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Intraspecific competition

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739: 82:). However, a population can only grow to a very limited number within an environment. The carrying capacity, defined by the variable k, of an environment is the maximum number of individuals or species an environment can sustain and support over a longer period of time. The resources within an environment are limited, and are not endless. An environment can only support a certain number of individuals before its resources completely diminish. Numbers larger than this will suffer a negative population growth until eventually reaching the carrying capacity, whereas populations smaller than the carrying capacity will grow until they reach it. 135: 339: 20: 150:) have evolved varying levels of aggression depending on the intensity of intraspecific competition. In populations where the resources are scarcer, more aggressive behaviours are likely to evolve. It is a more effective strategy to fight rivals within the species harder instead of searching for other options due to the lack of available food. More aggressive salamanders are more likely obtain the resources they require to reproduce whereas timid salamanders may starve before reproducing, so aggression can 265:) have different energy intakes based on their ranking within the group. Both males and females compete for territories with the best access to food and the most successful monkeys are able to obtain a disproportionately large quantity of food and therefore have a higher fitness in comparison to the subordinate members of the group. In the case of 325:. For instance, the caterpillars of cinnabar moths feed via scramble competition, and when there are too many caterpillars competing very few are able to pupate and there is a large population crash. Subsequently, very few cinnabar moths are competing intraspecifically in the next generation so the population grows rapidly before crashing again. 165:) found that birds in a bond were much more aggressive than single birds. The paired birds were significantly more likely to start an agonistic encounter in defense of their mate or young whereas single birds were typically non-breeding and less likely to fight. Not all flamingos can mate in the population because of an unsuitable 296:
is very uneven between males. The reproductive success of most males is zero; they die before breeding age or are prevented from mating by higher ranked males. In addition, just a few dominant males account for the majority of copulations. The potential reproductive success for males is so great that
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In stationary organisms, such as plants, exploitative competition plays a much larger role than interference competition because individuals are rooted to a specific area and utilise resources in their immediate surroundings. Saplings will compete for light, most of which will be blocked and utilised
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grown in test tubes initially grew exponentially. But as resources became scarcer, their growth rates slowed until reaching the carrying capacity. If the populations were moved to a larger container with more resources they would continue to grow until reaching their new carrying capacity. The shape
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Contest competition produces relatively stable population dynamics. The uneven distribution of resources results in some individuals dying off but helps to ensure that the members of the population that hold a territory can reproduce. As the number of territories in an area stays the same over time,
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The major impact of intraspecific competition is reduced population growth rates as population density increases. When resources are infinite, intraspecific competition does not occur and populations can grow exponentially. Exponential population growth is exceedingly rare, but has been documented,
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The logistic growth curve is initially very similar to the exponential growth curve. When population density is low, individuals are free from competition and can grow rapidly. However, as the population reaches its maximum (the carrying capacity), intraspecific competition becomes fiercer and the
196:). Both increasing the density of young spiders and reducing the available food supply lowered the growth of individual spiders. Food is clearly a limiting resource for the wolf spiders but there was no direct competition between juveniles for food, just a reduction in fitness due to the increased 316:
involves a more equal distribution of resources than contest competition and occurs when there is a common resource pool that an individual cannot be excluded from. For instance, grazing animals compete more strongly for grass as their population grows and food becomes a limiting resource. Each
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Apparent competition occurs in populations that are predated upon. An increase in population of the prey species will bring more predators to the area, which increases the risk of an individual being eaten and hence lowers its survivorship. Like exploitative competition, the individuals aren’t
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which then excludes other animals from entering the area. There may not be an actual conflict between the two competitors, but the animal excluded from the territory suffers a fitness loss due to a reduced foraging area and is unable to enter the area as it risks confrontation from a more
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When resources are limited, an increase in population size reduces the quantity of resources available for each individual, reducing the per capita fitness in the population. As a result, the growth rate of a population slows as intraspecific competition becomes more intense, making it a
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Aggressive encounters are potentially costly for individuals as they can get injured and be less able to reproduce. As a result, many species have evolved forms of ritualised combat to determine who wins access to a resource without having to undertake a dangerous fight. Male adders
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by taller trees. The saplings can be easily out-competed by larger members of their own species, which is one of the reasons why seed dispersal distances can be so large. Seeds that germinate in close proximity to the parents are very likely to be out-competed and die.
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and contest competition. Scramble competition involves a relatively even distribution of resources among a population as all individuals exploit a common resource pool. In contrast, contest competition is the uneven distribution of resources and occurs when
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interacting directly but rather suffer a reduction in fitness as a consequence of the increasing population size. Apparent competition is generally associated with inter rather than intraspecific competition, whereby two different species share a common
224:. An adaptation that makes one species less likely to be eaten results in a reduction in fitness for the other prey species because the predator species hunts more intensely as food has become more difficult to obtain. For example, native skinks ( 516:
per capita growth rate slows until the population reaches a stable size. At the carrying capacity, the rate of change of population density is zero because the population is as large as possible based on the resources available. Experiments on
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Scramble completion can lead to unstable population dynamics, the equal division of resources can result in very few of the organisms obtaining enough to survive and reproduce and this can cause population crashes. This phenomenon is called
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which is required for survival or reproduction. The resource must be limited for competition to occur; if every member of the species can obtain a sufficient amount of every resource then individuals do not compete and the population
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The logistic growth equation is an effective tool for modelling intraspecific competition despite its simplicity, and has been used to model many real biological systems. At low population densities,
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or some dominant flamingos mating with multiple partners. Mates are a fiercely contested resource in many species as the production of offspring is essential for an individual to propagate its genes.
200:. The negative density dependence in young wolf spiders is evident: as the population density increases further, growth rates continues to fall and could potentially reach zero (as predicted by the 62:. Prolonged exponential growth is rare in nature because resources are finite and so not every individual in a population can survive, leading to intraspecific competition for the scarce resources. 641: 85:
Intraspecific competition does not just involve direct interactions between members of the same species (such as male deer locking horns when competing for mates) but can also include
131:. As organisms are encountering each other during interference competition, they are able to evolve behavioural strategies and morphologies to out-compete rivals in their population. 829:
Perdue, Bonnie M.; Gaalema, Diann E.; Martin, Allison L.; Dampier, Stephanie M.; Maple, Terry L. (2010-02-22). "Factors affecting aggression in a captive flock of Chilean flamingos (
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occurs when members of different species compete for a shared resource. Members of the same species have rather similar requirements for resources, whereas different species have a
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Young, Kim; Ferreira, Van Aarde (March 2009). "The influence of increasing population size and vegetation productivity on elephant distribution in the Kruger National Park".
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Olsson, Mats; Schwartz, Tonia; Uller, Tobias; Healey, Mo (February 2009). "Effects of sperm storage and male colour on probability of paternity in a polychromatic lizard".
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Contest competition takes place when a resource is associated with a territory or hierarchical structure within the population. For instance: white-faced capuchin monkeys (
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where an individual depletes a shared resource (such as a grizzly bear catching a salmon that can then no longer be eaten by bears at different points along a river).
283:) undertake complex ritualised confrontations when courting females. Generally, the larger male will win and fights rarely escalate to injury to either combatant. 950:
Norbury, Grant (December 2001). "Conserving dryland lizards by reducing predator-mediated apparent competition and direct competition with introduced rabbits".
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or at the top of the hierarchies obtain a sufficient quantity of the resources, whereas individuals without a territory don’t obtain any of the resource.
292:, engage in fierce competitive displays in an attempt to control a large harem of females with which to mate. The distribution of females and subsequent 496:
Population growth against time in a population growing logistically. The steepest parts of the graph are where the population growth is most rapid.
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Madsen, Thomas; Shine, Richard (1993). "Temporal variability in sexual selection acting on reproductive tactics and body size in male snakes".
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approaches the carrying capacity the second term in the logistic equation becomes smaller, reducing the rate of change of population density.
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Schoener, Thomas (March 1973). "Population growth regulated by intraspecific competition for energy or time: Some simple representations".
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Interference competition is the process by which individuals directly compete with one another in pursuit of a resource. It can involve
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However, sometimes the resource may be so prized that potentially fatal confrontations can occur to acquire them. Male elephant seals,
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as a result. The organisms may not actually come into contact and only interact via the shared resource indirectly.
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variants, red lizards have are more aggressive in defending their territory compared to their yellow counterparts.
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Wise, David; Wagner (August 1992). "Evidence of exploitative competition among young stages of the wolf spider
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population density graph occurred at half the carrying capacity, as predicted by the logistic growth model.
2179: 359:(South Africa) also grew exponentially in the mid-1900s after strict poaching controls were put in place. 178: 86: 74:. The rate of change of population density eventually falls to zero, the point ecologists have termed the 50:, resulting in intraspecific competition generally being a stronger force than interspecific competition. 2536: 1427: 642:"On the prevalence and relative importance of interspecific competition: evidence from field experiments" 181:. Exploitative competition involves individuals depleting a shared resource and both suffering a loss in 70:
process. The falling population growth rate as population increases can be modelled effectively with the
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Male hartebeest locking horns and fiercely defending their territories. An example of direct competition.
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in a population influence the amount of resource each individual receives. Organisms in the most prized
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Crawley, Mick; Gillman (April 1990). "A comparative evaluation of models of cinnabar moth dynamics".
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Vogel, Erin (August 2005). "Rank differences in energy intake rates in white-faced capuchin monkeys,
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growth rates showed a striking adherence to the logistic growth curve. The inflexion point in the
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and so the main determinant for population growth is just the per capita growth rate. However, as
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many are killed before breeding age as they attempt to move up the hierarchy in their population.
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for both individuals, but the more fit individual survives and is able to reproduce. By contrast,
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Flamingos competing via interference competition, potentially for territories, mates or food.
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remains constant which produces a similar number of new individuals every breeding season.
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The way in which resources are partitioned by organisms also varies and can be split into
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herbivore receives less food as more individuals compete for the same quantity of food.
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For instance, exploitative competition has been shown experimentally between juvenile
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Hanson, Floyd (1981). "Logistic growth with random density independent disasters".
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of their growth can be modeled very effectively with the logistic growth model.
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1930s lab experiments showed logistic growth in microorganisms. Populations of
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Individuals can compete for food, water, space, light, mates, or any other
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Exponential human population growth in the last 1,000 years.
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compete for limited resources. This leads to a reduction in
828: 1031: 586: 1201: 367: 1066: 704:"Experimental studies on the struggle for existence" 454: 589:– extreme result of intraspecific competition in 2864: 269:lizards, males compete for territory. Among the 1150: 610: 608: 606: 2061: 1314: 177:Organisms can compete indirectly, either via 1257: 758: 1144: 1111: 733: 731: 729: 697: 695: 693: 691: 689: 687: 685: 603: 2282:Latitudinal gradients in species diversity 2068: 2054: 1321: 1307: 1230: 1060: 943: 916: 867: 633: 142:For example, different populations of the 1195: 1135: 978: 822: 764: 329:Consequences of intraspecific competition 2180:Predator–prey (Lotka–Volterra) equations 1819:Tritrophic interactions in plant defense 1263: 1117: 726: 682: 614: 491: 337: 249: 133: 18: 2212:Random generalized Lotka–Volterra model 989:: the effects of contest competition". 949: 922: 861: 639: 468:= rate of change of population density 120:fighting, stealing or ritualised combat 2865: 2020:Herbivore adaptations to plant defense 1236: 929:. The Blackburn Press. pp. 9–23. 333: 2049: 1302: 984: 737: 701: 16:Species members compete for resources 2035:Predator avoidance in schooling fish 179:exploitative or apparent competition 2485:Intermediate disturbance hypothesis 1124:Integrative and Comparative Biology 991:Behavioral Ecology and Sociobiology 347:most notably in humans since 1900. 13: 2238:Ecological effects of biodiversity 48:smaller contested resource overlap 14: 2884: 1574:Generalist and specialist species 926:Perspectives on Plant Competition 640:Connell, Joseph (November 1983). 129:dominant member of the population 2297:Occupancy–abundance relationship 1224:10.1111/j.1442-9993.2009.01934.x 972:10.1046/j.0021-8901.2001.00685.x 2317:Relative abundance distribution 2030:Plant defense against herbivory 1897:Competitive exclusion principle 1609:Mesopredator release hypothesis 1025: 708:Journal of Experimental Biology 1902:Consumer–resource interactions 1266:Theoretical Population Biology 1239:Theoretical Population Biology 702:Gause, Georgy (October 1932). 582:Female intrasexual competition 438: 432: 412: 406: 383: 377: 34:, whereby members of the same 1: 2748:Biological data visualization 2575:Environmental niche modelling 2302:Population viability analysis 1046:10.1016/j.anbehav.2008.10.017 596: 238:). Both species are eaten by 152:spread through the population 108: 2233:Density-dependent inhibition 1278:10.1016/0040-5809(73)90006-3 1251:10.1016/0040-5809(81)90032-0 68:negatively density dependent 7: 2702:Liebig's law of the minimum 2537:Resource selection function 1428:Metabolic theory of ecology 619:. Wiley. pp. 103–105. 540: 308: 172: 10: 2889: 2602:Niche apportionment models 2322:Relative species abundance 1526:Primary nutritional groups 1423:List of feeding behaviours 952:Journal of Applied Ecology 474:= population size at time 254: 2851: 2783:Ecosystem based fisheries 2725: 2625: 2550: 2423: 2395:Interspecific competition 2360: 2287:Minimum viable population 2220: 2145:Maximum sustainable yield 2130:Intraspecific competition 2125:Effective population size 2088: 2005:Anti-predator adaptations 1990: 1869: 1796: 1753: 1675: 1642: 1539: 1516:Photosynthetic efficiency 1451: 1345: 1118:Le Bouef, Burney (1974). 1003:10.1007/s00265-005-0960-4 765:Nishikawa, Kiisa (1985). 552:Interspecific competition 483:= per capita growth rate 144:northern slimy salamander 113: 44:interspecific competition 28:Intraspecific competition 2773:Ecological stoichiometry 2738:Alternative stable state 923:Connell, Joseph (1990). 831:Phoenicopterus chilensis 204:). This is also seen in 163:Phoenicopterus chilensis 157:In addition, a study on 2873:Biological interactions 2617:Ontogenetic niche shift 2480:Ideal free distribution 2390:Ecological facilitation 2140:Malthusian growth model 2110:Consumer-resource model 1967:Paradox of the plankton 1932:Energy systems language 1652:Chemoorganoheterotrophy 1619:Optimal foraging theory 1594:Heterotrophic nutrition 1069:The American Naturalist 289:Mirounga augustirostris 2763:Ecological forecasting 2707:Marginal value theorem 2505:Landscape epidemiology 2440:Cross-boundary subsidy 2375:Biological interaction 1725:Microbial intelligence 1413:Green world hypothesis 497: 456: 343: 139: 24: 2768:Ecological humanities 2667:Ecological energetics 2612:Niche differentiation 2475:Habitat fragmentation 2243:Ecological extinction 2190:Small population size 1942:Feed conversion ratio 1922:Ecological succession 1854:San Francisco Estuary 1768:Ecological efficiency 1710:Microbial cooperation 617:Essentials of Ecology 547:Competition (biology) 504:is much smaller than 495: 457: 341: 250:Resource partitioning 236:Oryctolagus cuniculus 202:logistic growth model 137: 87:indirect interactions 72:logistic growth model 30:is an interaction in 22: 2793:Evolutionary ecology 2758:Ecological footprint 2753:Ecological economics 2677:Ecological threshold 2672:Ecological indicator 2542:Source–sink dynamics 2495:Land change modeling 2490:Insular biogeography 2342:Species distribution 2081:Modelling ecosystems 1740:Microbial metabolism 1579:Intraguild predation 1368:Biogeochemical cycle 1334:Modelling ecosystems 1137:10.1093/icb/14.1.163 738:Keddy, Paul (2001). 489:= carrying capacity 365: 357:Kruger National Park 314:Scramble competition 294:reproductive success 148:Plethodon glutinosus 2843:Theoretical ecology 2818:Natural environment 2682:Ecosystem diversity 2652:Ecological collapse 2642:Bateman's principle 2597:Limiting similarity 2510:Landscape limnology 2332:Species homogeneity 2170:Population modeling 2165:Population dynamics 1982:Trophic state index 1216:2009AusEc..34..329Y 1165:1990Oecol..82..437G 964:2001JApEc..38.1350N 886:1992Oecol..91....7W 720:10.1242/jeb.9.4.389 649:American Naturalist 334:Slowed growth rates 303:breeding population 60:grows exponentially 2854:Outline of ecology 2803:Industrial ecology 2798:Functional ecology 2662:Ecological deficit 2607:Niche construction 2570:Ecosystem engineer 2347:Species–area curve 2268:Introduced species 2083:: Other components 2015:Deimatic behaviour 1917:Ecological network 1849:North Pacific Gyre 1834:hydrothermal vents 1773:Ecological pyramid 1720:Microbial food web 1531:Primary production 1476:Foundation species 1173:10.1007/BF00319783 894:10.1007/BF00317234 870:Schizocosa ocreata 567:Population ecology 498: 452: 353:Loxodonta africana 344: 267:Ctenophorus pictus 198:population density 194:Schizocosa ocreata 140: 32:population ecology 25: 2860: 2859: 2743:Balance of nature 2500:Landscape ecology 2385:Community ecology 2327:Species diversity 2263:Indicator species 2258:Gradient analysis 2135:Logistic function 2043: 2042: 2000:Animal coloration 1977:Trophic mutualism 1715:Microbial ecology 1506:Photoheterotrophs 1491:Myco-heterotrophy 1403:Ecosystem ecology 1388:Carrying capacity 1353:Abiotic component 847:10.1002/zoo.20313 626:978-1-4051-5658-5 615:Townsend (2008). 572:Sexual dimorphism 445: 395: 355:) populations in 206:Viviparous lizard 159:Chilean flamingos 76:carrying capacity 2880: 2560:Ecological niche 2532:selection theory 2352:Umbrella species 2337:Species richness 2273:Invasive species 2253:Flagship species 2160:Population cycle 2155:Overexploitation 2120:Ecological yield 2070: 2063: 2056: 2047: 2046: 1952:Mesotrophic soil 1892:Climax community 1824:Marine food webs 1763:Biomagnification 1564:Chemoorganotroph 1418:Keystone species 1378:Biotic component 1323: 1316: 1309: 1300: 1299: 1290: 1289: 1261: 1255: 1254: 1234: 1228: 1227: 1199: 1193: 1192: 1148: 1142: 1141: 1139: 1115: 1109: 1108: 1064: 1058: 1057: 1034:Animal Behaviour 1029: 1023: 1022: 982: 976: 975: 958:(6): 1350–1361. 947: 941: 940: 920: 914: 913: 865: 859: 858: 826: 820: 819: 817: 816: 810: 804:. Archived from 780:(6): 1282–1294. 771: 762: 756: 755: 735: 724: 723: 699: 680: 679: 677: 671:. Archived from 646: 637: 631: 630: 612: 577:Sexual selection 461: 459: 458: 453: 451: 447: 446: 441: 427: 396: 394: 386: 369: 323:overcompensation 210:Lacerta vivipara 2888: 2887: 2883: 2882: 2881: 2879: 2878: 2877: 2863: 2862: 2861: 2856: 2847: 2833:Systems ecology 2721: 2692:Extinction debt 2657:Ecological debt 2647:Bioluminescence 2628: 2621: 2590:marine habitats 2565:Ecological trap 2546: 2426: 2419: 2362: 2356: 2312:Rapoport's rule 2307:Priority effect 2248:Endemic species 2216: 2175:Population size 2091: 2084: 2074: 2044: 2039: 1992: 1986: 1972:Trophic cascade 1882:Bioaccumulation 1865: 1792: 1749: 1671: 1638: 1535: 1447: 1408:Ecosystem model 1341: 1327: 1296: 1294: 1293: 1262: 1258: 1235: 1231: 1204:Austral Ecology 1200: 1196: 1149: 1145: 1116: 1112: 1065: 1061: 1030: 1026: 987:Cebus capucinus 983: 979: 948: 944: 937: 921: 917: 866: 862: 827: 823: 814: 812: 808: 786:10.2307/2408785 769: 763: 759: 752: 736: 727: 700: 683: 675: 644: 638: 634: 627: 613: 604: 599: 543: 428: 426: 419: 415: 387: 370: 368: 366: 363: 362: 336: 331: 311: 262:Cebus capucinus 257: 252: 175: 116: 111: 17: 12: 11: 5: 2886: 2876: 2875: 2858: 2857: 2852: 2849: 2848: 2846: 2845: 2840: 2835: 2830: 2825: 2820: 2815: 2813:Microecosystem 2810: 2805: 2800: 2795: 2790: 2785: 2780: 2775: 2770: 2765: 2760: 2755: 2750: 2745: 2740: 2735: 2729: 2727: 2723: 2722: 2720: 2719: 2714: 2712:Thorson's rule 2709: 2704: 2699: 2694: 2689: 2684: 2679: 2674: 2669: 2664: 2659: 2654: 2649: 2644: 2639: 2637:Assembly rules 2633: 2631: 2623: 2622: 2620: 2619: 2614: 2609: 2604: 2599: 2594: 2593: 2592: 2582: 2577: 2572: 2567: 2562: 2556: 2554: 2548: 2547: 2545: 2544: 2539: 2534: 2522: 2520:Patch dynamics 2517: 2515:Metapopulation 2512: 2507: 2502: 2497: 2492: 2487: 2482: 2477: 2472: 2467: 2462: 2457: 2452: 2447: 2442: 2437: 2431: 2429: 2421: 2420: 2418: 2417: 2412: 2410:Storage effect 2407: 2402: 2397: 2392: 2387: 2382: 2377: 2372: 2366: 2364: 2358: 2357: 2355: 2354: 2349: 2344: 2339: 2334: 2329: 2324: 2319: 2314: 2309: 2304: 2299: 2294: 2292:Neutral theory 2289: 2284: 2279: 2277:Native species 2270: 2265: 2260: 2255: 2250: 2245: 2240: 2235: 2230: 2224: 2222: 2218: 2217: 2215: 2214: 2209: 2208: 2207: 2202: 2192: 2187: 2182: 2177: 2172: 2167: 2162: 2157: 2152: 2150:Overpopulation 2147: 2142: 2137: 2132: 2127: 2122: 2117: 2112: 2107: 2102: 2096: 2094: 2086: 2085: 2073: 2072: 2065: 2058: 2050: 2041: 2040: 2038: 2037: 2032: 2027: 2022: 2017: 2012: 2007: 2002: 1996: 1994: 1988: 1987: 1985: 1984: 1979: 1974: 1969: 1964: 1959: 1957:Nutrient cycle 1954: 1949: 1947:Feeding frenzy 1944: 1939: 1934: 1929: 1927:Energy quality 1924: 1919: 1914: 1909: 1904: 1899: 1894: 1889: 1887:Cascade effect 1884: 1879: 1873: 1871: 1867: 1866: 1864: 1863: 1862: 1861: 1856: 1851: 1846: 1841: 1836: 1831: 1821: 1816: 1811: 1806: 1800: 1798: 1794: 1793: 1791: 1790: 1785: 1780: 1775: 1770: 1765: 1759: 1757: 1751: 1750: 1748: 1747: 1742: 1737: 1732: 1730:Microbial loop 1727: 1722: 1717: 1712: 1707: 1702: 1697: 1695:Lithoautotroph 1692: 1687: 1681: 1679: 1677:Microorganisms 1673: 1672: 1670: 1669: 1664: 1659: 1654: 1648: 1646: 1640: 1639: 1637: 1636: 1634:Prey switching 1631: 1626: 1621: 1616: 1611: 1606: 1601: 1596: 1591: 1586: 1581: 1576: 1571: 1566: 1561: 1556: 1551: 1545: 1543: 1537: 1536: 1534: 1533: 1528: 1523: 1518: 1513: 1511:Photosynthesis 1508: 1503: 1498: 1493: 1488: 1483: 1478: 1473: 1468: 1466:Chemosynthesis 1463: 1457: 1455: 1449: 1448: 1446: 1445: 1440: 1435: 1430: 1425: 1420: 1415: 1410: 1405: 1400: 1395: 1390: 1385: 1380: 1375: 1370: 1365: 1360: 1358:Abiotic stress 1355: 1349: 1347: 1343: 1342: 1326: 1325: 1318: 1311: 1303: 1292: 1291: 1256: 1229: 1210:(3): 329–342. 1194: 1159:(4): 437–445. 1143: 1130:(1): 163–176. 1110: 1081:10.1086/285467 1075:(1): 166–171. 1059: 1040:(2): 419–424. 1024: 997:(4): 333–344. 977: 942: 936:978-1930665859 935: 915: 860: 821: 757: 751:978-1402002298 750: 725: 714:(4): 389–402. 681: 678:on 2014-10-26. 661:10.1086/284165 655:(5): 661–696. 632: 625: 601: 600: 598: 595: 594: 593: 584: 579: 574: 569: 564: 559: 557:Logistic model 554: 549: 542: 539: 450: 444: 440: 437: 434: 431: 425: 422: 418: 414: 411: 408: 405: 402: 399: 393: 390: 385: 382: 379: 376: 373: 335: 332: 330: 327: 310: 307: 256: 253: 251: 248: 174: 171: 115: 112: 110: 107: 15: 9: 6: 4: 3: 2: 2885: 2874: 2871: 2870: 2868: 2855: 2850: 2844: 2841: 2839: 2838:Urban ecology 2836: 2834: 2831: 2829: 2826: 2824: 2821: 2819: 2816: 2814: 2811: 2809: 2806: 2804: 2801: 2799: 2796: 2794: 2791: 2789: 2786: 2784: 2781: 2779: 2776: 2774: 2771: 2769: 2766: 2764: 2761: 2759: 2756: 2754: 2751: 2749: 2746: 2744: 2741: 2739: 2736: 2734: 2731: 2730: 2728: 2724: 2718: 2715: 2713: 2710: 2708: 2705: 2703: 2700: 2698: 2697:Kleiber's law 2695: 2693: 2690: 2688: 2685: 2683: 2680: 2678: 2675: 2673: 2670: 2668: 2665: 2663: 2660: 2658: 2655: 2653: 2650: 2648: 2645: 2643: 2640: 2638: 2635: 2634: 2632: 2630: 2624: 2618: 2615: 2613: 2610: 2608: 2605: 2603: 2600: 2598: 2595: 2591: 2588: 2587: 2586: 2583: 2581: 2578: 2576: 2573: 2571: 2568: 2566: 2563: 2561: 2558: 2557: 2555: 2553: 2549: 2543: 2540: 2538: 2535: 2533: 2531: 2527: 2523: 2521: 2518: 2516: 2513: 2511: 2508: 2506: 2503: 2501: 2498: 2496: 2493: 2491: 2488: 2486: 2483: 2481: 2478: 2476: 2473: 2471: 2470:Foster's rule 2468: 2466: 2463: 2461: 2458: 2456: 2453: 2451: 2448: 2446: 2443: 2441: 2438: 2436: 2433: 2432: 2430: 2428: 2422: 2416: 2413: 2411: 2408: 2406: 2403: 2401: 2398: 2396: 2393: 2391: 2388: 2386: 2383: 2381: 2378: 2376: 2373: 2371: 2368: 2367: 2365: 2359: 2353: 2350: 2348: 2345: 2343: 2340: 2338: 2335: 2333: 2330: 2328: 2325: 2323: 2320: 2318: 2315: 2313: 2310: 2308: 2305: 2303: 2300: 2298: 2295: 2293: 2290: 2288: 2285: 2283: 2280: 2278: 2274: 2271: 2269: 2266: 2264: 2261: 2259: 2256: 2254: 2251: 2249: 2246: 2244: 2241: 2239: 2236: 2234: 2231: 2229: 2226: 2225: 2223: 2219: 2213: 2210: 2206: 2203: 2201: 2198: 2197: 2196: 2193: 2191: 2188: 2186: 2183: 2181: 2178: 2176: 2173: 2171: 2168: 2166: 2163: 2161: 2158: 2156: 2153: 2151: 2148: 2146: 2143: 2141: 2138: 2136: 2133: 2131: 2128: 2126: 2123: 2121: 2118: 2116: 2113: 2111: 2108: 2106: 2103: 2101: 2098: 2097: 2095: 2093: 2087: 2082: 2078: 2071: 2066: 2064: 2059: 2057: 2052: 2051: 2048: 2036: 2033: 2031: 2028: 2026: 2023: 2021: 2018: 2016: 2013: 2011: 2008: 2006: 2003: 2001: 1998: 1997: 1995: 1989: 1983: 1980: 1978: 1975: 1973: 1970: 1968: 1965: 1963: 1960: 1958: 1955: 1953: 1950: 1948: 1945: 1943: 1940: 1938: 1935: 1933: 1930: 1928: 1925: 1923: 1920: 1918: 1915: 1913: 1910: 1908: 1905: 1903: 1900: 1898: 1895: 1893: 1890: 1888: 1885: 1883: 1880: 1878: 1875: 1874: 1872: 1868: 1860: 1857: 1855: 1852: 1850: 1847: 1845: 1842: 1840: 1837: 1835: 1832: 1830: 1827: 1826: 1825: 1822: 1820: 1817: 1815: 1812: 1810: 1807: 1805: 1802: 1801: 1799: 1795: 1789: 1788:Trophic level 1786: 1784: 1781: 1779: 1776: 1774: 1771: 1769: 1766: 1764: 1761: 1760: 1758: 1756: 1752: 1746: 1745:Phage ecology 1743: 1741: 1738: 1736: 1735:Microbial mat 1733: 1731: 1728: 1726: 1723: 1721: 1718: 1716: 1713: 1711: 1708: 1706: 1703: 1701: 1698: 1696: 1693: 1691: 1690:Bacteriophage 1688: 1686: 1683: 1682: 1680: 1678: 1674: 1668: 1665: 1663: 1660: 1658: 1657:Decomposition 1655: 1653: 1650: 1649: 1647: 1645: 1641: 1635: 1632: 1630: 1627: 1625: 1622: 1620: 1617: 1615: 1612: 1610: 1607: 1605: 1604:Mesopredators 1602: 1600: 1597: 1595: 1592: 1590: 1587: 1585: 1582: 1580: 1577: 1575: 1572: 1570: 1567: 1565: 1562: 1560: 1557: 1555: 1552: 1550: 1549:Apex predator 1547: 1546: 1544: 1542: 1538: 1532: 1529: 1527: 1524: 1522: 1519: 1517: 1514: 1512: 1509: 1507: 1504: 1502: 1499: 1497: 1494: 1492: 1489: 1487: 1484: 1482: 1479: 1477: 1474: 1472: 1469: 1467: 1464: 1462: 1459: 1458: 1456: 1454: 1450: 1444: 1441: 1439: 1436: 1434: 1431: 1429: 1426: 1424: 1421: 1419: 1416: 1414: 1411: 1409: 1406: 1404: 1401: 1399: 1396: 1394: 1391: 1389: 1386: 1384: 1383:Biotic stress 1381: 1379: 1376: 1374: 1371: 1369: 1366: 1364: 1361: 1359: 1356: 1354: 1351: 1350: 1348: 1344: 1339: 1335: 1331: 1324: 1319: 1317: 1312: 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Dordrecht. 743: 742: 734: 732: 730: 721: 717: 713: 709: 705: 698: 696: 694: 692: 690: 688: 686: 674: 670: 666: 662: 658: 654: 650: 643: 636: 628: 622: 618: 611: 609: 607: 602: 592: 588: 585: 583: 580: 578: 575: 573: 570: 568: 565: 563: 562:Plant density 560: 558: 555: 553: 550: 548: 545: 544: 538: 535: 531: 527: 525: 521: 520: 513: 511: 507: 503: 494: 490: 488: 484: 482: 478: 477: 473: 469: 467: 463: 448: 442: 435: 429: 423: 420: 416: 409: 403: 400: 397: 391: 388: 380: 374: 371: 360: 358: 354: 350: 340: 326: 324: 318: 315: 306: 304: 298: 295: 291: 290: 284: 282: 281: 274: 272: 268: 264: 263: 247: 245: 241: 237: 233: 229: 228: 223: 217: 213: 211: 207: 203: 199: 195: 191: 186: 184: 180: 170: 168: 164: 160: 155: 153: 149: 145: 136: 132: 130: 125: 121: 106: 104: 100: 95: 90: 88: 83: 81: 77: 73: 69: 63: 61: 56: 51: 49: 45: 41: 37: 33: 29: 21: 2823:Regime shift 2808:Macroecology 2529: 2525: 2465:Edge effects 2435:Biogeography 2380:Commensalism 2228:Biodiversity 2129: 2105:Allee effect 1844:kelp forests 1797:Example webs 1662:Detritivores 1501:Organotrophs 1481:Kinetotrophs 1433:Productivity 1295: 1272:(1): 56–84. 1269: 1265: 1259: 1242: 1238: 1232: 1207: 1203: 1197: 1156: 1152: 1146: 1127: 1123: 1113: 1072: 1068: 1062: 1037: 1033: 1027: 994: 990: 986: 980: 955: 951: 945: 925: 918: 877: 873: 869: 863: 841:(1): 59–64. 838: 834: 830: 824: 813:. 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Index

Male hartebeest locking horns and fiercely defending their territories. An example of direct competition
population ecology
species
fitness
interspecific competition
smaller contested resource overlap
resource
grows exponentially
negatively density dependent
logistic growth model
carrying capacity
indirect interactions
scramble
hierarchies
territories
fighting, stealing or ritualised combat
territory
dominant member of the population
Captive flamingos fighting one another in shallow water
northern slimy salamander
spread through the population
Chilean flamingos
sex ratio
exploitative or apparent competition
fitness
wolf spiders
population density
logistic growth model
Viviparous lizard
predator

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