|
|
(One intermediate revision by one other user not shown) |
Line 1: |
Line 1: |
| {{Other uses}}
| | Msvcr71.dll is an significant file which helps support Windows process different components of the system including significant files. Specifically, the file is used to help run corresponding files in the "Virtual C Runtime Library". These files are significant in accessing any settings which help the different applications plus programs inside the system. The msvcr71.dll file fulfills numerous significant functions; still it's not spared from getting damaged or corrupted. Once the file gets corrupted or damaged, the computer might have a hard time processing plus reading components of the system. Nonetheless, users need not panic considering this issue might be solved by following several procedures. And I will show you certain tricks regarding Msvcr71.dll.<br><br>Carry out window's system restore. It is rather important to do this considering it removes wrong changes which have happened inside the program. Some of the mistakes outcome from inability of the program to create restore point regularly.<br><br>One of the many overlooked reasons a computer may slow down is considering the registry has become corrupt. The registry is essentially the computer's running system. Anytime you're running a computer, entries are being created and deleted from a registry. The impact this has is it leaves false entries inside your registry. So, your computer's resources must function around these false entries.<br><br>The problem with most of the individuals is the fact that they do not wish to spend money. In the cracked adaptation one refuses to have to pay anything plus could download it from web easily. It is easy to install also. However, the problem comes whenever it is not able to identify all possible viruses, spyware plus malware inside the program. This really is because it happens to be obsolete in nature plus refuses to get any regular updates within the url downloaded. Thus, your system is accessible to issues like hacking.<br><br>These are the results which the [http://bestregistrycleanerfix.com/regzooka regzooka] found: 622 incorrect registry entries, 45,810 junk files, 15,643 unprotected confidentiality files, 8,462 bad Active X items that were not blocked, 16 performance features which were not optimized, and 4 updates which the computer required.<br><br>Files with all the DOC extension are furthermore susceptible to viruses, but this can be solved by advantageous antivirus programs. Another problem is the fact that .doc files may be corrupted, unreadable or damaged due to spyware, adware, plus malware. These situations usually avoid users from correctly opening DOC files. This is when efficient registry products become useful.<br><br>Your registry is the spot all the significant configurations for hardware, software and user profile configurations and needs are stored. Every time 1 of these points is changed, the database then starts to expand. Over time, the registry may become bloated with unnecessary files. This causes a general slow down but in extreme cases may result significant jobs plus programs to stop functioning all together.<br><br>So inside summary, whenever comparing registry cleaning, make sure the 1 we choose provides we the following.A backup plus restore facility, rapidly surgery, automatic deletion facility, start-up administration, an effortless way of contact and a money back guarantee. |
| {{infobox
| |
| | title = Ecology
| |
| | data1 = [[File:The Earth seen from Apollo 17.jpg|250px]]
| |
| | data2 = [[File:Hawk eating prey.jpg|119px]][[File:European honey bee extracts nectar.jpg|131px]]
| |
| | data3 = [[File:Bufo boreas.jpg|160px]][[File:Blue Linckia Starfish.JPG|90px]]
| |
| | data4 = Ecology addresses the full scale of life, from tiny bacteria to processes that span the entire planet. Ecologists study many diverse and [[interspecific interactions|complex relations]] among species, such as [[predation]] and [[pollination]]. The diversity of life is organized into different [[habitats]], from [[terrestrial ecosystem|terrestrial]] (middle) to [[aquatic ecosystem]]s.
| |
| }}
| |
| | |
| '''Ecology''' (from {{lang-el|οἶκος}}, "house"; -λογία, "study of"{{Cref2|A}}) is the [[science|scientific]] study of interactions among organisms and their environment, such as the interactions [[organism]]s have with each other and with their abiotic [[environment (biophysical)|environment]]. Topics of interest to ecologists include the [[biodiversity|diversity]], distribution, amount ([[biomass]]), number ([[population]]) of organisms, as well as competition between them within and among [[ecosystems]]. Ecosystems are composed of dynamically interacting parts including [[organisms]], the [[Community (ecology)|communities]] they make up, and the non-living components of their environment. Ecosystem processes, such as [[primary production]], [[pedogenesis]], [[nutrient cycling]], and various [[niche construction]] activities, regulate the flux of energy and matter through an environment. These processes are sustained by organisms with specific life history traits, and the variety of organisms is called [[biodiversity]]. Biodiversity, which refers to the varieties of [[species]], [[gene]]s, and [[ecosystem]]s, enhances certain [[ecosystem services]]. | |
| | |
| Ecology is an [[interdisciplinary]] field that includes [[biology]] and [[Earth science]]. The word "ecology" ("Ökologie") was coined in 1866 by the German scientist [[Ernst Haeckel]] (1834–1919). Ancient Greek philosophers such as [[Hippocrates]] and [[Aristotle]] laid the foundations of ecology in their studies on [[natural history]]. Modern ecology transformed into a more rigorous [[natural sciences|science]] in the late 19th century. [[Evolution]]ary concepts on adaptation and [[natural selection]] became cornerstones of modern [[Theoretical ecology|ecological theory]]. Ecology is not synonymous with environment, [[environmentalism]], natural history, or [[environmental science]]. It is closely related to [[evolutionary biology]], [[genetics]], and [[ethology]]. An understanding of how biodiversity affects ecological function is an important focus area in ecological studies. Ecologists seek to explain:
| |
| | |
| *Life processes, interactions and [[adaptations]]
| |
| *The movement of materials and [[energy]] through living communities
| |
| *The [[ecological succession|successional]] development of ecosystems, and
| |
| *The [[Abundance (ecology)|abundance]] and distribution of organisms and biodiversity in the context of the [[environment (biophysical)|environment]].
| |
| | |
| Ecology is a human science as well. There are many practical applications of ecology in [[conservation biology]], wetland management, [[natural resource management]] ([[agroecology]], [[agriculture]], [[forestry]], [[agroforestry]], [[fisheries]]), city planning ([[urban ecology]]), [[community health]], [[Ecological economics|economics]], [[basic science|basic]] and [[applied science]], and human social interaction ([[human ecology]]). Organisms and resources compose [[ecosystem]]s which, in turn, maintain [[Biophysics|biophysical]] feedback mechanisms that moderate processes acting on living ([[Biotic component|biotic]]) and nonliving ([[abiotic]]) components of the planet. Ecosystems sustain life-supporting functions and produce [[natural capital]] like biomass production (food, fuel, fiber and medicine), the regulation of [[climate]], global [[biogeochemical cycles]], [[water filtration]], [[soil formation]], erosion control, flood protection and many other natural features of scientific, historical, economic, or intrinsic value.
| |
| | |
| ==Integrative levels, scope, and scale of organization==
| |
| {{See also|Integrative level}}
| |
| | |
| [[File:Seral stages 4.JPG|thumb|400px|Ecosystems regenerate after a disturbance such as fire, forming [[Mosaic (ecology)|mosaics]] of different age groups structured across a [[Landscape ecology|landscape]]. Pictured are different seral stages in forested ecosystems starting from pioneers colonizing a disturbed site and maturing in [[succession(ecology)|successional stages]] leading to [[old-growth forests]].]]
| |
| | |
| The scope of ecology covers a wide array of interacting levels of organization spanning micro-level (e.g., [[cell (biology)|cells]]) to planetary scale (e.g., [[Earth's spheres|biosphere]]) [[phenomena]]. Ecosystems, for example, contain abiotic resources and interacting life forms (i.e., individual organisms that aggregate into [[population]]s which aggregate into distinct ecological communities). Ecosystems are dynamic, they do not always follow a linear successional path, but they are always changing, sometimes rapidly and sometimes so slowly that it can take thousands of years for ecological processes to bring about certain [[ecological succession|successional stages]] of a forest. An ecosystem's area can vary greatly, from tiny to vast. A single tree is of little consequence to the classification of a forest ecosystem, but critically relevant to organisms living in and on it.<ref name="Stadler98"/> Several generations of an [[aphid]] population can exist over the lifespan of a single leaf. Each of those aphids, in turn, support diverse [[bacteria]]l communities.<ref name="Humphreys97"/> The nature of connections in ecological communities cannot be explained by knowing the details of each species in isolation, because the emergent pattern is neither revealed nor predicted until the ecosystem is studied as an integrated whole.<ref name=Liere2012>{{cite journal|last=Liere|first=Heidi|coauthors=Jackson, Doug; Vandermeer, John; Wilby, Andrew|title=Ecological Complexity in a Coffee Agroecosystem: Spatial Heterogeneity, Population Persistence and Biological Control|journal=PLoS ONE | date=20 September 2012|volume=7|issue=9 | pages=e45508 | doi=10.1371/journal.pone.0045508|bibcode = 2012PLoSO...745508L |pmid=23029061|pmc=3447771}}</ref> Some ecological principles, however, do exhibit collective properties where the sum of the components explain the properties of the whole, such as birth rates of a population being equal to the sum of individual births over a designated time frame.<ref name="Odum05" />
| |
| | |
| ===Hierarchical ecology===
| |
| {{See also|Biological organisation|Biological classification}}
| |
| | |
| {{quote box
| |
| | quote = System behaviors must first be arrayed into different levels of organization. Behaviors corresponding to higher levels occur at slow rates. Conversely, lower organizational levels exhibit rapid rates. For example, individual tree leaves respond rapidly to momentary changes in light intensity, CO<sub>2</sub> concentration, and the like. The growth of the tree responds more slowly and integrates these short-term changes.
| |
| | source = O'Neill et al. (1986)<ref name="O'Neill86" />{{Rp|76}}
| |
| | width = 25%
| |
| | align = right}}
| |
| | |
| The scale of ecological dynamics can operate like a closed system, such as aphids migrating on a single tree, while at the same time remain open with regard to broader scale influences, such as atmosphere or climate. Hence, ecologists classify [[ecosystems]] hierarchically by analyzing data collected from finer scale units, such as vegetation associations, climate, and soil types, and integrate this information to identify emergent patterns of uniform organization and processes that operate on local to regional, [[landscape]], and chronological scales.
| |
| | |
| To structure the study of ecology into a conceptually manageable framework, the biological world is organized into a [[Biological classification|nested hierarchy]], ranging in scale from [[gene]]s, to [[cell (biology)|cell]]s, to [[tissue (biology)|tissues]], to [[Organ (anatomy)|organs]], to [[organism]]s, to [[species]], to [[population ecology|population]]s, to [[Community (ecology)|communities]], to [[ecosystem]]s, to [[biome]]s, and up to the level of the [[biosphere]].<ref name="Nachtomy01"/> This framework forms a [[panarchy]]<ref name="Holling01"/> and exhibits [[non-linear]] behaviors; this means that "effect and cause are disproportionate, so that small changes to critical variables, such as the number of [[nitrogen fixation|nitrogen fixers]], can lead to disproportionate, perhaps irreversible, changes in the system properties."<ref name="Levin99"/>{{rp|14}}
| |
| | |
| ===Biodiversity===
| |
| {{main|Biodiversity}}
| |
| {{quote box
| |
| | quote = Biodiversity refers to the variety of life and its processes. It includes the variety of living organisms, the genetic differences among them, the communities and ecosystems in which they occur, and the ecological and [[evolution]]ary processes that keep them functioning, yet ever changing and adapting.
| |
| | source= Noss & Carpenter (1994)<ref name="Noss94"/>{{Rp|5}}
| |
| | width = 25%
| |
| | align = left}}
| |
| | |
| Biodiversity (an abbreviation of "biological diversity") describes the diversity of life from genes to ecosystems and spans every level of biological organization. The term has several interpretations, and there are many ways to index, measure, characterize, and represent its complex organization.<ref name="Noss90"/><ref name="Scholes08"/><ref name=cardinale2012>{{cite journal|last=Cardinale|first=Bradley J.|coauthors=Duffy, J. Emmett; Gonzalez, Andrew; Hooper, David U.; Perrings, Charles; Venail, Patrick; Narwani, Anita; Mace, Georgina M.; Tilman, David; Wardle, David A.; Kinzig, Ann P.; Daily, Gretchen C.; Loreau, Michel; Grace, James B.; Larigauderie, Anne; Srivastava, Diane S.; Naeem, Shahid|title=Biodiversity loss and its impact on humanity|journal=Nature|date=6 June 2012|volume=486|issue=7401|pages=59–67|doi=10.1038/nature11148|bibcode = 2012Natur.486...59C |pmid=22678280}}</ref> Biodiversity includes [[species diversity]], [[ecosystem diversity]], and [[genetic diversity]] and scientists are interested in the way that this diversity affects the complex ecological processes operating at and among these respective levels.<ref name="Scholes08" /><ref name="Wilson00b"/><ref name="Purvis00"/> Biodiversity plays an important role in [[ecosystem service]]s which by definition maintain and improve human quality of life.<ref name="cardinale2012"/><ref name="Ostfeld09"/><ref name="Tierney09"/> Preventing [[extinction|species extinctions]] is one way to preserve biodiversity and that goal rests on techniques that preserve genetic diversity, habitat and the ability for species to migrate.{{citation needed|date=May 2013}} Conservation priorities and management techniques require different approaches and considerations to address the full ecological scope of biodiversity. [[Natural capital]] that supports populations is critical for maintaining [[ecosystem services]]<ref name="Ceballos02"/><ref name="Palumbi09"/> and species [[Animal migration|migration]] (e.g., riverine fish runs and avian insect control) has been implicated as one mechanism by which those service losses are experienced.<ref name="Wilcove08"/> An understanding of biodiversity has practical applications for species and ecosystem-level conservation planners as they make management recommendations to consulting firms, governments, and industry.<ref name="Hammond09"/>
| |
| | |
| ===Habitat===
| |
| {{Main|Habitat}}
| |
| | |
| The habitat of a species describes the environment over which a species is known to occur and the type of community that is formed as a result.<ref name="Whittaker73"/> More specifically, "habitats can be defined as regions in environmental space that are composed of multiple dimensions, each representing a biotic or abiotic environmental variable; that is, any component or characteristic of the environment related directly (e.g. forage biomass and quality) or indirectly (e.g. elevation) to the use of a location by the animal."<ref name="Beyer10"/>{{Rp|745}} For example, a habitat might be an aquatic or terrestrial environment that can be further categorized as a [[Montane ecology|montane]] or [[alpine climate|alpine]] ecosystem. Habitat shifts provide important evidence of competition in nature where one population changes relative to the habitats that most other individuals of the species occupy. For example, one population of a species of tropical lizards (''Tropidurus hispidus'') has a flattened body relative to the main populations that live in open savanna. The population that lives in an isolated rock outcrop hides in crevasses where its flattened body offers a selective advantage. Habitat shifts also occur in the developmental life history of amphibians and in insects that transition from aquatic to terrestrial habitats. [[Biotope]] and habitat are sometimes used interchangeably, but the former applies to a community's environment, whereas the latter applies to a species' environment.<ref name="Whittaker73"/><ref name="Schoener75"/><ref name="Vitt97"/>
| |
| | |
| Additionally, some species are [[ecosystem engineers]], altering the environment within a localized region. For instance, beavers manage water levels by building dams which improves their habitat in a landscape.
| |
| | |
| [[File:Blue Linckia Starfish.JPG|thumb|Biodiversity of a [[coral reef]]. [[Coral]]s adapt to and modify their environment by forming [[calcium carbonate]] skeletons. This provides growing conditions for future generations and forms a habitat for many other species.<ref name="Kiessling09" />]]
| |
| | |
| ===Niche===
| |
| {{Main|Ecological niche}}
| |
| | |
| [[File:Termite mound-Tanzania.jpg|thumb|[[Termite]] mounds with varied heights of chimneys regulate gas exchange, temperature and other environmental parameters that are needed to sustain the internal physiology of the entire colony.<ref name="Laland99" /><ref name="Hughes08"/>]]
| |
| | |
| Definitions of the niche date back to 1917,<ref name="Wiens05"/> but [[G. Evelyn Hutchinson]] made conceptual advances in 1957<ref name="Hutchinson57"/><ref name="Hutchinson57b"/> by introducing a widely adopted definition: "the set of biotic and abiotic conditions in which a species is able to persist and maintain stable population sizes."<ref name="Wiens05" />{{Rp|519}} The ecological niche is a central concept in the ecology of organisms and is sub-divided into the ''fundamental'' and the ''realized'' niche. The fundamental niche is the set of environmental conditions under which a species is able to persist. The realized niche is the set of environmental plus ecological conditions under which a species persists.<ref name="Wiens05"/><ref name="Hutchinson57b"/><ref name="Begon05"/> The Hutchinsonian niche is defined more technically as a "[[Euclidean space|Euclidean]] [[N-dimensional space|hyperspace]] whose ''dimensions'' are defined as environmental variables and whose ''size'' is a function of the number of values that the environmental values may assume for which an organism has ''positive fitness''."<ref name="Hardesty75"/>{{rp|71}}
| |
| | |
| [[Biogeography|Biogeographical]] patterns and [[Range (biology)|range]] distributions are explained or predicted through knowledge of a species' [[trait (biology)|traits]] and niche requirements.<ref name="Pearman08"/> Species have functional traits that are uniquely adapted to the ecological niche. A trait is a measurable property, [[phenotype]], or [[Phenotypic trait|characteristic]] of an organism that may influence its survival. Genes play an important role in the interplay of development and environmental expression of traits.<ref name="Levins80" /> Resident species evolve traits that are fitted to the selection pressures of their local environment. This tends to afford them a competitive advantage and discourages similarly adapted species from having an overlapping geographic range. The [[competitive exclusion principle]] states that two species cannot coexist indefinitely by living off the same limiting resource; one will always outcompete the other. When similarly adapted species overlap geographically, closer inspection reveals subtle ecological differences in their habitat or dietary requirements.<ref name="Hardin60"/> Some models and empirical studies, however, suggest that disturbances can stabilize the coevolution and shared niche occupancy of similar species inhabiting species-rich communities.<ref name="Scheffer06"/> The habitat plus the niche is called the [[ecotope]], which is defined as the full range of environmental and biological variables affecting an entire species.<ref name="Whittaker73" />
| |
| | |
| ====Niche construction====
| |
| {{Main|Niche construction}}
| |
| {{See also|Ecosystem engineering}}
| |
| | |
| Organisms are subject to environmental pressures, but they also modify their habitats. The [[negative feedback|regulatory feedback]] between organisms and their environment can affect conditions from local (e.g., a [[beaver]] [[pond]]) to global scales, over time and even after death, such as decaying logs or [[silica]] skeleton deposits from marine organisms.<ref name="Hastings07"/> The process and concept of [[ecosystem engineering]] has also been called [[niche construction]]. Ecosystem engineers are defined as: "organisms that directly or indirectly modulate the availability of resources to other species, by causing physical state changes in biotic or abiotic materials. In so doing they modify, maintain and create habitats."<ref name="Jones94"/>{{Rp|373}}
| |
| | |
| The ecosystem engineering concept has stimulated a new appreciation for the influence that organisms have on the ecosystem and evolutionary process. The term "niche construction" is more often used in reference to the under-appreciated feedback mechanisms of natural selection imparting forces on the abiotic niche.<ref name="Laland99"/><ref name="Write06"/> An example of natural selection through ecosystem engineering occurs in the nests of [[social insects]], including ants, bees, wasps, and termites. There is an emergent [[homeostasis]] or [[homeorhesis]] in the structure of the nest that regulates, maintains and defends the physiology of the entire colony. Termite mounds, for example, maintain a constant internal temperature through the design of air-conditioning chimneys. The structure of the nests themselves are subject to the forces of natural selection. Moreover, a nest can survive over successive generations, so that progeny inherit both genetic material and a legacy niche that was constructed before their time.<ref name="Odum05" /><ref name="Laland99"/><ref name="Hughes08"/>
| |
| | |
| ===Biome===
| |
| {{main|Biome}}
| |
| | |
| Biomes are larger units of organization that categorize regions of the Earth's ecosystems, mainly according to the structure and composition of vegetation.<ref name="Palmer94"/> There are different methods to define the continental boundaries of biomes dominated by different functional types of vegetative communities that are limited in distribution by climate, precipitation, weather and other environmental variables. Biomes include [[tropical rainforest]], [[temperate broadleaf and mixed forest]], [[temperate deciduous forest]], [[taiga]], [[tundra]], [[hot desert]], and [[polar desert]].<ref name="Prentice92"/> Other researchers have recently categorized other biomes, such as the human and oceanic [[microbiome]]s. To a microbe, the human body is a habitat and a landscape.<ref name="Turnbaugh07"/> Microbiomes were discovered largely through advances in [[molecular genetics]], which have revealed a hidden richness of microbial diversity on the planet. The oceanic microbiome plays a significant role in the ecological biogeochemistry of the planet's oceans.<ref name="DeLong09"/>
| |
| | |
| ===Biosphere===
| |
| {{main|Biosphere}}
| |
| {{See also|Earth's spheres}}
| |
| The largest scale of ecological organization is the biosphere: the total sum of ecosystems on the planet. [[Ecological relationship]]s regulate the flux of energy, nutrients, and climate all the way up to the planetary scale. For example, the dynamic history of the planetary atmosphere's CO<sub>2</sub> and O<sub>2</sub> composition has been affected by the biogenic flux of gases coming from respiration and photosynthesis, with levels fluctuating over time in relation to the ecology and evolution of plants and animals.<ref name="igamberdiev06"/> Ecological theory has also been used to explain self-emergent regulatory phenomena at the planetary scale: for example, the [[Gaia hypothesis]] is an example of [[holism]] applied in ecological theory.<ref name="Lovelock73"/> The Gaia hypothesis states that there is an emergent [[feedback loop]] generated by the metabolism of living organisms that maintains the core temperature of the Earth and atmospheric conditions within a narrow self-regulating range of tolerance.<ref name="Lovelock03"/>
| |
| | |
| ===Population ecology===
| |
| {{Main|Population ecology}}
| |
| {{See also|Lists of organisms by population}}
| |
| | |
| Population ecology studies the dynamics of specie populations and how these populations interact with the wider environment.<ref name="Odum05" /> A population consists of individuals of the same species that live, interact and migrate through the same niche and habitat.<ref name="Waples06"/>
| |
| | |
| A primary law of population ecology is the [[Malthusian growth model]]<ref name="Turchin01"/> which states, "a population will grow (or decline) exponentially as long as the environment experienced by all individuals in the population remains constant."<ref name="Turchin01" />{{Rp|18}} Simplified population [[Scientific modelling|models]] usually start with four variables: death, birth, [[immigration]], and [[emigration]].
| |
| | |
| An example of an introductory population model describes a closed population, such as on an island, where immigration and emigration does not take place. Hypotheses are evaluated with reference to a null hypothesis which states that [[random]] processes create the observed data. In these island models, the rate of population change is described by:
| |
| | |
| :<math>\frac{\operatorname{d}N}{\operatorname{d}T} = B - D = bN - dN = (b - d)N = rN, </math>
| |
| | |
| where ''N'' is the total number of individuals in the population, ''B'' is the number of births, ''D'' is the number of deaths, ''b'' and ''d'' are the per capita rates of birth and death respectively, and ''r'' is the per capita rate of population change. The formula states that the rate of change in population size (''dN/dT'') is equal to births minus deaths (''B'' – ''D'').<ref name="Turchin01"/><ref name="Vandermeer03"/>
| |
| | |
| Using these modelling techniques, Malthus' population principle of growth was later transformed into a model known as the [[Law of population growth|logistic equation]]:
| |
| | |
| :<math>\frac{dN}{dT} = aN\left(1-\frac{N}{K}\right),</math>
| |
| | |
| where ''N'' is the number of individuals measured as [[biomass (ecology)|biomass]] density, ''a'' is the maximum per-capita rate of change, and ''K'' is the [[carrying capacity]] of the population. The formula states that the rate of change in population size (''dN/dT'') is equal to growth (''aN'') that is limited by carrying capacity (1 – ''N''/''K'').
| |
| | |
| Population ecology builds upon these introductory models to further understand demographic processes in real study populations. Commonly used types of data include [[Biological life cycle|life history]], [[fecundity]], and survivorship, and these are analysed using mathematical techniques such as [[matrix (mathematics)|matrix algebra]]. The information is used for managing wildlife stocks and setting harvest quotas.<ref name="Vandermeer03" /><ref name="Berryman92"/> In cases where basic models are insufficient, ecologists may adopt different kinds of statistical methods, such as the [[Akaike information criterion]],<ref name="Anderson00">{{cite journal | last1=Anderson | first1=D. R. | last2=Burnham | first2=K. P. | last3=Thompson | first3=W. L. | year=2000 | title=Null hypotheses testing: Problems, prevalence, and an alternative | journal=J. Wildl. Mngt. | volume=64 | issue=4 | pages=912–923 | url=http://people.nnu.edu/jocossel/BIOL4240/Anderson%20et%20al%202000.pdf}}</ref> or use models that can become mathematically complex as "several competing hypotheses are simultaneously confronted with the data."<ref name="Johnson04"/>
| |
| | |
| ====Metapopulations and migration====
| |
| {{Main|Metapopulation}}
| |
| {{See also|Animal migration}}
| |
| The concept of metapopulations was defined in 1969<ref name="Levins69"/> as "a population of populations which go extinct locally and recolonize."<ref name="Levins70"/>{{Rp|105}} Metapopulation ecology is another statistical approach that is often used in [[conservation biology|conservation research]].<ref name="Smith05"/> Metapopulation models simplify the landscape into patches of varying levels of quality,<ref name="Hanski98"/> and metapopulations are linked by the migratory behaviours of organisms. Animal migration is set apart from other kinds of movement because it involves the seasonal departure and return of individuals from a habitat.<ref name="Nebel10"/> Migration is also a population-level phenomenon, as with the migration routes followed by plants as they occupied northern post-glacial environments. Plant ecologists use pollen records that accumulate and stratify in wetlands to reconstruct the timing of plant migration and dispersal relative to historic and contemporary climates. These migration routes involved an expansion of the range as plant populations expanded from one area to another. There is a larger taxonomy of movement, such as commuting, foraging, territorial behaviour, stasis, and ranging. Dispersal is usually distinguished from migration because it involves the one way permanent movement of individuals from their birth population into another population.<ref name="Clark98"/><ref name="Dingle96"/>
| |
| | |
| In metapopulation terminology, migrating individuals are classed as emigrants (when they leave a region) or immigrants (when they enter a region), and sites are classed either as sources or sinks. A site is a generic term that refers to places where ecologists sample populations, such as ponds or defined sampling areas in a forest. Source patches are productive sites that generate a seasonal supply of [[Juvenile (organism)|juveniles]] that migrate to other patch locations. Sink patches are unproductive sites that only receive migrants; the population at the site will disappear unless rescued by an adjacent source patch or environmental conditions become more favourable. Metapopulation models examine patch dynamics over time to answer potential questions about spatial and demographic ecology. The ecology of metapopulations is a dynamic process of extinction and colonization. Small patches of lower quality (i.e., sinks) are maintained or rescued by a seasonal influx of new immigrants. A dynamic metapopulation structure evolves from year to year, where some patches are sinks in dry years and are sources when conditions are more favourable. Ecologists use a mixture of computer models and [[field study|field studies]] to explain metapopulation structure.<ref name="Hanski04"/><ref name="MacKenzie06"/>
| |
| | |
| ===Community ecology===
| |
| {{Main|Community ecology}}
| |
| [[File:Male Lion and Cub Chitwa South Africa Luca Galuzzi 2004 edit1.jpg|right|thumb|Interspecific interactions such as [[predation]] are a key aspect of [[community ecology]].]]
| |
| | |
| {{quote box
| |
| | quote = Community ecology examines how interactions among species and their environment affect the abundance, distribution and diversity of species within communities.
| |
| | source = Johnson & Stinchcomb (2007)<ref name="Johnson07" />{{Rp|250}}
| |
| | width = 25%
| |
| | align = left}}
| |
| | |
| Community ecology is the study of the interactions among a collections of species that inhabit the same geographic area. Research in community ecology might measure [[primary production]] in a [[wetland]] in relation to decomposition and consumption rates. This requires an understanding of the community connections between plants (i.e., primary producers) and the decomposers (e.g., [[fungi]] and bacteria),<ref name="Brinson81">{{cite journal|last1 = Brinson| first1 = M. M.|last2=Lugo|first2=A. E.|last3=Brown|first3=S|title = Primary Productivity, Decomposition and Consumer Activity in Freshwater Wetlands|journal = Annual Review of Ecology and Systematics|volume = 12|pages=123–161|year = 1981|doi = 10.1146/annurev.es.12.110181.001011|ref = harv}}</ref> or the analysis of predator-prey dynamics affecting amphibian biomass.<ref name="Davic04" /> [[Food web]]s and [[trophic level]]s are two widely employed conceptual models used to explain the linkages among species.<ref name="Odum05" />
| |
| | |
| ===Ecosystem ecology===
| |
| {{main|Ecosystem ecology}}
| |
| | |
| {{quote box
| |
| | quote = These ecosystems, as we may call them, are of the most various kinds and sizes. They form one category of the multitudinous physical systems of the universe, which range from the universe as a whole down to the atom.
| |
| | source = Tansley (1935)<ref name="Tansley35"/>{{Rp|299}}
| |
| | width = 25%
| |
| | align = left}}
| |
| | |
| [[Image:Ecoecolfigure1.jpg|thumb|280px|A [[riparian forest]] in the [[White Mountains (New Hampshire)|White Mountains]], [[New Hampshire]] (USA), an example of [[ecosystem ecology]]]]
| |
| | |
| Ecosystems are habitats within biomes that form an integrated whole and a dynamically responsive system having both physical and biological complexes. The underlying concept can be traced back to 1864 in the published work of [[George Perkins Marsh]] ("Man and Nature").<ref name="Marsh64"/><ref name="O'Neil01"/> Within an ecosystem, organisms are linked to the physical and biological components of their environment to which they are adapted.<ref name="Tansley35"/> Ecosystems are complex adaptive systems where the interaction of life processes form self-organizing patterns across different scales of time and space.<ref name="Levin98"/> Ecosystems are broadly categorized as [[Terrestrial ecosystem|terrestrial]], [[Freshwater ecosystem|freshwater]], atmospheric, or [[Marine ecosystem|marine]]. Differences stem from the nature of the unique physical environments that shapes the biodiversity within each. A more recent addition to ecosystem ecology are [[technoecosystems]], which are affected by or primarily the result of human activity.<ref name="Odum05" />
| |
| | |
| ====Food webs====
| |
| {{Main|Food web}}
| |
| {{See also|Food chain}}
| |
| | |
| A food web is the archetypal [[ecological network]]. Plants capture [[solar energy]] and use it to synthesize [[simple sugars]] during [[photosynthesis]]. As plants grow, they accumulate nutrients and are eaten by grazing [[herbivores]], and the energy is transferred through a chain of organisms by consumption. The simplified linear feeding pathways that move from a basal [[trophic species]] to a top consumer is called the [[food chain]]. The larger interlocking pattern of food chains in an ecological community creates a complex food web. Food webs are a type of [[concept map]] or a [[heuristic]] device that is used to illustrate and study pathways of energy and material flows.<ref name="O'Neill86"/><ref name="Pimm02"/><ref name="Pimm91"/>
| |
| | |
| [[File:Chesapeake Waterbird Food Web.jpg|thumb|left|Generalized food web of waterbirds from [[Chesapeake Bay]]]]
| |
| | |
| Food webs are often limited relative to the real world. Complete empirical measurements are generally restricted to a specific habitat, such as a cave or a pond, and principles gleaned from food web [[Microcosm (experimental ecosystem)|microcosm]] studies are extrapolated to larger systems.<ref name="Worm03"/> Feeding relations require extensive investigations into the gut contents of organisms, which can be difficult to decipher, or stable isotopes can be used to trace the flow of nutrient diets and energy through a food web.<ref name="McCann07"/> Despite these limitations, food webs remain a valuable tool in understanding community ecosystems.<ref name="Wilbur97"/>
| |
| | |
| Food webs exhibit principles of ecological emergence through the nature of trophic relationships: some species have many weak feeding links (e.g., [[omnivores]]) while some are more specialized with fewer stronger feeding links (e.g., [[predator|primary predators]]). Theoretical and empirical studies identify [[Random#In biology|non-random]] emergent patterns of few strong and many weak linkages that explain how ecological communities remain stable over time.<ref name="Emmerson"/> Food webs are composed of subgroups where members in a community are linked by strong interactions, and the weak interactions occur between these subgroups. This increases food web stability.<ref name="Kraus03"/> Step by step lines or relations are drawn until a web of life is illustrated.<ref name="Pimm91"/><ref name="Egerton07b"/><ref name="Shurin06"/><ref name="Edwards83"/>
| |
| | |
| ====Trophic levels====
| |
| {{Main|Trophic level}}
| |
| | |
| [[File:TrophicWeb.jpg|thumb|left|450px|A trophic pyramid (a) and a food-web (b) illustrating [[ecological relationship]]s among creatures that are typical of a northern [[Boreal ecosystem|Boreal]] terrestrial ecosystem. The trophic pyramid roughly represents the biomass (usually measured as total dry-weight) at each level. Plants generally have the greatest biomass. Names of trophic categories are shown to the right of the pyramid. Some ecosystems, such as many wetlands, do not organize as a strict pyramid, because aquatic plants are not as productive as long-lived terrestrial plants such as trees. Ecological trophic pyramids are typically one of three kinds: 1) pyramid of numbers, 2) pyramid of biomass, or 3) pyramid of energy.<ref name="Odum05"/>{{rp|598}}]]
| |
| | |
| A trophic level (from Greek ''troph'', τροφή, trophē, meaning "food" or "feeding") is "a group of organisms acquiring a considerable majority of its energy from the adjacent level nearer the abiotic source."<ref name="Hariston93"/>{{rp|383}} Links in food webs primarily connect feeding relations or [[trophism]] among species. Biodiversity within ecosystems can be organized into trophic pyramids, in which the vertical dimension represents feeding relations that become further removed from the base of the food chain up toward top predators, and the horizontal dimension represents the [[Relative species abundance|abundance]] or biomass at each level.<ref name="Duffy07"/> When the relative abundance or biomass of each species is sorted into its respective trophic level, they naturally sort into a 'pyramid of numbers'.<ref name="Elton27" />
| |
| | |
| Species are broadly categorized as [[autotrophs]] (or [[primary producers]]), [[heterotrophs]] (or [[consumer]]s), and [[Detritivore]]s (or [[decomposers]]). Autotrophs are organisms that produce their own food (production is greater than respiration) by photosynthesis or [[chemosynthesis]]. Heterotrophs are organisms that must feed on others for nourishment and energy (respiration exceeds production).<ref name="Odum05" /> Heterotrophs can be further sub-divided into different functional groups, including [[primary consumers]] (strict herbivores), [[Trophic dynamics|secondary consumers]] ([[carnivorous]] predators that feed exclusively on herbivores) and tertiary consumers (predators that feed on a mix of herbivores and predators).<ref name="David03"/> Omnivores do not fit neatly into a functional category because they eat both plant and animal tissues. It has been suggested that omnivores have a greater functional influence as predators, because compared to herbivores they are relatively inefficient at grazing.<ref name="Oksanen91"/>
| |
| | |
| Trophic levels are part of the [[holistic]] or [[complex systems]] view of ecosystems.<ref name="Loehle88"/><ref name="Ulanowicz79"/> Each trophic level contains unrelated species that are grouped together because they share common ecological functions, giving a macroscopic view of the system.<ref name="Li00"/> While the notion of trophic levels provides insight into energy flow and top-down control within food webs, it is troubled by the prevalence of omnivory in real ecosystems. This has led some ecologists to "reiterate that the notion that species clearly aggregate into discrete, homogeneous trophic levels is fiction."<ref name="Polis96"/>{{rp|815}} Nonetheless, recent studies have shown that real trophic levels do exist, but "above the herbivore trophic level, food webs are better characterized as a tangled web of omnivores."<ref name="Thompson07"/>{{rp|612}}
| |
| {{-}}
| |
| | |
| ====Keystone species====
| |
| {{main|Keystone species}}
| |
| [[File:Sea otters holding hands, cropped.jpg|thumb|[[Sea otter]]s, an example of a keystone species]]
| |
| A keystone species is a species that is connected to a disproportionately large number of other species in the [[food-web]]. Keystone species have lower levels of biomass in the trophic pyramid relative to the importance of their role. The many connections that a keystone species holds means that it maintains the organization and structure of entire communities. The loss of a keystone species results in a range of dramatic cascading effects that alters trophic dynamics, other food web connections, and can cause the extinction of other species.<ref name="Fisher06"/><ref name="Libralato06"/>
| |
| | |
| [[Sea otter]]s (''Enhydra lutris'') are commonly cited as an example of a keystone species because they limit the density of [[sea urchins]] that feed on [[kelp]]. If sea otters are removed from the system, the urchins graze until the kelp beds disappear and this has a dramatic effect on community structure.<ref name="Mills93"/> Hunting of sea otters, for example, is thought to have indirectly led to the extinction of the [[Steller's Sea Cow]] (''Hydrodamalis gigas'').<ref name="Anderson95"/> While the keystone species concept has been used extensively as a [[Conservation biology|conservation]] tool, it has been criticized for being poorly defined from an operational stance. It is difficult to experimentally determine what species may hold a keystone role in each ecosystem. Furthermore, food web theory suggests that keystone species may not be common, so it is unclear how generally the keystone species model can be applied.<ref name="Mills93"/><ref name="Polis00"/>
| |
| | |
| ==Ecological complexity==
| |
| {{Main|Complexity}}
| |
| {{See also|Emergence}}
| |
| | |
| Complexity is understood as a large computational effort needed to piece together numerous interacting parts exceeding the iterative memory capacity of the human mind. Global patterns of biological diversity are complex. This [[biocomplexity]] stems from the interplay among ecological processes that operate and influence patterns at different scales that grade into each other, such as transitional areas or [[ecotones]] spanning landscapes. Complexity stems from the interplay among levels of biological organization as energy and matter is integrated into larger units that superimpose onto the smaller parts. "What were wholes on one level become parts on a higher one."<ref name="Novikoff45"/>{{rp|209}} Small scale patterns do not necessarily explain large scale phenomena, otherwise captured in the expression (coined by Aristotle) 'the sum is greater than the parts'.<ref name="Schneider01"/><ref name="Molnar04"/>{{Cref2|E}}
| |
| | |
| "Complexity in ecology is of at least six distinct types: spatial, temporal, structural, process, behavioral, and geometric."<ref name="Loehle04"/>{{rp|3}} From these principles, ecologists have identified [[emergence|emergent]] and [[Self-organization#Self-organization in biology|self-organizing]] phenomena that operate at different environmental scales of influence, ranging from molecular to planetary, and these require different explanations at each integrative level.<ref name="Lovelock03" /><ref name="Odum1977"/> Ecological complexity relates to the dynamic resilience of ecosystems that transition to multiple shifting steady-states directed by random fluctuations of history.<ref name="Holling01"/><ref name="Carpenter01"/> Long-term ecological studies provide important track records to better understand the complexity and resilience of ecosystems over longer temporal and broader spatial scales. These studies are managed by the [[International Long Term Ecological Network]] (LTER).<ref name="urlWelcome to ILTER — ILTER"/> The longest experiment in existence is the [[Park Grass Experiment]], which was initiated in 1856.<ref name="Siverton06"/> Another example is the [[Hubbard Brook Experimental Forest|Hubbard Brook study]], which has been in operation since 1960.<ref>{{cite web |url=http://www.hubbardbrook.org/ |title=Hubbard Brook Ecosystem Study Front Page |accessdate = 2010-03-16}}</ref>
| |
| | |
| ===Holism===
| |
| {{Main|Holism}}
| |
| | |
| Holism remains a critical part of the theoretical foundation in contemporary ecological studies. Holism addresses the [[Biological organisation|biological organization]] of life that [[Systems biology|self-organizes]] into layers of emergent whole systems that function according to nonreducible properties. This means that higher order patterns of a whole functional system, such as an [[ecosystem]], cannot be predicted or understood by a simple summation of the parts.<ref name="Liu09"/> "New properties emerge because the components interact, not because the basic nature of the components is changed."<ref name="Odum05"/>{{rp|8}}
| |
| | |
| Ecological studies are necessarily holistic as opposed to [[reductionistic]].<ref name="Levins80" /><ref name="Odum1977"/><ref name="Mikkelson10"/> Holism has three scientific meanings or uses that identify with ecology: 1) the mechanistic complexity of ecosystems, 2) the practical description of patterns in quantitative reductionist terms where correlations may be identified but nothing is understood about the causal relations without reference to the whole system, which leads to 3) a [[metaphysics|metaphysical]] hierarchy whereby the causal relations of larger systems are understood without reference to the smaller parts. Scientific holism differs from [[mysticism]] that has appropriated the same term. An example of metaphysical holism is identified in the trend of increased exterior thickness in shells of different species. The reason for a thickness increase can be understood through reference to principles of natural selection via predation without need to reference or understand the [[biomolecular]] properties of the exterior shells.<ref name="Wilson88"/>
| |
| | |
| ==Relation to evolution==
| |
| {{main|Evolutionary ecology}}
| |
| | |
| Ecology and evolution are considered sister disciplines of the life sciences. [[Natural selection]], [[Biological life cycle|life history]], [[Developmental biology|development]], [[adaptation]], [[populations]], and [[heredity|inheritance]] are examples of concepts that thread equally into ecological and evolutionary theory. Morphological, behavioural and genetic traits, for example, can be mapped onto evolutionary trees to study the historical development of a species in relation to their functions and roles in different ecological circumstances. In this framework, the analytical tools of ecologists and evolutionists overlap as they organize, classify and investigate life through common systematic principals, such as [[phylogenetics]] or the [[Linnaean taxonomy|Linnaean system of taxonomy]].<ref name="Miles93"/> The two disciplines often appear together, such as in the title of the journal ''[[Trends in Ecology and Evolution]]''.<ref name="TREE">{{cite web | editor-last=Craze | editor-first=P. | title=Trends in Ecology and Evolution | publisher=Cell Press, Elsevier, Inc | url=http://www.cell.com/trends/ecology-evolution/home | date=August 2, 2012}}</ref> There is no sharp boundary separating ecology from evolution and they differ more in their areas of applied focus. Both disciplines discover and explain emergent and unique properties and processes operating across different spatial or temporal scales of organization.<ref name="Levins80" /><ref name="Lovelock03" /> While the boundary between ecology and evolution is not always clear, ecologists study the abiotic and biotic factors that influence evolutionary processes,<ref name="Allee49"/><ref name="Ricklefs96"/> and evolution can be rapid, occurring on ecological timescales as short as one generation.<ref>{{cite web | last=Yoshida | first=T | title=Rapid evolution drives ecological dynamics in a predator–prey system | publisher=Nature Publishing Group | url=http://www.nature.com/nature/journal/v424/n6946/abs/nature01767.html}}</ref>
| |
| | |
| ===Behavioural ecology===
| |
| {{Main|Behavioural ecology}}
| |
| | |
| [[File:Chameleon spectra.jpg|left|320px|thumb|Social display and colour variation in differently adapted species of [[chameleons]] (''Bradypodion'' spp.). Chameleons change their skin colour to match their background as a behavioural defence mechanism and also use colour to communicate with other members of their species, such as dominant (left) versus submissive (right) patterns shown in the three species (A-C) above.<ref name="Stuart-Fox08"/>]]
| |
| | |
| All organisms can exhibit behaviours. Even plants express complex behaviour, including memory and communication.<ref name="Karban08"/> Behavioural ecology is the study of an organism's behaviour in its environment and its ecological and evolutionary implications. Ethology is the study of observable movement or behaviour in animals. This could include investigations of motile [[sperm]] of plants, mobile [[phytoplankton]], [[zooplankton]] swimming toward the female egg, the cultivation of fungi by [[weevils]], the mating dance of a [[salamander]], or social gatherings of [[amoeba]].<ref name="Tinbergen63"/><ref name="Hamner85"/><ref name="Strassmann00"/><ref name="Sakurai85"/><ref name="Anderson61"/>
| |
| | |
| Adaptation is the central unifying concept in behavioural ecology.<ref>{{cite web |url=http://www.behavecol.com/pages/society/welcome.html |title=Behavioral Ecology |publisher=International Society for Behavioral Ecology |accessdate=15 April 2011}}</ref> Behaviours can be recorded as traits and inherited in much the same way that eye and hair colour can. Behaviours can evolve by means of natural selection as adaptive traits conferring functional utilities that increases reproductive fitness.<ref name="Gould82"/><ref name="Wilson00"/>
| |
| | |
| Predator-prey interactions are an introductory concept into food-web studies as well as behavioural ecology.<ref name="Ives04"/> Prey species can exhibit different kinds of behavioural adaptations to predators, such as avoid, flee or defend. Many prey species are faced with multiple predators that differ in the degree of danger posed. To be adapted to their environment and face predatory threats, organisms must balance their energy budgets as they invest in different aspects of their life history, such as growth, feeding, mating, socializing, or modifying their habitat. Hypotheses posited in behavioural ecology are generally based on adaptive principles of conservation, optimization or efficiency.<ref name="Begon05"/><ref name="Allee49"/><ref name="Krebs93"/> For example, "[t]he threat-sensitive predator avoidance hypothesis predicts that prey should assess the degree of threat posed by different predators and match their behaviour according to current levels of risk"<ref name="Webb10"/> or "[t]he optimal [[Escape distance|flight initiation distance]] occurs where expected postencounter fitness is maximized, which depends on the prey's initial fitness, benefits obtainable by not fleeing, energetic escape costs, and expected fitness loss due to predation risk."<ref name="Cooper10"/>
| |
| | |
| [[File:Common jassid nymphs and ants02.jpg|thumb|'''Symbiosis:''' [[Leafhopper]]s (''Eurymela fenestrata'') are protected by [[meat ant|ants]] (''Iridomyrmex purpureus'') in a [[symbiosis|symbiotic]] relationship. The ants protect the leafhoppers from predators and in return the leafhoppers feeding on plants exude honeydew from their anus that provides energy and nutrients to tending ants.<ref name="Eastwood04"/>]]
| |
| | |
| Elaborate sexual [[display (zoology)|displays]] and posturing are encountered in the behavioural ecology of animals. The [[birds of paradise]], for example, sing and display elaborate ornaments during [[courtship]]. These displays serve a dual purpose of signalling healthy or well-adapted individuals and desirable genes. The displays are driven by [[sexual selection]] as an advertisement of quality of traits among [[suitors]].<ref name="Kodric-Brown84"/>
| |
| | |
| ===Social ecology===
| |
| {{main|Social ecology}}
| |
| | |
| Social ecological behaviours are notable in the [[social insects]], [[slime moulds]], [[social spider]]s, [[human society]], and [[naked mole rat]]s where [[eusocialism]] has evolved. Social behaviours include reciprocally beneficial behaviours among kin and nest mates<ref name="Strassmann00" /><ref name="Wilson00" /><ref name="Sherman95"/> and evolve from kin and group selection. [[Kin selection]] explains altruism through genetic relationships, whereby an altruistic behaviour leading to death is rewarded by the survival of genetic copies distributed among surviving relatives. The social insects, including [[ant]]s, [[bee]]s and [[wasp]]s are most famously studied for this type of relationship because the male drones are [[clones]] that share the same genetic make-up as every other male in the colony.<ref name="Wilson00" /> In contrast, [[group selection]]ists find examples of altruism among non-genetic relatives and explain this through selection acting on the group, whereby it becomes selectively advantageous for groups if their members express altruistic behaviours to one another. Groups with predominantly altruistic members beat groups with predominantly selfish members.<ref name="Wilson00" /><ref name="Wilson07"/>
| |
| | |
| ===Coevolution===
| |
| {{main|Coevolution}}
| |
| [[Image:Bombus 6867.JPG|250px|thumb|[[Bumblebee]]s and the [[flower]]s they [[pollinisation|pollinate]] have coevolved so that both have become dependent on each other for survival.]]
| |
| Ecological interactions can be classified broadly into a [[host (biology)|host]] and an associate relationship. A host is any entity that harbours another that is called the associate.<ref name="Page91"/> Relationships [[Interspecific interaction|within a species]] that are mutually or reciprocally beneficial are called [[mutualisms]]. Examples of mutualism include [[fungus-growing ants]] employing agricultural symbiosis, bacteria living in the guts of insects and other organisms, the [[fig wasp]] and [[yucca moth]] pollination complex, [[lichen]]s with fungi and photosynthetic [[algae]], and [[coral]]s with photosynthetic algae.<ref name="Herre99"/><ref name="Gilbert90"/> If there is a physical connection between host and associate, the relationship is called [[symbiosis]]. Approximately 60% of all plants, for example, have a symbiotic relationship with [[arbuscular mycorrhizal fungi]] living in their roots forming an exchange network of carbohydrates for [[nutrients|mineral nutrients]].<ref name="Kiers06"/>
| |
| | |
| Indirect mutualisms occur where the organisms live apart. For example, trees living in the equatorial regions of the planet supply oxygen into the atmosphere that sustains species living in distant polar regions of the planet. This relationship is called [[commensalism]] because many others receive the benefits of clean air at no cost or harm to trees supplying the oxygen.<ref name="Odum05" /><ref>{{cite journal|last1=Strain | first1=B. R.|year=1985|title=Physiological and ecological controls on carbon sequestering in terrestrial ecosystems|journal=Biogeochemistry|volume=1|issue=3|pages=219–232|doi=10.1007/BF02187200}}</ref> If the associate benefits while the host suffers, the relationship is called [[parasitism]]. Although parasites impose a cost to their host (e.g., via damage to their reproductive organs or [[propagule]]s, denying the services of a beneficial partner), their net effect on host fitness is not necessarily negative and, thus, becomes difficult to forecast.<ref name="Bronstein01"/><ref name="Irwin10"/> Coevolution is also driven by competition among species or among members of the same species under the banner of reciprocal antagonism, such as grasses competing for growth space. The [[Red Queen Hypothesis]], for example, posits that parasites track down and specialize on the locally common genetic defence systems of its host that drives the evolution of sexual reproduction to diversify the genetic constituency of populations responding to the antagonistic pressure.<ref name="Boucher82"/><ref name="King09">{{cite journal | last1=King | first1=K. C. | last2=Delph | first2=L. F. | last3=Jokela | first3=J. | last4=Lively | first4=C. M. | title=The geographic mosaic of sex and the Red Queen | journal=Current Biology | volume=19 | issue=17 | pages=1438–1441 | url=http://www.sciencedirect.com/science/article/pii/S0960982209013797 | doi=10.1016/j.cub.2009.06.062| year=2009 | pmid=19631541 }}</ref>
| |
| | |
| [[File:Parasitismus.jpg|right|thumb|300px|'''Parasitism:''' A harvestman [[arachnid]] being parasitized by [[mites]]. The harvestman is being consumed, while the mites benefit from traveling on and feeding off of their host.]]
| |
| | |
| ===Biogeography===
| |
| {{Main|Biogeography}}
| |
| | |
| Biogeography (an amalgamation of ''biology'' and ''geography'') is the comparative study of the geographic distribution of organisms and the corresponding evolution of their traits in space and time.<ref name="Parenti90"/> The ''[[Journal of Biogeography]]'' was established in 1974.<ref name="JBiog">{{cite web | title = Journal of Biogeography | publisher = Wiley | url = http://www.wiley.com/bw/journal.asp?ref=0305-0270 | accessdate = August 3, 2012}}</ref> Biogeography and ecology share many of their disciplinary roots. For example, [[Island biogeography|the theory of island biogeography]], published by the mathematician Robert MacArthur and ecologist [[Edward O. Wilson]] in 1967<ref name="MacArthur67" /> is considered one of the fundamentals of ecological theory.<ref name="Wiens04"/>
| |
| | |
| Biogeography has a long history in the natural sciences concerning the spatial distribution of plants and animals. Ecology and evolution provide the explanatory context for biogeographical studies.<ref name="Parenti90" /> Biogeographical patterns result from ecological processes that influence range distributions, such as [[Animal migration|migration]] and [[Biological dispersal|dispersal]].<ref name="Wiens04" /> and from historical processes that split populations or species into different areas. The biogeographic processes that result in the natural splitting of species explains much of the modern distribution of the Earth's biota. The splitting of lineages in a species is called [[Allopatric speciation|vicariance biogeography]] and it is a sub-discipline of biogeography.<ref name="Morrone95"/> There are also practical applications in the field of biogeography concerning ecological systems and processes. For example, the range and distribution of biodiversity and invasive species responding to climate change is a serious concern and active area of research in the context of [[global warming]].<ref name="Svennin08" /><ref name="Landhäusser09"/>
| |
| | |
| ====''r/K''-Selection theory====
| |
| {{Main|r/K selection}}
| |
| | |
| A population ecology concept is r/K selection theory,{{Cref2|D}} one of the first predictive models in ecology used to explain [[Life history theory|life-history evolution]]. The premise behind the r/K selection model is that natural selection pressures change according to [[population densities|population density]]. For example, when an island is first colonized, density of individuals is low. The initial increase in population size is not limited by competition, leaving an abundance of available resources for rapid population growth. These early phases of [[population growth]] experience ''density-independent'' forces of natural selection, which is called ''r''-selection. As the population becomes more crowded, it approaches the island's carrying capacity, thus forcing individuals to compete more heavily for fewer available resources. Under crowded conditions, the population experiences density-dependent forces of natural selection, called ''K''-selection.<ref name="Reznick02"/>
| |
| | |
| In the ''r/K''-selection model, the first variable ''r'' is the intrinsic rate of natural increase in population size and the second variable ''K'' is the carrying capacity of a population.<ref name="Begon05" /> Different species evolve different life-history strategies spanning a continuum between these two selective forces. An ''r''-selected species is one that has high birth rates, low levels of parental investment, and high rates of mortality before individuals reach maturity. Evolution favours high rates of [[fecundity]] in ''r''-selected species. Many kinds of insects and [[invasive species]] exhibit ''r''-selected [[Phenotypic trait|characteristics]]. In contrast, a ''K''-selected species has low rates of fecundity, high levels of parental investment in the young, and low rates of mortality as individuals mature. Humans and elephants are examples of species exhibiting ''K''-selected characteristics, including longevity and efficiency in the conversion of more resources into fewer offspring.<ref name="MacArthur67"/><ref name="Pianka72"/>
| |
| | |
| ===Molecular ecology===
| |
| {{Main|Molecular ecology}}
| |
| | |
| The important relationship between ecology and genetic inheritance predates modern techniques for molecular analysis. Molecular ecological research became more feasible with the development of rapid and accessible genetic technologies, such as the [[Polymerase chain reaction|polymerase chain reaction (PCR)]]. The rise of molecular technologies and influx of research questions into this new ecological field resulted in the publication ''[[Molecular Ecology]]'' in 1992.<ref name="MolEcol">{{Cite journal| title = Molecular Ecology | editor-last=Rieseberg | editor-first= L. | publisher = Wiley | doi = 10.1111/(ISSN)1365-294X | journal = Molecular Ecology }}</ref> [[Molecular ecology]] uses various analytical techniques to study genes in an evolutionary and ecological context. In 1994, [[John Avise]] also played a leading role in this area of science with the publication of his book, ''Molecular Markers, Natural History and Evolution''.<ref name="Avise94"/> Newer technologies opened a wave of genetic analysis into organisms once difficult to study from an ecological or evolutionary standpoint, such as bacteria, fungi and [[nematodes]]. Molecular ecology engendered a new research paradigm for investigating ecological questions considered otherwise intractable. Molecular investigations revealed previously obscured details in the tiny intricacies of nature and improved resolution into probing questions about behavioural and biogeographical ecology.<ref name="Avise94"/> For example, molecular ecology revealed [[promiscuous]] sexual behaviour and multiple male partners in [[tree swallow]]s previously thought to be socially [[monogamous]].<ref name="Obryan07"/> In a biogeographical context, the marriage between genetics, ecology and evolution resulted in a new sub-discipline called [[phylogeography]].<ref name="Avise00"/>
| |
| | |
| ==Human ecology==
| |
| {{Main|Human ecology}}
| |
| {{quote box
| |
| | quote = The history of life on Earth has been a history of interaction between living things and their surroundings. To a large extent, the physical form and the habits of the earth's vegetation and its animal life have been molded by the environment. Considering the whole span of earthly time, the opposite effect, in which life actually modifies its surroundings, has been relatively slight. Only within the moment of time represented by the present century has one species man acquired significant power to alter the nature of his world.
| |
| | source = Rachel Carson, "Silent Spring"<ref name=Carson/>
| |
| | width = 25%
| |
| | align = left}}
| |
| | |
| Ecology is as much a biological science as it is a human science.<ref name="Odum05" /> Human ecology is an [[interdisciplinary]] investigation into the ecology of our species. "Human ecology may be defined: (1) from a bio-ecological standpoint as the study of man as the ecological dominant in plant and animal communities and systems; (2) from a bio-ecological standpoint as simply another animal affecting and being affected by his physical environment; and (3) as a human being, somehow different from animal life in general, interacting with physical and modified environments in a distinctive and creative way. A truly interdisciplinary human ecology will most likely address itself to all three."<ref name="Young74"/>{{rp|3}} The term was formally introduced in 1921, but many sociologists, geographers, psychologists, and other disciplines were interested in human relations to natural systems centuries prior, especially in the late 19th century.<ref name="Young74"/><ref name="Gross04"/>
| |
| | |
| The ecological complexities human beings are facing through the technological transformation of the planetary biome has brought on the [[Anthropocene]]. The unique set of circumstances has generated the need for a new unifying science called [[coupled human and natural systems]] that builds upon, but moves beyond the field of human ecology.<ref name="Liu09" /> Ecosystems tie into human societies through the critical and all encompassing life-supporting functions they sustain. In recognition of these functions and the incapability of traditional economic valuation methods to see the value in ecosystems, there has been a surge of interest in [[social capital|social]]-[[natural capital]], which provides the means to put a value on the stock and use of information and materials stemming from [[ecosystem services|ecosystem goods and services]]. Ecosystems produce, regulate, maintain, and supply services of critical necessity and beneficial to human health (cognitive and physiological), economies, and they even provide an information or reference function as a living library giving opportunities for science and cognitive development in children engaged in the complexity of the natural world. Ecosystems relate importantly to human ecology as they are the ultimate base foundation of global economics as every commodity and the capacity for exchange ultimately stems from the ecosystems on Earth.<ref name="Liu09" /><ref name="MEA05"/><ref name="de Groot02"/><ref name="Aguirre09"/>
| |
| | |
| ===Restoration and management===
| |
| {{main|Restoration ecology}}
| |
| {{see also|Natural resource management}}
| |
| | |
| {{quote box
| |
| | quote = Ecosystem management is not just about science nor is it simply an extension of traditional resource management; it offers a fundamental reframing of how humans may work with nature.
| |
| | source = Grumbine (1994)<ref name="Grumbine94">{{cite journal | last1=Grumbine | first1=R. E. | year=1994 | title=What is ecosystem management? | journal=Conservation Biology | volume=8 | issue=1 | pages=27–38 | url=http://www.pelagicos.net/MARS6920_spring2010/readings/Grumbine_1994.pdf}}</ref>{{Rp|27}}
| |
| | width = 25%
| |
| | align = right}}
| |
| | |
| Ecology is an employed science of restoration, repairing disturbed sites through human intervention, in natural resource management, and in [[environmental impact assessment]]s. Edward O. Wilson predicted in 1992 that the 21st century "will be the era of restoration in ecology".<ref name="Wilson92">{{cite book | last1=Wilson | first1=E. O. | year=1992 | title=The Diversity of Life | publisher=Harvard University Press | isbn=978-0-674-05817-0 | page=440 | url=http://books.google.ca/books?id=ZSqehqH-qTYC&printsec=frontcover#v=onepage&q&f=false}}</ref> Ecological science has boomed in the industrial investment of restoring ecosystems and their processes in abandoned sites after disturbance. Natural resource managers, in [[silviculture|forestry]], for example, employ ecologists to develop, adapt, and implement [[Ecosystem management|ecosystem based methods]] into the planning, operation, and restoration phases of land-use. Ecological science is used in the methods of sustainable harvesting, disease and fire outbreak management, in fisheries stock management, for integrating land-use with protected areas and communities, and conservation in complex geo-political landscapes.<ref name="Hammond09" /><ref name="Grumbine94" /><ref name="Grumbine94">{{cite journal | last1=Grumbine | first1=R. E. | title=What is ecosystem management? | journal=Conservation Biology | volume=8 | issue=1 | year=1994 | pages=27–38 | url=http://www.pelagicos.net/MARS6920_spring2010/readings/Grumbine_1994.pdf}}</ref><ref name="Slocombe93">{{cite journal | last1=Slocombe | first1=D. S. | title=Implementing ecosystem-based management | volume=43 | issue=9 | pages=612–622 | year=1993 | jstor=1312148}}</ref><ref name="Hobbs01">{{cite journal | last1=Hobss | first1=R. J. | last2=Harris | first2=J. A. | title=Restoration ecology: Repairing the Earth's ecosystems in the new millennium | journal=Restoration Ecology | volume=9 | issue=2 | pages=239–246 | doi=10.1046/j.1526-100x.2001.009002239.x | url=http://planet.botany.uwc.ac.za/nisl/invasives/assignment1/hobbsandharris.pdf| year=2001 }}</ref>
| |
| | |
| ==Relation to the environment==
| |
| {{main|Natural environment}}
| |
| | |
| The environment of ecosystems includes both physical parameters and biotic attributes. It is dynamically interlinked, and contains resources for organisms at any time throughout their life cycle.<ref name="Odum05" /><ref name="Mason57"/> Like "ecology," the term "environment" has different conceptual meanings and overlaps with the concept of "nature." Environment "... includes the physical world, the social world of human relations and the built world of human creation."<ref name="Kleese01"/>{{Rp|62}} The physical environment is external to the level of biological organization under investigation, including [[abiotic]] factors such as temperature, radiation, light, chemistry, [[climate]] and geology. The biotic environment includes genes, cells, organisms, members of the same species ([[conspecific]]s) and other species that share a habitat.<ref name="Campbell06"/>
| |
| | |
| The distinction between external and internal environments, however, is an abstraction parsing life and environment into units or facts that are inseparable in reality. There is an interpenetration of cause and effect between the environment and life. The laws of [[thermodynamics]], for example, apply to ecology by means of its physical state. With an understanding of metabolic and thermodynamic principles, a complete accounting of energy and material flow can be traced through an ecosystem. In this way, the environmental and ecological relations are studied through reference to conceptually manageable and isolated [[materialism|material]] parts. After the effective environmental components are understood through reference to their causes, however, they conceptually link back together as an integrated whole, or ''holocoenotic'' system as it was once called. This is known as the [[dialectical]] approach to ecology. The dialectical approach examines the parts, but integrates the organism and the environment into a dynamic whole (or [[umwelt]]). Change in one ecological or environmental factor can concurrently affect the dynamic state of an entire ecosystem.<ref name="Levins80" /><ref name="Kormondy95"/>
| |
| | |
| ===Disturbance and resilience===
| |
| {{Main|Resilience (ecology)}}
| |
| | |
| Ecosystems are regularly confronted with natural environmental variations and disturbances over time and geographic space. A disturbance is any process that removes biomass from a community, such as a fire, flood, drought, or predation.<ref name="Hughes10"/> Disturbances occur over vastly different ranges in terms of magnitudes as well as distances and time periods,<ref name="Levin92"/> and are both the cause and product of natural fluctuations in death rates, species assemblages, and biomass densities within an ecological community. These disturbances create places of renewal where new directions emerge from the patchwork of natural experimentation and opportunity.<ref name="Hughes10"/><ref name="Holling73" /><ref name="Folke04"/> Ecological resilience is a cornerstone theory in ecosystem management. Biodiversity fuels the resilience of ecosystems acting as a kind of regenerative insurance.<ref name="Folke04"/>
| |
| | |
| ===Metabolism and the early atmosphere===
| |
| | |
| {{quote box
| |
| | quote = Metabolism – the rate at which energy and material resources are taken up from the environment, transformed within an organism, and allocated to maintenance, growth and reproduction – is a fundamental physiological trait.
| |
| | source = Ernest et al.<ref name="Ernest03"/>{{Rp|991}}
| |
| | width=25%
| |
| | align=right
| |
| }}
| |
| | |
| The Earth was formed approximately 4.5 billion years ago.<ref name="Allègre95"/> As it cooled and a crust and oceans formed, its atmosphere transformed from being dominated by [[hydrogen]] to one composed mostly of [[methane]] and [[ammonia]]. Over the next billion years, the metabolic activity of life transformed the atmosphere into a mixture of [[carbon dioxide]], [[nitrogen]], and water vapor. These gases changed the way that light from the sun hit the Earth's surface and greenhouse effects trapped heat. There were untapped sources of free energy within the mixture of [[Redox|reducing and oxidizing]] gasses that set the stage for primitive ecosystems to evolve and, in turn, the atmosphere also evolved.<ref name="Wills01"/>
| |
| | |
| [[File:Leaf 1 web.jpg|left|thumb|The [[leaf]] is the primary site of [[photosynthesis]] in most plants.]]
| |
| | |
| Throughout history, the Earth's atmosphere and [[biogeochemical cycles]] have been in a [[dynamic equilibrium]] with planetary ecosystems. The history is characterized by periods of significant transformation followed by millions of years of stability.<ref name="Goldblatt06"/> The evolution of the earliest organisms, likely anaerobic [[methanogen]] microbes, started the process by converting atmospheric hydrogen into methane (4H<sub>2</sub> + CO<sub>2</sub> → CH<sub>4</sub> + 2H<sub>2</sub>O). [[Anoxygenic photosynthesis]] reduced hydrogen concentrations and increased atmospheric methane, by converting [[hydrogen sulfide]] into water or other sulfur compounds (for example, 2H<sub>2</sub>S + CO<sub>2</sub> + h''v'' → CH<sub>2</sub>O + H<sub>2</sub>O + 2S). Early forms of [[Fermentation (biochemistry)|fermentation]] also increased levels of atmospheric methane. The transition to an oxygen-dominant atmosphere (the ''[[Great Oxygenation Event|Great Oxidation]]'') did not begin until approximately 2.4–2.3 billion years ago, but photosynthetic processes started 0.3 to 1 billion years prior.<ref name="Goldblatt06"/><ref name="Catling05"/>
| |
| | |
| ===Radiation: heat, temperature and light===
| |
| | |
| {{Anchor|Sunlight}}<!-- E.g. in [[Neritic zone]] -->
| |
| The biology of life operates within a certain range of temperatures. Heat is a form of energy that regulates temperature. Heat affects growth rates, activity, behaviour and [[primary production]]. Temperature is largely dependent on the incidence of [[solar radiation]]. The latitudinal and longitudinal spatial variation of [[temperature]] greatly affects climates and consequently the distribution of [[biodiversity]] and levels of primary production in different ecosystems or biomes across the planet. Heat and temperature relate importantly to metabolic activity. [[Poikilotherms]], for example, have a body temperature that is largely regulated and dependent on the temperature of the external environment. In contrast, [[homeotherms]] regulate their internal body temperature by expending [[food energy|metabolic energy]].<ref name="Allee49"/><ref name="Ricklefs96"/><ref name="Kormondy95"/>
| |
| | |
| There is a relationship between light, primary production, and ecological [[energy budget]]s. Sunlight is the primary input of energy into the planet's ecosystems. Light is composed of [[electromagnetic energy]] of different [[wavelength]]s. [[Radiant energy]] from the sun generates heat, provides photons of light measured as active energy in the chemical reactions of life, and also acts as a catalyst for [[genetic mutation]].<ref name="Allee49"/><ref name="Ricklefs96"/><ref name="Kormondy95"/> Plants, algae, and some bacteria absorb light and assimilate the energy through [[photosynthesis]]. Organisms capable of assimilating energy by photosynthesis or through inorganic fixation of [[hydrogen sulfide|H<sub>2</sub>S]] are [[autotrophs]]. Autotrophs — responsible for primary production — assimilate light energy which becomes metabolically stored as [[potential energy]] in the form of biochemical [[Enthalpy|enthalpic]] bonds.<ref name="Allee49"/><ref name="Ricklefs96"/><ref name="Kormondy95"/>
| |
| | |
| ===Physical environments===
| |
| | |
| ====Water====
| |
| {{Main|Aquatic ecosystem}}
| |
| {{quote box
| |
| | quote = Wetland conditions such as shallow water, high plant productivity, and anaerobic substrates provide a suitable environment for important physical, biological, and chemical processes. Because of these processes, wetlands play a vital role in global nutrient and element cycles.
| |
| | source = Cronk & Fennessy (2001)<ref name="Cronk01" />{{Rp|29}}
| |
| | width = 25%
| |
| | align = right}}
| |
| Diffusion of carbon dioxide and oxygen is approximately 10,000 times slower in water than in air. When soils are flooded, they quickly lose oxygen, becoming [[Hypoxia (environmental)|hypoxic]] (an environment with O<sub>2</sub> concentration below 2 mg/liter) and eventually completely [[Anoxic waters|anoxic]] where [[anaerobic bacteria]] thrive among the roots. Water also influences the intensity and [[Electromagnetic spectrum|spectral composition]] of light as it reflects off the water surface and submerged particles.<ref name="Cronk01"/> Aquatic plants exhibit a wide variety of morphological and physiological adaptations that allow them to survive, compete and diversify in these environments. For example, their roots and stems contain large air spaces ([[aerenchyma]]) that regulate the efficient transportation of gases (for example, CO<sub>2</sub> and O<sub>2</sub>) used in respiration and photosynthesis. Salt water plants ([[halophytes]]) have additional specialized adaptations, such as the development of special organs for shedding salt and [[osmoregulation|osmoregulating]] their internal salt (NaCl) concentrations, to live in [[estuarine]], [[brackish]], or [[ocean]]ic environments. Anaerobic soil microorganisms in aquatic environments use [[nitrate]], [[Manganese|manganese ions]], [[ferric|ferric ions]], [[sulfate]], [[carbon dioxide]] and some [[organic compounds]]; other microorganisms are [[facultative anaerobes]] and use oxygen during respiration when the soil becomes drier. The activity of soil microorganisms and the chemistry of the water reduces the [[Reduction potential|oxidation-reduction]] potentials of the water. Carbon dioxide, for example, is reduced to methane (CH<sub>4</sub>) by methanogenic bacteria.<ref name="Cronk01"/> The physiology of fish is also specially adapted to compensate for environmental salt levels through osmoregulation. Their gills form [[electrochemical gradient]]s that mediate salt excretion in salt water and uptake in fresh water.<ref name="Evans99"/>
| |
| | |
| ====Gravity====
| |
| The shape and energy of the land is significantly affected by gravitational forces. On a large scale, the distribution of gravitational forces on the earth is uneven and influences the shape and movement of [[tectonic plates]] as well as influencing [[geomorphic]] processes such as [[orogeny]] and [[erosion]]. These forces govern many of the geophysical properties and distributions of ecological biomes across the Earth. On the organismal scale, gravitational forces provide directional cues for plant and fungal growth ([[gravitropism]]), orientation cues for animal migrations, and influence the [[biomechanics]] and size of animals.<ref name="Allee49"/> Ecological traits, such as allocation of biomass in trees during growth are subject to mechanical failure as gravitational forces influence the position and structure of branches and leaves.<ref name="Swenson08"/> The [[Circulatory system|cardiovascular systems]] of animals are functionally adapted to overcome pressure and gravitational forces that change according to the features of organisms (e.g., height, size, shape), their behaviour (e.g., diving, running, flying), and the habitat occupied (e.g., water, hot deserts, cold tundra).<ref name="Garnter10"/>
| |
| | |
| ====Pressure====
| |
| Climatic and [[osmotic pressure]] places [[physiological]] constraints on organisms, especially those that fly and respire at high altitudes, or dive to deep ocean depths. These constraints influence vertical limits of ecosystems in the biosphere, as organisms are physiologically sensitive and adapted to atmospheric and osmotic water pressure differences.<ref name="Allee49"/> For example, oxygen levels decrease with decreasing pressure and are a limiting factor for life at higher altitudes.<ref name="Jacobsen08"/> [[Xylem|Water transportation]] by plants is another important ecophysiological parameter affected by osmotic pressure gradients.<ref name="Strook08"/><ref name="Pockman95"/><ref name="Zimmermann02"/> [[Fluid pressure|Water pressure]] in the depths of oceans requires that organisms adapt to these conditions. For example, diving animals such as [[whale]]s, [[dolphin]]s and [[seal (animal)|seals]] are specially adapted to deal with changes in sound due to water pressure differences.<ref name="Kastak98"/> Differences between [[hagfish]] species provide another example of adaptation to deep-sea pressure through specialized protein adaptations.<ref name="Nishiguchi10"/>
| |
| | |
| ====Wind and turbulence====
| |
| [[File:Grassflowers.jpg|thumb|The architecture of the [[inflorescence]] in grasses is subject to the physical pressures of wind and shaped by the forces of natural selection facilitating wind-pollination ([[anemophily]]).<ref name="Friedman04"/><ref name="Harder09"/>]]
| |
| | |
| [[Turbulent forces]] in air and water affect the environment and ecosystem distribution, form and dynamics. On a planetary scale, ecosystems are affected by circulation patterns in the global [[trade winds]]. Wind power and the turbulent forces it creates can influence heat, nutrient, and biochemical profiles of ecosystems.<ref name="Allee49"/> For example, wind running over the surface of a lake creates turbulence, mixing the [[water column]] and influencing the environmental profile to create [[thermally layered zones]], affecting how fish, algae, and other parts of the [[aquatic ecosystem]] are structured.<ref name="Shimeta95"/><ref name="Etemad01"/> Wind speed and turbulence also influence [[evapotranspiration rates]] and energy budgets in plants and animals.<ref name="Cronk01" /><ref name="Wolf96"/> Wind speed, temperature and moisture content can vary as winds travel across different land features and elevations. For example, the [[westerlies]] come into contact with the coastal and interior mountains of western North America to produce a [[rain shadow]] on the leeward side of the mountain. The air expands and moisture condenses as the winds increase in elevation; this is called [[orographic lift]] and can cause precipitation.{{clarify|this sounds as if the rain would fall on the leeward side of the mountains, which can't be right|date=August 2012}} This environmental process produces spatial divisions in biodiversity, as species adapted to wetter conditions are range-restricted to the coastal mountain valleys and unable to migrate across the [[xeric]] ecosystems (e.g., of the [[Columbia Basin]] in western North America) to intermix with sister lineages that are segregated to the interior mountain systems.<ref name="Daubenmire75"/><ref name="Steele05"/>
| |
| | |
| ====Fire====
| |
| {{Main|Fire ecology}}
| |
| | |
| {{multiple image
| |
| | footer = Forest fires modify the land by leaving behind an environmental mosaic that diversifies the landscape into different [[seral community|seral]] stages and habitats of varied quality (left). Some species are adapted to forest fires, such as pine trees that open their cones only after fire exposure (right).
| |
| | align = left
| |
| | image1 = Mosaic fire burn.jpg
| |
| | width1 = {{#expr: (100 * 1999 / 1277) round 0}}
| |
| | image2 = Lodgepole pine cone after fire.jpg
| |
| | width2 = {{#expr: (100 * 1999 / 1355) round 0}}
| |
| }}
| |
| | |
| Plants convert carbon dioxide into biomass and emit oxygen into the atmosphere. By approximately 350 million years ago (the end of the [[Devonian period]]), photosynthesis had brought the concentration of atmospheric oxygen above 17%, which allowed combustion to occur.<ref name="Lenton00"/> Fire releases CO<sub>2</sub> and converts fuel into ash and tar. Fire is a significant ecological parameter that raises many issues pertaining to its control and suppression.<ref name="Lobert93"/> While the issue of fire in relation to ecology and plants has been recognized for a long time,<ref name="Garren43"/> [[Charles F. Cooper (ecologist)|Charles Cooper]] brought attention to the issue of forest fires in relation to the ecology of forest fire suppression and management in the 1960s.<ref name="Cooper60"/><ref name="Cooper61"/>
| |
| | |
| [[Indigenous peoples of the Americas|Native North Americans]] were among the first to influence fire regimes by controlling their spread near their homes or by lighting fires to stimulate the production of herbaceous foods and basketry materials.<ref name="Wagtendonk07"/> Fire creates a heterogenous ecosystem age and canopy structure, and the altered soil nutrient supply and cleared canopy structure opens new ecological niches for seedling establishment.<ref name="Boerner82"/><ref name="Goubitz03"/> Most ecosystems are adapted to natural fire cycles. Plants, for example, are equipped with a variety of adaptations to deal with forest fires. Some species (e.g., ''[[Pinus halepensis]]'') cannot [[germination|germinate]] until after their seeds have lived through a fire or been exposed to certain compounds from smoke. Environmentally triggered germination of seeds is called [[serotiny]].<ref name="Neeman04"/><ref name="Flematti04"/> Fire plays a major role in the persistence and [[Resilience (ecology)|resilience]] of ecosystems.<ref name="Holling73"/>
| |
| | |
| ====Soils====
| |
| {{main|Soil ecology}}
| |
| | |
| Soil is the living top layer of mineral and organic dirt that covers the surface of the planet. It is the chief organizing centre of most ecosystem functions, and it is of critical importance in agricultural science and ecology. The [[decomposition]] of dead organic matter (for example, leaves on the forest floor), results in soils containing [[minerals]] and nutrients that feed into plant production. The whole of the planet's soil ecosystems is called the [[pedosphere]] where a large biomass of the Earth's biodiversity organizes into trophic levels. Invertebrates that feed and shred larger leaves, for example, create smaller bits for smaller organisms in the feeding chain. Collectively, these organisms are the [[detritivore]]s that regulate soil formation.<ref name="Coleman04"/><ref name="Wilkinson09"/> Tree roots, fungi, bacteria, worms, ants, beetles, centipedes, spiders, mammals, birds, reptiles, amphibians and other less familiar creatures all work to create the trophic web of life in soil ecosystems. Soils form composite phenotypes where inorganic matter is enveloped into the physiology of a whole community. As organisms feed and migrate through soils they physically displace materials, an ecological process called [[bioturbation]]. This aerates soils and stimulates heterotrophic growth and production. Soil [[microorganisms]] are influenced by and feed back into the trophic dynamics of the ecosystem. No single axis of causality can be discerned to segregate the biological from geomorphological systems in soils.<ref name="Phillips09">{{cite journal | last1=Phillips | first1=J. D. | year=2009 | title=Soils as extended composite phenotypes | volume=149 | issue=1–2 | pages=143–151 | journal=Geoderma | doi=10.1016/j.geoderma.2008.11.028}}</ref><ref name="Reinhard10">{{cite journal | last1=Reinhardt | first1=L. | last2=Jerolmack | first2=D. | last3=Cardinale | first3=B. J. | last4=Vanacker | first4=V. | last5=Wright | first5=J. | title=Dynamic interactions of life and its landscape: Feedbacks at the interface of geomorphology and ecology | journal=Earth Surf. Process. Landforms | volume=35 | pages=78–101 | doi=10.1002/esp | url=http://www.snre.umich.edu/cardinale/pdfs/reinhardt_earthsur_2010.pdf| doi_inactivedate=2014-02-02 }}</ref> [[Paleoecology|Paleoecological]] studies of soils places the origin for bioturbation to a time before the Cambrian period. Other events, such as the [[Tree#Evolutionary history|evolution of trees]] and the [[Evolutionary history of life#Colonization of land|colonization of land]] in the Devonian period played a significant role in the early development of ecological trophism in soils.<ref name="Davic04"/><ref name="Wilkinson09"/><ref name="Hasiotis03"/>
| |
| | |
| ====Biogeochemistry and climate====
| |
| {{Main|Biogeochemistry}}
| |
| {{See also|Nutrient cycle|Climate}}
| |
| | |
| Ecologists study and measure nutrient budgets to understand how these materials are regulated, flow, and [[recycling (ecological)|recycled]] through the environment.<ref name="Allee49"/><ref name="Ricklefs96"/><ref name="Kormondy95"/> This research has led to an understanding that there is global feedback between ecosystems and the physical parameters of this planet, including minerals, soil, pH, ions, water and atmospheric gases. Six major elements ([[hydrogen]], [[carbon]], [[nitrogen]], [[oxygen]], [[sulfur]], and [[phosphorus]]; H, C, N, O, S, and P) form the constitution of all biological macromolecules and feed into the Earth's geochemical processes. From the smallest scale of biology, the combined effect of billions upon billions of ecological processes amplify and ultimately regulate the [[biogeochemical cycle]]s of the Earth. Understanding the relations and cycles mediated between these elements and their ecological pathways has significant bearing toward understanding global biogeochemistry.<ref name="Falkowoski08"/>
| |
| | |
| The ecology of global carbon budgets gives one example of the linkage between biodiversity and biogeochemistry. It is estimated that the Earth's oceans hold 40,000 gigatonnes (Gt) of carbon, that vegetation and soil hold 2070 Gt, and that fossil fuel emissions are 6.3 Gt carbon per year.<ref name="Grace04"/> There have been major restructurings in these global carbon budgets during the Earth's history, regulated to a large extent by the ecology of the land. For example, through the early-mid Eocene volcanic [[outgassing]], the oxidation of methane stored in wetlands, and seafloor gases increased atmospheric CO<sub>2</sub> (carbon dioxide) concentrations to levels as high as 3500 [[Parts per million|ppm]].<ref name="Pearson00"/>
| |
| | |
| In the [[Oligocene]], from 25 to 32 million years ago, there was another significant restructuring of the global [[carbon cycle]] as grasses evolved a new mechanism of photosynthesis, [[C4 carbon fixation|C<sub>4</sub> photosynthesis]], and expanded their ranges. This new pathway evolved in response to the drop in atmospheric CO<sub>2</sub> concentrations below 550 ppm.<ref name="Pagani05"/> The relative abundance and distribution of biodiversity alters the dynamics between organisms and their environment such that ecosystems can be both cause and effect in relation to climate change. Human-driven modifications to the planet's ecosystems (e.g., disturbance, biodiversity loss, agriculture) contributes to rising atmospheric greenhouse gas levels. Transformation of the global carbon cycle in the next century is projected to raise planetary temperatures, lead to more extreme fluctuations in weather, alter species distributions, and increase extinction rates. The effect of global warming is already being registered in melting glaciers, melting mountain ice caps, and rising sea levels. Consequently, species distributions are changing along waterfronts and in continental areas where migration patterns and breeding grounds are tracking the prevailing shifts in climate. Large sections of [[permafrost]] are also melting to create a new mosaic of flooded areas having increased rates of soil decomposition activity that raises methane (CH<sub>4</sub>) emissions. There is concern over increases in atmospheric methane in the context of the global carbon cycle, because methane is a [[greenhouse gas]] that is 23 times more effective at absorbing long-wave radiation than CO<sub>2</sub> on a 100-year time scale.<ref name="Zhuan07"/> Hence, there is a relationship between global warming, decomposition and respiration in soils and wetlands producing significant climate feedbacks and globally altered biogeochemical cycles.<ref name="Liu09"/><ref name="Cox00"/><ref name="Erwin09">{{cite journal | last1=Erwin | first1=D. H. | year=2009 | title=Climate as a driver of evolutionary change | journal=Current Biology | volume=19 |issue=14 | pages=R575–R583 | url=http://www.sciencedirect.com/science/article/pii/S0960982209011828 | doi=10.1016/j.cub.2009.05.047| pmid=19640496 }}</ref><ref name="Bamber12">{{cite journal | last1=Bamber | first1=J. | year=2012 | title=Shrinking glaciers under scrutiny | journal=Nature | volume= 482 | pages=482–483 | url=http://mason.gmu.edu/~bklinger/CLIM690/onjacobetal12.pdf | doi=10.1038/nature10948|bibcode = 2012Natur.482..482B | issue=7386 | pmid=22318516 }}</ref><ref name="Heiman08"/><ref name="Davidson06"/>
| |
| | |
| ==History==
| |
| {{Main|History of ecology}}
| |
| | |
| ===Early beginnings===
| |
| Ecology has a complex origin, due in large part to its interdisciplinary nature.<ref name="Egerton01"/> Ancient Greek philosophers such as [[Hippocrates]] and [[Aristotle]] were among the first to record observations on natural history. However, they viewed life in terms of [[essentialism]], where species were conceptualized as static unchanging things while varieties were seen as aberrations of an [[Idealism|idealized type]]. This contrasts against the modern understanding of [[Theoretical ecology|ecological theory]] where varieties are viewed as the real phenomena of interest and having a role in the origins of adaptations by means of [[natural selection]].<ref name="Odum05" /><ref name="Benson00"/><ref name="Sober80">{{cite journal | last1=Sober | first1=E. | title=Evolution, population thinking, and essentialism | journal=Philosophy of Science | volume=47 | issue=3 | pages=350–383 | jstor=186950}}</ref> Early conceptions of ecology, such as a balance and regulation in nature can be traced to [[Herodotus]] (died ''c''. 425 BC), who described one of the earliest accounts of [[mutualism (biology)|mutualism]] in his observation of "natural dentistry". Basking [[Nile crocodile]]s, he noted, would open their mouths to give [[sandpiper]]s safe access to pluck [[leech]]es out, giving nutrition to the sandpiper and oral hygiene for the crocodile.<ref name="Egerton01" /> Aristotle was an early influence on the philosophical development of ecology. He and his student [[Theophrastus]] made extensive observations on plant and animal migrations, biogeography, physiology, and on their behaviour, giving an early analogue to the modern concept of an ecological niche.<ref name="Hughes85"/><ref name="Hughes75"/>
| |
| | |
| Ecological concepts such as food chains, population regulation, and productivity were first developed in the 1700s, through the published works of microscopist [[Antoni van Leeuwenhoek]] (1632–1723) and botanist [[Richard Bradley (botanist)|Richard Bradley]] (1688?–1732).<ref name="Odum05" /> Biogeographer [[Alexander von Humboldt]] (1769–1859) was an early pioneer in ecological thinking and was among the first to recognize ecological gradients, where species are replaced or altered in form along [[environmental gradient]]s, such as a [[cline (biology)|cline]] forming along a rise in elevation. Humboldt drew inspiration from [[Isaac Newton]] as he developed a form of "terrestrial physics." In Newtonian fashion, he brought a scientific exactitude for measurement into natural history and even alluded to concepts that are the foundation of a modern ecological law on species-to-area relationships.<ref name="Kingsland04" /><ref name="Rosenzweig03"/><ref name="Hawkins01"/> Natural historians, such as Humboldt, [[James Hutton]] and [[Jean-Baptiste Lamarck]] (among others) laid the foundations of the modern ecological sciences.<ref name="McIntosh85">{{cite book | last1=McIntosh | first1=R. P. | title=The Background of Ecology: Concept and Theory | publisher=Cambridge University Press | year=1985 | isbn=0-521-27087-1 | page=400 | url=http://books.google.ca/books?id=1bYSnG7RITAC&printsec=frontcover#v=onepage&q&f=false}}</ref> The term "ecology" ({{lang-de|Oekologie, Ökologie}}) is of a more recent origin and was first coined by the German biologist [[Ernst Haeckel]] in his book ''Generelle Morphologie der Organismen'' (1866). Haeckel was a zoologist, artist, writer, and later in life a professor of comparative anatomy.<ref name="Stauffer57"/><ref name="Friederichs58"/>
| |
| | |
| {{quote box
| |
| | quote = By ecology, we mean the whole science of the relations of the organism to the environment including, in the broad sense, all the "conditions of existence."... Thus the theory of evolution explains the housekeeping relations of organisms mechanistically as the necessary consequences of effectual causes and so forms the [[monism|monistic]] groundwork of ecology.
| |
| | source = Ernst Haeckel (1866)<ref name="Stauffer57" />{{Rp|140}} {{Cref2|B}}
| |
| | width = 30%
| |
| | align = right}}
| |
| | |
| <div class="thumb tleft" style="background:#f9f9f9; padding:5px; border:1px solid gray; margin:0.5em; font-size:11px;">
| |
| [[File:Nicola Perscheid - Ernst Haeckel.jpg|90px]] [[File:Warming,Eugen-c1900.jpg|90px]]
| |
| <div style="border: none; width:180px;"><div class="thumbcaption"> [[Ernst Haeckel]] (left) and [[Eugenius Warming]] (right), two founders of ecology</div></div></div>
| |
| | |
| Opinions differ on who was the founder of modern ecological theory. Some mark Haeckel's definition as the beginning;<ref name="Hinchman07"/> others say it was [[Eugenius Warming]] with the writing of [[Plantesamfund|Oecology of Plants: An Introduction to the Study of Plant Communities]] (1895),<ref name="Goodland75"/> or [[Carl Linnaeus]]' principles on the economy of nature that matured in the early 18th century.<ref name="Egerton07"/><ref name="Kormandy78"/> Linnaeus founded an early branch of ecology that he called the economy of nature.<ref name="Egerton07"/> His works influenced Charles Darwin, who adopted Linnaeus' phrase on the ''economy or polity of nature'' in ''[[The Origin of Species]]''.<ref name="Stauffer57" /> Linnaeus was the first to frame the [[balance of nature]] as a testable hypothesis. Haeckel, who admired Darwin's work, defined ecology in reference to the economy of nature, which has led some to question whether ecology and the economy of nature are synonymous.<ref name="Kormandy78" />
| |
| | |
| [[File:Darwin EcoExperiment.JPG|thumb|The layout of the first ecological experiment, carried out in a grass garden at [[Woburn Abbey]] in 1816, was noted by Charles Darwin in ''The Origin of Species''. The experiment studied the performance of different mixtures of species planted in different kinds of soils.<ref name="Hector02" /><ref name="Sinclair26" />]]
| |
| | |
| From Aristotle until Darwin, the natural world was predominantly considered static and unchanging. Prior to ''The Origin of Species'', there was little appreciation or understanding of the dynamic and reciprocal relations between organisms, their adaptations, and the environment.<ref name="Benson00"/> An exception is the 1789 publication ''Natural History of Selborne'' by [[Gilbert White]] (1720–1793), considered by some to be one of the earliest texts on ecology.<ref name="May99"/> While [[Charles Darwin]] is mainly noted for his treatise on evolution,<ref name=Darwin/> he was one of the founders of [[soil ecology]],<ref name="Meysman06"/> and he made note of the first ecological experiment in ''The Origin of Species''.<ref name="Hector02"/> Evolutionary theory changed the way that researchers approached the ecological sciences.<ref name="Acot97"/>
| |
| | |
| {{quote box
| |
| | quote = Nowhere can one see more clearly illustrated what may be called the sensibility of such an organic complex,--expressed by the fact that whatever affects any species belonging to it, must speedily have its influence of some sort upon the whole assemblage. He will thus be made to see the impossibility of studying any form completely, out of relation to the other forms,--the necessity for taking a comprehensive survey of the whole as a condition to a satisfactory understanding of any part.
| |
| | source = Stephen Forbes (1887)<ref name="Forbes1887"/>
| |
| | width = 30%
| |
| | align = left}}
| |
| | |
| ===Since 1900===
| |
| Modern ecology is a young science that first attracted substantial scientific attention toward the end of the 19th century (around the same time that evolutionary studies were gaining scientific interest). Notable scientist [[Ellen Swallow Richards]] may have first introduced the term "[[oekology]]" (which eventually morphed into [[home economics]]) in the U.S. as early 1892.<ref name="Hunt">{{cite book | last = Hunt | first = Caroline Louisa | authorlink = Caroline Louisa Hunt | title = The life of Ellen H. Richards | publisher = [[Whitcomb & Barrows]] | edition = 1st | location = Boston | year = 1912 | isbn = | url = http://archive.org/details/lifeofellenhrich00huntrich }}</ref>
| |
| | |
| In the early 20th century, ecology transitioned from a more [[metaphysics|descriptive form]] of [[natural history]] to a more [[scientific method|analytical form]] of ''scientific natural history''.<ref name="Kingsland04"/><ref name="McIntosh85" /> [[Frederic Clements]] published the first American ecology book in 1905,<ref name="Clements05">{{cite book | last1=Clements | first1=F. E. | title=Research methods in ecology | publisher = University Pub. Comp. | place=Lincoln, Neb. | year=1905 | isbn=0-405-10381-6 | url=http://books.google.com/?id=vRy-VJctJjcC&printsec=frontcover&dq=Research+Methods+in+Ecology#v=onepage&q=Research%20Methods%20in%20Ecology&f=false}}</ref> presenting the idea of plant communities as a [[superorganism]]. This publication launched a debate between ecological holism and individualism that lasted until the 1970s. Clements' superorganism concept proposed that ecosystems progress through regular and determined stages of [[seral development]] that are analogous to the developmental stages of an organism. The Clementsian paradigm was challenged by [[Henry Gleason]],<ref name="Simberloff80"/> who stated that ecological communities develop from the unique and coincidental association of individual organisms. This perceptual shift placed the focus back onto the life histories of individual organisms and how this relates to the development of community associations.<ref name="Gleason26"/>
| |
| | |
| The Clementsian superorganism theory was an overextended application of an [[idealism|idealistic form]] of holism.<ref name="Levins80">{{cite journal | last1=Levins | first1=R. | last2=Lewontin | first2=R. | title=Dialectics and reductionism in ecology | journal=Synthese | volume=43 | pages=47–78 | year=1980 | url=http://www.ecologia.unam.mx/laboratorios/comunidades/pdf/pdf%20curso%20posgrado%20Elena/Tema%201/LevinsLewontinSynthese1980.pdf}}</ref><ref name="Wilson88" /> The term "holism" was coined in 1926 by [[Jan Christiaan Smuts]], a South African general and polarizing historical figure who was inspired by Clements' superorganism concept.<ref name="Foster08"/>{{Cref2|C}} Around the same time, [[Charles Sutherland Elton|Charles Elton]] pioneered the concept of food chains in his classical book ''Animal Ecology''.<ref name="Elton27">{{cite book|last=Elton|first=C. S.|title=Animal Ecology|publisher=Sidgwick and Jackson|place=London, UK.|year=1927|isbn=0-226-20639-4}}</ref> Elton<ref name="Elton27" /> defined ecological relations using concepts of food chains, food cycles, and food size, and described numerical relations among different functional groups and their relative abundance. Elton's 'food cycle' was replaced by 'food web' in a subsequent ecological text.<ref name="Allee32"/> [[Alfred J. Lotka]] brought in many theoretical concepts applying thermodynamic principles to ecology.
| |
| | |
| In 1942, [[Raymond Lindeman]] wrote a landmark paper on the [[Trophic dynamics#Trophic dynamics|trophic dynamics]] of ecology, which was published posthumously after initially being rejected for its theoretical emphasis. Trophic dynamics became the foundation for much of the work to follow on energy and material flow through ecosystems. [[Robert E. MacArthur]] advanced mathematical theory, predictions and tests in ecology in the 1950s, which inspired a resurgent school of theoretical mathematical ecologists.<ref name="McIntosh85" /><ref name="Cook77">{{cite journal | last1=Cook | first1=R. E. | title=Raymond Lindeman and the trophic-dynamic concept in ecology | journal=Science | volume=198 | issue=4312 | pages=22–26 | year=1977 | doi=10.1126/science.198.4312.22 | url=http://www.esf.edu/efb/schulz/Seminars/Cook.pdf|bibcode = 1977Sci...198...22C | pmid=17741875}}</ref><ref name="Odum68">{{cite journal | last1=Odum | first1=E. P. | year=1968 | title=Energy flow in ecosystems: A historical review | journal=American Zoologist | volume=8 | issue=1 | pages=11–18 | jstor=3881528}}</ref> Ecology also has developed through contributions from other nations, including Russia's [[Vladimir Vernadsky]] and his founding of the biosphere concept in the 1920s<ref name="Ghilarov95"/> and Japan's [[Kinji Imanishi]] and his concepts of harmony in nature and habitat segregation in the 1950s.<ref name="Itô91"/> Scientific recognition of contributions to ecology from non-English-speaking cultures is hampered by language and translation barriers.<ref name="Ghilarov95" />
| |
| | |
| {{quote box
| |
| | quote = This whole chain of poisoning, then, seems to rest on a base of minute plants which must have been the original concentrators. But what of the opposite end of the food chain—the human being who, in probable ignorance of all this sequence of events, has rigged his fishing tackle, caught a string of fish from the waters of Clear Lake, and taken them home to fry for his supper?
| |
| | source = Rachel Carson (1962)<ref name="Carson62">{{cite book | last1=Carson | first1=R. | title=Silent Spring | publisher=Houghton Mifflin Company | page=348 | url=http://books.google.ca/books?id=HeR1l0V0r54C&printsec=frontcover#v=onepage&q&f=false | isbn=0-618-24906-0| year=2002 }}</ref>{{Rp|48}}
| |
| | width = 30%
| |
| | align = right}}
| |
| | |
| Ecology surged in popular and scientific interest during the 1960–1970s [[environmental movement]]. There are strong historical and scientific ties between ecology, environmental management, and protection.<ref name="McIntosh85" /> The historic emphasis and poetic naturalist writings for protection was on wild places, from notable ecologists in the history of [[conservation biology]], such as [[Aldo Leopold]] and [[Arthur Tansley]], were far removed from urban centres where the concentration of pollution and environmental degradation is located.<ref name="McIntosh85" /><ref name="Palamar08">{{cite journal | last1=Palamar | first1=C. R. | year=2008 | title=The justice of ecological restoration: Environmental history, health, ecology, and justice in the United States | journal=Human Ecology Review | volume=15 | issue=1 | pages=82–94 | url=http://www.humanecologyreview.org/pastissues/her151/palamar.pdf}}</ref> Palamar (2008)<ref name="Palamar08" /> notes an overshadowing by mainstream environmentalism of pioneering women in the early 1900s who fought for urban health ecology (then called [[euthenics]])<ref name="Hunt" /> and brought about changes in environmental legislation. Women such as [[Ellen Swallow Richards]] and [[Julia Lathrop]], among others, were precursors to the more popularized environmental movements after the 1950s.
| |
| | |
| In 1962, marine biologist and ecologist [[Rachel Carson]]'s book ''[[Silent Spring]]'' helped to mobilize the environmental movement by alerting the public to toxic [[pesticides]], such as [[DDT]], [[Bioaccumulation|bioaccumulating]] in the environment. Carson used ecological science to link the release of environmental toxins to human and [[ecosystem health]]. Since then, ecologists have worked to bridge their understanding of the degradation of the planet's ecosystems with environmental politics, law, restoration, and natural resources management.<ref name="Hammond09" /><ref name="McIntosh85" /><ref name="Palamar08" /><ref name="Krebs99">{{cite journal | last1=Krebs | first1=J. R. | last2=Wilson | first2=J. D. | last3=Bradbury | first3=R. B. | last4=Siriwardena | first4=G. M. | title=The second Silent Spring | journal=Nature | volume=400 | year=1999 | pages=611–612 | doi=10.1038/23127 | url=http://www.hillnet.com/silent_spring.pdf|bibcode = 1999Natur.400..611K | issue=6745 }}</ref>
| |
| | |
| ==See also==
| |
| {{Main|Outline of ecology}}
| |
| {{colbegin|3}}
| |
| *[[Agroecology]]
| |
| *[[Chemical ecology]]
| |
| *[[Cultural ecology]]
| |
| *[[Dialectical naturalism]]
| |
| *[[Earth science]]
| |
| *[[Ecological death]]
| |
| *[[Ecological psychology]]
| |
| *[[Ecology movement]]
| |
| *[[Euthenics]]
| |
| *[[Industrial ecology]]
| |
| *[[Information ecology]]
| |
| *[[Landscape ecology]]
| |
| *[[Natural resource]]
| |
| *[[Political ecology]]
| |
| *[[Restoration ecology]]
| |
| *[[Spiritual ecology]]
| |
| *[[Sustainable development]]
| |
| | |
| {{colend}}
| |
| | |
| ;Lists
| |
| {{colbegin|2}}
| |
| *[[Glossary of ecology]]
| |
| *[[Index of biology articles]]
| |
| *[[List of ecologists]]
| |
| *[[Outline of biology]]
| |
| {{colend}}
| |
| | |
| == Notes ==
| |
| {{Cnote2 Begin|list-style=upper-alpha|colwidth=30em}}
| |
| | |
| {{Cnote2|A|In Ernst Haeckel's (1866) footnote where the term ecology originates, he also gives attribute to {{lang-grc|χώρας|khōrā |χωρα}}, meaning "dwelling place, distributional area" - quoted from Stauffer (1957)}}
| |
| {{Cnote2|B|This is a copy of Haeckel's original definition (Original: Haeckel, E. (1866) Generelle Morphologie der Organismen. Allgemeine Grundzige der organischen Formen- Wissenschaft, mechanisch begriindet durch die von Charles Darwin reformirte Descendenz-Theorie. 2 vols. Reimer, Berlin.) translated and quoted from Stauffer (1957).}}
| |
| {{Cnote2|C|Foster & Clark (2008) note how Smut's holism contrasts starkly against his racial political views as the father of [[apartheid]].}}
| |
| {{Cnote2|D|First introduced in MacArthur & Wilson's (1967) book of notable mention in the history and theoretical science of ecology, ''[[The Theory of Island Biogeography]]''}}
| |
| {{Cnote2|E|Aristotle wrote about this concept in ''[[Metaphysics (Aristotle)|Metaphysics]]'' (Quoted from [http://classics.mit.edu/Aristotle/metaphysics.mb.txt The Internet Classics Archive] translation by [[W. D. Ross]]. Book VIII, Part 6): "To return to the difficulty which has been stated with respect both to definitions and to numbers, what is the cause of their unity? In the case of all things which have several parts and in which the totality is not, as it were, a mere heap, but the whole is something beside the parts, there is a cause; for even in bodies contact is the cause of unity in some cases, and in others viscosity or some other such quality."''}}
| |
| | |
| {{Cnote2 End}}
| |
| | |
| ==References==
| |
| {{Reflist|colwidth=30em|refs=
| |
| | |
| <ref name="Acot97">{{Cite journal |last=Acot |first=P. |title=The Lamarckian cradle of scientific ecology |journal=Acta Biotheoretica |volume=45 |issue=3–4 |pages=185–193 |year=1997 |doi=10.1023/A:1000631103244 }}</ref>
| |
| | |
| <ref name="Aguirre09">{{Cite journal |last=Aguirre |first=A. A. |title=Biodiversity and human health |journal=EcoHealth |year=2009 |doi=10.1007/s10393-009-0242-0 |volume=6 |pages=153–156 }}</ref>
| |
| | |
| <ref name="Allee32">{{Cite book |last=Allee |first=W. C. |title=Animal Life and Social Growth |publisher=The Williams & Wilkins Company and Associates |location=Baltimore |year=1932}}</ref>
| |
| | |
| <ref name="Allee49">{{Cite book |last1=Allee |first1=W. C. |last2=Park |first2=O. |last3=Emerson |first3=A. E. |last4=Park |first4=T. |last5=Schmidt |first5=K. P. |title=Principles of Animal Ecology |publisher=W. B. Sunders, Co. |year=1949 |page=837 |url=http://www.archive.org/stream/principlesofanim00alle#page/n5/mode/2up |isbn=0-7216-1120-6}}</ref>
| |
| | |
| <ref name="Allègre95">{{Cite journal |last1=Allègre |first1=Claude J. |last2=Manhès |first2=Gérard |last3=Göpel |first3=Christa |title=The age of the Earth |journal=Geochimica et Cosmochimica Acta |volume=59 |issue=8 |year=1995 |pages=1455–1456 |doi=10.1016/0016-7037(95)00054-4 |bibcode=1995GeCoA..59.1445A}}</ref>
| |
| | |
| <ref name="Anderson61">{{Cite journal |last=Anderson |first=J. D. |title=The courtship behaviour of ''Ambystoma macrodactylum croceum'' |journal=Copeia |volume=2 |pages=132–139 |year=1961 |issue=2 |jstor=1439987}}</ref>
| |
| | |
| <ref name="Anderson95">{{Cite journal |last=Anderson|first=P. K. |title=Competition, predation, and the evolution and extinction of Stellar's sea cow, ''Hydrodamalis gigas'' |year=1995 |journal=Marine Mammal Science |volume=11 |issue=3 |pages=391–394 |doi=10.1111/j.1748-7692.1995.tb00294.x }}</ref>
| |
| | |
| <ref name="Avise94">{{Cite book |last=Avise |first=J. |title=Molecular Markers, Natural History and Evolution |publisher=Kluwer Academic Publishers |year=1994 |url=http://books.google.com/books?id=2zYnQfnXNr8C |isbn=0-412-03771-8}}</ref>
| |
| | |
| <ref name="Avise00">{{Cite book |last=Avise |first=J. |title=Phylogeography: The History and Formation of Species |publisher=President and Fellows of Harvard College |year=2000 |url=http://books.google.com/books?id=lA7YWH4M8FUC |isbn=0-674-66638-0}}</ref>
| |
| | |
| <ref name="Begon05">{{Cite book |last1=Begon |first1=M. |last2=Townsend |first2=C. R. |last3=Harper |first3=J. L. |title=Ecology: From Individuals to Ecosystems |year=2005 |edition=4th |publisher=Wiley-Blackwell |page=752 |isbn=1-4051-1117-8 |url=http://ca.wiley.com/WileyCDA/WileyTitle/productCd-1405111178.html}}</ref>
| |
| | |
| <ref name="Benson00">{{Cite journal |last=Benson |first=Keith R. |title=The emergence of ecology from natural history |journal=Endeavour |volume=24 |issue=2 |pages=59–62 |year=2000 |doi=10.1016/S0160-9327(99)01260-0 |pmid=10969480 }}</ref>
| |
| | |
| <ref name="Berryman92">{{Cite journal |last=Berryman |first=A. A. |title=The origins and evolution of predator-prey theory |journal=Ecology |volume=73 |issue=5 |pages=1530–1535 |year=1992 |doi=10.2307/1940005 |jstor=1940005}}</ref>
| |
| | |
| <ref name="Beyer10">{{Cite journal |last1=Beyer |first1=Hawthorne, L. |last2=Haydon |first2=Daniel, T. |last3=Morales |first3=Juan M. |last4=Frair |first4=Jacqueline L. |last5=Hebblewhite |first5=Mark |last6=Mitchell |first6=Michael |last7=Matthiopoulos |first7=Jason |title=The interpretation of habitat preference metrics under use–availability designs |journal=Philosophical Transactions of the Royal Society B |volume=365 |issue=1550 |pages=2245–2254 |year=2010 |pmid=20566501 |pmc=2894962 |doi=10.1098/rstb.2010.0083 }}</ref>
| |
| | |
| <ref name="Boerner82">{{Cite journal |last=Boerner |first=R. E. J. |title=Fire and nutrient cycling in temperate ecosystems |journal=BioScience |volume=32 |issue=3 |pages=187–192 |year=1982 |doi=10.2307/1308941 |jstor=1308941}}</ref>
| |
| | |
| <ref name="Boucher82">{{Cite journal |last=Boucher |first=D. H. |last2=James |first2=S. |last3=Keeler |first3=K. H. |title=The ecology of mutualism |journal=Annual Review of Ecology and Systematics |volume=13 |pages=315–347 |year=1982 |doi=10.1146/annurev.es.13.110182.001531 }}</ref>
| |
| | |
| <ref name="Bronstein01">{{cite journal | last1=Bronstein | first1= J. L. | year=2001 | title=The exploitation of mutualisms | journal=Ecology Letters | volume=4 | pages=277–287 | doi=10.1046/j.1461-0248.2001.00218.x| issue=3 }}</ref>
| |
| | |
| <ref name="Campbell06">{{Cite book |last=Campbell |first=Neil A. |last2=Williamson |first2=Brad |last3=Heyden |first3=Robin J. |title=Biology: Exploring Life |publisher=Pearson Prentice Hall |year=2006 |location=Boston, Massachusetts |url=http://www.phschool.com/el_marketing.html |isbn=0-13-250882-6}}</ref>
| |
| | |
| <ref name="Carpenter01">{{Cite journal |last1=Scheffer |first1=M. |last2=Carpenter |first2=S. |last3=Foley |first3=J. A. |last4=Walker |first4=B. |last5=Walker |first5=B. |title=Catastrophic shifts in ecosystems |journal=Nature |volume=413 |issue=6856 |pages=591–596 |url=http://bio.classes.ucsc.edu/bioe107/Scheffer%202001%20Nature.pdf |doi=10.1038/35098000 |pmid=11595939 |year=2001 |bibcode=2001Natur.413..591S}}</ref>
| |
| | |
| <ref name="Catling05">{{Cite journal |last1=Catling |first1=D. C. |last2=Claire |first2=M. W. |title=How Earth's atmosphere evolved to an oxic state: A status report |journal=Earth and Planetary Science Letters |volume=237 |year=2005 |pages=1–20 |url=http://www.atmos.washington.edu/~davidc/papers_mine/Catling2005-EPSL.pdf |doi=10.1016/j.epsl.2005.06.013 |bibcode=2005E&PSL.237....1C}}</ref>
| |
| | |
| <ref name="Ceballos02">{{Cite journal |last=Ceballos |first=G. |last2=Ehrlich |first2=P. R. |title=Mammal population losses and the extinction crisis |journal=Science |volume=296 |issue=5569 |pages=904–907 |year=2002 |url=http://epswww.unm.edu/facstaff/gmeyer/envsc330/CeballosEhrlichmammalextinct2002.pdf |accessdate=2010-03-16 |doi=10.1126/science.1069349 |pmid=11988573 |bibcode=2002Sci...296..904C}}</ref>
| |
| | |
| <ref name="Clark98">{{Cite journal |last1=Clark |first1=J. S. |last2=Fastie |first2=C. |last3=Hurtt |first3=G. |last4=Jackson |first4=S. T. |last5=Johnson |first5=C. |last6=King |first6=G. A. |first7=M. |last8=Lynch |first8=J. |last9=Pacala |first9=S. |title=Reid's paradox of rapid plant migration |journal=BioScience |volume=48 |issue=1 |year=1998 |pages=13–24 |url=http://www.mathstat.ualberta.ca/~mlewis/publications/25Clark1998B.pdf |doi=10.2307/1313224|display-authors=9 }}</ref>
| |
| | |
| <ref name="Coleman04">{{Cite book |last1=Coleman |first1=D. C. |last2=Corssley |first2=D. A. |last3=Hendrix |first3=P. F. |title=Fundamentals of Soil Ecology |publisher=Academic Press |year=2004 |edition=2nd |isbn=0-12-179726-0 |url=http://books.google.com/books?id=pKKDJwu_OlkC}}</ref>
| |
| | |
| <ref name="Cooper60">{{Cite journal |last=Cooper |first=C. F. |title=Changes in vegetation, structure, and growth of southwestern pine forests since white settlement |journal=Ecological Monographs |volume=30 |issue=2 |pages=130–164 |year=1960 |jstor=1948549}}</ref>
| |
| | |
| <ref name="Cooper61">{{Cite journal |last=Cooper |first=C. F. |title=The ecology of fire |journal=Scientific American |volume=204 |issue=4 |pages=150–160 |year=1961 |doi=10.1038/scientificamerican0461-150 }}</ref>
| |
| | |
| <ref name="Cooper10">{{Cite journal |last=Cooper |first=W. E. |last2=Frederick |first2=W. G. |title=Predator lethality, optimal escape behavior, and autotomy |journal=Behavioral Ecology |volume=21 |issue=1 |pages=91–96 |year=2010 |doi=10.1093/beheco/arp151 }}</ref>
| |
| | |
| <ref name="Cox00">{{Cite journal |last1=Cox |DUPLICATE_last2=Peter M. |last2=Betts |first2=Richard A. |last3=Jones |first3=Chris D. |last4=Spall |first4=Steven A. |last5=Totterdell |first5=Ian J. |title=Acceleration of global warming due to carbon-cycle feedbacks in a coupled climate model |journal=Nature |volume=408 |pages=184–187 |year=2000 |url=http://quercus.igpp.ucla.edu/teaching/papers_to_read/cox_etal_nat_00.pdf |doi=10.1038/35041539 |pmid=11089968 |issue=6809 }}</ref>
| |
| | |
| <ref name="Cronk01">{{Cite book |last1=Cronk |first1=J. K. |last2=Fennessy |first2=M. S. |title=Wetland Plants: Biology and Ecology |location=Washington, D.C. |publisher=Lewis Publishers |year=2001 |url=http://books.google.com/books?id=FNI1GFbH2eQC |isbn=1-56670-372-7}}</ref>
| |
| | |
| <ref name=Darwin>{{Cite book |last=Darwin |first=Charles |authorlink=Charles Darwin |year=1859 |title=On the Origin of Species |location=London, UK |publisher=John Murray |edition=1st |page=1 |url=http://darwin-online.org.uk/content/frameset?itemID=F373&viewtype=text&pageseq=16 |isbn=0-8014-1319-2}}</ref>
| |
| | |
| <ref name="Daubenmire75">{{Cite journal |last=Daubenmire |first=R. |title=Floristic plant geography of eastern Washington and northern Idaho |journal=Journal of Biogeography |volume=2 |issue=1 |pages=1–18 |year=1975 |doi=10.2307/3038197 |jstor=3038197}}</ref>
| |
| | |
| <ref name="Davic04">{{Cite journal |last1=Davic |first1=R. D. |last2=Welsh |first2=H. H. |title=On the ecological role of salamanders |journal=Annual Review of Ecology and Systematics |volume=35 |pages=405–434 |year=2004 |url=http://www.fs.fed.us/psw/publications/welsh/captured/psw_2004_welsh008.pdf |doi=10.1146/annurev.ecolsys.35.112202.130116 }}</ref>
| |
| | |
| <ref name="David03">{{Cite journal |last=Davic |first=R. D. |title=Linking keystone species and functional groups: a new operational definition of the keystone species concept |journal=Conservation Ecology |volume=7 |issue=1 |pages=r11 |year=2003 |url=http://www.consecol.org/vol7/iss1/resp11/ }}</ref>
| |
| | |
| <ref name="Davidson06">{{Cite journal |last1=Davidson |first1=Eric A. |last2=Janssens |first2=Ivan A. |title=Temperature sensitivity of soil carbon decomposition and feedbacks to climate change |journal=Nature |volume=440 |pages=165–173 |year=2006 |doi=10.1038/nature04514 |pmid=16525463 |issue=7081 |bibcode=2006Natur.440..165D}}</ref>
| |
| | |
| <ref name="de Groot02">{{Cite journal |last=de Groot |first=R. S. |last2=Wilson |first2=M. A. |last3=Boumans |first3=R. M. J. |title=A typology for the classification, description and valuation of ecosystem functions, goods and services |journal=Ecological Economics |volume=41 |issue=3 |pages=393–408 |year=2002 |url=http://yosemite.epa.gov/SAB/sabcvpess.nsf/e1853c0b6014d36585256dbf005c5b71/1c7c986c372fa8d485256e29004c7084/$FILE/deGroot%20et%20al.pdf |doi=10.1016/S0921-8009(02)00089-7 }}</ref>
| |
| | |
| <ref name="DeLong09">{{Cite journal |last=DeLong |first=E. F. |title=The microbial ocean from genomes to biomes |journal=Nature |volume=459 |pages=200–206 |year=2009 |url=http://researchpages.net/media/resources/2009/07/30/nature08059.pdf |doi=10.1038/nature08059 |pmid=19444206 |issue=7244 |bibcode=2009Natur.459..200D}}</ref>
| |
| | |
| <ref name="Dingle96">{{Cite book |last=Dingle |first=H. |title=Migration: The Biology of Life on the Move |publisher=Oxford University Press |isbn=0-19-509723-8 |page=480 |url=http://books.google.com/books?id=adguyA_ZlAMC|date=1996-01-18 }}</ref>
| |
| | |
| <ref name="Duffy07">{{Cite journal |last1=Duffy |DUPLICATE_last2=J. Emmett |last2=Cardinale |first2=Bradley J. |last3=France |first3=Kristin E. |last4=McIntyre |first4=Peter B. |last5=Thébault |first5=Elisa |last6=Loreau |first6=Michel |title=The functional role of biodiversity in ecosystems: incorporating trophic complexity |journal=Ecology Letters |volume=10 |issue=6 |pages=522–538 |year=2007 |doi=10.1111/j.1461-0248.2007.01037.x |pmid=17498151 }}</ref>
| |
| | |
| <ref name="Eastwood04">{{Cite journal |last=Eastwood |first=R. |title=Successive replacement of tending ant species at aggregations of scale insects (Hemiptera: Margarodidae and Eriococcidae) on ''Eucalyptus'' in south-east Queensland |journal=Australian Journal of Entomology |volume=43 |pages=1–4 |year=2004 |url=http://www.oeb.harvard.edu/faculty/pierce/people/eastwood/resources/pdfs/Scale-ant2004.pdf |doi=10.1111/j.1440-6055.2003.00371.x }}</ref>
| |
| | |
| <ref name="Edwards83">{{Cite journal |last=Edwards |first=J. |last2=Fraser |first2=K. |title=Concept maps as reflectors of conceptual understanding |journal=Research in Science Education |volume=13 |pages=19–26 |year=1983 |doi=10.1007/BF02356689 |bibcode=1983RScEd..13...19E}}</ref>
| |
| | |
| <ref name="Egerton01">{{Cite journal |last=Egerton |first=F. N. |title=A history of the ecological sciences: early Greek origins |journal=Bulletin of the Ecological Society of America |volume=82 |issue=1 |pages=93–97 |year=2001 |url=http://esapubs.org/bulletin/current/history_list/history_part1.pdf |format=PDF }}</ref>
| |
| | |
| <ref name="Egerton07">{{Cite journal |last=Egerton |first=F. N. |title=A history of the ecological sciences, part 23: Linnaeus and the economy of nature |journal=Bulletin of the Ecological Society of America |volume=88 |issue=1 |pages=72–88 |year=2007 |doi=10.1890/0012-9623(2007)88[72:AHOTES]2.0.CO;2 |issn=0012-9623}}</ref>
| |
| | |
| <ref name="Egerton07b">{{Cite journal |last=Egerton |first=Frank N. |title=Understanding food chains and food webs, 1700–1970 |year=2007 |journal=Bulletin of the Ecological Society of America |volume=88 |pages=50–69 |doi=10.1890/0012-9623(2007)88[50:UFCAFW]2.0.CO;2 |issn=0012-9623}}</ref>
| |
| | |
| <ref name="Emmerson">{{Cite journal |last1=Emmerson |first1=M. |last2=Yearsley |first2=J. M. |title=Weak interactions, omnivory and emergent food-web properties |journal=Philosophical Transactions of the Royal Society B |volume=271 |issue=1537 |pages=397–405 |doi=10.1098/rspb.2003.2592 |year=2004 |url=http://www.ucc.ie/people/memmers/pdfs/Emmerson.Yearsley.Proc.Roy.Soc.B.2004.pdf}}</ref>
| |
| | |
| <ref name="Ernest03">{{Cite journal |last1=Morgan Ernest |first1=S. K. |last3=Brown |first3=James H. |last4=Charnov |first4=Eric L. |last5=Gillooly |first5=James F. |last6=Savage |first6=Van M. |last7=White |first7=Ethan P. |last8=Smith |first8=Felisa A. |last9=Hadly |first9=Elizabeth A. |title=Thermodynamic and metabolic effects on the scaling of production and population energy use |journal=Ecology Letters |volume=6 |issue=11 |year=2003 |pages=990–995 |url=https://www.msu.edu/~maurerb/Ernest_etal_2003.pdf |doi=10.1046/j.1461-0248.2003.00526.x |last2=Enquist |first2=Brian J. |last10=Haskell |first10=John P. |last11=Lyons |first11=S. Kathleen |last12=Maurer |first12=Brian A. |last13=Niklas |first13=Karl J. |last14=Tiffney |first14=Bruce }}</ref>
| |
| | |
| <ref name="Etemad01">{{Cite journal |last1=Etemad-Shahidi |first1=A. |last2=Imberger |first2=J. |title=Anatomy of turbulence in thermally stratified lakes |journal=Limnolology and Oceanography |volume=46 |issue=5 |year=2001 |pages=1158–1170 |url=http://nospam.aslo.org/lo/toc/vol_46/issue_5/1158.pdf |doi=10.4319/lo.2001.46.5.1158 }}</ref>
| |
| | |
| <ref name="Evans99">{{Cite journal |last=Evans |first=D. H. |last2=Piermarini |first2=P. M. |last3=Potts |first3=W. T. W. |title=Ionic transport in the fish gill epithelium |journal=Journal of Experimental Zoology |volume=283 |issue=7 |pages=641–652 |year=1999 |url=http://people.biology.ufl.edu/devans/DHEJEZ.pdf |doi=10.1002/(SICI)1097-010X(19990601)283:7<641::AID-JEZ3>3.0.CO;2-W }}</ref>
| |
| | |
| <ref name="Falkowoski08">{{Cite journal |last1=Falkowski |first1=P. G. |last2=Fenchel |first2=T. |last3=Delong |first3=E. F. |title=The microbial engines that drive Earth's biogeochemical cycles |pmid=18497287 |journal=Science |volume=320 |issue=5879 |pages=1034–1039 |year=2008 |doi=10.1126/science.1153213 |bibcode=2008Sci...320.1034F}}</ref>
| |
| | |
| <ref name="Fisher06">{{Cite journal |last1=Fischer |first1=J. |last2=Lindenmayer |first2=D. B. |last3=Manning |first3=A. D. |title=Biodiversity, ecosystem function, and resilience: ten guiding principles for commodity production landscapes |journal=Frontiers in Ecology and the Environment |volume=4 |issue=2 |pages=80–86 |year=2006 |url=http://www.tecniflora.com.br/1_-_Guidelines_commodity_production.pdf |doi=10.1890/1540-9295(2006)004[0080:BEFART]2.0.CO;2 |issn=1540-9295}}</ref>
| |
| | |
| <ref name="Flematti04">{{Cite journal |last=Flematti |first=Gavin R. |last2=Ghisalberti |first2=Emilio L. |last3=Dixon |first3=Kingsley W. |last4=Trengove |first4=R. D. |title=A compound from smoke that promotes seed germination |journal=Science |volume=305 |issue=5686 |page=977 |year=2004 |url=http://www.sciencemag.org/content/305/5686/977.full.pdf?sid=f51e6d8f-5ad8-4a3a-90da-824b5c3a2c58 |format=PDF |doi=10.1126/science.1099944 |pmid=15247439}}</ref>
| |
| | |
| <ref name="Folke04">{{Cite journal |last1=Folke |first1=C. |last2=Carpenter |first2=S. |last3=Walker |first3=B. |last4=Scheffer |first4=M. |last5=Elmqvist |first5=T. |last6=Gunderson |first6=L. |title=Regime shifts, resilience, and biodiversity in ecosystem management |journal=Annual Review of Ecology and Systematics |year=2004 |volume=35 |pages=557–581 |doi=10.1146/annurev.ecolsys.35.021103.105711 |url=http://www.colorado.edu/AmStudies/lewis/ecology/ecobiodiver.pdf |last7=Holling |first7=C.S. |jstor=2096802}}</ref>
| |
| | |
| <ref name="Forbes1887">{{Cite journal |last=Forbes |first=S. |title=The lake as a microcosm |journal=Bulletin of the Scientific Association |pages=77–87 |location=Peoria, IL |year=1887 |url=http://www.uam.es/personal_pdi/ciencias/scasado/documentos/Forbes.PDF }}</ref>
| |
| | |
| <ref name="Foster08">{{Cite journal |last1=Foster |first1=J. B. |last2=Clark |first2=B. |title=The sociology of ecology: ecological organicism versus ecosystem ecology in the social construction of ecological science, 1926–1935 |journal=Organization & Environment |volume=21 |issue=3 |pages=311–352 |year=2008 |url=http://ibcperu.org/doc/isis/10408.pdf |doi=10.1177/1086026608321632 }}</ref>
| |
| | |
| <ref name="Friederichs58">{{Cite journal |doi=10.2307/1929981 |last=Friederichs |first=K. |title=A definition of ecology and some thoughts about basic concepts |journal=Ecology |volume=39 |issue=1 |pages=154–159 |year=1958 |jstor=1929981}}</ref>
| |
| | |
| <ref name="Friedman04">{{Cite journal |last=Friedman |first=J. |last2=Harder |first2=L. D. |title=Inflorescence architecture and wind pollination in six grass species |journal=Functional Ecology |volume=18 |issue=6 |pages=851–860 |year=2004 |url=http://www.bio.ucalgary.ca/contact/faculty/pdf/FriedmanHarder2004.pdf |doi=10.1111/j.0269-8463.2004.00921.x }}</ref>
| |
| | |
| <ref name="Garren43">{{Cite journal |last=Garren |first=K. H. |title=Effects of fire on vegetation of the southeastern United States |journal=Botanical Review |volume=9 |issue=9 |pages=617–654 |year=1943 |doi=10.1007/BF02872506 }}</ref>
| |
| | |
| <ref name="Garnter10">{{Cite journal |DUPLICATE_last1=Gartner |last1=Gabriel E. A. |last2=Hicks |first2=James W. |last3=Manzani |first3=Paulo R. |last4=Andrade |first4=Denis V. |last5=Abe |first5=Augusto S. |last6=Wang |first6=Tobias |last7=Secor |first7=Stephen M. |last8=Garland Jr. |first8=Theodore |title=Phylogeny, ecology, and heart position in snakes |journal=Physiological and Biochemical Zoology |volume=83 |issue=1 |pages=43–54 |year=2010 |url=http://www.naherpetology.org/pdf_files/1407.pdf |doi=10.1086/648509 |pmid=19968564 }}</ref>
| |
| | |
| <ref name="Ghilarov95">{{Cite journal |last=Ghilarov |first=A. M. |title=Vernadsky's biosphere concept: an historical perspective |journal=The Quarterly Review of Biology |volume=70 |issue=2 |pages=193–203 |year=1995 |doi=10.1086/418982 |jstor=3036242}}</ref>
| |
| | |
| <ref name="Gilbert90">{{Cite book |last=Gilbert |first=F. S. |title=Insect life cycles: Genetics, evolution, and co-ordination |publisher=Springer-Verlag |year=1990 |location=New York, NY |page=258 |url=http://books.google.com/?id=2jIgAQAAMAAJ&q=Insect+Life+Cycles:+Genetics,+Evolution,+and+Co-ordination&dq=Insect+Life+Cycles:+Genetics,+Evolution,+and+Co-ordination |isbn=0-387-19550-5}}</ref>
| |
| | |
| <ref name="Gleason26">{{Cite journal |last=Gleason |first=H. A. |title=The individualistic concept of the plant association |journal=Bulletin of the Torrey Botanical Club |year=1926 |volume=53 |issue=1 |pages=7–26 |url=http://www.ecologia.unam.mx/laboratorios/comunidades/pdf/pdf%20curso%20posgrado%20Elena/Tema%201/gleason1926.pdf |doi=10.2307/2479933 |jstor=2479933 }}</ref>
| |
| | |
| <ref name="Goldblatt06">{{Cite journal |last1=Goldblatt |first1=Colin |last2=Lenton |first2=Timothy M. |last3=Watson |first3=Andrew J. |title=Bistability of atmospheric oxygen and the Great Oxidation |journal=Nature |volume=443 |pages=683–686 |year=2006 |url=http://lgmacweb.env.uea.ac.uk/ajw/Reprints/goldblatt_et_al_2006.pdf |doi=10.1038/nature05169 |pmid=17036001 |issue=7112 |bibcode=2006Natur.443..683G}}</ref>
| |
| | |
| <ref name="Goodland75">{{Cite journal |last=Goodland |first=R. J. |title=The tropical origin of ecology: Eugen Warming's jubilee |journal=Oikos |volume=26 |issue=2 |pages=240–245 |year=1975 |doi=10.2307/3543715 |jstor=3543715}}</ref>
| |
| | |
| <ref name="Goubitz03">{{Cite journal |last1=Goubitz |first1=S. |last2=Werger |first2=M. J. A. |last3=Ne'eman |first3=G. |title=Germination response to fire-related factors of seeds from non-serotinous and serotinous cones |journal=Plant Ecology |volume=169 |issue=2 |pages=195–204 |year=2009 |doi=10.1023/A:1026036332277 }}</ref>
| |
| | |
| <ref name="Gould82">{{Cite journal |last1=Gould |first1=Stephen J. |last2=Vrba |first2=Elizabeth S. |title=Exaptation–a missing term in the science of form |journal=Paleobiology |volume=8 |issue=1 |year=1982 |pages=4–15 }}</ref>
| |
| | |
| <ref name="Grace04">{{Cite journal |last=Grace |first=J. |title=Understanding and managing the global carbon cycle |journal=Journal of Ecology |volume=92 |pages=189–202 |year=2004 |doi=10.1111/j.0022-0477.2004.00874.x |issue=2}}</ref>
| |
| | |
| <ref name="Gross04">{{Cite journal |last1=Gross |first1=M. |year=2004 |title=Human geography and ecological sociology: the unfolding of human ecology, 1890 to 1930 – and beyond |journal=Social Science History |volume=28 |issue=4 |pages=575–605 |url=http://ssh.dukejournals.org/cgi/content/abstract/28/4/575 |doi=10.1215/01455532-28-4-575}}</ref>
| |
| | |
| <ref name="Hamner85">{{Cite journal |last=Hamner |first=W. M. |title=The importance of ethology for investigations of marine zooplankton |journal=Bulletin of Marine Science |volume=37 |issue=2 |pages=414–424 |year=1985 |url=http://www.ingentaconnect.com/content/umrsmas/bullmar/1985/00000037/00000002/art00005 }}</ref>
| |
| | |
| <ref name="Hammond09">{{Cite book |last=Hammond |first=H. |title=Maintaining Whole Systems on the Earth's Crown: Ecosystem-based Conservation Planning for the Boreal Forest |location=Slocan Park, BC |publisher=Silva Forest Foundation |year=2009 |page=380 |url=http://www.silvafor.org/crown |isbn=978-0-9734779-0-0}}</ref>
| |
| | |
| <ref name="Hanski98">{{Cite journal |last=Hanski |first=I. |title=Metapopulation dynamics |journal=Nature |volume=396 |pages=41–49 |year=1998 |url=http://www.helsinki.fi/~ihanski/Articles/Nature%201998%20Hanski.pdf |doi=10.1038/23876 |issue=6706|bibcode=1998Natur.396...41H }}</ref>
| |
| | |
| <ref name="Hanski04">{{Cite book |editor-last=Hanski |editor-first=I. |editor2-last=Gaggiotti |editor2-first=O. E. |title=Ecology, Genetics and Evolution of Metapopulations |publisher=Elsevier Academic Press |year=2004 |location=Burlington, MA |url=http://books.google.com/books?id=EP8TAQAAIAAJ |isbn=0-12-323448-4}}</ref>
| |
| | |
| <ref name="Harder09">{{Cite journal |last1=Harder |first1=L. D. |last2=Johnson |first2=S. D. |title=Darwin's beautiful contrivances: evolutionary and functional evidence for floral adaptation |journal=New Phytologist |volume=183 |issue=3 |pages=530–545 |year=2009 |url=http://www.bio.ucalgary.ca/contact/faculty/pdf/Harder_Johnson_09.pdf |doi=10.1111/j.1469-8137.2009.02914.x |pmid=19552694 }}</ref>
| |
| | |
| <ref name="Hardesty75">{{Cite journal |doi=10.1007/BF01552263 |first=Hardesty |last=D. L. |title=The niche concept: suggestions for its use in human ecology |journal=Human Ecology |volume=3 |issue=2 |pages=71–85 |year=1975 |jstor=4602315}}</ref>
| |
| | |
| <ref name="Hardin60">{{Cite journal |last=Hardin |first=G. |title=The competitive exclusion principal |year=1960 |journal=Science |volume=131 |issue=3409 |pages=1292–1297 |doi=10.1126/science.131.3409.1292 |pmid=14399717 |bibcode=1960Sci...131.1292H}}</ref>
| |
| | |
| <ref name="Hariston93">{{Cite journal |last1=Hairston Jr. |first1=N. G. |last2=Hairston Sr. |first2=N. G. |title=Cause-effect relationships in energy flow, trophic structure, and interspecific interactions |journal=The American Naturalist |volume=142 |issue=3 |pages=379–411 |year=1993 |url=http://limnology.wisc.edu/courses/zoo955/Spring2005/food%20web%20seminar%20papers/hairston93AmNat.pdf |doi=10.1086/285546}}</ref>
| |
| | |
| <ref name="Hasiotis03">{{Cite journal |last=Hasiotis |first=S. T. |title=Complex ichnofossils of solitary and social soil organisms: Understanding their evolution and roles in terrestrial paleoecosystems |journal=Palaeogeography, Palaeoclimatology, Palaeoecology |volume=192 |issue=2 |pages=259–320 |year=2003 |doi=10.1016/S0031-0182(02)00689-2 }}</ref>
| |
| | |
| <ref name="Hastings07">{{Cite journal |last1=Hastings |first1=Alan |last2=Byers |first2=James E. |last3=Crooks |first3=Jeffrey A. |last4=Cuddington |first4=Kim |last5=Jones |first5=Clive G. |last6=Lambrinos |first6=John G. |last7=Talley |first7=Theresa S. |last8=Wilson |first8=William G. |title=Ecosystem engineering in space and time |journal=Ecology Letters |volume=10 |issue=2 |pages=153–164 |year=2007 |doi=10.1111/j.1461-0248.2006.00997.x |pmid=17257103 }}</ref>
| |
| | |
| <ref name="Hawkins01">{{Cite journal |last=Hawkins |first=B. A. |title=Ecology's oldest pattern |journal=Endeavor |volume=25 |issue=3 |page=133 |year=2001 |doi=10.1016/S0160-9327(00)01369-7 }}</ref>
| |
| | |
| <ref name="Hector02">{{Cite journal |last1=Hector |first1=A. |last2=Hooper |first2=R. |title=Darwin and the first ecological experiment |journal=Science |volume=295 |pages=639–640 |year=2002 |doi=10.1126/science.1064815 |pmid=11809960 |issue=5555 }}</ref>
| |
| | |
| <ref name="Heiman08">{{Cite journal |last=Heimann |first=Martin |last2=Reichstein |first2=Markus |title=Terrestrial ecosystem carbon dynamics and climate feedbacks |journal=Nature |volume=451 |issue=7176 |pages=289–292 |year=2008 |url=http://courses.washington.edu/ocean450/Discussion_Topics_Papers/Heinmann_clim_chng_08.pdf |doi=10.1038/nature06591 |pmid=18202646 |bibcode=2008Natur.451..289H}}</ref>
| |
| | |
| <ref name="Herre99">{{Cite journal |last1=Herre |first1=E. A. |last2=Knowlton |first2=N. |last3=Mueller |first3=U. G. |last4=Rehner |first4=S. A. |title=The evolution of mutualisms: exploring the paths between conflict and cooperation |journal=Trends in Ecology and Evolution |volume=14 |issue=2 |pages=49–53 |year=1999 |url=http://www.biology.lsu.edu/webfac/kharms/HerreEA_etal_1999_TREE.pdf |doi=10.1016/S0169-5347(98)01529-8 |pmid=10234251 }}</ref>
| |
| | |
| <ref name="Hinchman07">{{Cite journal |last1=Hinchman |first1=L. P. |last2=Hinchman |first2=S. K. |title=What we owe the Romantics |journal=Environmental Values |volume=16 |issue=3 |pages=333–354 |year=2007 |doi=10.3197/096327107X228382 }}</ref>
| |
| | |
| <ref name="Holling01">{{Cite journal |last=Holling |first=C. S. |title=Understanding the complexity of economic, ecological, and social systems |journal=Ecosystems |volume=4 |issue=5 |pages =390–405 |year=2004 |doi=10.1007/s10021-001-0101-5 }}</ref>
| |
| | |
| <ref name="Holling73">{{Cite journal |last=Holling |first=C. S. |title=Resilience and stability of ecological systems |journal=Annual Review of Ecology and Systematics |volume=4 |issue=1 |pages=1–23 |year=1973 |jstor=2096802 |doi=10.1146/annurev.es.04.110173.000245}}</ref>
| |
| | |
| <ref name="Hughes75">{{Cite journal |last=Hughes |first=J. D. |title=Ecology in ancient Greece |journal=Inquiry |volume=18 |issue=2 |pages=115–125 |year=1975 |url=http://www.informaworld.com/smpp/content~db=all~content=a902027058 |doi=10.1080/00201747508601756}}</ref>
| |
| | |
| <ref name="Hughes85">{{Cite journal |last=Hughes |first=J. D. |title=Theophrastus as ecologist |journal=Environmental Review |volume=9 |issue=4 |pages=296–306 |year=1985 |doi=10.2307/3984460 |jstor=3984460}}</ref>
| |
| | |
| <ref name="Hughes08">{{Cite journal |last=Hughes |first=D. P. |last2=Pierce |first2=N. E. |last3=Boomsma |first3=J. J. |title=Social insect symbionts: evolution in homeostatic fortresses |journal=Trends in Ecology & Evolution |volume=23 |issue=12 |pages=672–677 |year=2008 |url=http://www.csub.edu/~psmith3/Teaching/discussion3C.pdf |doi=10.1016/j.tree.2008.07.011 |pmid=18951653 }}</ref>
| |
| | |
| <ref name="Hughes10">{{Cite journal |last=Hughes |first=A. R. |title=Disturbance and diversity: an ecological chicken and egg problem |journal=Nature Education Knowledge |volume=1 |issue=8 |page=26 |url=http://www.nature.com/scitable/knowledge/library/disturbance-and-diversity-an-ecological-chicken-and-13256228 }}</ref>
| |
| | |
| <ref name="Humphreys97">{{Cite journal |last1=Humphreys |first1=N. J. |last2=Douglas |first2=A. E. |title=Partitioning of symbiotic bacteria between generations of an insect: a quantitative study of a ''Buchnera'' sp. in the pea aphid (''Acyrthosiphon pisum'') reared at different temperatures |journal=Applied and Environmental Microbiology |volume=63 |issue=8 |pages=3294–3296 |year=1997 |pmid=16535678 |pmc=1389233 }}</ref>
| |
| | |
| <ref name="Hutchinson57">{{Cite book |last=Hutchinson |first=G. E. |title=A Treatise on Limnology |publisher=Wiley |year=1957 |location=New York, NY |page=1015 |isbn=0-471-42572-9}}</ref>
| |
| | |
| <ref name="Hutchinson57b">{{Cite journal |last=Hutchinson |first=G. E. |title=Concluding remarks |journal=Cold Spring Harbor Symposia on Quantitative Biology |volume=22 |pages=415–427 |year=1957 |url=http://symposium.cshlp.org/content/22/415.full.pdf+html |doi=10.1101/SQB.1957.022.01.039}}</ref>
| |
| | |
| <ref name="igamberdiev06">{{Cite journal |last=Igamberdiev |first=Abir U. |last2=Lea |first2=P. J. |title=Land plants equilibrate O<sub>2</sub> and CO<sub>2</sub> concentrations in the atmosphere |journal=Photosynthesis Research |volume=87 |issue=2 |pages=177–194 |year=2006 |url=http://www.mun.ca/biology/igamberdiev/PhotosRes_CO2review.pdf |doi=10.1007/s11120-005-8388-2 |pmid=16432665 }}</ref>
| |
| | |
| <ref name="Irwin10">{{cite journal |last1=Irwin |first1=Rebecca E. |DUPLICATE_last2=Bronstein |first2=Judith L. |last2=Manson |last3=Jessamyn S. |last4=Richardson |first4=Leif |title=Nectar robbing: Ecological and evolutionary perspectives |journal=Annual Review of Ecology, Evolution, and Systematics |year=2010 |volume=41 |issue=2 |pages=271–292 |doi=10.1146/annurev.ecolsys.110308.120330}}</ref>
| |
| | |
| <ref name="Itô91">{{Cite journal |last=Itô |first=Y. |title=Development of ecology in Japan, with special reference to the role of Kinji Imanishi |journal=Journal of Ecological Research |volume=6 |issue=2 |pages=139–155 |year=1991 |doi=10.1007/BF02347158 }}</ref>
| |
| | |
| <ref name="Ives04">{{Cite journal |last1=Ives |first1=A. R. |last2=Cardinale |first2=B. J. |last3=Snyder |first3=W. E. |title=A synthesis of subdisciplines: Predator–prey interactions, and biodiversity and ecosystem functioning |journal=Ecology Letters |volume=8 |issue=1 |pages=102–116 |year=2004 |url=http://www.lifesci.ucsb.edu/eemb/labs/cardinale/pdfs/ives_ecol_lett_2005.pdf |doi=10.1111/j.1461-0248.2004.00698.x }}</ref>
| |
| | |
| <ref name="Jacobsen08">{{Cite journal |last=Jacobsen |first=D. |title=Low oxygen pressure as a driving factor for the altitudinal decline in taxon richness of stream macroinvertebrates |journal=Oecologia |volume=154 |issue=4 |pages=795–807 |year=2008 |doi=10.1007/s00442-007-0877-x |pmid=17960424 }}</ref>
| |
| | |
| <ref name="Johnson04">{{Cite journal |last=Johnson |first=J. B. |last2=Omland |first2=K. S. |title=Model selection in ecology and evolution |journal=Trends in Ecology and Evolution |volume=19 |issue=2 |pages=101–108 |year=2004 |url=http://faculty.washington.edu/skalski/classes/QERM597/papers/Johnson%20and%20Omland.pdf |doi=10.1016/j.tree.2003.10.013 |pmid=16701236 }}</ref>
| |
| | |
| <ref name="Johnson07">{{Cite journal |last1=Johnson |first1=M. T. |last2=Strinchcombe |first2=J. R. |title=An emerging synthesis between community ecology and evolutionary biology |journal=Trends in Ecology and Evolution |volume=22 |issue=5 |pages=250–257 |year=2007 |doi=10.1016/j.tree.2007.01.014 |pmid=17296244 }}</ref>
| |
| | |
| <ref name="Jones94">{{Cite journal |last1=Jones |first1=Clive G. |last2=Lawton |first2=John H. |last3=Shachak |first3=Moshe |title=Organisms as ecosystem engineers |journal=Oikos |volume=69 |issue=3 |pages=373–386 |year=1994 |doi=10.2307/3545850 |jstor=3545850}}</ref>
| |
| | |
| <ref name="Karban08">{{Cite journal |last=Karban |first=R. |title=Plant behaviour and communication |journal=Ecology Letters |volume=11 |issue=7 |pages=727–739 |year=2008 |pmid=18400016 |doi=10.1111/j.1461-0248.2008.01183.x }}</ref>
| |
| | |
| <ref name="Kastak98">{{Cite journal |last1=Kastak |first1=D. |last2=Schusterman |first2=R. J. |title=Low-frequency amphibious hearing in pinnipeds: Methods, measurements, noise, and ecology |journal=Journal of the Acoustical Society of America |volume=103 |issue=4 |pages=2216–2228 |year=1998 |doi=10.1121/1.421367 |pmid=9566340 |bibcode=1998ASAJ..103.2216K}}</ref>
| |
| | |
| <ref name="Kiers06">{{Cite journal |last1=Kiers |first1=E. T. |last2=van der Heijden |first2=M. G. A. |title=Mutualistic stability in the arbuscular mycorrhizal symbiosis: Exploring hypotheses of evolutionary cooperation |journal=Ecology |volume=87 |issue=7 |pages=1627–1636 |year=2006 |url=http://people.umass.edu/lsadler/adlersite/kiers/Kiers_Ecology_2006.pdf |doi=10.1890/0012-9658(2006)87[1627:MSITAM]2.0.CO;2 |pmid=16922314 |issn=0012-9658}}</ref>
| |
| | |
| <ref name="Kiessling09">{{Cite journal |last1=Kiessling |first1=W. |last2=Simpson|first2=C. |last3=Foote |first3=M. |title=Reefs as cradles of evolution and sources of biodiversity in the Phanerozoic |journal=Science |volume=327 |issue=5962 |pages=196–198 |year=2009 |doi=10.1126/science.1182241 |pmid=20056888 |bibcode=2010Sci...327..196K}}</ref>
| |
| | |
| <ref name="Kingsland04">{{Cite journal |last=Kingsland |first=S. |title=Conveying the intellectual challenge of ecology: An historical perspective |journal=Frontiers in Ecology and the Environment |volume=2 |issue=7 |pages=367–374 |year=2004 |url=http://www.isa.utl.pt/dbeb/ensino/txtapoio/HistEcology.pdf |doi=10.1890/1540-9295(2004)002[0367:CTICOE]2.0.CO;2 |issn=1540-9295}}</ref>
| |
| | |
| <ref name="Kleese01">{{Cite journal |last=Kleese |first=D. A. |title=Nature and nature in Psychology |journal=Journal of Theoretical and Philosophical Psychology |volume=21 |pages=61–79 |year=2001 |doi=10.1037/h0091199 }}</ref>
| |
| | |
| <ref name="Kodric-Brown84">{{Cite journal |last1=Kodric-Brown |first1=A. |last2=Brown |first2=J. H. |title=Truth in advertising: The kinds of traits favored by sexual selection |journal=The American Naturalist|volume=124 |issue=3 |pages=309–323 |year=1984 |url=http://dbs.umt.edu/courses/biol406/readings/Wk6-Kodric-Brown%20and%20Brown%201984.pdf |doi=10.1086/284275 }}{{dead link|date=August 2012}}</ref>
| |
| | |
| <ref name="Kormandy78">{{Cite journal |last1=Kormandy |first1=E. J. |last2=Wooster |first2=Donald |title=Review: Ecology/economy of nature—synonyms? |journal=Ecology |volume=59 |issue=6 |pages=1292–1294 |year=1978 |doi=10.2307/1938247 |jstor=1938247}}</ref>
| |
| | |
| <ref name="Kormondy95">{{Cite book |last=Kormondy |first=E. E. |title=Concepts of Ecology |edition=4th |year=1995 |publisher=Benjamin Cummings |isbn=0-13-478116-3}}</ref>
| |
| | |
| <ref name="Kraus03">{{Cite journal |last1=Krause |first1=A. E. |last2=Frank |first2=K. A. |last3=Mason |first3=D. M. |last4=Ulanowicz |first4=R. E. |last5=Taylor |first5=W. W. |title=Compartments revealed in food-web structure |year=2003 |journal=Nature |volume=426 |issue=6964 |pages=282–285 |url=http://www.glerl.noaa.gov/pubs/fulltext/2003/20030014.pdf |doi=10.1038/nature02115 |pmid=14628050 |bibcode=2003Natur.426..282K }}</ref>
| |
| | |
| <ref name="Krebs93">{{Cite book |last1=Krebs |first1=J. R. |last2=Davies |first2=N. B. |title=An Introduction to Behavioural Ecology |publisher=Wiley-Blackwell |year=1993 |page=432 |url=http://books.google.com/books?id=CA31asx7zq4C |isbn=978-0-632-03546-5}}</ref>
| |
| | |
| <ref name="Laland99">{{Cite journal |last1=Laland |first1=K. N. |last2=Odling-Smee |first2=F. J. |last3=Feldman |first3=M. W. |title=Evolutionary consequences of niche construction and their implications for ecology |journal=Proceedings of the National Academy of Sciences of the United States of America |volume=96 |pages=10242–10247 |year=1999 |doi=10.1073/pnas.96.18.10242 |pmid=10468593 |issue=18 |pmc=17873 |bibcode=1999PNAS...9610242L}}</ref>
| |
| | |
| <ref name="Landhäusser09">{{Cite journal |last=Landhäusser |first=Simon M. |last2=Deshaies |first2=D. |last3=Lieffers |first3=V. J. |title=Disturbance facilitates rapid range expansion of aspen into higher elevations of the Rocky Mountains under a warming climate |journal=Journal of Biogeography |volume=37 |issue=1 |pages=68–76 |year=2009 |doi=10.1111/j.1365-2699.2009.02182.x }}</ref>
| |
| | |
| <ref name="Lenton00">{{Cite journal |last1=Lenton |first1=T. M. |last2=Watson |first2=A. |title=Redfield revisited. 2. What regulates the oxygen content of the atmosphere |journal=Global Biogeochemical Cycles |volume=14 |issue=1 |pages=249–268 |year=2000 |url=http://lgmacweb.env.uea.ac.uk/esmg/papers/Redfield_revisited_2.pdf |doi=10.1029/1999GB900076 |bibcode=2000GBioC..14..249L}}</ref>
| |
| | |
| <ref name="Levins69">{{Cite journal |last=Levins |first=R. |title=Some demographic and genetic consequences of environmental heterogeneity for biological control |journal=Bulletin of the Entomological Society of America |volume=15 |pages=237–240 |year=1969 |url=http://books.google.com/?id=8jfmor8wVG4C&pg=PA162 |isbn=978-0-231-12680-9 }}</ref>
| |
| | |
| <ref name="Levins70">{{Cite book |last=Levins |first=R. |editor-last=Gerstenhaber |editor-first=M. |chapter=Extinction |title=Some Mathematical Questions in Biology |year=1970 |pages=77–107 |url=http://books.google.com/books?id=CfZHU1aZqJsC |isbn=978-0-8218-1152-8}}</ref>
| |
| | |
| <ref name="Levin92">{{Cite journal |last=Levin |first=S. A. |title=The problem of pattern and scale in ecology: The Robert H. MacArthur Award |journal=Ecology |volume=73 |issue=6 |pages=1943–1967 |year=1992 |url=http://www.biology.duke.edu/upe301/LEVIN92.pdf |accessdate=2010-03-16 |doi=10.2307/1941447 |jstor=1941447 }}</ref>
| |
| | |
| <ref name="Levin98">{{Cite journal |doi=10.1007/s100219900037 |last=Levin |first=S. A. |title=Ecosystems and the biosphere as complex adaptive systems |journal=Ecosystems |volume=1 |issue=5 |pages=431–436 |year=1998 |id = {{citeseerx|10.1.1.83.6318}} }}</ref>
| |
| | |
| <ref name="Levin99">{{Cite book |last1=Levin |first1=S. A. |title=Fragile Dominion: Complexity and the Commons |publisher=Perseus Books |year=1999 | location=Reading, MA |url=http://books.google.com/books?id=FUJsj2KOEeoC |isbn=978-0-7382-0319-5}}</ref>
| |
| | |
| <ref name="Li00">{{Cite journal |last=Li |first=B. |title=Why is the holistic approach becoming so important in landscape ecology? |journal=Landscape and Urban Planning |volume=50 |issue=1–3 |pages=27–41 |year=2000 |doi=10.1016/S0169-2046(00)00078-5 }}</ref>
| |
| | |
| <ref name="Libralato06">{{Cite journal |last1=Libralato |first1=S. |last2=Christensen |first2=V. |last3=Pauly |first3=D. |title=A method for identifying keystone species in food web models |journal=Ecological Modelling |volume=195 |issue=3–4 |pages=153–171 |year=2006 |url=http://www.seaaroundus.org/researcher/dpauly/PDF/2005/JournalArticles/MethodIdentifyKeystoneSpeciesFoodWebModels.pdf |doi=10.1016/j.ecolmodel.2005.11.029 }}</ref>
| |
| | |
| <ref name="Liu09">{{Cite journal |last1=Liu |first1=J. |last2=Dietz |first2=Thomas |last3=Carpenter |first3=Stephen R. |last4=Folke |first4=Carl |last5=Alberti |first5=Marina |last6=Redman |first6=Charles L. |last7=Schneider |first7=Stephen H. |last8=Ostrom |first8=Elinor |last9=Pell |first9=Alice N. |title=Coupled human and natural systems |journal=AMBIO: A Journal of the Human Environment |volume=36 |issue=8 |pages=639–649 |year=2009 |url=http://ambio.allenpress.com/archive/0044-7447/36/8/pdf/i0044-7447-36-8-639.pdf |doi=10.1579/0044-7447(2007)36[639:CHANS]2.0.CO;2 |issn=0044-7447|display-authors=9 }}</ref>
| |
| | |
| <ref name="Lobert93">{{Cite book |last1=Lobert |first1=J. M. |last2=Warnatz |first2=J. |chapter=Emissions from the combustion process in vegetation |title=Fire in the Environment: The Ecological, Atmospheric and Climatic Importance of Vegetation Fires |editor-last=Crutzen |editor-first=P. J. |editor2-last=Goldammer |editor2-first=J. G. |publisher=Wiley |year=1993 |url=http://jurgenlobert.org/papers_data/Lobert.Warnatz.Wiley.1993.pdf |isbn=978-0-471-93604-6}}</ref>
| |
| | |
| <ref name="Loehle88">{{Cite journal |last1=Loehle |first1=C. |last2=Pechmann |first2=Joseph H. K. |title=Evolution: The missing ingredient in systems ecology |journal=The American Naturalist |volume=132 |issue=9 |pages=884–899 |year=1988 |doi=10.1086/284895 |jstor=2462267}}</ref>
| |
| | |
| <ref name="Loehle04">{{Cite journal |last=Loehle |first=C. |title=Challenges of ecological complexity |journal=Ecological Complexity |volume=1 |issue=1 |pages=3–6 |year=2004 |doi=10.1016/j.ecocom.2003.09.001 }}</ref>
| |
| | |
| <ref name="Lovelock73">{{Cite journal |last1=Lovelock |first1=J. |last2=Margulis |first2=Lynn |title=Atmospheric homeostasis by and for the biosphere: The Gaia hypothesis |journal=Tellus |volume=26 |pages=2–10 |year=1973 |doi=10.1111/j.2153-3490.1974.tb01946.x |bibcode=1974Tell...26....2L}}</ref>
| |
| | |
| <ref name="Lovelock03">{{Cite journal |last=Lovelock |first=J. |title=The living Earth |year=2003 |journal=Nature |volume=426|pages=769–770 |doi=10.1038/426769a |pmid=14685210 |issue=6968 |bibcode = 2003Natur.426..769L }}</ref>
| |
| | |
| <ref name="MacArthur67">{{Cite journal |last1=MacArthur |first1=R. |last2=Wilson |first2=E. O. |title=The Theory of Island Biogeography |location=Princeton, NJ |publisher=Princeton University Press |year=1967}}</ref>
| |
| | |
| <ref name="MacKenzie06">{{Cite book |last1=MacKenzie |last2=D.I. |title=Occupancy Estimation and Modeling: Inferring Patterns and Dynamics of Species Occurrence |publisher=Elsevier Academic Press |year=2006 |location=London, UK |page=324 |url=http://books.google.com/books?id=RaCmF9PioCIC |isbn=978-0-12-088766-8}}</ref>
| |
| | |
| <ref name="Marsh64">{{Cite book |last1=Marsh |first1=G. P. |title=Man and Nature: Physical Geography as Modified by Human Action |publisher=Belknap Press |location=Cambridge, MA |url=http://books.google.com/books?id=q-7wEQi0Gj0C |year=1864 |page=560}}</ref>
| |
| | |
| <ref name="Mason57">{{Cite journal |last1=Mason |first1=H. L. |last2=Langenheim |first2=J. H. |title=Language analysis and the concept "environment" |journal=Ecology |volume=38 |issue=2 |pages=325–340 |year=1957 |doi=10.2307/1931693 |jstor=1931693}}</ref>
| |
| | |
| <ref name="May99">{{Cite journal |last1=May |first1=R. |title=Unanswered questions in ecology |journal=Philosophical Transactions of the Royal Society B |volume=354 |issue=1392 |pages=1951–1959 |year=1999 |doi=10.1098/rstb.1999.0534 |pmc=1692702 |pmid=10670015}}</ref>
| |
| | |
| <ref name="McCann07">{{Cite journal |last1=McCann |first1=K. |title=Protecting biostructure |journal=Nature |year=2007 |volume=446 |issue=7131 |page=29 |url=http://www.bolinfonet.org/pdf/McCann_2007_biostructure.pdf |doi=10.1038/446029a |pmid=17330028 |bibcode=2007Natur.446...29M}}</ref>
| |
| | |
| <ref name="MEA05">{{cite web |url=http://www.millenniumassessment.org/en/Synthesis.aspx |title=Millennium Ecosystem Assessment – Synthesis Report |year=2005 |publisher=United Nations |accessdate=4 February 2010}}</ref>
| |
| | |
| <ref name="Meysman06">{{Cite journal |last1=Meysman |first1=F. J. R. |last2=Middelburg |first2=Jack J. |last3=Heip |first3=C. H. R. |title=Bioturbation: A fresh look at Darwin's last idea |journal=Trends in Ecology and Evolution |volume=21 |issue=22 |pages=688–695 |year=2006 |url=http://www.sciencedirect.com/science/article/pii/S0169534706002436 |doi=10.1016/j.tree.2006.08.002 |pmid=16901581 }}</ref>
| |
| | |
| <ref name="Mikkelson10">{{Cite book |last1=Mikkelson |first1=G. M. |editor1-last=Skipper |editor1-first=R. A. |editor2-last=Allen |editor2-first=C. |editor3-last=Ankeny |editor3-first=R. |editor4-last=Craver |editor4-first=C. F. |editor5-last=Darden |editor5-first=L. |editor6-last=Richardson |editor6-first=R.C. |chapter=Part-whole relationships and the unity of ecology |title=Philosophy Across the Life Sciences |location=Cambridge, MA |publisher=MIT Press |year=2010 |url=http://webpages.mcgill.ca/staff/Group3/gmikke/web/pwrue.pdf}}</ref>
| |
| | |
| <ref name="Miles93">{{Cite journal |last1=Miles |first1=D. B. |last2=Dunham |first2=A. E. |title=Historical perspectives in ecology and evolutionary biology: The use of phylogenetic comparative analyses |journal=Annual Review of Ecology and Systematics |volume=24 |pages=587–619 |year=1993 |doi=10.1146/annurev.es.24.110193.003103 }}</ref>
| |
| | |
| <ref name="Mills93">{{Cite journal |last1=Mills |first1=L. S. |last2=Soule |first2=M. E. |last3=Doak |first3=D. F. |title=The keystone-species concept in ecology and conservation |year=1993 |journal=BioScience |volume=43 |issue=4 |pages=219–224 |doi=10.2307/1312122 |jstor=1312122}}</ref>
| |
| | |
| <ref name="Molnar04">{{Cite journal |last1=Molnar |first1=J. |last2=Marvier |first2=M. |last3=Kareiva |first3=P. |title=The sum is greater than the parts |journal=Conservation Biology |volume=18 |issue=6 |pages=1670–1671 |year=2004 |url=http://www.environmental-expert.com/Files%5C8392%5Carticles%5C9961%5CTheSumIsGreaterthantheParts.pdf |doi=10.1111/j.1523-1739.2004.00l07.x }}</ref>
| |
| | |
| <ref name="Morrone95">{{Cite journal |last1=Morrone |first1=J. J. |last2=Crisci |first2=J. V. |title=Historical biogeography: Introduction to methods |journal=Annual Review of Ecology and Systematics |volume=26 |pages=373–401 |year=1995 |doi=10.1146/annurev.es.26.110195.002105 }}</ref>
| |
| | |
| <ref name="Nachtomy01">{{Cite journal |last1=Nachtomy |first1=Ohad |last2=Shavit |first2=Ayelet |last3=Smith |first3=Justin |title=Leibnizian organisms, nested individuals, and units of selection |journal=Theory in Biosciences |volume=121 |issue=2 |year=2002 |doi=10.1007/s12064-002-0020-9 |page=205 }}</ref>
| |
| | |
| <ref name="Nebel10">{{Cite journal |last1=Nebel |first1=S. |title=Animal migration |journal=Nature Education Knowledge |volume=10 |issue=1 |year=2010 |page=29 |url=http://www.nature.com/scitable/knowledge/library/animal-migration-13259533}}</ref>
| |
| | |
| <ref name="Neeman04">{{Cite journal |last1=Ne'eman |first1=G. |last2=Goubitz |first2=S. |last3=Nathan |first3=R. |title=Reproductive traits of ''Pinus halepensis'' in the light of fire: a critical review |journal=Plant Ecology |volume=171 |issue=1/2 |pages=69–79 |year=2004 |doi=10.1023/B:VEGE.0000029380.04821.99 }}</ref>
| |
| | |
| <ref name="Nishiguchi10">{{Cite journal |last1=Nishiguchi |first1=Y. |last2=Ito |first2=I. |last3=Okada |first3=M. |title=Structure and function of lactate dehydrogenase from hagfish |journal=Marine Drugs |volume=8 |issue=3 |pages=594–607 |year=2010 |pmid=20411117 |pmc=2857353 |doi=10.3390/md8030594 }}</ref>
| |
| | |
| <ref name="Noss90">{{Cite journal |last1=Noss |first1=R. F. |title=Indicators for monitoring biodiversity: A hierarchical approach |journal=Conservation Biology |volume=4 |issue=4 |pages=355–364 |year=1990 |doi=10.1111/j.1523-1739.1990.tb00309.x |jstor=2385928}}</ref>
| |
| | |
| <ref name="Noss94">{{Cite book |last1=Noss |first1=R. F. |last2=Carpenter |first2=A. Y. |title=Saving Nature's Legacy: Protecting and Restoring Biodiversity |publisher=Island Press |year=1994 |isbn=978-1-55963-248-5 |url=http://books.google.ca/books?id=xsjDp8jK3-AC&printsec=frontcover#v=onepage&q&f=false |page=443}}</ref>
| |
| | |
| <ref name="Novikoff45">{{Cite journal |last1=Novikoff |first2=A. B. |title=The concept of integrative levels and biology |journal=Science |volume=101 |issue=2618 |pages=209–215 |url=http://rogov.zwz.ru/Macroevolution/novikoff.pdf |doi=10.1126/science.101.2618.209 |pmid=17814095 |year=1945 |first1=AB|bibcode=1945Sci...101..209N}}</ref>
| |
| | |
| <ref name="Obryan07">{{Cite journal |last1=O'Brian |first1=E. |last2=Dawson |first2=R. |title=Context-dependent genetic benefits of extra-pair mate choice in a socially monogamous passerine |journal=Behavioral Ecology and Sociobiology |volume=61 |issue=5 |pages=775–782 |year=2007|url=http://web.unbc.ca/~dawsonr/2007_bes61_775-782.pdf |doi=10.1007/s00265-006-0308-8 }}</ref>
| |
| | |
| <ref name="Odum1977">{{Cite journal |last1=Odum |first1=E. P. |title=The emergence of ecology as a new integrative discipline |journal=Science |volume=195 |issue=4284 |pages=1289–1293 |year=1977 |doi=10.1126/science.195.4284.1289 |pmid=17738398 |bibcode=1977Sci...195.1289O}}</ref>
| |
| | |
| <ref name="Odum05">{{Cite book |last1=Odum |first1=E. P. |last2=Barrett |first2=G. W. |title=Fundamentals of Ecology |publisher=Brooks Cole |isbn=978-0-534-42066-6 |year=2005 |page=598 |url=http://books.google.com/?id=vC9FAQAAIAAJ&q=fundamentals+of+ecology&dq=fundamentals+of+ecology}}</ref>
| |
| | |
| <ref name="Oksanen91">{{Cite journal |last1=Oksanen| first1=L. |title=Trophic levels and trophic dynamics: A consensus emerging? |year=1991 |journal=Trends in Ecology and Evolution |volume=6 |issue=2 |pages=58–60 |doi=10.1016/0169-5347(91)90124-G |pmid=21232425}}</ref>
| |
| | |
| <ref name="O'Neill86">{{Cite book |last1=O'Neill |first1=D. L. |last2=Deangelis |first2=D. L. |last3=Waide |first3=J. B. |last4=Allen |first4=T. F. H. |title=A Hierarchical Concept of Ecosystems |year=1986 |publisher=Princeton University Press |page=253 |isbn=0-691-08436-X |url=http://books.google.com/books?id=Bj1cx_UeLK4C}}</ref>
| |
| | |
| <ref name="O'Neil01">{{Cite journal |last1=O'Neil |first1=R. V. |title=Is it time to bury the ecosystem concept? (With full military honors, of course!) |journal=Ecology |volume=82 |issue=12 |pages=3275–3284 |year=2001 |url=http://www.esa.org/history/Awards/papers/ONeill_RV_MA.pdf |doi=10.1890/0012-9658(2001)082[3275:IITTBT]2.0.CO;2 |issn=0012-9658}}</ref>
| |
| | |
| <ref name="Ostfeld09">{{Cite journal |last=Ostfeld |first=R. S. |title=Biodiversity loss and the rise of zoonotic pathogens |journal=Clinical Microbiology and Infection|volume=15|issue=s1 |pages=40–43 |year=2009 |url=http://www.ecostudies.org/reprints/Ostfeld_2009_Clin_Microbiol_Inf.pdf |doi=10.1111/j.1469-0691.2008.02691.x |pmid=19220353 }}</ref>
| |
| | |
| <ref name="Pagani05">{{Cite journal |last1=Pagani |first1=M. |last2=Zachos |first2=J. C. |last3=Freeman |first3=K. H. |last4=Tipple |first4=B. |last5=Bohaty |first5=S. |title=Marked decline in atmospheric carbon dioxide concentrations during the Paleogene |journal=Science |volume=309 |pages=600–603 |year=2005 |doi=10.1126/science.1110063 |pmid=15961630 |issue=5734 |bibcode=2005Sci...309..600P}}</ref>
| |
| | |
| <ref name="Page91">{{Cite journal |last1=Page |first1=R. D. M. |title=Clocks, clades, and cospeciation: Comparing rates of evolution and timing of cospeciation events in host-parasite assemblages |journal=Systematic Zoology |volume=40 |issue=2 |pages=188–198 |year=1991 |doi=10.2307/2992256 |jstor=2992256}}</ref>
| |
| | |
| <ref name="Palmer94">{{Cite journal |last1=Palmer |first1=M. |last2=White |first2=P. S. |title=On the existence of ecological communities |journal=Journal of Vegetation Sciences |volume=5 |issue=2 |pages=279–282 |year=1994 |url=http://labs.bio.unc.edu/Peet/courses/bio669/papers/Ch1_supp_readings/Palmer_White.pdf |doi=10.2307/3236162 |jstor=3236162 }}</ref>
| |
| | |
| <ref name="Palumbi09">{{Cite journal |last1=Palumbi |last2=S. R. |last3=Allan |first3=J. David |last4=Beck |first4=Michael W. |last5=Fautin |first5=Daphne G. |last6=Fogarty |first6=Michael J. |last7=Halpern |first7=Benjamin S. |last8=Incze |first8=Lewis S. |last9=Leong |first9=Jo-Ann |title=Managing for ocean biodiversity to sustain marine ecosystem services |journal=Frontiers in Ecology and the Environment |volume=7 |issue=4 |pages=204–211 |year=2009 |url=http://research.usm.maine.edu/gulfofmaine-census/wp-content/docs/Palumbi-et-al-2009_Managing-for-ocean-biodiversity.pdf |doi=10.1890/070135 |display-authors=9 }}</ref>
| |
| | |
| <ref name="Parenti90">{{Cite book |last1=Parenti |first1=L. R. |last2=Ebach |first2=M. C. |title=Comparative Biogeography: Discovering and Classifying Biogeographical Patterns of a Dynamic Earth |location=London, England |publisher=University of California Press |year=2009 |url=http://books.google.com/books?id=K1GU_1I6bG4C |isbn=978-0-520-25945-4}}</ref>
| |
| | |
| <ref name="Pearman08">{{Cite journal |last1=Pearman |first1=P. B. |last2=Guisan |first2=A. |last3=Broennimann |first3=O. |last4=Randin |first4=C. F. |title=Niche dynamics in space and time |journal=Trends in Ecology & Evolution |volume=23 |issue=3 |pages=149–158 |year=2008 |doi=10.1016/j.tree.2007.11.005 |pmid=18289716| url=http://www.isa.utl.pt/dm/biodiv/biodiv09_10/Niche%20dynamics%20in%20space%20and%20time.pdf}}</ref>
| |
| | |
| <ref name="Pearson00">{{Cite journal |last1=Pearson |first1=P. N. |last2=Palmer |first2=M. R. |title=Atmospheric carbon dioxide concentrations over the past 60 million years |journal=Nature |volume=406 |pages=695–699 |year=2000 |url=http://paleolands.com/pdf/cenozoicCO2.pdf |doi=10.1038/35021000 |pmid=10963587 |issue=6797 }}</ref>
| |
| | |
| <ref name="Pianka72">{{Cite journal |last1=Pianka |first1=E. R. |title=r and K Selection or b and d Selection? |journal=The American Naturalist |volume=106 |issue=951 |pages=581–588 |year=1972 |doi=10.1086/282798 }}</ref>
| |
| | |
| <ref name="Pimm91">{{Cite journal |last1=Pimm |first1=S. L. |last2=Lawton |first2=J. H. |last3=Cohen |first3=J. E. |title=Food web patterns and their consequences |journal=Nature |volume=350 |pages=669–674 |year=1991 |url=http://www.nicholas.duke.edu/people/faculty/pimm/publications/pimmreprints/71_Pimm_Lawton_Cohen_Nature.pdf |doi=10.1038/350669a0 |issue=6320 |bibcode=1991Natur.350..669P |format=PDF}}</ref>
| |
| | |
| <ref name="Pimm02">{{Cite book |last1=Pimm |first1=S. |title=Food Webs |year=2002 |publisher=University of Chicago Press |page=258 |isbn=978-0-226-66832-1 |url=http://books.google.com/books?id=tjHOtK4amfQC&pg=PA173}}</ref>
| |
| | |
| <ref name="Pockman95">{{Cite journal |last1=Pockman |first1=W. T. |last2=Sperry |first2=J. S. |last3=O'Leary |first3=J. W. |title=Sustained and significant negative water pressure in xylem |journal=Nature |volume=378 |pages=715–716 |year=1995 |doi=10.1038/378715a0 |issue=6558 |bibcode=1995Natur.378..715P}}</ref>
| |
| | |
| <ref name="Polis96">{{Cite journal |last1=Polis |first1=G. A. |last2=Strong |first2=D. R. |title=Food web complexity and community dynamics |journal=The American Naturalist |volume=147 |issue=5 |year=1996 |pages=813–846 |url=http://limnology.wisc.edu/courses/zoo955/Spring2005/food%20web%20seminar%20papers/polis96AmNat.pdf |doi=10.1086/285880}}</ref>
| |
| | |
| <ref name="Polis00">{{Cite journal |last1=Polis |first1=G. A. |last2=Sears |first2=Anna L. W. |last3=Huxel |first3=Gary R. |last4=Strong |first4=Donald R. |last5=Maron |first5=John |title=When is a trophic cascade a trophic cascade? |year=2000 |journal=Trends in Ecology and Evolution |volume=15 |issue=11 |pages=473–475 |url=http://www.cof.orst.edu/leopold/class-reading/Polis%202000.pdf |doi=10.1016/S0169-5347(00)01971-6 |pmid=11050351 }}</ref>
| |
| | |
| <ref name="Prentice92">{{Cite journal |last1=Prentice |last2=I. C. |last3=Harrison |first3=S. P. |last4=Leemans |first4=R. |last5=Monserud |first5=R. A. |last6=Solomon |first6=A. M. |title=Special paper: A global biome model based on plant physiology and dominance, soil properties and climate |journal=Journal of Biogeography |volume=19 |issue=2 |pages=117–134 |year=1992 |doi=10.2307/2845499 |jstor=2845499}}</ref>
| |
| | |
| <ref name="Purvis00">{{Cite journal |last1=Purvis |first1=A. |last2=Hector |first2=A. |title=Getting the measure of biodiversity |journal=Nature |volume=405 |issue=6783 |pages=212–218 |year=2000 |url=http://www.botanischergarten.ch/BiodivVorles-2005WS/Nature-Insight-Biodiversity-2000.pdf |doi=10.1038/35012221 |pmid=10821281 }}</ref>
| |
| | |
| <ref name="Reznick02">{{Cite journal |last1=Reznick |first1=D. |last2=Bryant |first2=M. J. |last3=Bashey |first3=F. |title=r- and K-selection revisited: The role of population regulation in life-history evolution |journal=Ecology |volume=83 |issue=6 |pages=1509–1520 |year=2002 |url=http://www2.hawaii.edu/~taylor/z652/Reznicketal.pdf |doi=10.1890/0012-9658(2002)083[1509:RAKSRT]2.0.CO;2 |issn=0012-9658}}</ref>
| |
| | |
| <ref name="Ricklefs96">{{Cite book |title=The Economy of Nature |last1=Rickleffs |first1=Robert, E. |year=1996 |publisher=University of Chicago Press |isbn=0-7167-3847-3 |page=678}}</ref>
| |
| | |
| <ref name="Rosenzweig03">{{Cite journal |last1=Rosenzweig |first1=M. L. |title=Reconciliation ecology and the future of species diversity |journal=Oryx |volume=37 |issue=2 |pages=194–205 |year=2003 |url=http://eebweb.arizona.edu/COURSES/Ecol302/Lectures/ORYXRosenzweig.pdf |format=PDF }}</ref>
| |
| | |
| <ref name="Sakurai85">{{Cite journal |last1=Sakurai |first1=K. |title=An attelabid weevil (''Euops splendida'') cultivates fungi |journal=Journal of Ethology |volume=3 |issue=2 |pages=151–156 |year=1985 |doi=10.1007/BF02350306 }}</ref>
| |
| | |
| <ref name="Scheffer06">{{Cite journal |last1=Scheffer |first1=M. |last2=van Nes |first2=E. H. |title=Self-organized similarity, the evolutionary emergence of groups of similar species |journal=Proceedings of the National Academy of Sciences |volume=103 |issue=16 |pages=6230–6235 |url=http://theory.bio.uu.nl/rdb/te/Projects/Papers/Scheffer_pnas06_comments.pdf |doi=10.1073/pnas.0508024103 |year=2006 |bibcode=2006PNAS..103.6230S}}</ref>
| |
| | |
| <ref name="Schneider01">{{Cite journal |last1=Schneider |first1=D. D. |title=The rise of the concept of scale in ecology |journal=BioScience |volume=51 |issue=7 |pages=545–553 |year=2001 |url=http://www.mun.ca/biology/dschneider/Publications/2001DCS_AIBS_RiseOfScale.pdf |doi=10.1641/0006-3568(2001)051[0545:TROTCO]2.0.CO;2 |issn=0006-3568}}</ref>
| |
| | |
| <ref name="Schoener75">{{Cite journal |last1=Schoener |first1=T. W. |title=Presence and absence of habitat shift in some widespread lizard species |journal=Ecological Monographs |volume=45 |issue=3 |pages=233–258 |jstor=1942423 |year=1975 |doi=10.2307/1942423}}</ref>
| |
| | |
| <ref name="Scholes08">{{Cite journal |last1=Scholes |first1=R. J. |last2=Mace |first2=G. M. |last3=Turner |first3=W. |last4=Geller |first4=G. N. |last5=Jürgens |first5=N. |last6=Larigauderie |first6=A. |last7=Muchoney |first7=D. |last8=Walther |first8=B. A. |last9=Mooney |first9=H. A. |title=Toward a global biodiversity observing system |journal=Science |volume=321 |issue=5892 |pages=1044–1045 |year=2008 |url=http://www.earthobservations.com/documents/committees/uic/200809_8thUIC/07b-Health0Montira-Pongsiri-BON-Article-in-Science.pdf |doi=10.1126/science.1162055 |pmid=18719268 |display-authors=9 }}</ref>
| |
| | |
| <ref name="Sherman95">{{Cite journal |last1=Sherman |first1=P. W. |last2=Lacey |first2=E. A. |last3=Reeve |first3=H. K. |last4=Keller |first4=L. |title=The eusociality continuum |journal=Behavioural Ecology |volume=6 |issue=1 |pages=102–108 |year=1995 |url=http://www.nbb.cornell.edu/neurobio/BioNB427/READINGS/ShermanEtAl1995.pdf |format=PDF }}</ref>
| |
| | |
| <ref name="Shimeta95">{{Cite journal |last1=Shimeta |first1=J. |last2=Jumars |first2=P. A. |last3=Lessard |first3=E. J. |title=Influences of turbulence on suspension feeding by planktonic protozoa; experiments in laminar shear fields |journal=Limnolology and Oceanography |volume=40 |issue=5 |year=1995 |pages=845–859 |url=http://www.aslo.org/lo/toc/vol_40/issue_5/0845.pdf |doi=10.4319/lo.1995.40.5.0845 }}</ref>
| |
| | |
| <ref name="Shurin06">{{Cite journal |last1=Shurin |first1=J. B. |last2=Gruner |first2=D. S. |last3=Hillebrand |first3=H. |title=All wet or dried up? Real differences between aquatic and terrestrial food webs |journal=Proceedings of the Royal Society B |volume=273 |issue=1582 |pages=1–9 |year=2006 |doi=10.1098/rspb.2005.3377 |pmid=16519227 |pmc=1560001 }}</ref>
| |
| | |
| <ref name="Siverton06">{{Cite journal |last1=Silverton |first1=Jonathan |last2=Poulton |first2=Paul |last3=Johnston |first3=Edward |last4=Edwards |first4=Grant |last5=Heard |first5=Matthew |last6=Biss |first6=Pamela M. |title=The Park Grass Experiment 1856–2006: Its contribution to ecology |journal=Journal of Ecology |volume=94 |issue=4 |pages=801–814 |year=2006 |url=http://www.demonsineden.com/Site/Research_publications_files/Silvertown%20et%20al.%202006.pdf |doi=10.1111/j.1365-2745.2006.01145.x }}</ref>
| |
| | |
| <ref name="Simberloff80">{{Cite journal |last1=Simberloff |first1=D. |title=A succession of paradigms in ecology: Essentialism to materialism and probalism |journal=Synthese |volume=43 |pages=3–39 |year=1980 |doi=10.1007/BF00413854}}</ref>
| |
| | |
| <ref name="Sinclair26">{{Cite news |last1=Sinclair |first1=G. |title=On cultivating a collection of grasses in pleasure-grounds or flower-gardens, and on the utility of studying the Gramineae |location=New-Street-Square |publisher=A. & R. Spottiswoode |magazine=London Gardener's Magazine |year=1826 |volume=1 |page=115 |url=http://books.google.com/?id=fF0CAAAAYAAJ&pg=PA230}}</ref>
| |
| | |
| <ref name="Smith05">{{Cite journal |last1=Smith |first1=M. A. |last2=Green |first2=D. M. |title=Dispersal and the metapopulation paradigm in amphibian ecology and conservation: Are all amphibian populations metapopulations? |journal=Ecography |volume=28 |issue=1 |pages=110–128 |year=2005 |doi=10.1111/j.0906-7590.2005.04042.x }}</ref>
| |
| | |
| <ref name="Stadler98">{{Cite journal |last1=Stadler |first1=B. |last2=Michalzik |first2=B. |last3=Müller |first3=T. |title=Linking aphid ecology with nutrient fluxes in a coniferous forest |journal=Ecology |volume=79 |issue=5 |pages=1514–1525 |year=1998 |doi=10.1890/0012-9658(1998)079[1514:LAEWNF]2.0.CO;2 |issn=0012-9658}}</ref>
| |
| | |
| <ref name="Stauffer57">{{Cite journal |last1=Stauffer |first1=R. C. |title=Haeckel, Darwin and ecology |journal=The Quarterly Review of Biology |volume=32 |issue=2 |pages=138–144 |year=1957 |doi=10.1086/401754 }}</ref>
| |
| | |
| <ref name="Steele05">{{Cite journal |last1=Steele |first1=C. A. |last2=Carstens |first2=B. C. |last3=Storfer |first3=A. |last4=Sullivan |first4=J. |title=Testing hypotheses of speciation timing in ''Dicamptodon copei'' and ''Dicamptodon aterrimus'' (Caudata: Dicamptodontidae) |journal=Molecular Phylogenetics and Evolution |volume=36 |issue=1 |pages=90–100 |year=2005 |url=http://www.lsu.edu/faculty/carstens/pdfs/Steele.etal.2005.pdf |doi=10.1016/j.ympev.2004.12.001 |pmid=15904859 }}</ref>
| |
| | |
| <ref name="Strassmann00">{{Cite journal |last1=Strassmann |first1=J. E. |last2=Zhu |first2=Y. |last3=Queller |first3=D. C. |title=Altruism and social cheating in the social amoeba ''Dictyostelium discoideum'' |journal=Nature |volume=408 |issue=6815 |pages=965–967 |year=2000 |doi=10.1038/35050087 |pmid=11140681 }}</ref>
| |
| | |
| <ref name="Strook08">{{Cite journal |last1=Wheeler |first1=T. D. |last2=Stroock |first2=A. D. |title=The transpiration of water at negative pressures in a synthetic tree |journal=Nature |volume=455 |pages=208–212 |year=2008 |doi=10.1038/nature07226 |pmid=18784721 |issue=7210 |bibcode=2008Natur.455..208W}}</ref>
| |
| | |
| <ref name="Stuart-Fox08">{{Cite journal |last1=Stuart-Fox |first1=D. |last2=Moussalli |first2=A. |title=Selection for social signalling drives the evolution of chameleon colour change |journal=PLoS Biology |volume=6 |issue=1 |pages=e25 |year=2008 |doi=10.1371/journal.pbio.0060025 |pmid=18232740 |pmc=2214820 }}</ref>
| |
| | |
| <ref name="Svennin08">{{Cite journal |last1=Svenning |first1=Jens-Christian |last2=Condi |first2=R. |title=Biodiversity in a warmer world |journal=Science |volume=322 |issue=5899 |pages=206–207 |year=2008 |doi=10.1126/science.1164542 |pmid=18845738 }}</ref>
| |
| | |
| <ref name="Swenson08">{{Cite journal |last1=Swenson |first1=N. G. |last2=Enquist |first2=B. J. |title=The relationship between stem and branch wood specific gravity and the ability of each measure to predict leaf area |journal=American Journal of Botany |volume=95 |issue=4 |pages=516–519 |year=2008 |doi=10.3732/ajb.95.4.516 |pmid=21632377}}</ref>
| |
| | |
| <ref name="Tansley35">{{Cite journal |doi=10.2307/1930070 |last1=Tansley |first1=A. G.|title=The use and abuse of vegetational concepts and terms |journal=Ecology |volume=16 |issue=3 |pages=284–307 |year=1935 |url=http://karljaspers.org/files/tansley.pdf |jstor=1930070 }}</ref>
| |
| | |
| <ref name="Thompson07">{{Cite journal |last1=Thompson |first1=R. M. |last2=Hemberg |first2=M. |last3=Starzomski |first3=B. M. |last4=Shurin |first4=J. B. |title=Trophic levels and trophic tangles: The prevalence of omnivory in real food webs |journal=Ecology |volume=88 |issue=3 |pages=612–617 |doi=10.1890/05-1454 |url=http://myweb.dal.ca/br238551/thompson_hem_star_shur_ecology07.pdf |year=2007 |pmid=17503589}}</ref>
| |
| | |
| <ref name="Tierney09">{{Cite journal |last1=Tierney |DUPLICATE_first2=Geraldine L. |last2=Faber-Langendoen |first2=Don |last3=Mitchell |first3=Brian R. |last4=Shriver |first4=W. Gregory |last5=Gibbs |first5=James P. |title=Monitoring and evaluating the ecological integrity of forest ecosystems |journal=Frontiers in Ecology and the Environment |volume=7 |issue=6 |pages=308–316 |year=2009 |url=http://www.uvm.edu/~bmitchel/Publications/Tierney_Forest_monitoring.pdf |doi=10.1890/070176 }}</ref>
| |
| | |
| <ref name="Tinbergen63">{{Cite journal |last1=Tinbergen |first1=N. |title=On aims and methods of ethology |journal=Zeitschrift für Tierpsychologie |volume=20 |issue=4 |pages=410–433 |year=1963 |url=http://www.esf.edu/EFB/faculty/documents/Tinbergen1963onethology.pdf |format=PDF |doi=10.1111/j.1439-0310.1963.tb01161.x}}</ref>
| |
| | |
| <ref name="Turchin01">{{Cite journal |last1=Turchin |first1=P. |title=Does population ecology have general laws? |journal=Oikos |volume=94 |issue=1 |pages=17–26 |year=2001 |doi=10.1034/j.1600-0706.2001.11310.x }}</ref>
| |
| | |
| <ref name="Turnbaugh07">{{Cite journal |last1=Turnbaugh |first1=Peter J. |last2=Ley |first2=Ruth E. |last3=Hamady |first3=Micah |last4=Fraser-Liggett |first4=Claire M. |last5=Knight |first5=Rob |last6=Gordon |first6=Jeffrey I. |title=The human microbiome project |journal=Nature |volume=449 |pages=804–810 |year=2007 |doi=10.1038/nature06244 |pmid=17943116 |issue=7164 |bibcode=2007Natur.449..804T}}</ref>
| |
| | |
| <ref name="Ulanowicz79">{{Cite journal |last1=Ulanowicz |first1=R. E. |last2=Kemp |first2=W. Michael |title=Toward canonical trophic aggregations |journal=The American Naturalist |volume=114 |issue=6 |pages=871–883 |year=1979 |doi=10.1086/283534 |jstor=2460557}}</ref>
| |
| | |
| <ref name="urlWelcome to ILTER — ILTER">{{cite web |url=http://www.ilternet.edu/ |title=Welcome to ILTER — ILTER |publisher=International Long Term Ecological Research |accessdate=2010-03-16}}</ref>
| |
| | |
| <ref name="Vandermeer03">{{Cite book |last1=Vandermeer |first1=J. H. |last2=Goldberg |first2=D. E. |title=Population Ecology: First Principles |location=Woodstock, Oxfordshire |publisher=Princeton University Press |year=2003 |isbn=0-691-11440-4}}</ref>
| |
| | |
| <ref name="Vitt97">{{Cite journal |last1=Vitt |first1=L. J. |last2=Caldwell |first2=J. P. |last3=Zani |first3=P. A. |last4=Titus |first4=T. A. |title=The role of habitat shift in the evolution of lizard morphology: Evidence from tropical ''Tropidurus'' |journal=Proceedings of the National Academy of Sciences U.S.A |year=1997 |volume=94 |issue=8 |pages=3828–3832 |doi=10.1073/pnas.94.8.3828 |pmid=9108063 |pmc=20526 |bibcode=1997PNAS...94.3828V}}</ref>
| |
| | |
| <ref name="Wagtendonk07">{{Cite journal |last1=van Wagtendonk |first1=Jan W. |title=History and evolution of wildland fire use |journal=Fire Ecology Special Issue |volume=3 |issue=2 |pages=3–17 |year=2007 |url=http://faculty.fortlewis.edu/KORB_J/global%20fire/wildland_fire_use.pdf |format=PDF }}</ref>
| |
| | |
| <ref name="Waples06">{{Cite journal |last1=Waples |first1=R. S. |last2=Gaggiotti |first2=O. |title=What is a population? An empirical evaluation of some genetic methods for identifying the number of gene pools and their degree of connectivity |journal=Molecular Ecology |volume=15 |issue=6 |pages=1419–1439 |year=2006 |doi=10.1111/j.1365-294X.2006.02890.x |pmid=16629801 }}</ref>
| |
| | |
| <ref name="Webb10">{{Cite journal |last1=Webb |first1=J. K. |last2=Pike |first2=D. A. |last3=Shine |first3=R. |title=Olfactory recognition of predators by nocturnal lizards: safety outweighs thermal benefits |journal=Behavioural Ecology |volume=21 |issue=1 |pages=72–77 |year=2010 |doi=10.1093/beheco/arp152 }}</ref>
| |
| | |
| <ref name="Whittaker73">{{Cite journal |last1=Whittaker |first1=R. H. |last2=Levin |first2=S. A. |last3=Root |first3=R. B. |title=Niche, habitat, and ecotope |journal=The American Naturalist |volume=107 |issue=955 |year=1973 |pages=321–338 |url=http://labs.bio.unc.edu/Peet/courses/bio669/papers/Ch1_supp_readings/Whittaker1973.pdf |doi=10.1086/282837}}</ref>
| |
| | |
| <ref name="Wiens04">{{Cite journal |last1=Wiens |first1=J. J. |last2=Donoghue |first2=M. J. |title=Historical biogeography, ecology and species richness |journal=Trends in Ecology and Evolution |volume=19 |issue=12 |pages=639–644 |year=2004 |url=http://www.phylodiversity.net/donoghue/publications/MJD_papers/2004/144_Wiens_TREE04.pdf |doi=10.1016/j.tree.2004.09.011 |pmid=16701326 }}</ref>
| |
| | |
| <ref name="Wiens05">{{Cite journal |last1=Wiens |first1=J. J. |last2=Graham |first2=C. H. |title=Niche conservatism: Integrating evolution, ecology, and conservation biology |journal=Annual Review of Ecology, Evolution, and Systematics |volume=36 |pages=519–539 |year=2005 |url=http://163.238.8.180/~fburbrink/Courses/Seminar%20in%20Systematics/Wiens_Graha_m_AnnRev2005.pdf |doi=10.1146/annurev.ecolsys.36.102803.095431 }}</ref>
| |
| | |
| <ref name="Wilbur97">{{Cite journal |last1=Wilbur |first1=H. W. |title=Experimental ecology of food webs: Complex systems in temporary ponds |journal=Ecology |volume=78 |issue=8 |pages=2279–2302 |year=1997 |doi=10.1890/0012-9658(1997)078[2279:EEOFWC]2.0.CO;2 |url=http://www.esa.org/history/papers/Wilbur_HM_MA.pdf |format=PDF |issn=0012-9658}}</ref>
| |
| | |
| <ref name="Wilcove08">{{Cite journal |last1=Wilcove |first1=D. S. |last2=Wikelski |first2=M. |title=Going, going, gone: Is animal migration disappearing |journal=PLoS Biology |volume=6 |issue=7 |pages=e188 |year=2008 |doi=10.1371/journal.pbio.0060188 |pmid=18666834 |pmc=2486312 }}</ref>
| |
| | |
| <ref name="Wilkinson09">{{Cite journal |last1=Wilkinson |first1=M. T. |last2=Richards |first2=P. J. |last3=Humphreys |first3=G. S. |title=Breaking ground: Pedological, geological, and ecological implications of soil bioturbation |journal=Earth-Science Reviews |volume=97 |issue=1–4 |pages=257–272 |year=2009 |url=https://www.uky.edu/AS/Geography/People/Faculty/Wilkinson/Wilkinson.ESR.pdf |doi=10.1016/j.earscirev.2009.09.005 | format=PDF}}</ref>
| |
| | |
| <ref name="Wilson00">{{Cite book |last1=Wilson |first1=E. O. |title=Sociobiology: The New Synthesis |publisher=President and Fellows of Harvard College |year=2000 |url=http://books.google.com/books?id=v7lV9tz8fXAC |edition=25th anniversary |isbn=978-0-674-00089-6}}</ref>
| |
| | |
| <ref name="Wills01">{{Cite book |last1=Wills |first1=C. |last2=Bada |first2=J. |title=The Spark of Life: Darwin and the Primeval Soup |publisher=Perseus Publishing |location=Cambridge, MA |year=2001 |url=http://books.google.com/books?id=UrGqxy0wMdkC |isbn=978-0-7382-0493-2}}</ref>
| |
| | |
| <ref name="Wilson88">{{Cite journal |last1=Wilson |first1=D. S. |title=Holism and reductionism in evolutionary ecology |journal=Oikos |volume=53 |issue=2 |pages=269–273 |year=1988 |doi=10.2307/3566073 |jstor=3566073}}</ref>
| |
| | |
| <ref name="Wilson00">{{Cite book |last1=Wilson |first1=Edward, O. |title=Sociobiology: The New Synthesis |edition=25th Annotated |publisher=Belknap Press |location=United States |year=2000 |isbn=0-674-00089-7}}</ref>
| |
| | |
| <ref name="Wilson00b">{{Cite journal |last1=Wilson |first1=E. O. |title=A global biodiversity map |pmid=11041790 |journal=Science |volume=289 |issue=5488 |page=2279 |doi=10.1126/science.289.5488.2279 |year=2000 |doi_inactivedate=2014-02-02 }}</ref>
| |
| | |
| <ref name="Wilson07">{{Cite journal |last1=Wilson |first1=D. S. |last2=Wilson |first2=E. O. |title=Rethinking the theoretical foundation of sociobiology |journal=The Quarterly Review of Biology |volume=82 |issue=4 |pages=327–348 |year=2007 |doi=10.1086/522809 |pmid=18217526 }}</ref>
| |
| | |
| <ref name="Wolf96">{{Cite journal |last1=Wolf |first1=B. O. |last2=Walsberg |first2=G. E. |title=Thermal effects of radiation and wind on a small bird and implications for microsite selection |journal=Ecology |volume=77 |issue=7 |pages=2228–2236 |year=2006 |doi=10.2307/2265716 |jstor=2265716}}</ref>
| |
| | |
| <ref name="Worm03">{{Cite journal |last1=Worm |first1=B. |last2=Duffy |first2=J. E. |title=Biodiversity, productivity and stability in real food webs |year=2003 |journal=Trends in Ecology and Evolution |volume=18 |issue=12 |pages=628–632 |doi=10.1016/j.tree.2003.09.003 }}</ref>
| |
| | |
| <ref name="Write06">{{Cite journal |last1=Wright |first1=J. P. |last2=Jones |first2=C.G. |title=The concept of organisms as ecosystem engineers ten years on: Progress, limitations, and challenges |journal=BioScience |volume=56 |issue=3 |pages=203–209 |year=2006 |doi=10.1641/0006-3568(2006)056[0203:TCOOAE]2.0.CO;2 |issn=0006-3568}}</ref>
| |
| | |
| <ref name="Young74">{{Cite journal |last1=Young |first1=G. L. |year=1974 |title=Human ecology as an interdisciplinary concept: A critical inquiry |journal=Advances in Ecological Research |volume=8 |pages=1–105 |url=http://www.sciencedirect.com/science/article/pii/S0065250408602779 |doi=10.1016/S0065-2504(08)60277-9 |series=Advances in Ecological Research |isbn=978-0-12-013908-8}}</ref>
| |
| | |
| <ref name="Zhuan07">{{Cite journal |last1=Zhuan |first1=Q. |last2=Melillo |first2=J. M. |last3=McGuire |first3=A. D. |last4=Kicklighter |first4=D. W. |last5=Prinn |first5=R. G. |last6=Steudler |first6=P. A. |last7=Felzer |first7=B. S. |last8=Hu |first8=S. |title=Net emission of CH<sub>4</sub> and CO<sub>2</sub> in Alaska: Implications for the region's greenhouse gas budget |journal=Ecological Applications |volume=17 |issue=1 |pages=203–212 |year=2007 |url=http://picea.sel.uaf.edu/manuscripts/zhuang07-ea.pdf |doi=10.1890/1051-0761(2007)017[0203:NEOCAC]2.0.CO;2 |pmid=17479846 |issn=1051-0761}}</ref>
| |
| | |
| <ref name="Zimmermann02">{{Cite journal |last1=Zimmermann |first1=U. |last2=Schneider |first2=H. |last3=Wegner |first3=L. H. |last4=Wagner |first4=M. |last5=Szimtenings |first5=A. |last6=Haase |first6=F. |last7=Bentrup |first7=F. W. |title=What are the driving forces for water lifting in the xylem conduit? |journal=Physiologia Plantarum |volume=114 |issue=3 |pages=327–335 |year=2002 |pmid=12060254 |doi=10.1034/j.1399-3054.2002.1140301.x }}</ref>
| |
| | |
| <ref name=Carson>{{Cite web |url=http://core.ecu.edu/soci/juskaa/SOCI3222/carson.html |title= "Silent Spring" (excerpt) |author=Rachel Carson |publisher= Houghton Miffin |year=1962 |accessdate=4 October 2012}}</ref>
| |
| | |
| }}
| |
| | |
| ==External links==
| |
| {{Sister project links |wikt=ecology|commons=Category:Ecology|b=ecology|n=no|q=ecology|s=no|v=Topic:Ecology|species=no}}
| |
| *[http://plato.stanford.edu/entries/ecology/ Ecology (Stanford Encyclopedia of Philosophy)]
| |
| *[http://www.nature.com/scitable/knowledge/ecology-102 The Nature Education Knowledge Project: Ecology]
| |
| *[http://ekolojinet.com/journals.html Ecology Journals List of ecological scientific journals]
| |
| *[http://ecologydictionary.org/ Ecology Dictionary - Explanation of Ecological Terms]
| |
| *[http://www.gereon.es/theory/ecology/ Basic Terms of Ecology]
| |
| *[http://www.ecoevo.ca/en/index.htm Canadian Society for Ecology and Evolution]
| |
| *[http://www.esa.org/ Ecological Society of America]
| |
| *[http://ecology.com/ Ecology Global Network]
| |
| *[http://www.ecolsoc.org.au/ Ecological Society of Australia]
| |
| *[http://www.britishecologicalsociety.org/ British Ecological Society]
| |
| *[http://english.rcees.cas.cn/sp/zgstxxh/ Ecological Society of China]
| |
| *[http://www.isecoeco.org/ International Society for Ecological Economics]
| |
| *[http://www.europeanecology.org/ European Ecological Federation]
| |
| *[http://www.maweb.org/en/index.aspx UN Millennium Ecosystem Assessment]
| |
| *[http://www.eoearth.org/topics/view/49660/ The Encyclopedia of Earth{{spaced ndash}}Wilderness: Biology & Ecology]
| |
| *[http://www.ecologyandsociety.org/ Ecology and Society - A journal of integrative science for resilience and sustainability]
| |
| *[http://scienceaid.co.uk/biology/ecology/index.html Science Aid: Ecology, U.K. High School (GCSE, Alevel) Ecology]
| |
| | |
| {{Nature nav}}
| |
| {{Biology nav}}
| |
| {{Physical Earth}}
| |
| {{Portal bar|Environment|Ecology}}
| |
| | |
| {{Use dmy dates|date=December 2010}}
| |
| | |
| {{Good article}}
| |
| | |
| [[Category:Ecology| ]]
| |
| [[Category:Biogeochemistry]]
| |