1435: 1425: 1390: 1386: 1376: 1365:. Retrieved 1359: 1349: 1298: 1294: 1288: 1269: 1265: 1251: 1230: 1222: 1211:. Retrieved 1208:Khan Academy 1207: 1198: 1186:. Retrieved 1166: 1162: 1152: 1143: 1139: 1129: 1116: 1086:(1): 17–26. 1083: 1079: 1050: 1029:the original 1024: 1020: 1007: 996:. Retrieved 987: 968: 962: 951: 918: 885: 881: 871: 788: 782: 780: 775: 771: 769: 760: 752: 748: 740: 726: 723: 719: 715: 700: 691: 688: 679: 676: 656: 652: 637: 633: 631: 626: 622: 618: 616: 608: 599: 571: 567: 564: 559: 555: 551: 547: 540: 469: 467: 448:Natality or 435: 411: 407: 404: 376: 353: 343: 332: 311: 301: 291: 280: 270: 260: 250: 240: 230: 211: 207: 203: 173: 165: 157: 143: 132:who work in 107: 71: 70: 3758:Disturbance 3661:interaction 3483:Recruitment 3413:Depensation 3205:Copiotrophs 3076:Energy flow 2998:Lithotrophy 2942:Decomposers 2922:Planktivore 2897:Insectivore 2887:Heterotroph 2852:Bacterivore 2819:Phototrophs 2769:Chemotrophs 2741:Restoration 2691:Competition 2513:Agroecology 2234:Methodology 1256:Finley, C; 1188:16 November 888:(1): 3–20. 364:demographic 302:Immigration 261:Aggregation 225:Definition 200:Terminology 186:Eugene Odum 178:life cycles 99:immigration 95:death rates 87:environment 83:populations 4181:Population 4165:Categories 4126:Sexecology 3703:Parasitism 3668:Antibiosis 3503:Resistance 3498:Resilience 3388:Population 3308:Camouflage 3260:Oligotroph 3175:Ascendency 3137:intertidal 3127:cold seeps 3081:Food chain 2882:Herbivores 2857:Carnivores 2784:Mixotrophs 2759:Autotrophs 2638:components 2299:Synecology 2294:Autecology 1675:2021-12-08 1501:2021-12-08 1367:2023-08-20 1308:1603.04518 1258:Oreskes, N 1213:2021-12-08 1146:: 113–121. 998:2021-12-08 864:References 450:birth rate 430:See also: 339:demography 312:Emigration 251:Population 160:, "self"; 146:synecology 103:emigration 89:, such as 4031:Allometry 3985:Emergence 3713:Symbiosis 3698:Mutualism 3493:Stability 3398:Abundance 3210:Dominance 3168:Processes 3157:tide pool 3053:Food webs 2927:Predation 2912:Omnivores 2839:Consumers 2794:Mycotroph 2751:Producers 2696:Ecosystem 2661:Behaviour 2160:Oecologia 1760:(10): 18. 642:resources 524:− 512:− 462:Mortality 438:fisheries 194:ecosystem 182:behaviour 97:, and by 36:jellyfish 4086:Endolith 4015:Xerosere 3927:networks 3743:Ecocline 3289:Defense, 2965:Detritus 2867:Foraging 2736:Resource 2576:Ecosophy 2326:Taxonomy 2287:or scope 2188:15586292 2150:21070586 1735:28167770 1648:83947445 1417:23949368 1333:27755756 1260:(2013). 1183:23686557 1108:27090414 915:(1959). 797:See also 766:Journals 602:resource 4076:Ecopath 3883:Habitat 3753:Ecotype 3748:Ecotone 3725:ecology 3723:Spatial 3659:Species 3519:Species 3390:ecology 3375:Ecology 3323:Mimicry 3291:counter 3235:f-ratio 2983:Archaea 2671:Biomass 2644:General 2636:Trophic 2628:Ecology 2168:Bibcode 2109:Science 2099:4163726 2066:Bibcode 2029:Bibcode 1943:Bibcode 1852:Bibcode 1726:5338359 1703:Bibcode 1572:1938230 1552:Bibcode 1544:Ecology 1408:3758828 1341:1279459 1313:Bibcode 1088:Bibcode 346:Malthus 140:History 122:biology 118:habitat 80:species 76:ecology 3107:Rivers 3003:Marine 2186:  2148:  2097:  2058:Nature 2049:692692 2047:  2021:Nature 1987:  1887:  1844:Nature 1825:  1733:  1723:  1646:  1611:  1603:  1593:  1570:  1525:  1471:  1415:  1405:  1339:  1331:  1239:  1181:  1106:  1058:  975:  943:554879 941:  931:  578:refuge 539:where 64:  58:  52:  46:  40:  4024:Other 3925:Other 3878:Guild 3850:Niche 3102:Lakes 2547:Other 2363:Biome 2330:taxon 2095:JSTOR 1775:(PDF) 1644:S2CID 1601:JSTOR 1568:JSTOR 1337:S2CID 1303:arXiv 1179:JSTOR 1104:S2CID 1080:Oikos 1032:(PDF) 1017:(PDF) 790:Oikos 222:Term 174:lógos 170:λόγος 166:oíkos 162:οίκος 91:birth 3112:Soil 2184:PMID 2146:PMID 2045:PMID 1985:ISBN 1885:ISBN 1823:ISBN 1731:PMID 1591:ISBN 1523:ISBN 1469:ISBN 1413:PMID 1329:PMID 1237:ISBN 1190:2020 1056:ISBN 973:ISBN 939:OCLC 929:ISBN 440:and 370:and 271:Deme 192:and 180:and 158:aúto 154:αὐτο 128:and 101:and 93:and 2365:or 2328:or 2176:doi 2164:143 2138:doi 2117:doi 2113:203 2091:108 2074:doi 2062:396 2037:doi 2025:275 2008:doi 1977:doi 1951:doi 1909:doi 1860:doi 1848:396 1798:doi 1721:PMC 1711:doi 1699:114 1636:doi 1632:106 1560:doi 1444:doi 1403:PMC 1395:doi 1321:doi 1274:doi 1171:doi 1096:doi 925:546 890:doi 886:690 468:If 436:In 4167:: 3573:/ 3377:: 2634:: 2630:: 2182:. 2174:. 2162:. 2144:. 2134:86 2132:. 2111:. 2089:. 2072:. 2060:. 2043:. 2035:. 2023:. 2004:82 2002:. 1983:. 1949:. 1937:. 1933:. 1858:. 1846:. 1794:15 1792:. 1756:. 1752:. 1729:. 1719:. 1709:. 1697:. 1693:. 1667:. 1656:^ 1642:. 1630:. 1607:. 1599:. 1566:. 1558:. 1548:59 1546:. 1494:. 1483:^ 1440:37 1438:. 1434:. 1411:. 1401:. 1391:39 1389:. 1385:. 1358:. 1335:. 1327:. 1319:. 1311:. 1299:26 1297:. 1270:70 1268:. 1264:. 1206:. 1177:. 1167:10 1165:. 1161:. 1144:10 1142:. 1138:. 1102:. 1094:. 1084:94 1082:. 1070:^ 1040:^ 1025:23 1023:. 1019:. 937:. 927:. 904:^ 884:. 880:. 787:, 397:. 172:, 164:, 156:, 152:: 136:. 105:. 3828:K 3826:/ 3824:r 3367:e 3360:t 3353:v 2620:e 2613:t 2606:v 2218:e 2211:t 2204:v 2190:. 2178:: 2170:: 2152:. 2140:: 2123:. 2119:: 2101:. 2080:. 2076:: 2068:: 2051:. 2039:: 2031:: 2014:. 2010:: 1993:. 1979:: 1959:. 1953:: 1945:: 1939:1 1915:. 1911:: 1893:. 1866:. 1862:: 1854:: 1831:. 1804:. 1800:: 1777:. 1758:3 1737:. 1713:: 1705:: 1678:. 1650:. 1638:: 1615:. 1574:. 1562:: 1554:: 1531:. 1504:. 1477:. 1452:. 1446:: 1419:. 1397:: 1370:. 1343:. 1323:: 1315:: 1305:: 1282:. 1276:: 1245:. 1216:. 1192:. 1173:: 1110:. 1098:: 1090:: 1064:. 1001:. 981:. 945:. 898:. 892:: 638:K 634:K 627:r 623:K 619:r 560:E 556:I 552:D 548:B 544:0 541:N 527:E 521:I 518:+ 515:D 509:B 506:+ 501:0 497:N 493:= 488:1 484:N 473:1 470:N 20:)

Index

Population Ecology

jellyfish
ecology
species
populations
environment
birth
death rates
immigration
emigration
conservation biology
population viability analysis
habitat
biology
mathematicians
statisticians
population dynamics
synecology
Ancient Greek
αὐτο
οίκος
λόγος
life cycles
behaviour
Eugene Odum
community ecology
ecosystem
Population dynamics
population dynamics

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