Ecology (from Greek: οἶκος, "house" ; -λογία, "study of") is the interdisciplinary scientific study of the interactions between organisms and their environment.[1] Ecology is also the study of ecosystems. Ecosystems describe the web or network of relations among organisms at different scales of organization. Since ecology refers to any form of biodiversity, ecologists can conduct research on the smallest bacteria to the the global flux of atmospheric gases that are regulated by photosynthesis and respiration as organisms breath in and out of the biosphere. Ecology is a recent discipline that emerged from the natural sciences in the late 19th century. Ecology is not synonymous with environment, environmentalism, or environmental science.[1][2][3]
Like many of the natural sciences, a conceptual understanding of ecology is found in the broader details of study, including:
Ecology is distinguished from natural history, which deals primarily with the descriptive study of organisms. It is a sub-discpline of biology, which is the study of life.
There are many practical applications of ecology in conservation biology, wetland management, natural resource management (agriculture, forestry , fisheries), city planning (urban ecology), community health, economics, basic & applied science and it provides a conceptual framework for understanding and researching human social interaction (human ecology).[4][5][6][7]
Levels of organization and study
Ecology is challenged by a constant analytical problem of how to deal with different scales of pattern in space and time. Ecological processes can take decades and even hundreds of years to mature and cover broad geographic areas. Ecologists study ecosystems by sampling a certain number of individuals that are representative of a population. Long-term ecological studies, such as sites managed by the Long Term Ecological Network [1] including the Hubbard Brook study in operation since 1960 [2], provide important ecological track records. Most studies, however, cover only a fraction of the life-span in the development of an ecosystem, such as the different seral stages leading up to an old-growth forest. Ecology is also complicated by the fact that small scale patterns do not necessarily explain large scale phenomena, otherwise captured in the expression 'the sum is greater than the parts'.[8] These emergent phenomena operate at different environmental scales of influence, ranging from molecular to galactic spheres, and require different sets of scientific explanation.[9][10]
To simplify and place the study of ecology into a manageable framework of understanding, the biological world is conceptually organized as a nested hierarchy of individuality, ranging in scale from genes, to cells, to tissues, to organs, to organisms, to species and up to the level of the biosphere.[11] Ecosystems are primarily researched at (but not restricted to) three key levels of organization, including (1) organisms, (2) populations, and (3) communities. Ecosystems consist of communities containing different species of organisms. Communities consist of organisms living in different populations. [12][13] Ecosystem diversity is a part of biodiversity. Biodiversity includes all the varieties and processes of life, including organisms and their genetic differences that are evolutionarily classified into hierarchical, branching and coalescing dimensions.[14][15][16]
Ecological niche
|
We are not here concerned with an imaginary ecology based upon a hypothetical environment inhabited by fancied organisms evolved in some vaguely conceived system of life [...] Instead of dealing with imaginary situations, we are confronted by the ecology of the Earth as we know it, populated by organisms that have evolved here from the basis furnished principally by water, carbon dioxide, and their elements, together with nitrogen.
|
The ecological niche is a central concept in ecology. There are many definitions of the niche dating back to 1917[17], but George Evelyn Hutchinson made conceptual advances on the concept in 1957[18][19] and introduced the most widely accepted definition:
"The niche is the set of biotic and abiotic conditions in which a species is able to persist and maintain stable population sizes."[17]:519
There are two differentiated kinds of ecological niche known as the fundamental and the realized niche. The fundamental niche describes the abiotic conditions under which a species is able to persist. The realized niche is the set of conditions under which a species persists in the context of other resource competitors or predators.[19][17][12] Organisms fit into a particular ecological niche according to their functional traits. A trait is a measurable property of an individual that strongly influences its performance.[20] Moreover, species become specialized within their niche and competitively exclude other species from living in the same geographic area if they fit into the same ecological niche. This is called the competitive exclusion principle.[21] Equally important to the concept of niche is habitat. The habitat describes the environment over which a species is known to occur and the type of community that is formed as a result.[22] For example, habitat might refer to an aquatic versus terrestrial environment that can be further categorized as montane or alpine.
Organisms are subject to environmental pressures, but they are also modifiers of their habitats. The regulatory feedback relationship between organisms and their environment can significantly modify conditions from a local scale (e.g., a pond) to global scale (e.g., Gaia) and they can also modify conditions over time even after an organism has passed away, such as the remnants of an old beaver dam or silica skeleton deposits from marine organisms.[23] This process of ecosystem engineering has also been called niche construction. Ecosystem engineers are defined as:
"...organisms that directly or indirectly modulate the availability of resources to other species, by causing physical state changes in biotic or abiotic materials. In so doing they modify, maintain and create habitats." [24]:373
Although it has long been understood that organisms modify their environment, the ecological engineering concept has stimulated a new appreciation for the degree of modification and the influence organisms have on the ecosystem and evolutionary process.[25][26] The niche construction concept highlights a previously under appreciated feedback mechanism of natural selection imparting forces on the abiotic niche.
"For example, many ant and termite species regulate temperature by plugging nest entrances at night or in the cold, by adjusting the height or shape of their mounds to optimize the intake of the sun’s rays, or by carrying their brood around their nest to the place with the optimal temperature and humidity for the brood’s development."[26]:10242
Population ecology
The first journal publication of the Society of Population Ecology, titled Population Ecology (originally called Researches on Population Ecology), was released in 1952.[3] Population ecology is concerned with the study of groups of organisms that live together in time and space. One of the first laws of population ecology is the Thomas Malthus' exponential law of population growth.[27] This law states that:
"...a population will grow (or decline) exponentially as long as the environment experienced by all individuals in the population remains constant."[27]:18
This simplified premise in population ecology provides the basis for formulating predictive theories and tests that follow. Simplified models in population ecology usually start with four key variables including death, birth, immigration, and emigration. The ecology of populations are simplified in the mathematical models that calculate changes in population demographics and evolution under the assumption (or null hypothesis) of no external influence. Some models can become more mathematically complex where "...several competing hypotheses are simultaneously confronted with the data."[28] For example, in a closed system where immigration and emigration does not take place, the per capita rates of change in a population can be mathematically described as:
dN / dT = B − D = bN − dN = (b − d)N = rN,
where N is the total number of individuals in the population, B is the number of births, D is the number of deaths, b and d are the per capita rates of birth and death respectively, and r is the per capita rate of population change. In simple terms, this formula can be understood as the rate of change in the population (dN/dT) is equal to births minus deaths (B - D).[27][29]
Using these techniques, Malthus' population principal of growth was later transformed into a mathematical model known as the logistic equation:
dN / dT = aN(1 − N / K),
where N is the biomass density, a is the maximum per-capita rate of change, and K is the carrying capacity of the population. The formula can be read as follows, the rate of change in the population (dN/dT) is equal to growth (aN) that is limited by carrying capacity (1-N/K). From these basic mathematical principals the discipline of population ecology expands into a field of investigation that queries the demographics of real populations and tests these results against those of various statistical models. Beyond these, the field of population ecology often uses data on life history and matrix algebra to develop projection matrices on fecundity and survivorship. This kind of information can be used for managing wildlife stocks and harvest quotas [30][29]
These mathematical models introduce two important variables that are commonly invoked in population ecology, namely r (intrinsic rate of natural increase in population size, density independent) and K (carrying capacity of a population, density dependent).[12] These two variables where used in development of the concept of r and K selection. An r-selected species (e.g., many kinds of insects, such as aphids[31]) is one that has high rates of fecundity, low levels of parental investment in the young, and high rates of mortality before individuals reach maturity. In r-selected species evolution favors productivity. In contrast, a K-selected species (such as humans) has low rates of fecundity, high levels of parental investment in the young, and low rates of mortality as individuals develop toward maturity. Evolution in K-selected species favors efficiency in the conversion of resources into fewer offspring.[32][33]
|
Community ecology examines how interactions among species and their environment affect the abundance, distribution and diversity of species within communities. Most theoretical and empirical studies within community ecology ignore genetic variation and evolutionary change within species, and instead assume that species comprise homogeneous non-evolving populations.
—Johnson & Stinchcomb [34]:250
|
Ecosystems are most generally studied at the local or effective community scale, such as measuring primary production in a wetland in relation to decomposition and consumption rates[35] or the analysis of predator-prey dynamics affecting amphibian biomass[36]. The vast majority of research into community ecology examines population dynamics of pairs of species to understand how entire communities function. Two conceptual models that have been used in understanding community ecology include food webs and trophic levels.[37][38]
Food webs
A schematic illustration of a salamander food-web in a pond.
Early naturalists in the 16th-18th century realized the importance of food and feeding as an agent of transfer for energy and nutrients among species. They determined that the supply ultimately depended upon plants converting energy from the sun into organic matter. Food webs are a type of concept map that is used for understanding real pathways in the series of ecological events usually starting with solar energy being photosynthesized in plants. Plants grow and accumulate nutrients that are in turn eaten by grazing herbivores and step by step the lines are drawn and until the web of life is illustrated.[39][40]
The first person to fully elaborate and place the concept of food chains into a scientific framework was Charles Elton in his classical book 'Animal Ecology'.[41] Elton[41] defined ecological relations using concepts of food-chains, food-cycles, food-size, and described numerical relations among different functional groups and their relative abundance. Elton's term 'food-cycle' was replaced by 'food-web' in a subsequent ecological text[42]. Elton's book broke conceptual ground by illustrating complex ecological relations through simpler food-web diagrams.[39] Food-webs are an effective way to conceptually illustrate and teach about the interactive links among species in a community.[43][44]
There are different dimensions in ecological communities that can be used to create more complicated food-webs, including: species composition (type of species), richness (number of species), biomass (the dry weight of plants and animals), productivity (rates of conversion of energy and nutrients into growth), and stability (food-webs over time). A food-web diagram illustrating species composition shows how a change in one single species can directly and indirectly influence many others. Microcosm studies are used to simplify food-web research into semi-isolated units such as small springs, decaying logs and cowpats. Principals gleaned from these food-web microcosm studies are used to extrapolate smaller dynamic concepts to larger systems.[45] Food-chain length is an important parameter in describing larger food-web dynamics and is defined as:
"The number of transfers of energy or nutrients from the base to the top of a food web..."[46]:269
There are different ways of calculating food-chain length depending on what parameters of the food-web dynamic are being considered: connectance, energy, or interaction.[46] Hence, in a simple predator-prey example a deer is one step removed from the plants it eats (chain length = 1) and a wolf that eats the deer is two steps removed (chain length = 2). The relative amount or strength of influence that these parameters have on the food-web are used to address questions about:
- the identity or existence of a few dominant species (called strong interactors or keystone species)
- the total number of species and food-chain length (including many weak interactors) and
- how community structure, function and stability is determined.[45]
Trophic dynamics
Links in food-webs relate of primary importance to feeding relations or trophism (The Greek root of the word troph, τροφή, trophē, means food or feeding). Elton[41] noted how important an influence the feeding relations had on ecosystem structure. He proposed that ecosystems naturally sort into a ‘pyramid of numbers’ when the relative abundance of each functional group is stacked into their respective trophic levels.
Functional groups are broadly categorized as autotrophs (e.g., plants), heterotrophs (e.g., deer, wolves), and detrivores (e.g., bacteria, fungi). It is not always entirely clear what creatures belong in what group. Some organisms are omnivores, meaning they eat both plant and animal tissues and don't fit neatly into a category. However, it has been suggested that omnivores have a greater functional ecosystem influence as predators because relative to herbivores they are comparatively inefficient at grazing.[47]
Trophic levels are part of the holistic or systems view of ecosystems. Each trophic level contains different species that share common ecological functions. Different species, such as ferns and lillys, are grouped very differently from an evolutionary view of their ecology, but functionally they both photosynthesize the sun's energy and classified as autotrophs. Grouping these functionaly similar species into a trophic system gives a macroscopic image of the larger functional design. Trophic levels are abstractions of the system, but they explain real phenomena. For example, the autotrophs have the highest global proportion of biomass, followed closely behind by microbes (prokaryotes - decomposers), then heterotrophs.[48][49] Functional trophic groups sort out hierarchically into pyramidic trophic levels because it requires specialized adaptations to become a photosynthesizer or a predator, but rarely are their organisms having a skillful combination of both functional abilities. Hence, functional adaptations to trophism (feeding) organizes different species into emergent functional groups.[47]
Two reconstructions of fossilized food-web ecosystems also illustrating trophic levels sorted vertically. Primary producers are at the base as red spheres, predator's are at the top as yellow spheres, and the lines represent feeding links. Original food-webs (on the left) are simplified on the right panels by aggregating groups that feed on the same foods into trophic species. S: number of species (nodes). L: number of trophic links. C: connectance; L/S2. MaxTL: maximum trophic level of a species in the web.
[50]
Functional groups are usually depicted in hierarchical schemes with three or more trophic levels including primary producers (autotrophs) and levels of heterotrophic consumers including the herbivores (primary consumers), predators (secondary consumers), predators that eat predators (tertiary consumers), and ultimately ending at the detrivores in the soil ecosystems.[51] The pyramidal arrangement of trophic levels is a consistent feature across ecosystems with the primary producers having the larger base and consumer densities and amounts of energy decreasing as species become further removed from the photosynthetic source of production.[52] The size of each level in the pyramid generally represents biomass, which is often measured as the dry weight of an organism.[51] Trophic levels and food webs can be used to depict and calculate mathematical and statistical parameters such as those used in other kinds of network analysis, including graph theory.[53]
Food-web links point to direct trophic relationships among species, but there are also indirect effects that can alter the abundance, distribution, or biomass in the trophic levels. For example, predators eating herbivores indirectly influence the control and regulation of primary production in plants. Although the predators do not eat the plants directly, they regulate the population of herbibores that are directly linked to plant trophism. The net effect of direct and indirect relations is called trophic cascades. Trophic cascades are separated into species-level cascades, where only a subset of the food-web dynamic is impacted by a change in population numbers, and community-level cascades, where a change in population numbers has a dramatic effect on the entire food-web, such as the distribution of plant biomass.[54]
The keystone species concept is closely aligned to species-level cascades, where a single species occupies a particularly strong node in the food-web and its removal results in the collapse of the food-web structure and extinction of other species. Sea otters (Enhydra lutris) are the classical example of a keystone species because they limit the density of 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.[55] Hunting of sea otters, for example, is thought to have indirectly lead to the extinction of the Steller's Sea Cow (Hydrodamalis gigas).[56] While the keystone species concept has been used extensively as a conservation tool, it has been criticized for being poorly defined. Different ecosystems express different complexities and so it is unclear how applicable and general the keystone species model can be applied. To better understand the keystone species and trophic cascade models, ecologists conduct removal experiments to measure the relative impact, strength and influence of interaction among different species on community dynamics.[54][55]
Biosphere
The largest scale of ecological organization is the total sum of every ecosystem on the planet and the atmosphere it regulates, which is called the biosphere. Ecological relations regulate the flux of energy, nutrients, and climate all the way up to the planetary scale. For example, the dynamic history of the planetary CO2 and O2 composition of the atmosphere has been largely regulated by the biogenic flux of gases coming from respiration and photosynthesis with levels fluctuating in time and in relation to the ecology and evolution of plants and animals.[57] When sub-component parts, such as the full variety of ecosystems diversifying the planet, are organized into a whole there are oftentimes identifiable properties or characteristics that describe the nature of the system under investigation. Ecological theory has been used to explain self emergent regulatory phenomena at the planetary scale. This is known as the Gaia hypothesis[10]. The Gaia hypothesis is an example of holism in ecology because it tests for principals relating to an evolving and self regulating planetary ecosystem that requires different explanations than those governing ecosystems at a smaller scale.[58]
Ecology and evolution
Ecology and evolution are considered sister disciplines. Ecology and evolution are academic branches of the life sciences. Natural selection, life history, development, adaptation, populations, and inheritance all play an prominent conceptual roles in ecological as well as evolutionary theory. Both disciplines also employ genetics in their investigations. For example, morphological, behavioural and/or genetic traits can be mapped onto evolutionary trees to study principals of inheritance that relates back to the ecology of adaptations. Ecology and evolution are scientifically connected because they both study hierarchies, networks, relations, and kinship among genes, cells, individuals, communities, species, and the biosphere.[59] The two disciplines often appear together, such as in the title of the journal Trends in Ecology and Evolution.[60] There is no sharp dichotomous boundary that separates ecology from evolution and 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.[61][10][62] While the boundary between ecology and evolution is not always clear, it is understood that ecology studies the abiotic and biotic factors that influence the evolutionary process.[2][51]
Behavioral ecology
Behavioural ecology is the field of study concerned with ethology and its implications to broader ecological theory. Adaptation is the central unifying concept in behavioral ecology.[4] Behaviors can be recorded as traits and inherited in much the same way that eye and hair color can. As such, behaviors are subject to the forces of natural selection.[63] Hence, behaviors can be adaptive in nature, meaning that they evolved and serve a functional utility such as enhancing ones opportunity to successfully reproduce and increase fitness.[64] Fitness is measured in terms of reproductive success. An animal with behaviors that afford it some degree of leverage in the struggle for existence such that it survives to pass on its heritable traits to its offspring is considered fit if the adaptation succeeds and propagates more of its kind in subsequent generations. A measure of fitness is the numerical differential and representation in frequency of a trait over subsequent generations.[63]
Predator-prey interactions are a fundamental and introductory concept in food-web studies as well as behavioural ecology.[65] 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 predatory threats, organisms must balance their energy budgets as they invest in different aspects of their life history, such as feeding, mating, socializing, or modifying their habitat. Hypotheses posited in behavioural ecology are generally based on adaptive principals of conservation or efficiency. For example,
"The threat-sensitive predator avoidance hypothesis predicts that prey should assess the degree of threat posed by different predators and match their behavior according to current levels of risk."[66]
"The 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."[67]
The behaviour of long-toed salamanders (Ambystoma macrodactylum) present another example in this context. When threatened, the long-toed salamander will defend itself by waving its tail and secreting a white milky fluid.[68][69] The excreted fluid is distasteful, toxic and adhesive, but it is also used for nutrient and energy storage during hibernation. Hence, salamanders subjected to frequent predatory attack will be energetically compromised as they use up their energy stores.[70] [71] Some species are also able to avoid predators altogether, such as small velvet gecko's (Oedura lesueurii). This species is specially adapted to smell the body chemicals of snakes that linger after they pass through an area, even though snakes rarely pose a significant danger.[66]
A often quoted hypothesis in behavioural ecology is known as Lack's brood reduction hypothesis, which posits an evolutionary and ecological explanation as to why birds often lay a series of eggs with an asynchronous delay such that the young are of mixed age and weights. According to Lack, this brood-reducation behaviour is a sort of ecological insurance that allows some birds to survive in poor years and all birds to survive when food is plentiful.[72][73]
"The clutch size of each species of bird is characteristic, and in general seems adapted to correspond with the largest number of young which can be successfully raised. Probably there is a small hereditary variation, which is explicable through rather larger clutches being favoured in some years and rather smaller clutches in other years."[74]:333
Elaborate sexual displays and posturing are often encountered in the behavioural ecology of animals. Many birds, for example, display elaborate ornaments during courtship. These displays serve a dual purpose of signalling healthy or well-adapted individuals and good genes. The elaborate displays are driven by sexual selection as the displays serve as an advertisment of quality traits in sexual partners.[75]
Biogeography
Main article:
Biogeography
As the name implies, biogeography is an amalgamation of the words biology and geography. The word was first coined by the German geographer, Friedrich Ratzel in 1891.[76] The Journal of Biogeography was established in 1974 and publishes "...papers dealing with all aspects of spatial, ecological and historical biogeography."[5]Biogeography and ecology share much of the same disciplinary roots. For example, the theory of island biogeography, elucidated by Robert MacArthur and E. O. Wilson in 1967[32] is considered one of the fundamentals of ecological theory.[77]
Biogeography has a long and rich history in the natural sciences where questions arise concerning the spatial distribution of plants and animals. Ecology and evolution provides the explanatory context for biogeographical studies.[76] Biogeographical patterns result from ecological processes that influences dispersal (or dispersion)[77] and from historical processes that split populations or species into different areas.[78] The biogeographic processes that result in the natural splitting of species explains much of the modern distribution of the Earth's biota. This area of focus is called vicariance biogeography and it is a sub-discipline of biogeography. It is a separate discipline because it specifically studies the branching, phylogenetic, or speciation process in evolutionary studies and explains much of the patterns in biodiversity across the globe.[78][79][80]
There are many applications in the field of biogeography that concern 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 context of global warming. [81] [82]
Molecular Ecology
There has long been an understanding of the important relationship between ecology and genetic inheritance.[2] This branch of research became more feasible with the development of genetic technologies, such as the polymerase chain reaction (PCR), and through the publication Molecular Ecology starting in 1992.[83] Molecular ecology uses various analytical techniques to study genes in evolutionary and ecological context. In 1994, professor John Avise played a leading role in popularizing this field of study through the publication of his book, Molecular Markers, Natural History and Evolution .[84] Newer genetic technologies made genetic sampling of organisms simpler and engendered a new and collaborative research paradigm that investigates and probes ecological questions that were otherwise intractable. Molecular ecology revealed previously obscured details in the intricacies of nature and improved resolution into probing questions about behavioural and biogeographical ecology. For example, molecular ecology revealed promiscuous sexual behaviour that is driven by female choice in pocket gophers [85] and multiple male partners in tree swallows previously thought to be socially monogamous.[86] In a biogeographical context, the marriage between genetics, ecology and evolution created a new sub-discipline called phylogeography.[87]
Ecology and the environment
The environment is external yet interlinked directly with ecology. Chemistry, temperature, pressure, gravity, energy, and sunlight are properties of Earth's environment that are relevant to ecology. Environmental and ecological relations are often studied through conceptually and practically manageable parts. However, once the effective environmental components are understood they conceptually link as a holocoenotic[6] system.
Ecology is often misused as a synonym for environment, but it differs from environmental studies, for example, because it is one of the few academic disciplines dedicated to holism.[9] The environment describes all factors and scales of study that are external to an organism, including abiotic factors such as temperature, radiation, light, chemistry, climate and geology, and biotic factors, including genes, cells, organisms, members of the same species (conspecifics) and other species that share a habitat.[88] In contrast, ecology focuses on biological relations and studies how these relate to the environment.[9] Ecosystem processes are consistent with the laws of thermodynamics. Armed with an understanding of metabolic and thermodynamic principles, a complete accounting of energy and material flow can be traced through an ecosystem.[89]
Metabolism and the early atmosphere
|
Metabolism – the rate at which energy and material resources are taken up from the environment, transformed within an organism, and allocated to maintenance, growth and reproduction – is a fundamental physiological trait.
|
The Earth's environment has not always remained at a constant temperature and the atmosphere has changed significantly as a result of the gross metabolic activity of life on Earth. There is an evolving feedback loop between the ecological processes of life, geochemistry, and Earth's atmosphere. Proceeding through the early stages of life, major ecological transitions modified the Earth's geochemical cycles. The Earth formed approximately 4.5 billion years ago[91] and environmental conditions were too extreme for life to form for the first 500 million years. During this early Hadean period, the Earth started to cool allowing time for a crust and oceans to form. Environmental conditions were unsuitable for the origins of life until approximately 1 billion years after the Earth formed. The Earth's atmosphere transformed from hydrogen dominant, to one composed mostly of methane, and ammonia. Over the next billion years the metabolic activity of life transformed the atmosphere to higher concentrations 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 in heat. There were untapped sources of free energy within the mixture of reducing and oxidizing gasses that set the stages for primitive ecosystems to evolve and, in turn, the atmosphere also evolved.[92]
One of the earliest organisms was likely an anaerobic methanogen microbe that would have converted atmospheric hydrogen into methane (4H2 + CO2 → CH4 + 2H2O). Anoxygenic photosynthesis converting hydrogen sulfide into other sulfur compounds or water (2H2S + CO2 → hv → CH2O → H2O → + 2S or 2H2 + CO2 + hv → CH2O + H2O), as occurs in deep sea hydrothermal vents today, would have also reduced hydrogen and increased atmospheric methane. Early forms of fermentation would have also been a component of the primitive ecology producing higher levels of atmospheric methane. The transition to an oxygen dominant atmospheric transition did not begin until approximately 2.4-2.3 billion years ago, but photosynthetic processes had started 0.3 to 1 billion years prior. Hence, the transition to an oxygen environment was ecologically latent.[93] The evolution of the Earth's ecosystems demonstrates how smaller scale metabolic processes of life can regulate larger scale environmental phenomena, such as the Earth's atmosphere. This relationship has led to the development of the Gaia hypothesis, which states that there is a feedback process generated by living organisms that maintains the temperature of the Earth and atmospheric conditions within a narrow self-regulating range of tolerance. Hence, the gross ecology of the planet acts as a single regulatory or holistic unit called Gaia.[10]
Radiation: light, heat, and temperature
Almost all aspects of functional ecology is effected indirectly or directly by radiant energy from the sun. There are different wavelengths of electromagnetic energy emanating from the sun that provides inputs into the ecological energy budget of the planet. 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.[2][51][89]
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 also relate importantly and differently affects two metabolic divisions in animals, poikilotherms, having a body temperature that is largely regulated and dependent on the temperature of the external environment, and homeotherms, having a body temperature that is internally regulated and maintained by expending metabolic energy.[2][51][89]
Light is the primary source of energy on the planet. 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 are responsible for primary production and the assimilation of light energy that becomes metabolically stored as potentional energy in biochemical enthalpic bonds. Heterotrophs feed on autotrophs for their supply of energy and nutrients. Hence, there is a relationship between light, production, and supplies of energy that affects the distribution, composition and structure of ecosystem dynamics across the planet.[2][51][89]
Physical environments
Water
The rate of diffusion of carbon dioxide and oxygen is approximately 10,000 times slower in water than it is in air. When soils become flooded, they quickly loose oxygen from low-concentration (hypoxic) to an (anoxic) environment where anaerobic bacteria thrive among the roots[94]. Aquatic plants exhibit a wide variety of morphological and physiological adaptations that allow them to survive, compete and diversify these environments. For example, the roots and stems develop large cellular air spaces to allow for the efficient transportation gases (for example, CO2 and O2) used in respiration and photosynthesis. In drained soil, microorganisms use oxygen during respiration. In aquatic environments, anaerobic soil microorganisms use nitrate, manganic ions, ferric ions, sulfate, carbon dioxide and some organic compounds. 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 methanogen bacteria. Salt water also requires special physiological adaptations to deal with water loss. Salt water plants (or halophytes) are able to osmo-regulate their internal salt (NaCl) concentrations or develop special organs for shedding salt away.[94]. The physiology of fish is also specially adapted to deal with high levels of salt through osmoregulation. Their gills form electrochemical gradients that mediate salt excrusion in salt water and uptake in fresh water.[95]
Wetland conditions such as shallow water, high plant productivity, and anaerobic substrates provide a suitable environment for important physical, biological, and chemical processes. Because of these processes, wetlands play a vital role in global nutrient and element cylcles. :29[94]
|
Gravity
The shape and energy of the land is affected to a large degree by gravitational forces. On a larger scale, the distribution of gravitational forces on the earth are uneven and influence the shape and movement of tectonic plates as well as having an influence on geomorphic processes such as orogeny and erosion. These forces govern some of the geo-physical properties and distributions of biomes across the Earth. On a organism scale, gravitational forces provide directional cues for plant and fungal growth (gravitropism), orientation cues for animal migrations, and influences the biomechanics and size of animals.[2]
Pressure
Pressure effects the environment and the organism. It acts as a mechanical force with close connections to gravity causing increased levels of pressure moving toward the Earth. Pressure exerts significant influence over the atmosphere, climate, water environments, and on smaller scale there are osmotic forces at work. Organisms are physiologically sensitive and adapted to atmospheric and osmotic water pressures.[2] Water transportation through trees, for example, is an important eco-physiological parameter.[96][97] Water pressure in the depths of oceans requires adaptations to deal with the different living conditions. Mammals, such as whales, dolphins and seals require special adaptations to deal with the change in sound due to water pressure differences.[98] Climatic and osmotic pressure places physiological constraints on organisms, such as flight and respiration at high altitudes, or diving to deep ocean depths. These constraints influence vertical limits of ecosystems in the biosphere.[2]
Wind and turbulence
Turbulent forces in air and water have significant effects on the environment and ecosystem distribution, form and dynamics. On a planetary scale, ecosystems are affected by circulation patterns in the global trade winds. Locally, wind power and the turbulent forces it creates can influence heat, nutrient, and biochemical profiles of ecosystems.[2] For example, winds running over the surface of lakes winds creates turbulence that stirs the water column and influences the environmental profile to create thermally layered zones that partially governs how the fish, algae, and other parts of the aquatic ecology are structured.[99][100] Wind speed and turbulence also exert influence on rates of evapotranspiration rates and energy budgets in plants and animals [94][101]
Fire
Main article:
Fire ecology
Plants spew oxygen into the atmosphere. Approximately 350 million years ago the photosynthetic process brought atmospheric oxygen levels above 17% in concentration, which allowed for the combustion of fire.[102] 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 in management.[103] While the issue of fire in relation to ecology and plants has been recognized for a long time[104], Charles Cooper brought attention to the issue of forest fires in relation to the ecology of forest fire suppression and management in the 1960s.[105][106] The association for fire ecology launched a journal, "Fire Ecology", in 2005 that is specifically devoted to the study of fire ecology and management.[7].
Fire creates environmental mosaics and a patchiness to ecosystem age and canopy structure. 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.[107] Most ecosystem are adapted to some level of natural fire cycles. Plants, for example, are equipped with a variety of special adaptations to deal with forest fires. The altered state of soil nutrient supply and cleared canopy structure creates a new niche for seedling establishment.[108][109] Some species (e.g., Pinus halepensis) cannot germinate until after their seeds have lived through a fire. This environmental trigger for seedlings is called serotiny.[110] Some compounds from smoke also promote seed germination.[111]
Biogeochemistry
Ecologists study and measure nutrient budgets to understand how these materials are regulated and flow through the environment.[2][51][89] This research has led to an understanding that there is a global feedback between ecosystems and the physical parameters of this planet including minerals, soil, pH, ions, water and atmospheric gases. There are six major elements, including H (hydrogen), C (carbon), N (nitrogen), O (oxygen), S (sulfur), and P (phosphorus) that 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.[112]
The ecology of global carbon budgets gives one example of the linkage between biodiversity and biogeochemistry. For starters, the ocean is estimated to hold 40,000 Gt carbon, vegetation and soil is estimated to hold 2070 Gt carbon, and fossil fuel emissions are estimated to emit an annual flux of 6.3 Gt carbon.[113] At different times in the Earth's history there has been major restructuring in these global carbon budgets that was regulated to a large extent by the ecology of the land. For example, through the early-mid Eocene volcanic out gassing, the oxidation of methane stored in wetlands, seafloor gases and/or combinations thereof increased CO2 concentrations to levels as high as 3500 ppm.[114] In the Oligocene, from 25 to 32 million years ago, there was another significant restructuring in the global carbon cycle as grasses evolved a special type of C4 photosynthesis and expanded their ranges. This new photosynthetic pathway evolved in response to the drop in atmospheric CO2 concentrations below 550 ppm.[115] Ecosystem functions such as these feed back significantly into global atmospheric models for carbon cycling. Loss in the abundance and distribution of biodiversity causes global carbon cycle feedbacks that are expected to increase rates global warming in the next century.[116] Global warming melting large sections of permafrost creates a new mosaic of flooded areas where decomposition emits methane (CH4). Hence, there is a relationship between global warming, decomposition and respiration in soils and wetlands producing significant climate feedbacks and alters global biogeochemical cycles.[117][118] There is concern over methane increases in the atmosphere in context of the carbon cycle, because methane is also a greenhouse gas that is 23 times more effective at absorbing long-wave radiation on a 100 year time scale.[119]
Historical roots of ecology
In the early 20th century, ecology was called scientific natural history and was influenced by the analytical precision of Newtonian sciences.[120] A comprehensive historical account of ecology is a complicated task because ecology is one of the most diverse of the scientific disciplines.[121] Several published books provide extenstive coverage of the classics.[122][123] The term "ecology" (German: Oekologie) is a more recent scientific development and was first coined by the German biologist Ernst Haeckel in his book Generelle Morpologie der Organismen (1866). The definition offered by Haeckel appeared in the frontispiece of the classical text Principles of Animal Ecology.[2]
|
By ecology we mean the body of knowledge concerning the economy of nature-the investigation of the total relations of the animal both to its inorganic and its organic environment; including, above all, its friendly and inimical relations with those animals and plants with which it comes directly or indirectly into contact-in a word, ecology is the study of all those complex interrelations referred to by Darwin as the conditions of the struggle of existence.
—Haeckel's definition quoted in Esbjorn-Hargens [124]:6
|

While some mark Haeckel's definition as the beginning of ecology, others posit that the science of ecology began with Carl Linnaeus' research principals on the economy of nature that matured in the early 18th century.[125][39] The works of Carl Linnaeus influenced Darwin as evidenced by his reference to ecology through his adopted usage of Linnaeus' phrase economy or polity of nature in The Origin of Species.[126] Ernst Haeckel was strongly influenced by Darwin's work, defined ecology in reference to the economy of nature and this has lead some to question if ecology is synonymous with Linnaeus' concepts for the economy of nature.[125] Some have suggested that ecology started with Alexander von Humbolt (1809-1882), who was also admired by Charles Darwin.[120] Baron Humbolt was among the first to recognize ecological gradients and alluded to the modern law of species to area relationships in ecology.[127][128]
The modern synthesis of ecology is a young science that flourished and attracted much research attention around the same time as evolutionary studies at the end of the 19th century. However, many observations, interpretations and discoveries relating to ecology extend back to much earlier studies in natural history. For example, the concept on the balance or regulation of nature can be traced back to Herodotos (died c. 425 BC) who described an early account of mutualism along the Nile river where crocodiles open their mouths to beneficially allow sandpipers safe access to pluck leaches away.[121]. In the broader contributions to the historical development of the ecological sciences, Aristotle is considered one of the earliest naturalists who had a highly influential role in the philosophical development of ecological sciences. One of Aristotle's students, Theophrastus, made astute ecological observations about plants and posited a philosophical stance about the autonomous relations between plants and their environment that is more in line with modern ecological thought. Both Aristotle and Theophrastus made extensive observations on plant and animal migrations, biogeography, physiology, and their habits in what might be considered a modern analog of the ecological niche.[129][130]
Carl Linnaeus (1707–1778), a well known naturalist also holds a prominent place in the history of ecological sciences as he invented the first branch of ecological study he called the economy of nature.[39] Linnaeus was one of the first to attempt to define on the balance of nature, which had previously been held as an assumption rather than formulated as a testable hypothesis. From Aristotle to Darwin, however, the natural world was predominantly considered static and unchanged since its original creation. Hence, there was little appreciation and understanding for the dynamic and reciprocal relations between organisms, their adaptations and modifications to the environment.[131][124]
Nowhere can one see more clearly illustrated what may be called the sensibility of such an
organic complex,--expressed by the fact that whatever affects any species belonging to it, must speedily have its influence of some sort upon the whole assemblage. He will thus be made to see the impossibility of studying any form completely, out of relation to the other forms,--the necessity for taking a comprehensive survey of the whole as a condition to a satisfactory
understanding of any part.
—Stephen Forbes (1887) [132]
|
While Charles Darwin is most notable for his treatise on evolution[133], he was also a notable and astute ecologist as he meticuously researched earthworms in relation to soil ecology[134] and in The Origin of Species he made note of the very first ecological experiment that was published in 1816.[135][136] In the science leading up to Darwin the notion of evolving species was gaining popular support. This scientific paradigm changed the way that researchers approached the ecological sciences.
The first American ecology book was published in 1905 by Frederic Clements.[137] Frederic Clements forwarded the idea of plant communities as a superorganism. According to this premise, single species populations could be classified, using identifiable plant associations, into larger superorganism entities that were believed to progress through regular and determined stages of seral development analogous to developmental stages of a single organism. Not until the 1970's had the Clementsian paradigm been overthrown by the Gleasonian paradigm [138] which emphasized the overriding role of individual organisms and their life histories in the development of community associations.[139]
Notable pioneers and their contributions to ecology.
| Notable figure |
Lifespan |
Major contribution & citation |
| Carl Linnaeus |
1707–1778 |
Influential naturalist, inventor of science on the economy of nature[39][125] |
| Alexander Humboldt |
1769–1859 |
First to describe ecological gradient of latitudinal biodiversity increase toward the tropics[8] in 1807[128] |
| Charles Darwin |
1809-1882 |
Founder of evolution by means of natural selection, founder of ecological studies of soils[133][134] |
| Herbert Spencer |
1820–1903 |
Early founder of social ecology, coined the phrase 'survival of the fittest'[125][140] |
| Karl Möbius |
1825-1908 |
First to develop concept of ecological community, biocenosis, or living community[141][142][143] |
| Ernst Haeckel |
1834-1919 |
Invented the term ecology, popularized research links between ecology and evolution[124][126] |
| Victor Hensen |
1835-1924 |
Invented term plankton, developed quantitative and statistical measures of productivity in the seas[126] |
| Eugenius Warming |
1841-1924 |
Early founder of Ecological Plant Geography[144] |
| Stephen Forbes |
1844–1930 |
Early founder of entomology and ecological concepts in 1887[9][145][132] |
| Henry C. Cowles |
1869-1939 |
Pioneering studies and conceptual developing in ecological succession[146] |
| Arthur G. Tansley |
1871–1955 |
First to coin the term ecosystem in 1936 and notable researcher[147][142][148] |
| Charles Christopher Adams |
1873-1955 |
Animal ecologist, biogeographer, author of first American book on animal ecology in 1913, founded ecological energetics[149][150] |
| Frederic Clements |
1874-1945 |
Authored the first influential American ecology book in 1905[138] |
| Victor Ernest Shelford |
1877-1968 |
Founded physiological ecology, pioneered food-web and biome concepts, founded The Nature Conservancy[151][152] |
| Henry Gleason |
1882-1975 |
Early ecology pioneer, quantitative theorist, author, and founder of the individualistic concept of ecology[153][138] |
| Charles S. Elton |
1900-1991 |
'Father' of animal ecology, pioneered food-web & niche concepts and authored influential Animal Ecology text[154][151] |
| G. Evelyn Hutchinson |
1903-1991 |
Limnologist and conceptually advanced the niche concept[155][156][157] |
| Eugene P. Odum |
1913-2002 |
Co-founder of ecosystem ecology and ecological thermodynamic concepts[148][151][158][159] |
| Howard T. Odum |
1924–2002 |
Co-founder of ecosystem ecology and ecological thermodynamic concepts[148][151][160][161][158][159] |
See also
Lists
Notes
- ^ a b c Begon, M.; Townsend, C. R., Harper, J. L. (2006). Ecology: From individuals to ecosystems. (4th ed.). Blackwell. ISBN 1405111178.
- ^ a b c d e f g h i j k l m n Allee, W.; Emerson, A. E., Park, O., Park, T., and Schmidt, K. P. (1949). Principles of Animal Ecology. W. B. Saunders Company. ISBN 0721611206.
- ^ a b Smith, R.; Smith, R. M. (2000). Ecology and Field Biology. (6th ed.). Prentice Hall. ISBN 0321042905.
- ^ Omerod, S.J.; Pienkowski, M.W.; Watkinson, A.R. (1999). "Communicating the value of ecology". Journal of Applied Ecology 36: 847–855.
- ^ Phillipson, J.; Lowe, P.; Bullock, J.M. (2009). "Navigating the social sciences: interdisciplinarity and ecology". Journal of Applied Ecology 46: 261–264.
- ^ Steward T. A. Pickett, Mary L. Cadenasso, J. Morgan Grove, Peter M. Groffman, Lawrence E. Band, Christopher G. Boone, William R. Burch Jr., C. Susan B. Grimmond, John Hom, Jennifer C. Jenkins, Neely L. Law, Charles H. Nilon, Richard V. Pouyat, Katalin Szlavecz, Paige S. Warren, Matthew A. Wilson (2008). "Beyond Urban Legends: An Emerging Framework of Urban Ecology, as Illustrated by the Baltimore Ecosystem Study". BioScience 58: 139–150.
- ^ Aguirre, A.A. (2009). "Biodiversity and Human Health". EcoHealth. doi:10.1007/s10393-009-0242-0.
- ^ Schneider, D. D. (2001), "[The Rise of the Concept of Scale in Ecology The Rise of the Concept of Scale in Ecology]", BioScience 51 (7): 545–553, The Rise of the Concept of Scale in Ecology
- ^ a b c Odum, E. P. (1977). "The emergence of ecology as a new integrative discipline". Science 195: 1289–1293.
- ^ a b c d Lovelock, J. (2003). "The living Earth". Nature 426 (6968): 769–770. doi:10.1038/426769a. PMID 14685210.
- ^ Nachtomy, Ohad; Shavit, Ayelet; Smith, Justin (2002), "Leibnizian organisms, nested individuals, and units of selection", Theory in Biosciences 121 (2), http://www.springerlink.com/content/25625863427113r0/
- ^ a b c Begon, M.; Townsend, C. R.; Harper, J. L. (2006), Ecology: From Individuals to Ecosystems (4th ed.), Oxford, UK: Blackwell Publishing, ISBN 978-1-4051-1117-1, http://books.google.ca/books?id=Lsf1lkYKoHEC&printsec=frontcover&dq=ecology&lr=&as_drrb_is=b&as_minm_is=0&as_miny_is=2004&as_maxm_is=0&as_maxy_is=2009&as_brr=0&client=firefox-a&cd=1#v=onepage&q=&f=false
- ^ Zak, K. M.; Munson, B. H. (2008), "An Exploratory Study of Elementary Preservice Teachers’ Understanding of Ecology Using Concept Maps.", The Journal of Environmental Education 39 (3): 32–46, http://www.duluth.umn.edu/~kgilbert/ened5560-1/Readings/SciEd-JEESpring2008-ZakMunsonArticleUpdated.pdf
- ^ Edward O.Wilson, editor, Frances M.Peter, associate editor, Biodiversity, National Academy Press, March 1988 ISBN 0-309-03783-2 ; ISBN 0-309-03739-5 (pbk.), online edition
- ^ Noss, R.; Cooperrider, A. (1994), Saving Natures Legacy: Protecting and Restoring Biodiversity, Washington, DC: Island Press
- ^ Margulis, Lynn (1992). "Biodiversity: molecular biological domains, symbiosis and kingdom origins". Biosystems 28 (1-3): 107–108. http://www.sciencedirect.com/science?_ob=ArticleURL&_udi=B6T2K-49NY23W-65&_user=10&_rdoc=1&_fmt=&_orig=search&_sort=d&_docanchor=&view=c&_searchStrId=1142524797&_rerunOrigin=scholar.google&_acct=C000050221&_version=1&_urlVersion=0&_userid=10&md5=5993d10eb706481d7d7358a3dd9e06c8.
- ^ a b c Wiens, J. J.; Graham, C. H. (2005), "Integrating Evolution, Ecology, and Conservation Biology", Annual Review of Ecology, Evolution, and Systematics 36: 519–539, http://life.bio.sunysb.edu/ee/grahamlab/pdf/Wiens_Graham_AnnRev2005.pdf
- ^ Hutchinson, G. E. (1957). A Treatise on Limnology.. New York: Wiley & Sons.. pp. 1015. ISBN 0471425729.
- ^ a b Hutchinson, G. E. (1957). "Concluding remarks.". Cold Spring Harb Symp Quant Biol 22: 415–427. http://symposium.cshlp.org/content/22/415.full.pdf+html.
- ^ McGill, B. J.; Enquist, B. J.; Weiher, E.; Westoby, M. (2006). "Rebuilding community ecology from functional traits". Trends in Ecology and Evolution 21 (4): 178–185.
- ^ Hardin, G. (1960). "The competitive exclusion principal.". Science 131 (3409): 1292–1297. doi:10.1126/science.131.3409.1292.
- ^ Whittaker, R. H.; Levin, S. A.; Root, R. B. (1973). "Niche, Habitat, and Ecotope". The American Naturalist 107 (955): 321–338. http://www.jstor.org/stable/2459534?seq=6.
- ^ Hastings, A. Byers, J. E., Crooks, J. A., Cuddington, K., Jones, C. J., Lambrinos, J. G., Talley, T. S. and Wilson, W. G., A; Byers, JE; Crooks, JA; Cuddington, K; Jones, CG; Lambrinos, JG; Talley, TS; Wilson, WG (2007). "Ecosystem engineering in space and time". Ecology Letters 10 (2): 153–164. doi:10.1111/j.1461-0248.2006.00997.x. PMID 17257103.
- ^ Jones, Clive G.; Lawton, John H.; Shachak, Moshe (1994). "Organisms as ecosystem engineers". Oikos 69 (3): 373–386. 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: 203–209. doi:10.1641/0006-3568(2006)056[0203:TCOOAE]2.0.CO;2.
- ^ a b Laland, K. N.; Odling-Smee, F.J.; Feldman, M.W. (1999). "Evolutionary consequences of niche construction and their implications for ecology". PNAS 96 (18): 10242–10247. doi:10.1073/pnas.96.18.10242. PMID 10468593.
- ^ a b c Turchin, P. (2001), "Does Population Ecology Have General Laws?", Oikos 94 (1): 17–26
- ^ Johnson, J. B.; Omland, K. S. (2004), "Model selection in ecology and evolution.", Trends in Ecology and Evolution 19 (2): 101–108, http://www.usm.maine.edu/bio/courses/bio621/model_selection.pdf
- ^ a b 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.
- ^ Whitham, T. G. (1978). "Habitat Selection by Pemphigus Aphids in Response to Response Limitation and Competition". Ecology 59 (6): 1164–1176.
- ^ a b MacArthur, R.; Wilson, E. O. (1967), The Theory of Island Biogeography, Princeton, NJ: Princeton University Press
- ^ Pianka, E. R. (1972). "r and K Selection or b and d Selection?". The American Naturalist 106 (951): 581–588.
- ^ 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.
- ^ 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.
- ^ Davic, R. D.; Welsh, H. H. (2004). "On the Ecological Role of Salamanders". Annual Review of Ecology and Systematics 35: 405–434.
- ^ Paine, R. T. (1980), "Food Webs: Linkage, Interaction Strength and Community Infrastructure", Journal of Animal Ecology 49 (3): 667–685, http://www.jstor.org/stable/4220
- ^ Abrams, P. A. (1993), "Effect of Increased Productivity on the Abundances of Trophic Levels", The American Naturalist 141 (3): 351–371, http://www.jstor.org/stable/2462676?seq=1
- ^ a b c d e Egerton, Frank N. (2007). "Understanding Food Chains and Food Webs, 1700–1970". Bulletin of the Ecological Society of America 88: 50–69. 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.", Proc. R. Soc. B 273: 1–9, doi:10.1098/rspb.2005.3377, http://rspb.royalsocietypublishing.org/content/273/1582/1.full.pdf+html
- ^ a b c Elton, C. S. (1927). Animal Ecology. London, UK.: Sidgwick and Jackson.
- ^ Allee, W. C. (1932). Animal life and social growth. Baltimore: The Williams & Wilkins Company and Associates.
- ^ Edwards, J.; Fraser, K. (1983), "Concept maps as reflectors of conceptual understanding.", Research in science education 13: 19–26, http://www.springerlink.com/content/64x512327l427467/
- ^ Pimm, S. L. (2002). Food webs. Chicago: The University of Chicago Press.
- ^ a b 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.
- ^ a b Post, D. M. (1993). "The long and short of food-chain length". Trends in Ecology and Evolution 17 (6): 269–277. doi:10.1016/S0169-5347(02)02455-2.
- ^ a b Oksanen, L. (1991). "Trophic levels and trophic dynamics: A consensus emerging?". Trends in Ecology and Evolution 6 (2): 58–60. doi:10.1016/0169-5347(91)90124-G.
- ^ Whitman, W. B.; Coleman, D. C.; Wieb, W. J. (1998). "Prokaryotes: The unseen majority". Proc. Natl. Acad. Sci. USA 95: 6578–6583. http://www.pnas.org/content/95/12/6578.full.pdf.
- ^ Groombridge, B.; Jenkins, M. (2002), World atlas of biodiversity: earth's living resources in the 21st century, World Conservation Monitoring Centre, United Nations Environment Programme, ISBN 0-520-23688-8, http://books.google.ca/books?id=_kHeAXV5-XwC&printsec=frontcover&source=gbs_navlinks_s#v=onepage&q=biomass&f=false
- ^ Dunne JA, Williams RJ, Martinez ND, Wood RA, Erwin DH, Jennifer A.; Williams, Richard J.; Martinez, Neo D.; Wood, Rachel A.; Erwin, Douglas H.; Dobson, Andrew P. (2008). "Compilation and Network Analyses of Cambrian Food Webs.". PlosBiol 6 (4): e102. doi:10.1371/journal.pbio.0060102.
- ^ a b c d e f g Rickleffs, Robert, E. (1996). The Economy of Nature. University of Chicago Press. pp. 678. ISBN 0716738473.
- ^ Raffaelli, D. (2002). "From Elton to Mathematics and Back Again". Science 296 (5570): 1035–1037. doi:10.1126/science.1072080. PMID 12004106.
- ^ Proulx, Stephen R.; Promislow, Daniel E.L.; Phillips, Patrick C. (2005). "Network thinking in ecology and evolution". Trends in Ecology and Evolution 20 (6): 345–353. doi:10.1016/j.tree.2005.04.004. PMID 16701391.
- ^ a b Polis, G.A.; Sears, A.L.W.; Huxel, G.R.; Strong, D.R.; Maron, J. (2000). "When is a trophic cascade a trophic cascade?". Trends in Ecology and Evolution 15 (11): 473–475. doi:10.1016/S0169-5347(00)01971-6. PMID 11050351. http://www.cof.orst.edu/leopold/class-reading/Polis%202000.pdf.
- ^ a b Mills, L.S.; Soule, M.E.; Doak, D.F. (1993). "The Keystone-Species Concept in Ecology and Conservation". BioScience 43 (4): 219–224. doi:10.2307/1312122.
- ^ Anderson, P.K. (1995). "Competition, predation, and the evolution and extinction of Stellar's sea cow, Hydrodamalis gigas". Marine Mammal Science 11 (3): 391–394. doi:10.1111/j.1748-7692.1995.tb00294.x.
- ^ Igamberdiev, Abir U.; Lea, P. J. (2006). "Land plants equilibrate O2 and CO2 concentrations in the atmosphere.". Photosynthesis Research 87 (2): 177–194. http://www.mun.ca/biology/igamberdiev/PhotosRes_CO2review.pdf.
- ^ Margulis, L. (1973). "Atmospheric homeostasis by and for the biosphere: the gaia hypothesis.". Tellus 26: 2–10. http://people.uncw.edu/borretts/courses/BIO60209/Lovelock%20Margulis%201974%20atmospheric%20homeostasis%20by%20and%20for%20the%20biosphere%20-%20the%20gaia%20hypothesis.pdf.
- ^ 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. http://arjournals.annualreviews.org/doi/abs/10.1146/annurev.es.24.110193.003103.
- ^ Trends in Ecology and Evolution. Official Cell Press page the journal. Elsevier, Inc. 2009
- ^ Vrba, E. S.; Eldredge, N. (1984), "Individuals, Hierarchies and Processes: Towards a More Complete Evolutionary Theory", Paleobiology 10 (2): 146–171, http://www.jstor.org/stable/2400395
- ^ Gould, S.J.; Lloyd, E.A. (1999). "Individuality and adaptation across levels of selection: How shall we name and generalize the unit of Darwinism?". Proceedings of the National Academy of Science 96 (21): 11904–11909. doi:10.1073/pnas.96.21.11904.
- ^ a b Wilson, E. O. (2000). Sociobiology: The New Synthesis (25th aniversary Ed. ed.). President and Fellows of Harvard College. ISBN 978-0674000896. http://books.google.ca/books?id=v7lV9tz8fXAC&printsec=frontcover&dq=sociobiology&client=firefox-a&cd=2#v=onepage&q=&f=false.
- ^ Gould, Stephen, J.; Vrba, Elizabeth, S. (1982). "Exaptation-a missing term in the science of form.". Paleobiology 8 (1): 4–15.
- ^ Ives, A. R.; Cardinale, B. J.; Snyder, W. E. (2004), "A synthesis of subdisciplines: predator–prey interactions, and biodiversity and ecosystem functioning", Ecology Letters 8 (1): 102–116, http://www.lifesci.ucsb.edu/eemb/labs/cardinale/pdfs/ives_ecol_lett_2005.pdf
- ^ a b 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
- ^ Cooper, W. E.; Frederick, W. G. (2010), "Predator lethality, optimal escape behavior, and autotomy", Behavioral Ecology 21 (1): 91–96, http://library.unbc.ca:3000/cgi/content/abstract/21/1/91
- ^ Fukomoto J. (1995). Long-toed salamander (Ambystoma macrodactylum) ecology and management in Waterton Lakes National Park. The University of Calgary, Thesis or Dissertation, M.E.Des.
- ^ Toledo RC, Jared C. (1995). Cutaneous granular glands and amphibian venoms. Comparative Biochemistry and Physiology Part A: Physiology 111(1):1–29. Abstract
- ^ Williams TA, Larsen JH Jr. (2005). New function for the granular skin glands of the eastern long-toed salamander, Ambystoma macrodactylum columbianum. Journal of Experimental Zoology 239(3): 329–333.
- ^ Grant JB, Evans JA. (2007). A technique to collect and assay adhesive-free skin secretions from Ambystomatid salamanders. Herpetological Review 38(3):301–305.
- ^ Amundsen, T.; Slagsvold, T. (1996), "Lack's Brood Reduction Hypothesis and Avian Hatching Asynchrony: What's Next?", Oikos 76 (3): 613–620
- ^ Pijanowski, B. C. (1992), "A Revision of Lack's Brood Reduction Hypothesis", The American Naturalist 139 (6): 1270–1292
- ^ Lack, D. (1956), "Variations in the Reproductive Rate of Birds", Proceedings of the Royal Society of London. Series B, Biological Sciences 145 (920): 329–333, http://www.jstor.org/stable/82998
- ^ Kodric-Brown, A.; Brown, J. H. (1984), "Truth in advertising: The kinds of traits favored by sexual selection", The American Naturalist 124 (3): 309–323, http://dbs.umt.edu/courses/biol406/readings/Wk6-Kodric-Brown%20and%20Brown%201984.pdf
- ^ a b 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, http://books.google.ca/books?id=K1GU_1I6bG4C&printsec=frontcover&source=gbs_v2_summary_r&cad=0#v=onepage&q=&f=false
- ^ a b Wiens, J. J.; Donoghue, M. J. (2004), "Historical biogeography, ecology and species richness", Trends in Ecology and Evolution 19 (12): 639–644, http://www.phylodiversity.net/donoghue/publications/MJD_papers/2004/144_Wiens_TREE04.pdf
- ^ a b Croizat, L.; Nelson, G.; Rosen, D. E. (1974), "Centers of Origin and Related Concepts", Systematic Zoology 23 (2): 265–287, http://www.jstor.org/stable/2412139
- ^ Wiley, E. O. (1988), "Vicariance Biogeography", Annual Review of Ecology and Systematics 19: 513–542, http://www.jstor.org/stable/2097164
- ^ Morrone, J. J.; Crisci, J. V. (1995), "Historical Biogeography: Introduction to Methods", Annual Review of Ecology and Systematics 26: 373–401, http://arjournals.annualreviews.org/doi/abs/10.1146/annurev.es.26.110195.002105
- ^ 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, http://www3.interscience.wiley.com/journal/122574329/abstract
- ^ Svenning, Jens-Christian; Condi, R. (2008), "Biodiversity in a Warmer World", Science 322 (5899): 206–207, http://www.sciencemag.org/cgi/content/full/322/5899/206
- ^ http://www3.interscience.wiley.com/journal/117989598/home]
- ^ Avise, J. (1994). Molecular Markers, Natural History and Evolution. Kluwer Academic Publishers. ISBN 0-412-03771-8. http://books.google.ca/books?id=2zYnQfnXNr8C&printsec=frontcover&dq=john+avise+molecular&client=firefox-a&cd=1#v=onepage&q=&f=false.
- ^ Patton, J. L., and Smith, M. F. (1993). Molecular evidence for mating asymmetry and female choice in a pocket gopher (Thomomys) hybrid zone. Molecular Ecology, 2, 3-8.
- ^ O'Brian, E.; Dawson, R. (2007). "Context-dependent genetic benefits of extra-pair mate choice in a socially monogamous passerine". Behav Ecol Sociobiol 61: 775–782. doi:10.1007/s00265-006-0308-8. http://web.unbc.ca/~dawsonr/2007_bes61_775-782.pdf.
- ^ Avise, J. (2000). Phylogeography: The History and Formation of Species. President and Fellows of Harvard College. ISBN 0-674-66638-0. http://books.google.ca/books?id=lA7YWH4M8FUC&printsec=frontcover&dq=phylogeography&client=firefox-a&cd=1#v=onepage&q=&f=false.
- ^ Campbell, Neil A.; Brad Williamson; Robin J. Heyden (2006). Biology: Exploring Life. Boston, Massachusetts: Pearson Prentice Hall. ISBN 0-13-250882-6. http://www.phschool.com/el_marketing.html.
- ^ a b c d e Kormondy, E. (1995). Concepts of ecology. (4th ed.). Benjamin Cummings. ISBN 0134781163.
- ^ Ernst, S. K. Morgan; Enquist, Brian J.; Brown, James H.; Charnov, E. L.; Gillooly, J. F.; Savage, Van M.; et al. (2003). "Thermodynamic and metabolic effects on the scaling of production and population energy use". Ecology Letters 6: 990–995. doi:10.1046/j.1461-0248.2003.00526.x. https://www.msu.edu/~maurerb/Ernest_etal_2003.pdf.
- ^ Allègre, Claude J.; Manhès, Gérard; Göpel, Christa (1995). "The age of the Earth". Geochimica et Cosmochimica Acta 59: 1455–1456. http://www.sciencedirect.com/science?_ob=ArticleURL&_udi=B6V66-3YYTKC0-7Y&_user=10&_rdoc=1&_fmt=&_orig=search&_sort=d&_docanchor=&view=c&_searchStrId=1001748320&_rerunOrigin=scholar.google&_acct=C000050221&_version=1&_urlVersion=0&_userid=10&md5=c2e364efb25d1f6a73686ae3e7701b26.
- ^ Wills, C.; Bada, J. (2001). The Spark of Life: Darwin and the Primeval Soup. Cambridge, Massachusetts: Perseus Publishing. http://books.google.ca/books?id=UrGqxy0wMdkC&dq=The+Spark+of+Life:+Darwin+and+the+Primeval+Soup&printsec=frontcover&source=bl&ots=cpuX3xktry&sig=2ySEa55w1ca6yXXZcEf_fJovq_4&hl=en&ei=F7miSpqBAo6uswO3v4CNDw&sa=X&oi=book_result&ct=result&resnum=1#v=onepage&q=&f=false.
- ^ Catling, D. C.; Claire, M. W. (2005). "How Earth’s atmosphere evolved to an oxic state: A status report". Earth and Planetary Science Letters 237: 1–20. doi:10.1016/j.epsl.2005.06.013. http://www.atmos.washington.edu/~davidc/papers_mine/Catling2005-EPSL.pdf.
- ^ a b c d Cronk, J. K.; Fennessy, M. S. (2001), Wetland Plants: Biology and Ecology, Washington, D.C.: Lewis Publishers, ISBN 1-56670-372-7, http://books.google.ca/books?id=FNI1GFbH2eQC&printsec=frontcover&dq=wetland+plants&client=firefox-a&cd=1#v=onepage&q=&f=false
- ^ Evans, D. H.; Piermarini, P. M.; Potts, W. T. W. (1999), "Ionic Transport in the Fish Gill Epithelium", Journal of Experimental Zoology 283: 641–652, http://people.biology.ufl.edu/devans/DHEJEZ.pdf
- ^ Wheeler, T. D.; Stroock, A. D. (2008). "The transpiration of water at negative pressures in a synthetic tree". Nature 455: 208–212. http://www.nature.com/nature/journal/v455/n7210/abs/nature07226.html.
- ^ Pockman, W. T.; Sperry, J. S.; O'Leary, J. W. (1995). "Sustained and significant negative water pressure in xylem". Nature 378: 715–716. http://www.nature.com/nature/journal/v378/n6558/abs/378715a0.html.
- ^ Kastak, D.; Schusterman, R. J. (1998), "Low-frequency amphibious hearing in pinnipeds: Methods, measurements, noise, and ecology", J. Acoust. Soc. Am. 103 (4): 2216–2228, http://www.sea-inc.net/resources/lrni_KastakandSchusterman_JASA_LFpinnipedhearing_1998.pdf
- ^ Shimeta, J.; Jumars, P. A.; Lessard, E. J. (1995). "Influences of turbulence on suspension feeding by planktonic protozoa; experiments in laminar shear fields". Limnolology and Oceanography 40 (5): 845–859. http://www.aslo.org/lo/toc/vol_40/issue_5/0845.pdf.
- ^ Etemad-Shahidi, A.; Imberger, J. (2001). "Anatomy of turbulence in thermally stratified lakes". Limnolology and Oceanography 46 (5): 1158–1170. http://nospam.aslo.org/lo/toc/vol_46/issue_5/1158.pdf.
- ^ 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): 2228–236, http://www.jstor.org/stable/2265716
- ^ Lenton, T. M.; Watson, A. (2000), "Redfield revisited 2. What regulates the oxygen content of the atmosphere.", Global biogeochemical cycles 14 (1): 249–268, http://lgmacweb.env.uea.ac.uk/esmg/papers/Redfield_revisited_2.pdf
- ^ Lobert, J. M.; Warnatz, J. (1993), Crutzen, P. J.; Goldammer, J. G., eds., Emissions from the combustion process in vegetation., John Wiley & Sons, ISBN 0471936049, 9780471936046, http://jurgenlobert.org/papers_data/Lobert.Warnatz.Wiley.1993.pdf
- ^ Garren, K. H. (1943), "Effects of Fire on Vegetation of the Southeastern United States", Botanical Review 9 (9): 617–654, http://www.springerlink.com/content/a70310371q6l1414/
- ^ Cooper, C. F. (1960), "Changes in Vegetation, Structure, and Growth of Southwestern Pine Forests since White Settlement", Ecological Monographs 30 (2): 130–164, http://www.jstor.org/stable/1948549
- ^ Cooper, C. F. (1961), "The ecology of fire", Scientific American 204: 150–160
- ^ van Wagtendonk, Jan W. (2007), "History and Evolution of Wildland Fire Use", Fire Ecology Special Issue 3 (2): 3–17, http://fireecology.net/Journal/pdf/Volume03/Issue02/003.pdf
- ^ Boerner, R. E. J. (1982), "Fire and Nutrient Cycling in Temperate Ecosystems", BioScience 32 (3): 187–192, http://www.jstor.org/stable/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, http://www.springerlink.com/content/w28p341482tj4g4w/
- ^ 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
- ^ Flematti, Gavin R.; Ghisalberti, Emilio L.; Dixon, Kingsley W.; Trengove, R. D. (2004), "A Compound from Smoke That Promotes Seed Germination", Science 305. no. 5686, p. 977 (5686): 977, http://www.ice.mpg.de/main/news/positions/itb-004/DixonSmokepaper.pdf
- ^ Falkowski, P. G.; Fenchel, T.; Delong, E. F. (2008). "The microbial engines that drive Earth’s biogeochemical cycles". Science 320. http://www.sciencemag.org/cgi/reprint/320/5879/1034.pdf.
- ^ Grace, J. (2004). "Understanding and managing the global carbon cycle". Journal of Ecology 92: 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", Nature 406: 695–699, http://paleolands.com/pdf/cenozoicCO2.pdf
- ^ 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: 600–603, http://earth.geology.yale.edu/~mp364data/Pagani.Science.2005.pdf
- ^ Cox, P. M.; Betts, R. A.; Jones, C. D.; Spall, S. A.; Totterdell, I. J. (2000), "Acceleration of global warming due to carbon-cycle feedbacks in a coupled climatemodel", Nature 408: 184–187, https://www.up.ethz.ch/education/biogeochem_cycles/reading_list/cox_etal_nat_00.pdf
- ^ Heimann, Martin; Reichstein, Markus (2008), "Terrestrial ecosystem carbon dynamics and climate feedbacks", Nature 451: 289–292, http://courses.washington.edu/ocean450/Discussion_Topics_Papers/Heinmann_clim_chng_08.pdf
- ^ Davidson, Eric A.; Janssens, Ivan A. (2006), "Temperature sensitivity of soil carbon decomposition and feedbacks to climate change", Nature 440: 165–173, http://whrc.org/resources/published_literature/pdf/DavidsonetalNature.06.pdf
- ^ Zhuan, Q.; Melillo, J. M.; McGuire, A. D.; Kicklighter, D. W.; Prinn, R. G.; Steudler, P. A. (2007), "Net emission of CH4 and CO2 in Alaska: Implications for the region's greenhouse gas budget.", Ecological Applications 17 (1): 203–212, http://picea.sel.uaf.edu/manuscripts/zhuang07-ea.pdf
- ^ a b Kingsland, S. (2004), "Conveying the intellectual challenge of ecology: an historical perspective", Front Ecol Environ 2 (7): 367–374, http://www.isa.utl.pt/dbeb/ensino/txtapoio/HistEcology.pdf
- ^ a b Egerton, F. N. (2001). "A History of the Ecological Sciences: Early Greek Origins". Bulletin of the Ecological Society of America 82 (1): 93–97. http://www.jstor.org/stable/20168519?seq=1.
- ^ Keller, D. R.; Golley, F. B. (2000), The philosophy of ecology: from science to synthesis., Athens, GA: University of Georgia Press, ISBN 978-0820322209, http://books.google.ca/books?id=uYOxUAJThJEC&pg=PP1&dq=The+philosophy+of+ecology:+from+science+to+synthesis.&client=firefox-a&cd=1#v=onepage&q=&f=false
- ^ Real, L. A.; Brown, J. H. (1992), Foundations of ecology: classic papers with commentaries., Chicago: University of Chicago Press, ISBN 978-0226705941, http://books.google.ca/books?id=y2wwTZgrHmYC&dq=Foundations+of+ecology:+classic+papers+with+commentaries.&client=firefox-a&cd=1
- ^ a b c Esbjorn-Hargens, S. (2005). "Integral Ecology: An Ecology of Perspectives". Journal of Integral Theory and Practice 1 (1): 2–37. http://www.vancouver.wsu.edu/fac/tissot/IU_Ecology_Intro.pdf.
- ^ a b c d Kormandy, E. J. (1978). "Review: Ecology/Economy of Nature--Synonyms?". Ecology 59 (6): 1292–1294. http://www.jstor.org/pss/1938247.
- ^ a b c Stauffer, R. C. (1957), "Haeckel, Darwin and ecology.", The Quarterly Review of Biology 32 (2): 138–144, http://www.clt.astate.edu/aromero/ECO3.Haeckel.pdf
- ^ Rosenzweig, M.L. (2003). "Reconciliation ecology and the future of species diversity". Oryx 37 (2): 194–205. http://eebweb.arizona.edu/COURSES/Ecol302/Lectures/ORYXRosenzweig.pdf.
- ^ a b Hawkins, B. A. (2001). "Ecology's oldest pattern.". Endeavor 25 (3): 133. http://www4.ncsu.edu/~rrdunn/Hawkins%202001.pdf.
- ^ Hughes, J. D. (1975). "Ecology in ancient Greece". Inquiry 18 (2): 115–125. http://www.informaworld.com/smpp/content~content=a902027058&db=all.
- ^ Hughes, J. D. (1985). "Theophrastus as Ecologist". Environmental Review 9 (4): 296–306. http://www.jstor.org/stable/info/3984460?seq=1.
- ^ Benson, Keith R. (2000). "The emergence of ecology from natural history". Endeavour 24 (2): 59–62. http://www.sciencedirect.com/science?_ob=ArticleURL&_udi=B6V81-414X355-V&_user=1067466&_rdoc=1&_fmt=&_orig=search&_sort=d&_docanchor=&view=c&_searchStrId=1143381236&_rerunOrigin=scholar.google&_acct=C000051249&_version=1&_urlVersion=0&_userid=1067466&md5=07093484296081185c20fff99e870aab.
- ^ a b Forbes, S. (1887). "The lake as a microcosm". Bull. of the Scientific Association (Peoria, IL : .): 77–87. http://www.uam.es/personal_pdi/ciencias/scasado/documentos/Forbes.PDF.
- ^ a b Darwin, Charles (1859). On the Origin of Species (1st ed.). London: John Murray. p. 1. http://darwin-online.org.uk/content/frameset?itemID=F373&viewtype=text&pageseq=16.
- ^ a b 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, http://www.marbee.fmns.rug.nl/pdf/marbee/2006-Meysman-TREE.pdf
- ^ Hector, A.; Hooper, R. (2002). "Darwin and the First Ecological Experiment". Science 295: 639–640.
- ^ Acot, P. (1997). "The Lamarckian Cradle of Scientific Ecology". Acta Biotheoretica 45 (3-4): 185–193.
- ^ Clements, F. E. (1905). Research Methods in Ecology. Lincoln, Nebraska: University Publ..
- ^ a b c Simberloff, D. (1980). "A succession of paradigms in ecology: Essentialism to materialism and probalism.". Synthese 43 (1980) 3-39: 3–39.
- ^ Gleason, H. A. (1926). "The Individualistic Concept of the Plant Association". Bulletin of the Torrey Botanical Club 53 (1): 7–26. http://www.ecologia.unam.mx/laboratorios/comunidades/pdf/pdf%20curso%20posgrado%20Elena/Tema%201/gleason1926.pdf.
- ^ Futuyma, D. J. (2005). The Nature of Natural Selection. Ch. 8, pages 93-98 in Cracraft, J. and Bybee R. W. (Eds.) Evolutionary Science and Society: Educating a New Generation. American Institute of Biological Sciences.
- ^ Glaubrecht, M. (2008), "Homage to Karl August Möbius (1825-1908) and his contributions to biology: zoologist, ecologist, and director at the Museum für Naturkunde in Berlin", Zoosystematics and Evolution 84 (1): 9–30, http://www3.interscience.wiley.com/journal/117944310/abstract
- ^ a b Baker, H. G. (1966). "Resoning about adaptations in ecosystems". BioScience 16 (1): 35–37. http://www.jstor.org/pss/1293551.
- ^ Nyhart, L. K. (1998). "Civic and Economic Zoology in Nineteenth-Century Germany: The "Living Communities" of Karl Mobius". Isis 89 (4): 605–630. http://www.jstor.org/pss/236735.
- ^ Coleman, W. (1986). "Evolution into ecology? The strategy of warming's ecological plant geography". Journal of the History of Biology 19 (2): 181–196. http://www.springerlink.com/content/l620506185326641/.
- ^ Forbes, S. A. (1915). "The ecological foundations of applied entomology". Annals of the Entomological Society of America 8 (1): 1–19. http://www.uam.es/personal_pdi/ciencias/scasado/documentos/Forbes.PDF.
- ^ Adams, C. C.; Fuller, G. D. (1940), "Henry Chandler Cowles, Physiographic Plant Ecologist", Annals of the Association of American Geographers 31 (1): 39–43, http://www.jstor.org/stable/2561130
- ^ Cooper, W. S. (1957), "Sir Arthur Tansley and the Science of Ecology", Ecology 38 (4): 658–659, http://www.jstor.org/stable/1943136
- ^ a b c Kingsland, S. E. (1994). "Review: The History of Ecology". Journal of the History of Biology 27 (2): 349–357. http://www.springerlink.com/content/m51188130814962k/.
- ^ Ilerbaig, J. (1999), "Allied Sciences and Fundamental Problems: C.C. Adams and the Search for Method in Early American Ecology", Journal of the History of Biology 32: 439–463, http://www.jstor.org/stable/4331545?&Search=yes&term=Adams&term=contributions&term=C.&list=hide&searchUri=%2Faction%2FdoBasicSearch%3FQuery%3DC.%2BC.%2BAdams%2Bcontributions%26wc%3Don%26dc%3DAll%2BDisciplines&item=1&ttl=41072&returnArticleService=showArticle
- ^ Raup, H. M. (1959), "Charles C. Adams, 1873-1955", Annals of the Association of American Geographers 49 (2): 164–167, http://www.jstor.org/stable/2561526?&Search=yes&term=contributions&term=%22Charles+C.+Adams%22&list=hide&searchUri=%2Faction%2FdoBasicSearch%3FQuery%3D%2522Charles%2BC.%2BAdams%2522%2Bcontributions%26gw%3Djtx%26prq%3DCharles%2BC.%2BAdams%2Bcontributions%26Search%3DSearch%26hp%3D25%26wc%3Don&item=1&ttl=113&returnArticleService=showArticle
- ^ a b c d Ellison, A. M. (2006), "What Makes an Ecological Icon.", Bulletin of the Ecological Society of America 87 (4): 380–386, http://www.esajournals.org/doi/abs/10.1890/0012-9623%282006%2987%5B380:WMAEI%5D2.0.CO%3B2
- ^ Kendeigh, S. C. (1968), "Victor Ernest Shelford, Eminent Ecologist, 1968", Bulletin of the Ecological Society of America 49 (3): 97–100, http://www.jstor.org/stable/20165761?&Search=yes&term=%22Victor+Ernest+Shelford%22&term=contributions&list=hide&searchUri=%2Faction%2FdoBasicSearch%3FQuery%3D%2522Victor%2BErnest%2BShelford%2522%2Bcontributions%26gw%3Djtx%26prq%3D%2522Karl%2BM%25C3%25B6bius%2522%2Bcontributions%26Search%3DSearch%26hp%3D25%26wc%3Don&item=5&ttl=33&returnArticleService=showArticle
- ^ McIntosh, R. P. (1975), "H. A. Gleason-"Individualistic Ecologist" 1882-1975: His Contributions to Ecological Theory", 1975 105 (5): 253–278, http://www.jstor.org/stable/2484142
- ^ Southwood, R.; Clarke, J. R. (1999), "Charles Sutherland Elton. 29 March 1900-1 May 1991", Biographical Memoirs of Fellows of the Royal Society 45: 131–146, http://www.jstor.org/stable/770268?seq=1&Search=yes&term=%22Charles+Elton%22&term=contributions&list=hide&searchUri=%2Faction%2FdoBasicResults%3Fhp%3D25%26la%3D%26wc%3Don%26gw%3Djtx%26jcpsi%3D1%26artsi%3D1%26Query%3D%2522Charles%2BElton%2522%2Bcontributions%26sbq%3D%2522Charles%2BElton%2522%2Bcontributions%26prq%3D%2522Charles%2BC.%2BAdams%2522%2Bcontributions%26si%3D26%26jtxsi%3D26&item=29&ttl=233&returnArticleService=showArticle&resultsServiceName=doBasicResultsFromArticle
- ^ Flannery, M. C. (2003), "Evelyn Hutchinson: A Wonderful Mind", The American Biology Teacher 65 (6): 462–467, http://www.jstor.org/stable/4451536?&Search=yes&term=%22Evelyn+Hutchinson%22&term=contributions&list=hide&searchUri=%2Faction%2FdoBasicSearch%3FQuery%3D%2522Evelyn%2BHutchinson%2522%2Bcontributions%26wc%3Don%26dc%3DAll%2BDisciplines&item=2&ttl=273&returnArticleService=showArticle
- ^ Edmondson, Y. H. (1991), "In Memoriam: G. Evelyn Hutchinson, 1903-1991", Limnology and Oceanography 36 (3): 617, http://www.jstor.org/stable/2837527
- ^ Patrick, R. (1994), "George Evelyn Hutchinson (30 January 1903-17 May 1991)", Proceedings of the American Philosophical Society 138 (4): 531–535, http://www.jstor.org/stable/986851
- ^ a b Gunderson, L.; Folke, C.; Lee, M.; Holling, C. S. (2002), "In memory of mavericks.", Conservation Ecology 6 (2): 19, http://www.consecol.org/vol6/iss2/art19/
- ^ a b Rotabi, K. S. (2007), "Ecological Theory Origin from Natural to Social Science of Vice Versa? A Brief Conceptual History for Social Work", Advances in Social Work 8 (1): 113–129, http://journals.iupui.edu/index.php/advancesinsocialwork/article/viewFile/135/136
- ^ Patten, B. C. (1993), "Toward a more holistic ecology, and science: the contribution of H.T. Odum", Oecologia 93 (4): 597–602, http://www.springerlink.com/content/h83l866562302236/
- ^ Ewel, J. J. (2003), "Howard Thomas Odum (1924–2002)", Bulletin of the Ecological Society of America 84 (1): 13–15, http://www.esajournals.org/doi/abs/10.1890/0012-9623%282003%2984%5B13:HTO%5D2.0.CO%3B2
References
- Campbell, Neil A.; Brad Williamson; Robin J. Heyden (2006). Biology: Exploring Life. Boston, Massachusetts: Pearson Prentice Hall. ISBN 0132508826. http://www.phschool.com/el_marketing.html.
- Brinson, M. M., Lugo, A. E. and Brown, S. (1984). Primary Productivity, Decomposition and Consumer Activity in Freshwater Wetlands. Annual Review of Ecology and Systematics, 12, 123-161.
- David, R. D. and Welsh, H. H. (2004). On the ecological role of salamanders. Annual Review of Ecology and Systematics, 35, 405-434
- Gould, S. J. and Lloyd, E. A. (1999). Individuality and adaptation across levels of selection: How shall we name and generalize the unit of Darwinism? Proceedings of the National Academy of Science, 96(21), 11904-11909.[10]
- Haeckel, E. (1866) General Morphology of Organisms; General Outlines of the Science of Organic Forms based on Mechanical Principles through the Theory of Descent as reformed by Charles Darwin. Berlin
- Lovelock, J. (2003). Gaia: The living earth. Nature, 426, 769-770 [11]
- Odum, E. P. (1971) General Principles of Ecology, Third Edition W. B. Suanders Company. pp 17–20
- Odum, E. P. (1977) The emergence of ecology as a new integrative discipline. Science, 195, 1289-1293.
- Warming, E. (1909) Oecology of Plants - an introduction to the study of plant-communities. Clarendon Press, Oxford.
- Whiles, M. R., Lips, K. R., Pringle, C. M., Kilham, S. S., Bixby, R. J., Brenes, R., Connelly, S., Colon-Gaud, J. C., Hunte-Browjn, M., Huryn, A. D., Montgomery, C., and Peterson, S. 2006. The effects of amphibian population declines on the structure and function of Neotropical stream ecosystems. Front Ecol Environ, 4(1), 27–34
External links