|Ecology addresses the full scale of life, from tiny bacteria to processes that span the entire planet. Ecologists study many diverse and complex relations among species, such as predation and pollination. The diversity of life is organized into different habitats, from terrestrial (middle) to aquatic ecosystems.|
Ecology (from Greek: οἶκος, "house", or "environment"; -λογία, "study of")[A] is the scientific analysis and study of interactions among organisms and their environment. It is an interdisciplinary field that includes biology, geography, and Earth science. Ecology includes the study of interactions that organisms have with each other, other organisms, and with abiotic components of their environment. Topics of interest to ecologists include the diversity, distribution, amount (biomass), and number (population) of particular organisms, as well as cooperation and competition between organisms, both within and among ecosystems. Ecosystems are composed of dynamically interacting parts including organisms, the 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, genes, and ecosystems, enhances certain ecosystem services.
Ecology is not synonymous with environment, environmentalism, natural history, or environmental science. It is closely related to evolutionary biology, genetics, and ethology. An important focus for ecologists is to improve the understanding of how biodiversity affects ecological function. Ecologists seek to explain:
- Life processes, interactions, and adaptations
- The movement of materials and energy through living communities
- The successional development of ecosystems
- The abundance and distribution of organisms and biodiversity in the context of the environment.
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, economics, basic and applied science, and human social interaction (human ecology). For example, the Circles of Sustainability approach treats ecology as more than the environment 'out there'. It is not treated as separate from humans. Organisms (including humans) and resources compose ecosystems which, in turn, maintain biophysical feedback mechanisms that moderate processes acting on living (biotic) and non-living (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.
The word "ecology" ("Ökologie") was coined in 1866 by the German scientist Ernst Haeckel (1834–1919). Ecological thought is derivative of established currents in philosophy, particularly from ethics and politics. Ancient Greek philosophers such as Hippocrates and Aristotle laid the foundations of ecology in their studies on natural history. Modern ecology became a much more rigorous science in the late 19th century. Evolutionary concepts relating to adaptation and natural selection became the cornerstones of modern ecological theory.
- 1 Levels, scope, and scale of organization
- 2 Ecological complexity
- 3 Relation to evolution
- 4 Human ecology
- 5 Relation to the environment
- 6 History
- 7 See also
- 8 Notes
- 9 References
- 10 External links
Levels, scope, and scale of organization
The scope of ecology contains a wide array of interacting levels of organization spanning micro-level (e.g., cells) to a planetary scale (e.g., biosphere) phenomena. Ecosystems, for example, contain abiotic resources and interacting life forms (i.e., individual organisms that aggregate into populations 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 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. Several generations of an aphid population can exist over the lifespan of a single leaf. Each of those aphids, in turn, support diverse bacterial communities. 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. 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.
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 nested hierarchy, ranging in scale from genes, to cells, to tissues, to organs, to organisms, to species, to populations, to communities, to ecosystems, to biomes, and up to the level of the biosphere. This framework forms a panarchy 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 fixers, can lead to disproportionate, perhaps irreversible, changes in the system properties.":14
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. 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. Biodiversity plays an important role in ecosystem services which by definition maintain and improve human quality of life. Preventing 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. 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 and species migration (e.g., riverine fish runs and avian insect control) has been implicated as one mechanism by which those service losses are experienced. 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.
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. 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.":745 For example, a habitat might be an aquatic or terrestrial environment that can be further categorized as a montane or 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.
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.
Definitions of the niche date back to 1917, but G. Evelyn Hutchinson made conceptual advances in 1957 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.":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. The Hutchinsonian niche is defined more technically as a "Euclidean 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.":71
Biogeographical patterns and range distributions are explained or predicted through knowledge of a species' traits and niche requirements. Species have functional traits that are uniquely adapted to the ecological niche. A trait is a measurable property, phenotype, or characteristic of an organism that may influence its survival. Genes play an important role in the interplay of development and environmental expression of traits. 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 out-compete the other. When similarly adapted species overlap geographically, closer inspection reveals subtle ecological differences in their habitat or dietary requirements. Some models and empirical studies, however, suggest that disturbances can stabilize the co-evolution and shared niche occupancy of similar species inhabiting species-rich communities. 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.
Organisms are subject to environmental pressures, but they also modify their habitats. The 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. The process and concept of ecosystem engineering is related to niche construction, but the former relates only to the physical modifications of the habitat whereas the latter also considers the evolutionary implications of physical changes to the environment and the feedback this causes on the process of natural selection. 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.":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. 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.
Biomes are larger units of organization that categorize regions of the Earth's ecosystems, mainly according to the structure and composition of vegetation. 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. Other researchers have recently categorized other biomes, such as the human and oceanic microbiomes. To a microbe, the human body is a habitat and a landscape. 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.
The largest scale of ecological organization is the biosphere: the total sum of ecosystems on the planet. Ecological relationships 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 CO2 and O2 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. 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. 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.
Understanding traits of individual organisms helps explain patterns and processes at other levels of organization including populations, communities, and ecosystems. Several areas of ecology of evolution that focus on such traits are life history theory, ecophysiology, metabolic theory of ecology, and Ethology. Examples of such traits include features of an organisms life cycle such as age to maturity, life span, or metabolic costs of reproduction. Other traits may be related to structure, such as the spines of a cactus or dorsal spines of a bluegill sunfish, or behaviors such as courtship displays or pair bonding. Other traits include emergent properties that are the result at least in part of interactions with the surrounding environment such as growth rate, resource uptake rate, winter, and deciduous vs. drought deciduous trees and shrubs.
One set of characteristics relate to body size and temperature. The metabolic theory of ecology provides a predictive qualitative set of relationships between an organism’s body size and temperature and metabolic processes. In general, smaller, warmer organisms have higher metabolic rates and this results in a variety of predictions regarding individual somatic growth rates, reproduction and population growth rates, population size, and resource uptake rates.
The traits of organisms are subject to change through acclimation, development, and evolution. For this reason, individuals form a shared focus for ecology and for evolutionary ecology.
Population ecology studies the dynamics of species populations and how these populations interact with the wider environment. A population consists of individuals of the same species that live, interact, and migrate through the same niche and habitat.
A primary law of population ecology is the Malthusian growth model which states, "a population will grow (or decline) exponentially as long as the environment experienced by all individuals in the population remains constant.":18 Simplified population 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:
Using these modelling techniques, Malthus' population principle of growth was later transformed into a model known as the logistic equation:
where N is the number of individuals measured as 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 life history, fecundity, and survivorship, and these are analysed using mathematical techniques such as matrix algebra. The information is used for managing wildlife stocks and setting harvest quotas. In cases where basic models are insufficient, ecologists may adopt different kinds of statistical methods, such as the Akaike information criterion, or use models that can become mathematically complex as "several competing hypotheses are simultaneously confronted with the data."
Metapopulations and migration
The concept of metapopulations was defined in 1969 as "a population of populations which go extinct locally and recolonize".:105 Metapopulation ecology is another statistical approach that is often used in conservation research. Metapopulation models simplify the landscape into patches of varying levels of quality, 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. 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.
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 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 studies to explain metapopulation structure.
Community ecology is the study of the interactions among a collections of species that inhabit the same geographic area. Community ecologists study the determinants of patterns and processes for two or more interacting species. Research in community ecology might measure species diversity in grasslands in relation to soil fertility. It might also include the analysis of predator-prey dynamics, competition among similar plant species, or mutualistic interactions between crabs and corals.
Ecosystems may be habitats within biomes that form an integrated whole and a dynamically responsive system having both physical and biological complexes. Ecosystem ecology is the science of determining the fluxes of materials (e.g. carbon, phosphorus) between different pools (e.g., tree biomass, soil organic material). Ecosystem ecologist attempt to determine the underlying causes of these fluxes. Research in ecosystem ecology might measure primary production (g C/m^2) in a wetland in relation to decomposition and consumption rates (g C/m^2/y). This requires an understanding of the community connections between plants (i.e., primary producers) and the decomposers (e.g., fungi and bacteria),
The underlying concept of ecosystem can be traced back to 1864 in the published work of George Perkins Marsh ("Man and Nature"). Within an ecosystem, organisms are linked to the physical and biological components of their environment to which they are adapted. Ecosystems are complex adaptive systems where the interaction of life processes form self-organizing patterns across different scales of time and space. Ecosystems are broadly categorized as terrestrial, freshwater, atmospheric, or 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.
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.
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 studies are extrapolated to larger systems. 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. Despite these limitations, food webs remain a valuable tool in understanding community ecosystems.
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., primary predators). Theoretical and empirical studies identify non-random emergent patterns of few strong and many weak linkages that explain how ecological communities remain stable over time. 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. Step by step lines or relations are drawn until a web of life is illustrated.
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.":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 abundance or biomass at each level. When the relative abundance or biomass of each species is sorted into its respective trophic level, they naturally sort into a 'pyramid of numbers'.
Species are broadly categorized as autotrophs (or primary producers), heterotrophs (or consumers), and Detritivores (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). Heterotrophs can be further sub-divided into different functional groups, including primary consumers (strict herbivores), secondary consumers (carnivorous predators that feed exclusively on herbivores), and tertiary consumers (predators that feed on a mix of herbivores and predators). 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.
Trophic levels are part of the holistic or complex systems view of ecosystems. Each trophic level contains unrelated species that are grouped together because they share common ecological functions, giving a macroscopic view of the system. 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.":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.":612
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.
Sea otters (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. Hunting of sea otters, for example, is thought to have led indirectly to the extinction of the Steller's sea cow (Hydrodamalis gigas). While the keystone species concept has been used extensively as a 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.
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.":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'.[E]
"Complexity in ecology is of at least six distinct types: spatial, temporal, structural, process, behavioral, and geometric.":3 From these principles, ecologists have identified emergent and 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. Ecological complexity relates to the dynamic resilience of ecosystems that transition to multiple shifting steady-states directed by random fluctuations of history. 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). The longest experiment in existence is the Park Grass Experiment, which was initiated in 1856. Another example is the Hubbard Brook study, which has been in operation since 1960.
Holism remains a critical part of the theoretical foundation in contemporary ecological studies. Holism addresses the biological organization of life that self-organizes into layers of emergent whole systems that function according to non-reducible 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. "New properties emerge because the components interact, not because the basic nature of the components is changed.":8
Ecological studies are necessarily holistic as opposed to reductionistic. 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 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.
Relation to evolution
Ecology and evolutionary biology are considered sister disciplines of the life sciences. Natural selection, life history, development, adaptation, populations, and 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 system of taxonomy. The two disciplines often appear together, such as in the title of the journal Trends in Ecology and Evolution. 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. While the boundary between ecology and evolution is not always clear, ecologists study the abiotic and biotic factors that influence evolutionary processes, and evolution can be rapid, occurring on ecological timescales as short as one generation.
All organisms can exhibit behaviours. Even plants express complex behaviour, including memory and communication. 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.
Adaptation is the central unifying concept in behavioural ecology. 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.
Predator-prey interactions are an introductory concept into food-web studies as well as behavioural ecology. 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. 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" or "[t]he optimal 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."
Elaborate sexual 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.
Cognitive ecology integrates theory and observations from evolutionary ecology and neurobiology, primarily cognitive science, in order to understand the effect that animal interaction with their habitat has on their cognitive systems and how those systems restrict behavior within an ecological and evolutionary framework. "Until recently, however, cognitive scientists have not paid sufficient attention to the fundamental fact that cognitive traits evolved under particular natural settings. With consideration of the selection pressure on cognition, cognitive ecology can contribute intellectual coherence to the multidisciplinary study of cognition." As a study involving the 'coupling' or interactions between organism and environment, cognitive ecology is closely related to enactivism, a field based upon the view that "...we must see the organism and environment as bound together in reciprocal specification and selection...".
Social ecological behaviours are notable in the social insects, slime moulds, social spiders, human society, and naked mole-rats where eusocialism has evolved. Social behaviours include reciprocally beneficial behaviours among kin and nest mates 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 ants, bees, and wasps 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. In contrast, group selectionists 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.
Ecological interactions can be classified broadly into a host and an associate relationship. A host is any entity that harbours another that is called the associate. Relationships 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, lichens with fungi and photosynthetic algae, and corals with photosynthetic algae. 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 mineral nutrients.
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. 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 propagules, denying the services of a beneficial partner), their net effect on host fitness is not necessarily negative and, thus, becomes difficult to forecast. Co-evolution 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 defense systems of its host that drives the evolution of sexual reproduction to diversify the genetic constituency of populations responding to the antagonistic pressure.
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. The Journal of Biogeography was established in 1974. Biogeography and ecology share many of their disciplinary roots. For example, the theory of island biogeography, published by the mathematician Robert MacArthur and ecologist Edward O. Wilson in 1967 is considered one of the fundamentals of ecological theory.
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. Biogeographical patterns result from ecological processes that influence range distributions, such as migration and dispersal. 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 vicariance biogeography and it is a sub-discipline of biogeography. 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.
r/K selection theory
A population ecology concept is r/K selection theory,[D] one of the first predictive models in ecology used to explain life-history evolution. The premise behind the r/K selection model is that natural selection pressures change according to 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.
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. 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 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.
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 (PCR). The rise of molecular technologies and influx of research questions into this new ecological field resulted in the publication Molecular Ecology in 1992. 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. 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. For example, molecular ecology revealed promiscuous sexual behaviour and multiple male partners in tree swallows previously thought to be socially monogamous. In a biogeographical context, the marriage between genetics, ecology, and evolution resulted in a new sub-discipline called phylogeography.
Ecology is as much a biological science as it is a human science. Human ecology is an interdisciplinary investigation into the ecology of our species. "Human ecology may be defined: (1) from a bioecological standpoint as the study of man as the ecological dominant in plant and animal communities and systems; (2) from a bioecological 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.":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.
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. 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-natural capital, which provides the means to put a value on the stock and use of information and materials stemming from 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.
Restoration and management
Ecology is an employed science of restoration, repairing disturbed sites through human intervention, in natural resource management, and in environmental impact assessments. Edward O. Wilson predicted in 1992 that the 21st century "will be the era of restoration in ecology". Ecological science has boomed in the industrial investment of restoring ecosystems and their processes in abandoned sites after disturbance. Natural resource managers, in forestry, for example, employ ecologists to develop, adapt, and implement 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.
Relation to the 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. 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.":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 (conspecifics) and other species that share a habitat.
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 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.
Disturbance and resilience
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. Disturbances occur over vastly different ranges in terms of magnitudes as well as distances and time periods, 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. Ecological resilience is a cornerstone theory in ecosystem management. Biodiversity fuels the resilience of ecosystems acting as a kind of regenerative insurance.
Metabolism and the early atmosphere
The Earth was formed approximately 4.5 billion years ago. 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 reducing and oxidizing gasses that set the stage for primitive ecosystems to evolve and, in turn, the atmosphere also evolved.
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. The evolution of the earliest organisms, likely anaerobic methanogen microbes, started the process by converting atmospheric hydrogen into methane (4H2 + CO2 → CH4 + 2H2O). Anoxygenic photosynthesis reduced hydrogen concentrations and increased atmospheric methane, by converting hydrogen sulfide into water or other sulfur compounds (for example, 2H2S + CO2 + hv → CH2O + H2O + 2S). Early forms of fermentation also increased levels of atmospheric methane. The transition to an oxygen-dominant atmosphere (the 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.
Radiation: heat, temperature and light
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 metabolic energy.
There is a relationship between light, primary production, and ecological energy budgets. Sunlight is the primary input of energy into the planet's ecosystems. Light is composed of electromagnetic energy of different wavelengths. 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. 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 H2S are autotrophs. Autotrophs — responsible for primary production — assimilate light energy which becomes metabolically stored as potential energy in the form of biochemical enthalpic bonds.
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 hypoxic (an environment with O2 concentration below 2 mg/liter) and eventually completely anoxic where anaerobic bacteria thrive among the roots. Water also influences the intensity and spectral composition of light as it reflects off the water surface and submerged particles. 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, CO2 and O2) used in respiration and photosynthesis. Salt water plants (halophytes) have additional specialized adaptations, such as the development of special organs for shedding salt and osmoregulating their internal salt (NaCl) concentrations, to live in estuarine, brackish, or oceanic environments. Anaerobic soil microorganisms in aquatic environments use nitrate, manganese ions, 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 oxidation-reduction potentials of the water. Carbon dioxide, for example, is reduced to methane (CH4) by methanogenic bacteria. The physiology of fish is also specially adapted to compensate for environmental salt levels through osmoregulation. Their gills form electrochemical gradients that mediate salt excretion in salt water and uptake in fresh water.
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. 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. The 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).
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. For example, oxygen levels decrease with decreasing pressure and are a limiting factor for life at higher altitudes. Water transportation by plants is another important ecophysiological process affected by osmotic pressure gradients. Water pressure in the depths of oceans requires that organisms adapt to these conditions. For example, diving animals such as whales, dolphins, and seals are specially adapted to deal with changes in sound due to water pressure differences. Differences between hagfish species provide another example of adaptation to deep-sea pressure through specialized protein adaptations.
Wind and turbulence
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. 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. Wind speed and turbulence also influence evapotranspiration rates and energy budgets in plants and animals. 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.[clarification needed] 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.
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. Fire releases CO2 and converts fuel into ash and tar. Fire is a significant ecological parameter that raises many issues pertaining to its control and suppression. While the issue of fire in relation to ecology and plants has been recognized for a long time, Charles Cooper brought attention to the issue of forest fires in relation to the ecology of forest fire suppression and management in the 1960s.
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. Fire creates a heterogeneous ecosystem age and canopy structure, and the altered soil nutrient supply and cleared canopy structure opens new ecological niches for seedling establishment. 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 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. Fire plays a major role in the persistence and resilience of ecosystems.
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 detritivores that regulate soil formation. 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. Paleoecological studies of soils places the origin for bioturbation to a time before the Cambrian period. Other events, such as the evolution of trees and the colonization of land in the Devonian period played a significant role in the early development of ecological trophism in soils.
Biogeochemistry and climate
Ecologists study and measure nutrient budgets to understand how these materials are regulated, flow, and recycled through the environment. 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 cycles of the Earth. Understanding the relations and cycles mediated between these elements and their ecological pathways has significant bearing toward understanding global biogeochemistry.
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. 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 CO2 (carbon dioxide) concentrations to levels as high as 3500 ppm.
In the Oligocene, from twenty-five to thirty-two million years ago, there was another significant restructuring of the global carbon cycle as grasses evolved a new mechanism of photosynthesis, C4 photosynthesis, and expanded their ranges. This new pathway evolved in response to the drop in atmospheric CO2 concentrations below 550 ppm. 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 (CH4) 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 CO2 on a 100-year time scale. Hence, there is a relationship between global warming, decomposition and respiration in soils and wetlands producing significant climate feedbacks and globally altered biogeochemical cycles.
Ecology has a complex origin, due in large part to its interdisciplinary nature. 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 idealized type. This contrasts against the modern understanding of 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. 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 in his observation of "natural dentistry". Basking Nile crocodiles, he noted, would open their mouths to give sandpipers safe access to pluck leeches out, giving nutrition to the sandpiper and oral hygiene for the crocodile. 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.
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 (1688?–1732). 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 gradients, such as a 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. Natural historians, such as Humboldt, James Hutton, and Jean-Baptiste Lamarck (among others) laid the foundations of the modern ecological sciences. The term "ecology" (German: 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.
Opinions differ on who was the founder of modern ecological theory. Some mark Haeckel's definition as the beginning; others say it was Eugenius Warming with the writing of Oecology of Plants: An Introduction to the Study of Plant Communities (1895), or Carl Linnaeus' principles on the economy of nature that matured in the early 18th century. Linnaeus founded an early branch of ecology that he called the economy of nature. His works influenced Charles Darwin, who adopted Linnaeus' phrase on the economy or polity of nature in The Origin of Species. 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.
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. 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. While Charles Darwin is mainly noted for his treatise on evolution, he was one of the founders of soil ecology, and he made note of the first ecological experiment in The Origin of Species. Evolutionary theory changed the way that researchers approached the ecological sciences.
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.
In the early 20th century, ecology transitioned from a more descriptive form of natural history to a more analytical form of scientific natural history. Frederic Clements published the first American ecology book in 1905, 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, 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.
The Clementsian superorganism theory was an overextended application of an idealistic form of holism. 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.[C] Around the same time, Charles Elton pioneered the concept of food chains in his classical book Animal Ecology. Elton 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. 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 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 MacArthur advanced mathematical theory, predictions, and tests in ecology in the 1950s, which inspired a resurgent school of theoretical mathematical ecologists. Ecology also has developed through contributions from other nations, including Russia's Vladimir Vernadsky and his founding of the biosphere concept in the 1920s and Japan's Kinji Imanishi and his concepts of harmony in nature and habitat segregation in the 1950s. Scientific recognition of contributions to ecology from non-English-speaking cultures is hampered by language and translation barriers.
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. The historical emphasis and poetic naturalistic writings advocating the protection of wild places by notable ecologists in the history of conservation biology, such as Aldo Leopold and Arthur Tansley, have been seen as far removed from urban centres where, it is claimed, the concentration of pollution and environmental degradation is located. Palamar (2008) notes an overshadowing by mainstream environmentalism of pioneering women in the early 1900s who fought for urban health ecology (then called euthenics) 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, 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.
- Chemical ecology
- Circles of Sustainability
- Cultural ecology
- Dialectical naturalism
- Earth science
- Ecological death
- Ecological psychology
- Ecology movement
- Industrial ecology
- Information ecology
- Landscape ecology
- Natural resource
- Normative science
- Political ecology
- Restoration ecology
- Sensory ecology
- Spiritual ecology
- Sustainable development
- ^ In Ernst Haeckel's (1866) footnote where the term ecology originates, he also gives attribute to Ancient Greek: χώρας khōrā "χωρα", meaning "dwelling place, distributional area" - quoted from Stauffer (1957).
- ^ 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).
- ^ Foster & Clark (2008) note how Smut's holism contrasts starkly against his racial political views as the father of apartheid.
- ^ First introduced in MacArthur & Wilson's (1967) book of notable mention in the history and theoretical science of ecology, The Theory of Island Biogeography.
- ^ Aristotle wrote about this concept in Metaphysics (Quoted from 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."
- Eric Laferrière; Peter J. Stoett (2 September 2003). International Relations Theory and Ecological Thought: Towards a Synthesis. Routledge. pp. 25–. ISBN 978-1-134-71068-3.
- Stadler, B.; Michalzik, B.; Müller, T. (1998). "Linking aphid ecology with nutrient fluxes in a coniferous forest". Ecology. 79 (5): 1514–1525. ISSN 0012-9658. doi:10.1890/0012-9658(1998)079[1514:LAEWNF]2.0.CO;2.
- Humphreys, N. J.; Douglas, A. E. (1997). "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". Applied and Environmental Microbiology. 63 (8): 3294–3296. PMC . PMID 16535678.
- Liere, Heidi; Jackson, Doug; Vandermeer, John; Wilby, Andrew (20 September 2012). "Ecological Complexity in a Coffee Agroecosystem: Spatial Heterogeneity, Population Persistence and Biological Control". PLoS ONE. 7 (9): e45508. Bibcode:2012PLoSO...745508L. PMC . PMID 23029061. doi:10.1371/journal.pone.0045508.
- Odum, E. P.; Barrett, G. W. (2005). Fundamentals of Ecology. Brooks Cole. p. 598. ISBN 978-0-534-42066-6.
- O'Neill, D. L.; Deangelis, D. L.; Waide, J. B.; Allen, T. F. H. (1986). A Hierarchical Concept of Ecosystems. Princeton University Press. p. 253. ISBN 0-691-08436-X.
- Nachtomy, Ohad; Shavit, Ayelet; Smith, Justin (2002). "Leibnizian organisms, nested individuals, and units of selection". Theory in Biosciences. 121 (2): 205–230. doi:10.1007/s12064-002-0020-9.
- Holling, C. S. (2004). "Understanding the complexity of economic, ecological, and social systems". Ecosystems. 4 (5): 390–405. doi:10.1007/s10021-001-0101-5.
- Levin, S. A. (1999). Fragile Dominion: Complexity and the Commons. Reading, MA: Perseus Books. ISBN 978-0-7382-0319-5.
- Noss, R. F.; Carpenter, A. Y. (1994). Saving Nature's Legacy: Protecting and Restoring Biodiversity. Island Press. p. 443. ISBN 978-1-55963-248-5.
- Noss, R. F. (1990). "Indicators for monitoring biodiversity: A hierarchical approach". Conservation Biology. 4 (4): 355–364. JSTOR 2385928. doi:10.1111/j.1523-1739.1990.tb00309.x.
- Scholes, R. J.; Mace, G. M.; Turner, W.; Geller, G. N.; Jürgens, N.; Larigauderie, A.; Muchoney, D.; Walther, B. A.; Mooney, H. A. (2008). "Toward a global biodiversity observing system" (PDF). Science. 321 (5892): 1044–1045. PMID 18719268. doi:10.1126/science.1162055. Archived from the original (PDF) on 10 July 2011.
- Cardinale, Bradley J.; 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; 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 (6 June 2012). "Biodiversity loss and its impact on humanity". Nature. 486 (7401): 59–67. Bibcode:2012Natur.486...59C. PMID 22678280. doi:10.1038/nature11148.
- Wilson, E. O. (2000). "A global biodiversity map". Science. 289 (5488): 2279. PMID 11041790.
- Purvis, A.; Hector, A. (2000). "Getting the measure of biodiversity" (PDF). Nature. 405 (6783): 212–218. PMID 10821281. doi:10.1038/35012221. Archived from the original (PDF) on 28 April 2014.
- Ostfeld, R. S. (2009). "Biodiversity loss and the rise of zoonotic pathogens" (PDF). Clinical Microbiology and Infection. 15 (s1): 40–43. PMID 19220353. doi:10.1111/j.1469-0691.2008.02691.x.
- Tierney, Geraldine L.; Faber-Langendoen, Don; Mitchell, Brian R.; Shriver, W. Gregory; Gibbs, James P. (2009). "Monitoring and evaluating the ecological integrity of forest ecosystems" (PDF). Frontiers in Ecology and the Environment. 7 (6): 308–316. doi:10.1890/070176.
- Ceballos, G.; Ehrlich, P. R. (2002). "Mammal population losses and the extinction crisis" (PDF). Science. 296 (5569): 904–907. Bibcode:2002Sci...296..904C. PMID 11988573. doi:10.1126/science.1069349. Archived from the original (PDF) on 20 July 2011. Retrieved 2010-03-16.
- Palumbi, Stephen R.; Sandifer, Paul A.; Allan, J. David; Beck, Michael W.; Fautin, Daphne G.; Fogarty, Michael J.; Halpern, Benjamin S.; Incze, Lewis S.; Leong, Jo-Ann; et al. (2009). "Managing for ocean biodiversity to sustain marine ecosystem services" (PDF). Frontiers in Ecology and the Environment. 7 (4): 204–211. doi:10.1890/070135. Archived from the original (PDF) on 11 June 2010.
- Wilcove, D. S.; Wikelski, M. (2008). "Going, going, gone: Is animal migration disappearing". PLoS Biology. 6 (7): e188. PMC . PMID 18666834. doi:10.1371/journal.pbio.0060188.
- Hammond, H. (2009). Maintaining Whole Systems on the Earth's Crown: Ecosystem-based Conservation Planning for the Boreal Forest. Slocan Park, BC: Silva Forest Foundation. p. 380. ISBN 978-0-9734779-0-0.
- Whittaker, R. H.; Levin, S. A.; Root, R. B. (1973). "Niche, habitat, and ecotope" (PDF). The American Naturalist. 107 (955): 321–338. doi:10.1086/282837.
- Beyer, Hawthorne, L.; Haydon, Daniel, T.; Morales, Juan M.; Frair, Jacqueline L.; Hebblewhite, Mark; Mitchell, Michael; Matthiopoulos, Jason (2010). "The interpretation of habitat preference metrics under use–availability designs". Philosophical Transactions of the Royal Society B. 365 (1550): 2245–2254. PMC . PMID 20566501. doi:10.1098/rstb.2010.0083.
- Schoener, T. W. (1975). "Presence and absence of habitat shift in some widespread lizard species". Ecological Monographs. 45 (3): 233–258. JSTOR 1942423. doi:10.2307/1942423.
- Vitt, L. J.; Caldwell, J. P.; Zani, P. A.; Titus, T. A. (1997). "The role of habitat shift in the evolution of lizard morphology: Evidence from tropical Tropidurus". Proceedings of the National Academy of Sciences. 94 (8): 3828–3832. Bibcode:1997PNAS...94.3828V. PMC . PMID 9108063. doi:10.1073/pnas.94.8.3828.
- Kiessling, W.; Simpson, C.; Foote, M. (2009). "Reefs as cradles of evolution and sources of biodiversity in the Phanerozoic". Science. 327 (5962): 196–198. Bibcode:2010Sci...327..196K. PMID 20056888. doi:10.1126/science.1182241.
- Laland, K. N.; Odling-Smee, F. J.; Feldman, M. W. (1999). "Evolutionary consequences of niche construction and their implications for ecology". Proceedings of the National Academy of Sciences. 96 (18): 10242–10247. Bibcode:1999PNAS...9610242L. PMC . PMID 10468593. doi:10.1073/pnas.96.18.10242.
- Hughes, D. P.; Pierce, N. E.; Boomsma, J. J. (2008). "Social insect symbionts: evolution in homeostatic fortresses" (PDF). Trends in Ecology & Evolution. 23 (12): 672–677. PMID 18951653. doi:10.1016/j.tree.2008.07.011.
- Wiens, J. J.; Graham, C. H. (2005). "Niche conservatism: Integrating evolution, ecology, and conservation biology" (PDF). Annual Review of Ecology, Evolution, and Systematics. 36: 519–539. doi:10.1146/annurev.ecolsys.36.102803.095431. Archived from the original (PDF) on 24 October 2012.
- Hutchinson, G. E. (1957). A Treatise on Limnology. New York, NY: Wiley. p. 1015. ISBN 0-471-42572-9.
- Hutchinson, G. E. (1957). "Concluding remarks" (PDF). Cold Spring Harbor Symposia on Quantitative Biology. 22: 415–427. doi:10.1101/SQB.1957.022.01.039.
- Begon, M.; Townsend, C. R.; Harper, J. L. (2005). Ecology: From Individuals to Ecosystems (4th ed.). Wiley-Blackwell. p. 752. ISBN 1-4051-1117-8.
- D. L., Hardesty (1975). "The niche concept: suggestions for its use in human ecology". Human Ecology. 3 (2): 71–85. JSTOR 4602315. doi:10.1007/BF01552263.
- Pearman, P. B.; Guisan, A.; Broennimann, O.; Randin, C. F. (2008). "Niche dynamics in space and time" (PDF). Trends in Ecology & Evolution. 23 (3): 149–158. PMID 18289716. doi:10.1016/j.tree.2007.11.005.[permanent dead link]
- Levins, R.; Lewontin, R. (1980). "Dialectics and reductionism in ecology" (PDF). Synthese. 43: 47–78. doi:10.1007/bf00413856. Archived from the original (PDF) on 10 May 2013.
- Hardin, G. (1960). "The competitive exclusion principal". Science. 131 (3409): 1292–1297. Bibcode:1960Sci...131.1292H. PMID 14399717. doi:10.1126/science.131.3409.1292.
- Scheffer, M.; van Nes, E. H. (2006). "Self-organized similarity, the evolutionary emergence of groups of similar species" (PDF). Proceedings of the National Academy of Sciences. 103 (16): 6230–6235. Bibcode:2006PNAS..103.6230S. doi:10.1073/pnas.0508024103. Archived from the original (PDF) on 24 July 2011.
- Hastings, Alan; Byers, James E.; Crooks, Jeffrey A.; Cuddington, Kim; Jones, Clive G.; Lambrinos, John G.; Talley, Theresa S.; Wilson, William G. (2007). "Ecosystem engineering in space and time". Ecology Letters. 10 (2): 153–164. PMID 17257103. doi:10.1111/j.1461-0248.2006.00997.x.
- Jones, Clive G.; Lawton, John H.; Shachak, Moshe (1994). "Organisms as ecosystem engineers". Oikos. 69 (3): 373–386. JSTOR 3545850. doi:10.2307/3545850.
- Wright, J. P.; Jones, C.G. (2006). "The concept of organisms as ecosystem engineers ten years on: Progress, limitations, and challenges". BioScience. 56 (3): 203–209. ISSN 0006-3568. doi:10.1641/0006-3568(2006)056[0203:TCOOAE]2.0.CO;2.
- Palmer, M.; White, P. S. (1994). "On the existence of ecological communities" (PDF). Journal of Vegetation Sciences. 5 (2): 279–282. JSTOR 3236162. doi:10.2307/3236162.
- Prentice; I. C.; Harrison, S. P.; Leemans, R.; Monserud, R. A.; Solomon, A. M. (1992). "Special paper: A global biome model based on plant physiology and dominance, soil properties and climate". Journal of Biogeography. 19 (2): 117–134. JSTOR 2845499. doi:10.2307/2845499.
- Turnbaugh, Peter J.; Ley, Ruth E.; Hamady, Micah; Fraser-Liggett, Claire M.; Knight, Rob; Gordon, Jeffrey I. (2007). "The human microbiome project". Nature. 449 (7164): 804–810. Bibcode:2007Natur.449..804T. PMC . PMID 17943116. doi:10.1038/nature06244.
- DeLong, E. F. (2009). "The microbial ocean from genomes to biomes" (PDF). Nature. 459 (7244): 200–206. Bibcode:2009Natur.459..200D. PMID 19444206. doi:10.1038/nature08059.
- Igamberdiev, Abir U.; Lea, P. J. (2006). "Land plants equilibrate O2 and CO2 concentrations in the atmosphere" (PDF). Photosynthesis Research. 87 (2): 177–194. PMID 16432665. doi:10.1007/s11120-005-8388-2.
- Lovelock, J.; Margulis, Lynn (1973). "Atmospheric homeostasis by and for the biosphere: The Gaia hypothesis". Tellus. 26: 2–10. Bibcode:1974Tell...26....2L. doi:10.1111/j.2153-3490.1974.tb01946.x.
- Lovelock, J. (2003). "The living Earth". Nature. 426 (6968): 769–770. Bibcode:2003Natur.426..769L. PMID 14685210. doi:10.1038/426769a.
- Waples, R. S.; Gaggiotti, O. (2006). "What is a population? An empirical evaluation of some genetic methods for identifying the number of gene pools and their degree of connectivity". Molecular Ecology. 15 (6): 1419–1439. PMID 16629801. doi:10.1111/j.1365-294X.2006.02890.x.
- Turchin, P. (2001). "Does population ecology have general laws?". Oikos. 94 (1): 17–26. doi:10.1034/j.1600-0706.2001.11310.x.
- Vandermeer, J. H.; Goldberg, D. E. (2003). Population Ecology: First Principles. Woodstock, Oxfordshire: Princeton University Press. ISBN 0-691-11440-4.
- Berryman, A. A. (1992). "The origins and evolution of predator-prey theory". Ecology. 73 (5): 1530–1535. JSTOR 1940005. doi:10.2307/1940005.
- Anderson, D. R.; Burnham, K. P.; Thompson, W. L. (2000). "Null hypotheses testing: Problems, prevalence, and an alternative" (PDF). J. Wildl. Mngt. 64 (4): 912–923.
- Johnson, J. B.; Omland, K. S. (2004). "Model selection in ecology and evolution" (PDF). Trends in Ecology and Evolution. 19 (2): 101–108. PMID 16701236. doi:10.1016/j.tree.2003.10.013.
- Levins, R. (1969). "Some demographic and genetic consequences of environmental heterogeneity for biological control". Bulletin of the Entomological Society of America. 15: 237–240. ISBN 978-0-231-12680-9.
- Levins, R. (1970). "Extinction". In Gerstenhaber, M. Some Mathematical Questions in Biology. pp. 77–107. ISBN 978-0-8218-1152-8.
- Smith, M. A.; Green, D. M. (2005). "Dispersal and the metapopulation paradigm in amphibian ecology and conservation: Are all amphibian populations metapopulations?". Ecography. 28 (1): 110–128. doi:10.1111/j.0906-7590.2005.04042.x.
- Hanski, I. (1998). "Metapopulation dynamics" (PDF). Nature. 396 (6706): 41–49. Bibcode:1998Natur.396...41H. doi:10.1038/23876. Archived from the original (PDF) on 31 December 2010.
- Nebel, S. (2010). "Animal migration". Nature Education Knowledge. 10 (1): 29.
- Clark, J. S.; Fastie, C.; Hurtt, G.; Jackson, S. T.; Johnson, C.; King, G. A.; Lewis, M.; Lynch, J.; Pacala, S.; et al. (1998). "Reid's paradox of rapid plant migration" (PDF). BioScience. 48 (1): 13–24. JSTOR 1313224. doi:10.2307/1313224.
- Dingle, H. (1996-01-18). Migration: The Biology of Life on the Move. Oxford University Press. p. 480. ISBN 0-19-509723-8.
- Hanski, I.; Gaggiotti, O. E., eds. (2004). Ecology, Genetics and Evolution of Metapopulations. Burlington, MA: Elsevier Academic Press. ISBN 0-12-323448-4.
- MacKenzie; D.I. (2006). Occupancy Estimation and Modeling: Inferring Patterns and Dynamics of Species Occurrence. London, UK: Elsevier Academic Press. p. 324. ISBN 978-0-12-088766-8.
- Johnson, M. T.; Strinchcombe, J. R. (2007). "An emerging synthesis between community ecology and evolutionary biology". Trends in Ecology and Evolution. 22 (5): 250–257. PMID 17296244. doi:10.1016/j.tree.2007.01.014.
- Tansley, A. G. (1935). "The use and abuse of vegetational concepts and terms" (PDF). Ecology. 16 (3): 284–307. JSTOR 1930070. doi:10.2307/1930070.
- Brinson, M. M.; Lugo, A. E.; Brown, S (1981). "Primary Productivity, Decomposition and Consumer Activity in Freshwater Wetlands". Annual Review of Ecology and Systematics. 12: 123–161. doi:10.1146/annurev.es.12.110181.001011.
- Marsh, G. P. (1864). Man and Nature: Physical Geography as Modified by Human Action. Cambridge, MA: Belknap Press. p. 560.
- O'Neil, R. V. (2001). "Is it time to bury the ecosystem concept? (With full military honors, of course!)" (PDF). Ecology. 82 (12): 3275–3284. ISSN 0012-9658. doi:10.1890/0012-9658(2001)082[3275:IITTBT]2.0.CO;2.
- Levin, S. A. (1998). "Ecosystems and the biosphere as complex adaptive systems". Ecosystems. 1 (5): 431–436. CiteSeerX . doi:10.1007/s100219900037.
- Pimm, S. (2002). Food Webs. University of Chicago Press. p. 258. ISBN 978-0-226-66832-1.
- Pimm, S. L.; Lawton, J. H.; Cohen, J. E. (1991). "Food web patterns and their consequences" (PDF). Nature. 350 (6320): 669–674. Bibcode:1991Natur.350..669P. doi:10.1038/350669a0. Archived from the original (PDF) on 10 June 2010.
- Worm, B.; Duffy, J. E. (2003). "Biodiversity, productivity and stability in real food webs". Trends in Ecology and Evolution. 18 (12): 628–632. doi:10.1016/j.tree.2003.09.003.
- McCann, K. (2007). "Protecting biostructure" (PDF). Nature. 446 (7131): 29. Bibcode:2007Natur.446...29M. PMID 17330028. doi:10.1038/446029a. Archived from the original (PDF) on 22 July 2011.
- Wilbur, H. W. (1997). "Experimental ecology of food webs: Complex systems in temporary ponds" (PDF). Ecology. 78 (8): 2279–2302. ISSN 0012-9658. doi:10.1890/0012-9658(1997)078[2279:EEOFWC]2.0.CO;2.
- Emmerson, M.; Yearsley, J. M. (2004). "Weak interactions, omnivory and emergent food-web properties" (PDF). Philosophical Transactions of the Royal Society B. 271 (1537): 397–405. doi:10.1098/rspb.2003.2592.
- Krause, A. E.; Frank, K. A.; Mason, D. M.; Ulanowicz, R. E.; Taylor, W. W. (2003). "Compartments revealed in food-web structure" (PDF). Nature. 426 (6964): 282–285. Bibcode:2003Natur.426..282K. PMID 14628050. doi:10.1038/nature02115.
- Egerton, Frank N. (2007). "Understanding food chains and food webs, 1700–1970". Bulletin of the Ecological Society of America. 88: 50–69. ISSN 0012-9623. doi:10.1890/0012-9623(2007)88[50:UFCAFW]2.0.CO;2.
- Shurin, J. B.; Gruner, D. S.; Hillebrand, H. (2006). "All wet or dried up? Real differences between aquatic and terrestrial food webs". Proceedings of the Royal Society B. 273 (1582): 1–9. PMC . PMID 16519227. doi:10.1098/rspb.2005.3377.
- Edwards, J.; Fraser, K. (1983). "Concept maps as reflectors of conceptual understanding". Research in Science Education. 13: 19–26. Bibcode:1983RScEd..13...19E. doi:10.1007/BF02356689.
- Hairston Jr., N. G.; Hairston Sr., N. G. (1993). "Cause-effect relationships in energy flow, trophic structure, and interspecific interactions" (PDF). The American Naturalist. 142 (3): 379–411. doi:10.1086/285546. Archived from the original (PDF) on 20 July 2011.
- Duffy, J. Emmett; Cardinale, Bradley J.; France, Kristin E.; McIntyre, Peter B.; Thébault, Elisa; Loreau, Michel (2007). "The functional role of biodiversity in ecosystems: incorporating trophic complexity". Ecology Letters. 10 (6): 522–538. PMID 17498151. doi:10.1111/j.1461-0248.2007.01037.x.
- Elton, C. S. (1927). Animal Ecology. London, UK.: Sidgwick and Jackson. ISBN 0-226-20639-4.
- Davic, R. D. (2003). "Linking keystone species and functional groups: a new operational definition of the keystone species concept". Conservation Ecology. 7 (1): r11.
- Oksanen, L. (1991). "Trophic levels and trophic dynamics: A consensus emerging?". Trends in Ecology and Evolution. 6 (2): 58–60. PMID 21232425. doi:10.1016/0169-5347(91)90124-G.
- Loehle, C.; Pechmann, Joseph H. K. (1988). "Evolution: The missing ingredient in systems ecology". The American Naturalist. 132 (9): 884–899. JSTOR 2462267. doi:10.1086/284895.
- Ulanowicz, R. E.; Kemp, W. Michael (1979). "Toward canonical trophic aggregations". The American Naturalist. 114 (6): 871–883. JSTOR 2460557. doi:10.1086/283534.
- Li, B. (2000). "Why is the holistic approach becoming so important in landscape ecology?". Landscape and Urban Planning. 50 (1–3): 27–41. doi:10.1016/S0169-2046(00)00078-5.
- Polis, G. A.; Strong, D. R. (1996). "Food web complexity and community dynamics" (PDF). The American Naturalist. 147 (5): 813–846. doi:10.1086/285880. Archived from the original (PDF) on 20 July 2011.
- Thompson, R. M.; Hemberg, M.; Starzomski, B. M.; Shurin, J. B. (2007). "Trophic levels and trophic tangles: The prevalence of omnivory in real food webs" (PDF). Ecology. 88 (3): 612–617. PMID 17503589. doi:10.1890/05-1454. Archived from the original (PDF) on 15 August 2011.
- Fischer, J.; Lindenmayer, D. B.; Manning, A. D. (2006). "Biodiversity, ecosystem function, and resilience: ten guiding principles for commodity production landscapes" (PDF). Frontiers in Ecology and the Environment. 4 (2): 80–86. ISSN 1540-9295. doi:10.1890/1540-9295(2006)004[0080:BEFART]2.0.CO;2.
- Libralato, S.; Christensen, V.; Pauly, D. (2006). "A method for identifying keystone species in food web models" (PDF). Ecological Modelling. 195 (3–4): 153–171. doi:10.1016/j.ecolmodel.2005.11.029. Archived from the original (PDF) on 19 May 2012.
- Mills, L. S.; Soule, M. E.; Doak, D. F. (1993). "The keystone-species concept in ecology and conservation". BioScience. 43 (4): 219–224. JSTOR 1312122. doi:10.2307/1312122.
- Anderson, P. K. (1995). "Competition, predation, and the evolution and extinction of Steller's sea cow, Hydrodamalis gigas". Marine Mammal Science. 11 (3): 391–394. doi:10.1111/j.1748-7692.1995.tb00294.x.
- Polis, G. A.; Sears, Anna L. W.; Huxel, Gary R.; Strong, Donald R.; Maron, John (2000). "When is a trophic cascade a trophic cascade?" (PDF). Trends in Ecology and Evolution. 15 (11): 473–475. PMID 11050351. doi:10.1016/S0169-5347(00)01971-6.
- Novikoff, A. B. (1945). "The concept of integrative levels and biology" (PDF). Science. 101 (2618): 209–215. Bibcode:1945Sci...101..209N. PMID 17814095. doi:10.1126/science.101.2618.209. Archived from the original (PDF) on 15 May 2011.
- Schneider, D. D. (2001). "The rise of the concept of scale in ecology" (PDF). BioScience. 51 (7): 545–553. ISSN 0006-3568. doi:10.1641/0006-3568(2001)051[0545:TROTCO]2.0.CO;2.
- Molnar, J.; Marvier, M.; Kareiva, P. (2004). "The sum is greater than the parts" (PDF). Conservation Biology. 18 (6): 1670–1671. doi:10.1111/j.1523-1739.2004.00l07.x.[permanent dead link]
- Loehle, C. (2004). "Challenges of ecological complexity". Ecological Complexity. 1 (1): 3–6. doi:10.1016/j.ecocom.2003.09.001.
- Odum, E. P. (1977). "The emergence of ecology as a new integrative discipline". Science. 195 (4284): 1289–1293. Bibcode:1977Sci...195.1289O. PMID 17738398. doi:10.1126/science.195.4284.1289.
- Scheffer, M.; Carpenter, S.; Foley, J. A.; Walker, B.; Walker, B. (2001). "Catastrophic shifts in ecosystems" (PDF). Nature. 413 (6856): 591–596. Bibcode:2001Natur.413..591S. PMID 11595939. doi:10.1038/35098000.
- "Welcome to ILTER — ILTER". International Long Term Ecological Research. Retrieved 2010-03-16.
- Silverton, Jonathan; Poulton, Paul; Johnston, Edward; Edwards, Grant; Heard, Matthew; Biss, Pamela M. (2006). "The Park Grass Experiment 1856–2006: Its contribution to ecology" (PDF). Journal of Ecology. 94 (4): 801–814. doi:10.1111/j.1365-2745.2006.01145.x. Archived from the original (PDF) on 9 July 2011.
- "Hubbard Brook Ecosystem Study Front Page". Retrieved 2010-03-16.
- Liu, J.; Dietz, Thomas; Carpenter, Stephen R.; Folke, Carl; Alberti, Marina; Redman, Charles L.; Schneider, Stephen H.; Ostrom, Elinor; Pell, Alice N.; et al. (2009). "Coupled human and natural systems" (PDF). AMBIO: A Journal of the Human Environment. 36 (8): 639–649. ISSN 0044-7447. doi:10.1579/0044-7447(2007)36[639:CHANS]2.0.CO;2.[permanent dead link]
- Mikkelson, G. M. (2010). "Part-whole relationships and the unity of ecology". In Skipper, R. A.; Allen, C.; Ankeny, R.; Craver, C. F.; Darden, L.; Richardson, R.C. Philosophy Across the Life Sciences (PDF). Cambridge, MA: MIT Press.
- Wilson, D. S. (1988). "Holism and reductionism in evolutionary ecology". Oikos. 53 (2): 269–273. JSTOR 3566073. doi:10.2307/3566073.
- Miles, D. B.; Dunham, A. E. (1993). "Historical perspectives in ecology and evolutionary biology: The use of phylogenetic comparative analyses". Annual Review of Ecology and Systematics. 24: 587–619. doi:10.1146/annurev.es.24.110193.003103.
- Craze, P., ed. (2 August 2012). "Trends in Ecology and Evolution". Cell Press, Elsevier, Inc.
- Allee, W. C.; Park, O.; Emerson, A. E.; Park, T.; Schmidt, K. P. (1949). Principles of Animal Ecology. W. B. Sunders, Co. p. 837. ISBN 0-7216-1120-6.
- Rickleffs, Robert, E. (1996). The Economy of Nature. University of Chicago Press. p. 678. ISBN 0-7167-3847-3.
- Yoshida, T. "Rapid evolution drives ecological dynamics in a predator–prey system". Nature Publishing Group.
- Stuart-Fox, D.; Moussalli, A. (2008). "Selection for social signalling drives the evolution of chameleon colour change". PLoS Biology. 6 (1): e25. PMC . PMID 18232740. doi:10.1371/journal.pbio.0060025.
- Karban, R. (2008). "Plant behaviour and communication". Ecology Letters. 11 (7): 727–739. PMID 18400016. doi:10.1111/j.1461-0248.2008.01183.x.
- Tinbergen, N. (1963). "On aims and methods of ethology" (PDF). Zeitschrift für Tierpsychologie. 20 (4): 410–433. doi:10.1111/j.1439-0310.1963.tb01161.x.
- Hamner, W. M. (1985). "The importance of ethology for investigations of marine zooplankton". Bulletin of Marine Science. 37 (2): 414–424.
- Strassmann, J. E.; Zhu, Y.; Queller, D. C. (2000). "Altruism and social cheating in the social amoeba Dictyostelium discoideum". Nature. 408 (6815): 965–967. Bibcode:2000Natur.408..965S. PMID 11140681. doi:10.1038/35050087.
- Sakurai, K. (1985). "An attelabid weevil (Euops splendida) cultivates fungi". Journal of Ethology. 3 (2): 151–156. doi:10.1007/BF02350306.
- Anderson, J. D. (1961). "The courtship behaviour of Ambystoma macrodactylum croceum". Copeia. 2 (2): 132–139. JSTOR 1439987. doi:10.2307/1439987.
- "Behavioral Ecology". International Society for Behavioral Ecology. Archived from the original on 10 April 2011. Retrieved 15 April 2011.
- Gould, Stephen J.; Vrba, Elizabeth S. (1982). "Exaptation–a missing term in the science of form". Paleobiology. 8 (1): 4–15.
- Wilson, Edward. O. (2000). Sociobiology: The New Synthesis (25th anniversary ed.). President and Fellows of Harvard College. ISBN 978-0-674-00089-6.
- Ives, A. R.; Cardinale, B. J.; Snyder, W. E. (2004). "A synthesis of subdisciplines: Predator–prey interactions, and biodiversity and ecosystem functioning" (PDF). Ecology Letters. 8 (1): 102–116. doi:10.1111/j.1461-0248.2004.00698.x.
- Krebs, J. R.; Davies, N. B. (1993). An Introduction to Behavioural Ecology. Wiley-Blackwell. p. 432. ISBN 978-0-632-03546-5.
- Webb, J. K.; Pike, D. A.; Shine, R. (2010). "Olfactory recognition of predators by nocturnal lizards: safety outweighs thermal benefits". Behavioural Ecology. 21 (1): 72–77. doi:10.1093/beheco/arp152.
- Cooper, W. E.; Frederick, W. G. (2010). "Predator lethality, optimal escape behavior, and autotomy". Behavioral Ecology. 21 (1): 91–96. doi:10.1093/beheco/arp151.
- Eastwood, R. (2004). "Successive replacement of tending ant species at aggregations of scale insects (Hemiptera: Margarodidae and Eriococcidae) on Eucalyptus in south-east Queensland" (PDF). Australian Journal of Entomology. 43: 1–4. doi:10.1111/j.1440-6055.2003.00371.x. Archived from the original (PDF) on 17 September 2011.
- Kodric-Brown, A.; Brown, J. H. (1984). "Truth in advertising: The kinds of traits favored by sexual selection" (PDF). The American Naturalist. 124 (3): 309–323. doi:10.1086/284275. Archived from the original (PDF) on 2011-06-29.
- Adrian G Palacios, Francisco Bozinovic; Bozinovic (2003). "An "enactive" approach to integrative and comparative biology: Thoughts on the table" (PDF). Biology Research. 36 (1): 95–99. PMID 12795209. doi:10.4067/S0716-97602003000100008.
- Reuven Dukas (1998). "§1.3 Why study cognitive ecology?". In Reuven Dukas. Cognitive Ecology: The Evolutionary Ecology of Information Processing and Decision Making. University of Chicago Press. p. 4. ISBN 9780226169323.
- Reuven Dukas; John M. Ratcliffe (2009). "Introduction". In Reuven Dukas; John M. Ratcliffe. Cognitive Ecology II. University of Chicago Press. pp. 1 ff. ISBN 9780226169378.
Cognitive ecology focuses on he ecology and evolution of "cognition" defined as the neuronal processes concerned with the acquisition, retention, and use of information....we ought to rely on ecological and evolutionary knowledge for studying cognition.
- Francisco J Varela; Evan Thompson; Eleanor Rosch (1993). The Embodied Mind: Cognitive Science and Human Experience (Paperback ed.). MIT Press. p. 174. ISBN 9780262261234.
- Sherman, P. W.; Lacey, E. A.; Reeve, H. K.; Keller, L. (1995). "The eusociality continuum" (PDF). Behavioural Ecology. 6 (1): 102–108. doi:10.1093/beheco/6.1.102. Archived from the original (PDF) on 19 July 2011.
- Wilson, D. S.; Wilson, E. O. (2007). "Rethinking the theoretical foundation of sociobiology". The Quarterly Review of Biology. 82 (4): 327–348. PMID 18217526. doi:10.1086/522809.
- Page, R. D. M. (1991). "Clocks, clades, and cospeciation: Comparing rates of evolution and timing of cospeciation events in host-parasite assemblages". Systematic Zoology. 40 (2): 188–198. JSTOR 2992256. doi:10.2307/2992256.
- Herre, E. A.; Knowlton, N.; Mueller, U. G.; Rehner, S. A. (1999). "The evolution of mutualisms: exploring the paths between conflict and cooperation" (PDF). Trends in Ecology and Evolution. 14 (2): 49–53. PMID 10234251. doi:10.1016/S0169-5347(98)01529-8. Archived from the original (PDF) on 20 September 2009.
- Gilbert, F. S. (1990). Insect life cycles: Genetics, evolution, and co-ordination. New York, NY: Springer-Verlag. p. 258. ISBN 0-387-19550-5.
- Kiers, E. T.; van der Heijden, M. G. A. (2006). "Mutualistic stability in the arbuscular mycorrhizal symbiosis: Exploring hypotheses of evolutionary cooperation" (PDF). Ecology. 87 (7): 1627–1636. ISSN 0012-9658. PMID 16922314. doi:10.1890/0012-9658(2006)87[1627:MSITAM]2.0.CO;2.
- Strain, B. R. (1985). "Physiological and ecological controls on carbon sequestering in terrestrial ecosystems". Biogeochemistry. 1 (3): 219–232. doi:10.1007/BF02187200.
- Bronstein, J. L. (2001). "The exploitation of mutualisms". Ecology Letters. 4 (3): 277–287. doi:10.1046/j.1461-0248.2001.00218.x.
- Irwin, Rebecca E.; Bronstein, Judith L.; Manson, Jessamyn S.; Richardson, Leif (2010). "Nectar robbing: Ecological and evolutionary perspectives". Annual Review of Ecology, Evolution, and Systematics. 41 (2): 271–292. doi:10.1146/annurev.ecolsys.110308.120330.
- Boucher, D. H.; James, S.; Keeler, K. H. (1982). "The ecology of mutualism". Annual Review of Ecology and Systematics. 13: 315–347. doi:10.1146/annurev.es.13.110182.001531.
- King, K. C.; Delph, L. F.; Jokela, J.; Lively, C. M. (2009). "The geographic mosaic of sex and the Red Queen". Current Biology. 19 (17): 1438–1441. PMID 19631541. doi:10.1016/j.cub.2009.06.062.
- Parenti, L. R.; Ebach, M. C. (2009). Comparative Biogeography: Discovering and Classifying Biogeographical Patterns of a Dynamic Earth. London, England: University of California Press. ISBN 978-0-520-25945-4.
- "Journal of Biogeography". Wiley. Retrieved 3 August 2012.
- MacArthur, R.; Wilson, E. O. (1967). "The Theory of Island Biogeography". Princeton, NJ: Princeton University Press.
- Wiens, J. J.; Donoghue, M. J. (2004). "Historical biogeography, ecology and species richness" (PDF). Trends in Ecology and Evolution. 19 (12): 639–644. PMID 16701326. doi:10.1016/j.tree.2004.09.011.
- Morrone, J. J.; Crisci, J. V. (1995). "Historical biogeography: Introduction to methods". Annual Review of Ecology and Systematics. 26: 373–401. doi:10.1146/annurev.es.26.110195.002105.
- Svenning, Jens-Christian; Condi, R. (2008). "Biodiversity in a warmer world". Science. 322 (5899): 206–207. PMID 18845738. doi:10.1126/science.1164542.
- Landhäusser, Simon M.; Deshaies, D.; Lieffers, V. J. (2009). "Disturbance facilitates rapid range expansion of aspen into higher elevations of the Rocky Mountains under a warming climate". Journal of Biogeography. 37 (1): 68–76. doi:10.1111/j.1365-2699.2009.02182.x.
- Reznick, D.; Bryant, M. J.; Bashey, F. (2002). "r- and K-selection revisited: The role of population regulation in life-history evolution" (PDF). Ecology. 83 (6): 1509–1520. ISSN 0012-9658. doi:10.1890/0012-9658(2002)083[1509:RAKSRT]2.0.CO;2.
- Pianka, E. R. (1972). "r and K Selection or b and d Selection?". The American Naturalist. 106 (951): 581–588. doi:10.1086/282798.
- Rieseberg, L. (ed.). "Molecular Ecology". Molecular Ecology. Wiley. doi:10.1111/(ISSN)1365-294X.
- Avise, J. (1994). Molecular Markers, Natural History and Evolution. Kluwer Academic Publishers. ISBN 0-412-03771-8.
- O'Brian, E.; Dawson, R. (2007). "Context-dependent genetic benefits of extra-pair mate choice in a socially monogamous passerine" (PDF). Behavioral Ecology and Sociobiology. 61 (5): 775–782. doi:10.1007/s00265-006-0308-8.
- Avise, J. (2000). Phylogeography: The History and Formation of Species. President and Fellows of Harvard College. ISBN 0-674-66638-0.
- Rachel Carson (1962). ""Silent Spring" (excerpt)". Houghton Miffin. Retrieved 4 October 2012.
- Young, G. L. (1974). "Human ecology as an interdisciplinary concept: A critical inquiry". Advances in Ecological Research. Advances in Ecological Research. 8: 1–105. ISBN 978-0-12-013908-8. doi:10.1016/S0065-2504(08)60277-9.
- Gross, M. (2004). "Human geography and ecological sociology: the unfolding of human ecology, 1890 to 1930 – and beyond". Social Science History. 28 (4): 575–605. doi:10.1215/01455532-28-4-575.
- "Millennium Ecosystem Assessment – Synthesis Report". United Nations. 2005. Retrieved 4 February 2010.
- de Groot, R. S.; Wilson, M. A.; Boumans, R. M. J. (2002). "A typology for the classification, description and valuation of ecosystem functions, goods and services" (PDF). Ecological Economics. 41 (3): 393–408. doi:10.1016/S0921-8009(02)00089-7.
- Aguirre, A. A. (2009). "Biodiversity and human health". EcoHealth. 6: 153–156. doi:10.1007/s10393-009-0242-0.
- Grumbine, R. E. (1994). "What is ecosystem management?" (PDF). Conservation Biology. 8 (1): 27–38. doi:10.1046/j.1523-1739.1994.08010027.x. Archived from the original (PDF) on 2 May 2013.
- Wilson, E. O. (1992). The Diversity of Life. Harvard University Press. p. 440. ISBN 978-0-674-05817-0.
- Slocombe, D. S. (1993). "Implementing ecosystem-based management". BioScience. 43 (9): 612–622. JSTOR 1312148. doi:10.2307/1312148.
- Hobss, R. J.; Harris, J. A. (2001). "Restoration ecology: Repairing the Earth's ecosystems in the new millennium" (PDF). Restoration Ecology. 9 (2): 239–246. doi:10.1046/j.1526-100x.2001.009002239.x.
- Mason, H. L.; Langenheim, J. H. (1957). "Language analysis and the concept "environment"". Ecology. 38 (2): 325–340. JSTOR 1931693. doi:10.2307/1931693.
- Kleese, D. A. (2001). "Nature and nature in Psychology". Journal of Theoretical and Philosophical Psychology. 21: 61–79. doi:10.1037/h0091199.
- Campbell, Neil A.; Williamson, Brad; Heyden, Robin J. (2006). Biology: Exploring Life. Boston, Massachusetts: Pearson Prentice Hall. ISBN 0-13-250882-6.
- Kormondy, E. E. (1995). Concepts of Ecology (4th ed.). Benjamin Cummings. ISBN 0-13-478116-3.
- Hughes, A. R. "Disturbance and diversity: an ecological chicken and egg problem". Nature Education Knowledge. 1 (8): 26.
- Levin, S. A. (1992). "The problem of pattern and scale in ecology: The Robert H. MacArthur Award" (PDF). Ecology. 73 (6): 1943–1967. JSTOR 1941447. doi:10.2307/1941447. Archived from the original (PDF) on 18 June 2010. Retrieved 2010-03-16.
- Holling, C. S. (1973). "Resilience and stability of ecological systems". Annual Review of Ecology and Systematics. 4 (1): 1–23. JSTOR 2096802. doi:10.1146/annurev.es.04.110173.000245.
- Folke, C.; Carpenter, S.; Walker, B.; Scheffer, M.; Elmqvist, T.; Gunderson, L.; Holling, C.S. (2004). "Regime shifts, resilience, and biodiversity in ecosystem management" (PDF). Annual Review of Ecology and Systematics. 35: 557–581. JSTOR 2096802. doi:10.1146/annurev.ecolsys.35.021103.105711.
- Morgan Ernest, S. K.; Enquist, Brian J.; Brown, James H.; Charnov, Eric L.; Gillooly, James F.; Savage, Van M.; White, Ethan P.; Smith, Felisa A.; Hadly, Elizabeth A.; Haskell, John P.; Lyons, S. Kathleen; Maurer, Brian A.; Niklas, Karl J.; Tiffney, Bruce (2003). "Thermodynamic and metabolic effects on the scaling of production and population energy use" (PDF). Ecology Letters. 6 (11): 990–995. doi:10.1046/j.1461-0248.2003.00526.x.
- Allègre, Claude J.; Manhès, Gérard; Göpel, Christa (1995). "The age of the Earth". Geochimica et Cosmochimica Acta. 59 (8): 1455–1456. Bibcode:1995GeCoA..59.1445A. doi:10.1016/0016-7037(95)00054-4.
- Wills, C.; Bada, J. (2001). The Spark of Life: Darwin and the Primeval Soup. Cambridge, MA: Perseus Publishing. ISBN 978-0-7382-0493-2.
- Goldblatt, Colin; Lenton, Timothy M.; Watson, Andrew J. (2006). "Bistability of atmospheric oxygen and the Great Oxidation" (PDF). Nature. 443 (7112): 683–686. Bibcode:2006Natur.443..683G. PMID 17036001. doi:10.1038/nature05169. Archived from the original (PDF) on 20 August 2011.
- Catling, D. C.; Claire, M. W. (2005). "How Earth's atmosphere evolved to an oxic state: A status report" (PDF). Earth and Planetary Science Letters. 237: 1–20. Bibcode:2005E&PSL.237....1C. doi:10.1016/j.epsl.2005.06.013.
- Cronk, J. K.; Fennessy, M. S. (2001). Wetland Plants: Biology and Ecology. Washington, D.C.: Lewis Publishers. ISBN 1-56670-372-7.
- Evans, D. H.; Piermarini, P. M.; Potts, W. T. W. (1999). "Ionic transport in the fish gill epithelium" (PDF). Journal of Experimental Zoology. 283 (7): 641–652. doi:10.1002/(SICI)1097-010X(19990601)283:7<641::AID-JEZ3>3.0.CO;2-W.
- Swenson, N. G.; Enquist, B. J. (2008). "The relationship between stem and branch wood specific gravity and the ability of each measure to predict leaf area". American Journal of Botany. 95 (4): 516–519. PMID 21632377. doi:10.3732/ajb.95.4.516.
- Gartner, Gabriel E.A.; Hicks, James W.; Manzani, Paulo R.; et al. (2010). "Phylogeny, ecology, and heart position in snakes" (PDF). Physiological and Biochemical Zoology. 83 (1): 43–54. PMID 19968564. doi:10.1086/648509. Archived from the original (PDF) on 16 July 2011.
- Neri Salvadori, Pasquale Commendatore, Massimo Tamberi (14 May 2014). "Geography, structural Change and Economic Development: Theory and Empirics". Edward Elgar Publishing.
- Jacobsen, D. (2008). "Low oxygen pressure as a driving factor for the altitudinal decline in taxon richness of stream macroinvertebrates". Oecologia. 154 (4): 795–807. Bibcode:2008Oecol.154..795J. PMID 17960424. doi:10.1007/s00442-007-0877-x.
- Wheeler, T. D.; Stroock, A. D. (2008). "The transpiration of water at negative pressures in a synthetic tree". Nature. 455 (7210): 208–212. Bibcode:2008Natur.455..208W. PMID 18784721. doi:10.1038/nature07226.
- Pockman, W. T.; Sperry, J. S.; O'Leary, J. W. (1995). "Sustained and significant negative water pressure in xylem". Nature. 378 (6558): 715–716. Bibcode:1995Natur.378..715P. doi:10.1038/378715a0.
- Zimmermann, U.; Schneider, H.; Wegner, L. H.; Wagner, M.; Szimtenings, A.; Haase, F.; Bentrup, F. W. (2002). "What are the driving forces for water lifting in the xylem conduit?". Physiologia Plantarum. 114 (3): 327–335. PMID 12060254. doi:10.1034/j.1399-3054.2002.1140301.x.
- Kastak, D.; Schusterman, R. J. (1998). "Low-frequency amphibious hearing in pinnipeds: Methods, measurements, noise, and ecology". Journal of the Acoustical Society of America. 103 (4): 2216–2228. Bibcode:1998ASAJ..103.2216K. PMID 9566340. doi:10.1121/1.421367.
- Nishiguchi, Y.; Ito, I.; Okada, M. (2010). "Structure and function of lactate dehydrogenase from hagfish". Marine Drugs. 8 (3): 594–607. PMC . PMID 20411117. doi:10.3390/md8030594.
- Friedman, J.; Harder, L. D. (2004). "Inflorescence architecture and wind pollination in six grass species" (PDF). Functional Ecology. 18 (6): 851–860. doi:10.1111/j.0269-8463.2004.00921.x. Archived from the original (PDF) on 6 July 2011.
- Harder, L. D.; Johnson, S. D. (2009). "Darwin's beautiful contrivances: evolutionary and functional evidence for floral adaptation" (PDF). New Phytologist. 183 (3): 530–545. PMID 19552694. doi:10.1111/j.1469-8137.2009.02914.x. Archived from the original (PDF) on 6 July 2011.
- Shimeta, J.; Jumars, P. A.; Lessard, E. J. (1995). "Influences of turbulence on suspension feeding by planktonic protozoa; experiments in laminar shear fields" (PDF). Limnolology and Oceanography. 40 (5): 845–859. Bibcode:1995LimOc..40..845S. doi:10.4319/lo.1995.40.5.0845. Archived from the original (PDF) on 20 July 2011.
- Etemad-Shahidi, A.; Imberger, J. (2001). "Anatomy of turbulence in thermally stratified lakes" (PDF). Limnolology and Oceanography. 46 (5): 1158–1170. Bibcode:2001LimOc..46.1158E. doi:10.4319/lo.2001.46.5.1158. Archived from the original (PDF) on 25 July 2011.
- Wolf, B. O.; Walsberg, G. E. (2006). "Thermal effects of radiation and wind on a small bird and implications for microsite selection". Ecology. 77 (7): 2228–2236. JSTOR 2265716. doi:10.2307/2265716.
- Daubenmire, R. (1975). "Floristic plant geography of eastern Washington and northern Idaho". Journal of Biogeography. 2 (1): 1–18. JSTOR 3038197. doi:10.2307/3038197.
- Steele, C. A.; Carstens, B. C.; Storfer, A.; Sullivan, J. (2005). "Testing hypotheses of speciation timing in Dicamptodon copei and Dicamptodon aterrimus (Caudata: Dicamptodontidae)" (PDF). Molecular Phylogenetics and Evolution. 36 (1): 90–100. PMID 15904859. doi:10.1016/j.ympev.2004.12.001. Archived from the original (PDF) on 14 August 2010.
- Lenton, T. M.; Watson, A. (2000). "Redfield revisited. 2. What regulates the oxygen content of the atmosphere" (PDF). Global Biogeochemical Cycles. 14 (1): 249–268. Bibcode:2000GBioC..14..249L. doi:10.1029/1999GB900076. Archived from the original (PDF) on 15 September 2011.
- Lobert, J. M.; Warnatz, J. (1993). "Emissions from the combustion process in vegetation". In Crutzen, P. J.; Goldammer, J. G. Fire in the Environment: The Ecological, Atmospheric and Climatic Importance of Vegetation Fires (PDF). Wiley. ISBN 978-0-471-93604-6.
- Garren, K. H. (1943). "Effects of fire on vegetation of the southeastern United States". Botanical Review. 9 (9): 617–654. doi:10.1007/BF02872506.
- Cooper, C. F. (1960). "Changes in vegetation, structure, and growth of southwestern pine forests since white settlement". Ecological Monographs. 30 (2): 130–164. doi:10.2307/1948549.
- Cooper, C. F. (1961). "The ecology of fire". Scientific American. 204 (4): 150–160. Bibcode:1961SciAm.204d.150C. doi:10.1038/scientificamerican0461-150.
- van Wagtendonk, Jan W. (2007). "History and evolution of wildland fire use" (PDF). Fire Ecology Special Issue. 3 (2): 3–17. doi:10.4996/fireecology.0302003.
- Boerner, R. E. J. (1982). "Fire and nutrient cycling in temperate ecosystems". BioScience. 32 (3): 187–192. JSTOR 1308941. doi:10.2307/1308941.
- Goubitz, S.; Werger, M. J. A.; Ne'eman, G. (2009). "Germination response to fire-related factors of seeds from non-serotinous and serotinous cones". Plant Ecology. 169 (2): 195–204. doi:10.1023/A:1026036332277.
- Ne'eman, G.; Goubitz, S.; Nathan, R. (2004). "Reproductive traits of Pinus halepensis in the light of fire: a critical review". Plant Ecology. 171 (1/2): 69–79. doi:10.1023/B:VEGE.0000029380.04821.99.
- Flematti, Gavin R.; Ghisalberti, Emilio L.; Dixon, Kingsley W.; Trengove, R. D. (2004). "A compound from smoke that promotes seed germination" (PDF). Science. 305 (5686): 977. PMID 15247439. doi:10.1126/science.1099944.
- Coleman, D. C.; Corssley, D. A.; Hendrix, P. F. (2004). Fundamentals of Soil Ecology (2nd ed.). Academic Press. ISBN 0-12-179726-0.
- Wilkinson, M. T.; Richards, P. J.; Humphreys, G. S. (2009). "Breaking ground: Pedological, geological, and ecological implications of soil bioturbation" (PDF). Earth-Science Reviews. 97 (1–4): 257–272. Bibcode:2009ESRv...97..257W. doi:10.1016/j.earscirev.2009.09.005.
- Phillips, J. D. (2009). "Soils as extended composite phenotypes". Geoderma. 149 (1–2): 143–151. doi:10.1016/j.geoderma.2008.11.028.
- Reinhardt, L.; Jerolmack, D.; Cardinale, B. J.; Vanacker, V.; Wright, J. "Dynamic interactions of life and its landscape: Feedbacks at the interface of geomorphology and ecology" (PDF). Earth Surf. Process. Landforms. 35: 78–101. Bibcode:2010ESPL...35...78R. doi:10.1002/esp.1912.
- Davic, R. D.; Welsh, H. H. (2004). "On the ecological role of salamanders" (PDF). Annual Review of Ecology and Systematics. 35: 405–434. doi:10.1146/annurev.ecolsys.35.112202.130116.
- Hasiotis, S. T. (2003). "Complex ichnofossils of solitary and social soil organisms: Understanding their evolution and roles in terrestrial paleoecosystems". Palaeogeography, Palaeoclimatology, Palaeoecology. 192 (2): 259–320. Bibcode:2003PPP...192..259H. doi:10.1016/S0031-0182(02)00689-2.
- Falkowski, P. G.; Fenchel, T.; Delong, E. F. (2008). "The microbial engines that drive Earth's biogeochemical cycles". Science. 320 (5879): 1034–1039. Bibcode:2008Sci...320.1034F. PMID 18497287. doi:10.1126/science.1153213.
- Grace, J. (2004). "Understanding and managing the global carbon cycle". Journal of Ecology. 92 (2): 189–202. doi:10.1111/j.0022-0477.2004.00874.x.
- Pearson, P. N.; Palmer, M. R. (2000). "Atmospheric carbon dioxide concentrations over the past 60 million years" (PDF). Nature. 406 (6797): 695–699. PMID 10963587. doi:10.1038/35021000. Archived from the original (PDF) on 21 August 2011.
- Pagani, M.; Zachos, J. C.; Freeman, K. H.; Tipple, B.; Bohaty, S. (2005). "Marked decline in atmospheric carbon dioxide concentrations during the Paleogene". Science. 309 (5734): 600–603. Bibcode:2005Sci...309..600P. PMID 15961630. doi:10.1126/science.1110063.
- Zhuan, Q.; Melillo, J. M.; McGuire, A. D.; Kicklighter, D. W.; Prinn, R. G.; Steudler, P. A.; Felzer, B. S.; Hu, S. (2007). "Net emission of CH4 and CO2 in Alaska: Implications for the region's greenhouse gas budget" (PDF). Ecological Applications. 17 (1): 203–212. ISSN 1051-0761. PMID 17479846. doi:10.1890/1051-0761(2007)017[0203:NEOCAC]2.0.CO;2. Archived from the original (PDF) on 30 June 2007.
- Cox, Peter M.; Betts, Richard A.; Jones, Chris D.; Spall, Steven A.; Totterdell, Ian J. (2000). "Acceleration of global warming due to carbon-cycle feedbacks in a coupled climate model" (PDF). Nature. 408 (6809): 184–187. Bibcode:2000Natur.408..184C. PMID 11089968. doi:10.1038/35041539. Archived from the original (PDF) on 17 September 2012.
- Erwin, D. H. (2009). "Climate as a driver of evolutionary change". Current Biology. 19 (14): R575–R583. PMID 19640496. doi:10.1016/j.cub.2009.05.047.
- Bamber, J. (2012). "Shrinking glaciers under scrutiny" (PDF). Nature. 482 (7386): 482–483. Bibcode:2012Natur.482..482B. PMID 22318516. doi:10.1038/nature10948. Retrieved 12 June 2017.
- Heimann, Martin; Reichstein, Markus (2008). "Terrestrial ecosystem carbon dynamics and climate feedbacks" (PDF). Nature. 451 (7176): 289–292. Bibcode:2008Natur.451..289H. PMID 18202646. doi:10.1038/nature06591.
- Davidson, Eric A.; Janssens, Ivan A. (2006). "Temperature sensitivity of soil carbon decomposition and feedbacks to climate change". Nature. 440 (7081): 165–173. Bibcode:2006Natur.440..165D. PMID 16525463. doi:10.1038/nature04514.
- Egerton, F. N. (2001). "A history of the ecological sciences: early Greek origins" (PDF). Bulletin of the Ecological Society of America. 82 (1): 93–97.
- Benson, Keith R. (2000). "The emergence of ecology from natural history". Endeavour. 24 (2): 59–62. PMID 10969480. doi:10.1016/S0160-9327(99)01260-0.
- Sober, E. (1980). "Evolution, population thinking, and essentialism". Philosophy of Science. 47 (3): 350–383. JSTOR 186950. doi:10.1086/288942.
- Hughes, J. D. (1985). "Theophrastus as ecologist". Environmental Review. 9 (4): 296–306. JSTOR 3984460. doi:10.2307/3984460.
- Hughes, J. D. (1975). "Ecology in ancient Greece". Inquiry. 18 (2): 115–125. doi:10.1080/00201747508601756.
- Kingsland, S. (2004). "Conveying the intellectual challenge of ecology: An historical perspective" (PDF). Frontiers in Ecology and the Environment. 2 (7): 367–374. ISSN 1540-9295. doi:10.1890/1540-9295(2004)002[0367:CTICOE]2.0.CO;2.[permanent dead link]
- Rosenzweig, M. L. (2003). "Reconciliation ecology and the future of species diversity" (PDF). Oryx. 37 (2): 194–205. doi:10.1017/s0030605303000371.
- Hawkins, B. A. (2001). "Ecology's oldest pattern". Endeavor. 25 (3): 133. doi:10.1016/S0160-9327(00)01369-7.
- McIntosh, R. P. (1985). The Background of Ecology: Concept and Theory. Cambridge University Press. p. 400. ISBN 0-521-27087-1.
- Stauffer, R. C. (1957). "Haeckel, Darwin and ecology". The Quarterly Review of Biology. 32 (2): 138–144. doi:10.1086/401754.
- Friederichs, K. (1958). "A definition of ecology and some thoughts about basic concepts". Ecology. 39 (1): 154–159. JSTOR 1929981. doi:10.2307/1929981.
- Hinchman, L. P.; Hinchman, S. K. (2007). "What we owe the Romantics". Environmental Values. 16 (3): 333–354. doi:10.3197/096327107X228382.
- Goodland, R. J. (1975). "The tropical origin of ecology: Eugen Warming's jubilee". Oikos. 26 (2): 240–245. JSTOR 3543715. doi:10.2307/3543715.
- Egerton, F. N. (2007). "A history of the ecological sciences, part 23: Linnaeus and the economy of nature". Bulletin of the Ecological Society of America. 88 (1): 72–88. ISSN 0012-9623. doi:10.1890/0012-9623(2007)88[72:AHOTES]2.0.CO;2.
- Kormandy, E. J.; Wooster, Donald (1978). "Review: Ecology/economy of nature—synonyms?". Ecology. 59 (6): 1292–1294. JSTOR 1938247. doi:10.2307/1938247.
- Hector, A.; Hooper, R. (2002). "Darwin and the first ecological experiment". Science. 295 (5555): 639–640. PMID 11809960. doi:10.1126/science.1064815.
- Sinclair, G. (1826). "On cultivating a collection of grasses in pleasure-grounds or flower-gardens, and on the utility of studying the Gramineae". London Gardener's Magazine. 1. New-Street-Square: A. & R. Spottiswoode. p. 115.
- May, R. (1999). "Unanswered questions in ecology". Philosophical Transactions of the Royal Society B. 354 (1392): 1951–1959. PMC . PMID 10670015. doi:10.1098/rstb.1999.0534.
- Darwin, Charles (1859). On the Origin of Species (1st ed.). London, UK: John Murray. p. 1. ISBN 0-8014-1319-2.
- Meysman, F. J. R.; Middelburg, Jack J.; Heip, C. H. R. (2006). "Bioturbation: A fresh look at Darwin's last idea". Trends in Ecology and Evolution. 21 (22): 688–695. PMID 16901581. doi:10.1016/j.tree.2006.08.002.
- Acot, P. (1997). "The Lamarckian cradle of scientific ecology". Acta Biotheoretica. 45 (3–4): 185–193. doi:10.1023/A:1000631103244.
- Forbes, S. (1887). "The lake as a microcosm" (PDF). Bulletin of the Scientific Association. Peoria, IL: 77–87.
- Hunt, Caroline Louisa (1912). The life of Ellen H. Richards (1st ed.). Boston: Whitcomb & Barrows.
- Clements, F. E. (1905). Research methods in ecology. Lincoln, Neb.: University Pub. Comp. ISBN 0-405-10381-6.
- Simberloff, D. (1980). "A succession of paradigms in ecology: Essentialism to materialism and probalism". Synthese. 43: 3–39. doi:10.1007/BF00413854.
- Gleason, H. A. (1926). "The individualistic concept of the plant association" (PDF). Bulletin of the Torrey Botanical Club. 53 (1): 7–26. JSTOR 2479933. doi:10.2307/2479933. Archived from the original (PDF) on 22 July 2011.
- Foster, J. B.; Clark, B. (2008). "The sociology of ecology: ecological organicism versus ecosystem ecology in the social construction of ecological science, 1926–1935" (PDF). Organization & Environment. 21 (3): 311–352. doi:10.1177/1086026608321632. Archived from the original (PDF) on 9 May 2013.
- Allee, W. C. (1932). Animal Life and Social Growth. Baltimore: The Williams & Wilkins Company and Associates.
- Cook, R. E. (1977). "Raymond Lindeman and the trophic-dynamic concept in ecology" (PDF). Science. 198 (4312): 22–26. Bibcode:1977Sci...198...22C. PMID 17741875. doi:10.1126/science.198.4312.22.
- Odum, E. P. (1968). "Energy flow in ecosystems: A historical review". American Zoologist. 8 (1): 11–18. JSTOR 3881528. doi:10.1093/icb/8.1.11.
- Ghilarov, A. M. (1995). "Vernadsky's biosphere concept: an historical perspective". The Quarterly Review of Biology. 70 (2): 193–203. JSTOR 3036242. doi:10.1086/418982.
- Itô, Y. (1991). "Development of ecology in Japan, with special reference to the role of Kinji Imanishi". Journal of Ecological Research. 6 (2): 139–155. doi:10.1007/BF02347158.
- Carson, R. (2002). Silent Spring. Houghton Mifflin Company. p. 348. ISBN 0-618-24906-0.
- Palamar, C. R. (2008). "The justice of ecological restoration: Environmental history, health, ecology, and justice in the United States" (PDF). Human Ecology Review. 15 (1): 82–94.
- Krebs, J. R.; Wilson, J. D.; Bradbury, R. B.; Siriwardena, G. M. (1999). "The second Silent Spring" (PDF). Nature. 400 (6745): 611–612. Bibcode:1999Natur.400..611K. doi:10.1038/23127. Archived from the original (PDF) on 31 March 2013.
- Ecology (Stanford Encyclopedia of Philosophy)
- The Nature Education Knowledge Project: Ecology
- Ecology Journals List of ecological scientific journals
- Ecology Dictionary - Explanation of Ecological Terms
- Basic Terms of Ecology
- Canadian Society for Ecology and Evolution
- Ecological Society of America
- Ecology Global Network
- Ecological Society of Australia
- British Ecological Society
- Ecological Society of China
- International Society for Ecological Economics
- European Ecological Federation
- UN Millennium Ecosystem Assessment
- The Encyclopedia of Earth – Wilderness: Biology & Ecology
- Ecology and Society - A journal of integrative science for resilience and sustainability
- Science Aid: Ecology, U.K. High School (GCSE, Alevel) Ecology