Food web

A freshwater aquatic and terrestrial food web.

A food web (or food cycle) depicts feeding connections (what eats what) in an ecological community. Ecologists can broadly lump all life forms into one of two categories called trophic levels: 1) the autotrophs, and 2) the heterotrophs. To maintain their bodies, grow, develop, and to reproduce, autotrophs produce organic matter from inorganic substances, including both minerals and gases such as carbon dioxide. These chemical reactions require energy, which mainly comes from the sun and largely by photosynthesis, although a very small amount comes from hydrothermal vents and hot springs. A gradient exists between trophic levels running from complete autotrophs that obtain their sole source of carbon from the atmosphere, to mixotrophs (such as carnivorous plants) that are autotrophic organisms that partially obtain organic matter from sources other than the atmosphere, and complete heterotrophs that must feed to obtain organic matter. The linkages in a food web illustrate the feeding pathways, such as where heterotrophs obtain organic matter by feeding on autotrophs and other heterotrophs. The food web is a simplified illustration of the various methods of feeding that links an ecosystem into a unified system of exchange. There are different kinds of feeding relations that can be roughly divided into herbivory, carnivory, scavenging and parasitism. Some of the organic matter eaten by heterotrophs, such as sugars, provides energy. Autotrophs and heterotrophs come in all sizes, from microscopic to many tonnes - from cyanobacteria to giant redwoods, and from viruses and bdellovibrio to blue whales.

Charles Elton pioneered the concept of food cycles, food chains, and food size in his classical 1927 book "Animal Ecology"; Elton's 'food cycle' was replaced by 'food web' in a subsequent ecological text. Elton organized species into functional groups, which was the basis for Raymond Lindeman's classic and landmark paper in 1942 on trophic dynamics. Lindeman emphasized the important role of decomposer organisms in a trophic system of classification. The notion of a food web has a historical foothold in the writings of Charles Darwin and his terminology, including an "entangled bank", "web of life", "web of complex relations", and in reference to the decomposition actions of earthworms he talked about "the continued movement of the particles of earth". Even earlier, in 1768 John Bruckner described nature as "one continued web of life".

Food webs are limited representations of real ecosystems as they necessarily aggregate many species into trophic species, which are functional groups of species that have the same predators and prey in a food web. Ecologists use these simplifications in quantitative (or mathematical) models of trophic dynamics. Using these models they can measure and test for generalized patterns in the structure of real food web networks. Ecologists have identified non-random properties in the topographic structure of food webs. Published examples that are used in meta analysis are of variable quality with omissions. However, the number of empirical studies on community webs is on the rise and the mathematical treatment of food webs using network theory had identified patterns that are common to all. Scaling laws, for example, predict a relationship between the topology of food web predator-prey linkages and levels of species richness.

Taxonomy of a food web

A simplified food web illustrating a three trophic food chain (producers-herbivores-carnivores) linked to decomposers. The movement of mineral nutrients is cyclic, whereas the movement of energy is unidirectional and noncyclic. Trophic species are encircled as nodes and arrows depict the links.^[1][2]

Food webs are the road-maps through Darwin's famous 'entangled bank' and have a long history in ecology. Like maps of unfamiliar ground, food webs appear bewilderingly complex. They were often published to make just that point. Yet recent studies have shown that food webs from a wide range of terrestrial, freshwater, and marine communities share a remarkable list of patterns.^[3]:669

Links in food webs map the feeding connections (who eats whom) in an ecological community. Food cycle is the antiquated term that is synonymous with food web. Ecologists can broadly lump all life forms into one of two trophic layers, the autotrophs and the heterotrophs. Autotrophs produce more biomass energy, either chemically without the suns energy or by capturing the suns energy in photosynthesis, than they use during metabolic respiration. Heterotrophs consume rather than produce biomass energy as they metabolize, grow, and add to levels of secondary production. A food web depicts a collection of polyphagous heterotrophic consumers that network and cycle the flow of energy and nutrients from a productive base of self feeding autotrophs.^[3][4][5]

The base or basal species in a food web are those species without prey and can include autotrophs or saprophytic detrivores (i.e., the community of decomposer's in soil, biofilms, and periphyton). Feeding connections in the web are called trophic links. The number of trophic links per consumer is a measure of food web connectance. Food chains are nested within the trophic links of food webs. Food chains are linear (noncyclic) feeding pathways that trace monophagous consumers from a base species up to the top consumer, which is usually a larger predatory carnivore.^[6][7][8]

Linkages connect to nodes in a food web, which are aggregates of biological taxa called trophic species. Trophic species are functional groups that have the same predators and prey in a food web. Common examples of an aggregated node in a food web might include parasites, microbes, decomposers, saprotrophs, consumers, or predators, each containing many species in a web that can otherwise be connected to other trophic species.^[9][10]

Trophic levels

Main article: Trophic level

A trophic pyramid (a) and a simplified community food web (b) illustrating ecological relations among creatures that are typical of a northern Boreal terrestrial ecosystem. The trophic pyramid roughly represents the biomass (usually measured as total dry-weight) at each level. Plants generally have the greatest biomass. Names of trophic categories are shown to the right of the pyramid. Some ecosystems, such as many wetlands, do not organize as a strict pyramid, because aquatic plants are not as productive as long-lived terrestrial plants such as trees. Ecological trophic pyramids are typically one of three kinds: 1) pyramid of numbers, 2) pyramid of biomass, or 3) pyramid of energy.^[4]

Food webs have trophic levels and positions. Basal species, such as plants, form the first level and are the resource limited species that feed on no other living creature in the web. Basal species can be autotrophs or detrivores, including "decomposing organic material and its associated microorganisms which we defined as detritus, micro-inorganic material and associated microorganisms (MIP), and vascular plant material."^[11]:94 Most autotrophs capture the suns energy in chlorophyll, but some autotrophs (the chemolithotrophs) obtain energy by the chemical oxidation of inorganic compounds and can grow in dark environments, such as the sulfur bacterium Thiobacillus, which lives in hot sulfur springs. The top level has top (or apex) predators which no other species kills directly for its food resource needs. The intermediate levels are filled with omnivores that feed on more than one trophic level and cause energy to flow through a number of food pathways starting from a basal species.^[12]

In the simplest scheme, the first trophic level (level 1) is plants, then herbivores (level 2), and then carnivores (level 3). The trophic level is equal to one more than the chain length, which is the number of links connecting to the base. The base of the food chain (primary producers or detrivores) is set at zero.^[3][13] Ecologists identify feeding relations and organize species into trophic species through extensive gut content analysis of different species. The technique has been improved through the use of stable isotopes to better trace energy flow through the web.^[14] It was once thought that omnivory was rare, but recent evidence suggests otherwise. This realization has made trophic classifications more complex.^[15]

Trophic dynamics

The trophic level concept was introduced in a historical landmark paper on trophic dynamics in 1942 by Raymond L. Lindeman. The basis of trophic dynamics is the transfer of energy from one part of the ecosystem to another.^[13][16] The trophic dynamic concept has served as a useful quantitative heuristic, but it has several major limitations including the precision by which an organism can be allocated to a specific trophic level. Omnivores, for example, are not restricted to any single level. Nonetheless, recent research has found that discrete trophic levels do exist, but "above the herbivore trophic level, food webs are better characterized as a tangled web of omnivores."^[15]:612

A central question in the trophic dynamic literature is the nature of control and regulation over resources and production. Ecologists use simplified three trophic position food chain models (producer, carnivore, decomposer). Using these models, ecologists have tested various types of ecological control mechanisms. For example, herbivores generally have an abundance of vegetative resources, which meant that their populations were largely controlled or regulated by predators. This is known as the top-down hypothesis or 'green-world' hypothesis. Alternatively to the top-down hypothesis, not all plant material is edible and the nutritional quality or antiherbivore defenses of plants (structural and chemical) suggests a bottom-up form of regulation or control.^[17][18][19] Recent studies have concluded that both "top-down" and "bottom-up" forces can influence community structure and the strength of the influence is environmentally context dependent.^[20][21] These complex multitrophic interactions involve more than two trophic levels in a food web.^[22]

Another example of a multi-trophic interaction is a trophic cascade, in which predators help to increase plant growth and prevent overgrazing by suppressing herbivores. Links in a food-web illustrate direct trophic relations 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.^[23]

Energy flow and biomass

Main article: Energy flow (ecology)

See also: Ecological efficiency

The Law of Conservation of Mass dates from Antoine Lavoisier's 1789 discovery that mass is neither created nor destroyed in chemical reactions. In other words, the mass of any one element at the beginning of a reaction will equal the mass of that element at the end of the reaction.^[24]:11

Left: Energy flow diagram of a frog. The frog represents a node in an extended food web. The energy ingested is utilized for metabolic processes and transformed into biomass. The energy flow continues on its path if the frog is ingested by predators, parasites, or as a decaying carcass in soil. This energy flow diagram illustrates how energy is lost as it fuels the metabolic process that transform the energy and nutrients into biomass.
Right: An expanded three link energy food chain (1. plants, 2. herbivores, 3. carnivores) illustrating the relationship between food flow diagrams and energy transformity. The transformity of energy becomes degraded, dispersed, and diminished from higher quality to lesser quantity as the energy within a food chain flows from one trophic species into another. Abbreviations: I=input, A=assimilation, R=respiration, NU=not utilized, P=production, B=biomass.^[25]

Food webs depict energy flow via trophic linkages. Energy flow is directional, which contrasts against the cyclic flows of material through the food web systems.^[26] Energy flow "typically includes production, consumption, assimilation, non-assimilation losses (feces), and respiration (maintenance costs)."^[5]:5 In a very general sense, energy flow (E) can be defined as the sum of metabolic production (P) and respiration (R), such that E=P+R.

The mass (or biomass) of something is equal to its energy content. Mass and energy are closely intertwined. However, concentration and quality of nutrients and energy is variable. Many plant fibers, for example, are indigestible to many herbivores leaving grazer community food webs more nutrient limited than detrital food webs where bacteria are able to access and release the nutrient and energy stores.^[27][28] "Organisms usually extract energy in the form of carbohydrates, lipids, and proteins. These polymers have a dual role as supplies of energy as well as building blocks; the part that functions as energy supply results in the production of nutrients (and carbon dioxide, water, and heat). Excretion of nutrients is, therefore, basic to metabolism."^{[28]:1230-1231} The units in energy flow webs are typically a measure mass or energy per m² per unit time. Different consumers are going to have different metabolic assimilation efficiencies in their diets. Each trophic level transforms energy into biomass. Energy flow diagrams illustrate the rates and efficiency of transfer from one trophic level into another and up through the hierarchy.^[29][30]

It is the case that the biomass of each trophic level decreases from the base of the chain to the top. This is because energy is lost to the environment with each transfer as entropy increases. About eighty to ninety percent of the energy is expended for the organism’s life processes or is lost as heat or waste. Only about ten to twenty percent of the organism’s energy is generally passed to the next organism.^[31] The amount can be less than one percent in animals consuming less digestible plants, and it can be as high as forty percent in zooplankton consuming phytoplankton.^[32] Graphic representations of the biomass or productivity at each tropic level are called ecological pyramids or trophic pyramids. The transfer of energy from primary producers to top consumers can also be characterized by energy flow diagrams.^[33]

Food chain

Main article: food chain

A common metric used to quantify food web trophic structure is food chain length. Food chain length is another way of describing food webs as a measure of the number of species encountered as energy or nutrients move from the plants to top predators.^[34]: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.^[34] In its simplest form, the length of a chain is the number of links between a trophic consumer and the base of the web. The mean chain length of an entire web is the arithmetic average of the lengths of all chains in a food web.^[4][12]

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 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.^[35][36]

Ecological pyramids

See also: Ecological pyramid

Top Left: A four level trophic pyramid sitting on a layer of soil and its community of decomposers. Top right: A three layer trophic pyramid linked to the biomass and energy flow concepts. Bottom: Illustration of a range of ecological pyramids, including top pyramid of numbers, middle pyramid of biomass, and bottom pyramid of energy. The terrestrial forest (summer) and the English Channel ecosystems exhibit inverted pyramids.Note: trophic levels are not drawn to scale and the pyramid of numbers excludes microorganisms and soil animals. Abbreviations: P=Predators, C1=Primary consumers, C2=Secondary consumers, C3=Tertiary consumers, S=Saprotrophs.^[4]

In a pyramid of numbers, the number of consumers at each level decreases significantly, so that a single top consumer, (e.g., a polar bear or a human), will be supported by a much larger number of separate producers. There is usually a maximum of four or five links in a food chain, although food chains in aquatic ecosystems are more often longer than those on land. Eventually, all the energy in a food chain is dispersed as heat.^[4]

Ecological pyramids place the primary producers at the base. They can depict different numerical properties of ecosystems, including numbers of individuals per unit of area, biomass (g/m²), and energy (k cal m⁻² yr⁻¹). The emergent pyramidal arrangement of trophic levels with amounts of energy transfer decreasing as species become further removed from the source of production is one of several patterns that is repeated amongst the planets ecosystems.^[2][3][37] The size of each level in the pyramid generally represents biomass, which can be measured as the dry weight of an organism.^[38] Autotrophs may have the highest global proportion of biomass, but they are closely rivaled or surpassed by microbes.^[39][40]

Pyramid structure can vary across ecosystems and across time. In some instances biomass pyramids can be inverted. This pattern is often identified in aquatic and coral reef ecosystems. The pattern of biomass inversion is attributed to different sizes of producers. Aquatic communities are often dominated by producers that are smaller than the consumers that have high growth rates. Aquatic producers, such as planktonic algae or aquatic plants, lack the large accumulation of secondary growth as exists in the woody trees of terrestrial ecosystems. However, they are able to reproduce quickly enough to support a larger biomass of grazers. This inverts the pyramid. Primary consumers have longer lifespans and slower growth rates that accumulates more biomass than the producers they consume. Phytoplankton live just a few days, whereas the zooplankton eating the phytoplankton live for several weeks and the fish eating the zooplankton live for several consecutive years.^[41] Aquatic predators also tend to have a lower death rate than the smaller consumers, which contributes to the inverted pyramidal pattern. Population structure, migration rates, and environmental refuge for prey are other possible causes for pyramids with biomass inverted. Energy pyramids, however, will always have an upright pyramid shape if all sources of food energy are included and this is dictated by the second law of thermodynamics.^[4][42]

Material flux and recycling

Main article: Nutrient cycle

Many of the Earth's elements and minerals (or mineral nutrients) are contained within the tissues and diets of organisms. Hence, mineral and nutrient cycles trace food web energy pathways. Ecologists employ stoichiometry to analyze the ratios of the main elements found in all organisms: carbon (C), nitrogen (N), phosphorus (P). There is a large transitional difference between many terrestrial and aquatic systems as C:P and C:N ratios are much higher in terrestrial systems while N:P ratios are equal between the two systems.^[43][44][45] Mineral nutrients are the material resources that organisms need for growth, development, and vitality. Food webs depict the pathways of mineral nutrient cycling as they flow through organisms.^[4][16] Most of the primary production in an ecosystem is not consumed, but is recycled by detritus back into useful nutrients.^[46] Many of the Earth's microorganisms are involved in the formation of minerals in a process called biomineralization.^[47][48][49] Bacteria that live in detrital sediments create and cycle nutrients and biominerals.^[50] Food web models and nutrient cycles have traditionally been treated separately, but there is a strong functional connection between the two in terms of stability, flux, sources, sinks, and recycling of mineral nutrients.^[51][52]

Kinds of food webs

Food webs are necessarily aggregated and only illustrate a tiny portion of the complexity of real ecosystems. For example, the number of species on the planet are likely in the general order of 10⁷, over 95% of these species consist of microbes and invertebrates, and relatively few have been named or classified by taxonomists.^[53][54][55] It is explicitly understood that natural systems are 'sloppy' and that food web trophic positions simplify the complexity of real systems that sometimes overemphasizing many rare interactions. Most studies focus on the larger influences where the bulk of energy transfer occurs.^[17] "These omissions and problems are causes for concern, but on present evidence do not present insurmountable difficulties."^[3]:669

Paleoecological studies can reconstruct fossil food-webs and trophic levels. Primary producers form the base (red spheres), predators at top (yellow spheres), the lines represent feeding links. Original food-webs (left) are simplified (right) by aggregating groups feeding on common prey into coarser grained trophic species.^[56]

There are different kinds or categories of food webs:

• Source web - one or more node(s), all of their predators, all the food these predators eat, and so on.
• Sink web - one or more node(s), all of their prey, all the food that these prey eat, and so on.
• Community (or connectedness) web - a group of nodes and all the connections of who eats whom.
• Energy flow web - quantified fluxes of energy between nodes along links between a resource and a consumer.^[3][38]
• Paleoecological web - a web that reconstructs ecosystems from the fossil record.^[56]
• Functional web - emphasizes the functional significance of certain connections having strong interaction strength and greater bearing on community organization, more so than energy flow pathways. Functional webs have compartments, which are sub-groups in the larger network where there are different densities and strengths of interaction.^[36][57] Functional webs emphasize that "the importance of each population in maintaining the integrity of a community is reflected in its influence on the growth rates of other populations."^[38]:511

Within these categories, food webs can be further organized according to the different kinds of ecosystems being investigated. For example, human food webs, agricultural food webs, detrital food webs, marine food webs, aquatic food webs, soil food webs, Arctic (or polar) food webs, terrestrial food webs, and microbial food webs. These characterizations stem from the ecosystem concept, which assumes that the phenomena under investigation (interactions and feedback loops) are sufficient to explain patterns within boundaries, such as the edge of a forest, an island, a shoreline, or some other pronounced physical characteristic.^[58][59][60]

Detrital web

In a detrital web, plant and animal matter is broken down by decomposers, e.g., bacteria and fungi, and moves to detritivores and then carnivores.^[61] There are often relationships between the detrital web and the grazing web. Mushrooms produced by decomposers in the detrital web become a food source for deer, squirrels, and mice in the grazing web. Earthworms eaten by robins are detritivores consuming decaying leaves.^[62]

An illustration of a soil food web.

"Detritus can be broadly defined as any form of non-living organic matter, including different types of plant tissue (e.g. leaf litter, dead wood, aquatic macrophytes, algae), animal tissue (carrion), dead microbes, faeces (manure, dung, faecal pellets, guano, frass), as well as products secreted, excreted or exuded from organisms (e.g. extra-cellular polymers, nectar, root exudates and leachates, dissolved organic matter, extra-cellular matrix, mucilage). The relative importance of these forms of detritus, in terms of origin, size and chemical composition, varies across ecosystems."^[46]:585

Quantitative food webs

Ecologists collect data on trophic levels and food webs to statistically model and mathematically calculate parameters, such as those used in other kinds of network analysis (e.g., graph theory), to study emergent patterns and properties shared among ecosystems. There are different ecological dimensions that can be mapped 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 change in a 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 laboratory experiments using organisms that reproduce quickly, such as daphnia feeding on algae grown under controlled environments in jars of water.^[35][63]

While the complexity of real food webs connections are difficult to decipher, ecologists have found mathematical models on networks an invaluable tool for gaining insight into the structure, stability, and laws of food web behaviours relative to observable outcomes. "Food web theory centers around the idea of connectance."^[64]:1648 Quantitative formulas simplify the complexity of food web structure. The number of trophic links (t_L), for example, is converted into a connectance value:

$C= \cfrac{t_L}{S(S-1)/2}$,

where, S(S-1)/2 is the maximum number of binary connections among S species.^[64] "Connectance (C) is the fraction of all possible links that are realized (L/S²) and represents a standard measure of food web complexity..."^[65]:12913 The distance (d) between every species pair in a web is averaged to compute the mean distance between all nodes in a web (D)^[65] and multiplied by the total number of links (L) to obtain link-density (LD), which is influenced by scale dependent variables such as species richness. These formulas are the basis for comparing and investigating the nature of non-random patterns in the structure of food web networks among many different types of ecosystems.^[65][66]

Scaling laws, complexity, choas, and patterned correlates are common features attributed to food web structure.^{[67] [68]}

Complexity and stability

Food webs are complex. Complexity is a measure of an increasing number of permutations and it is also a metaphorical term that conveys the mental intractability or limits concerning unlimited algorithmic possibilities. In food web terminology, complexity is a product of the number of species and connectance.^[69][70][71] Connectance is "the fraction of all possible links that are realized in a network".^[72]:12917 These concepts were derived and stimulated through the suggestion that complexity leads to stability in food webs, such as increasing the number of trophic levels in more species rich ecosystems. This hypothesis was challenged through mathematical models suggesting otherwise, but subsequent studies have shown that the premise holds in real systems.^[69][73]

At different levels in the hierarchy of life, such as the stability of a food web, "the same overall structure is maintained in spite of an ongoing flow and change of components."^[74]:476 The farther a living system (e.g., ecosystem) sways from equilibrium, the greater its complexity.^[74] Complexity has multiple meanings in the life sciences and in the public sphere that confuse its application as a precise term for analytical purposes in science.^[71][75] Complexity in the life sciences (or biocomplexity) is defined by the "properties emerging from the interplay of behavioral, biological, physical, and social interactions that affect, sustain, or are modified by living organisms, including humans".^[76]:1018

Several concepts have emerged from the study of complexity in food webs. Complexity explains many principals pertaining to self-organization, non-linearity, interaction, cybernetic feedback, discontinuity, emergence, and stability in food webs. Nestedness, for example, is defined as "a pattern of interaction in which specialists interact with species that form perfect subsets of the species with which generalists interact"^[77]:575, "—that is, the diet of the most specialized species is a subset of the diet of the next more generalized species, and its diet a subset of the next more generalized, and so on."^[78] Until recently, it was thought that food webs had little nested structure, but empirical evidence shows that many published webs have nested subwebs in their assebly.^[79]

Food webs are complex networks. As networks, they exhibit similar structural properties and mathematical laws that have been used to describe other complex systems, such as small world and scale free properties. The small world attribute refers to the many loosely connected nodes, non-random dense clustering of a few nodes (i.e., trophic or keystone species in ecology), and small path length compared to a regular lattice.^[72][80] "Ecological networks, especially mutualistic networks, are generally very heterogeneous, consisting of areas with sparse links among species and distinct areas of tightly linked species. These regions of high link density are often referred to as cliques, hubs, compartments, cohesive sub-groups, or modules...Within food webs, especially in aquatic systems, nestedness appears to be related to body size because the diets of smaller predators tend to be nested subsets of those of larger predators (Woodward & Warren 2007; YvonDurocher et al. 2008), and phylogenetic constraints, whereby related taxa are nested based on their common evolutionary history, are also evident (Cattin et al. 2004)."^[81]:257 "Compartments in food webs are subgroups of taxa in which many strong interactions occur within the subgroups and few weak interactions occur between the subgroups. Theoretically, compartments increase the stability in networks, such as food webs."^[57]

Food webs are also complex in the way that they change in scale, seasonally, and geographically. The components of food webs, including organisms and mineral nutrients, cross the thresholds of ecosystem boundaries. This has led to the concept or area of study known as cross-boundary subsidy.^[58][59] "This leads to anomalies, such as food web calculations determining that an ecosystem can support one half of a top carnivore, without specifying which end."^[60] Nonetheless, real differences in structure and function have been identified when comparing different kinds of ecological food webs, such as terrestrial vs. aquatic food webs.^[82]

History of food webs

Victor Summerhayes and Charles Elton's 1923 food web of Bear Island (Arrows point to an organism being consumed by another organism).

Food webs serve as a framework to help ecologists organize the complex network of interactions among species observed in nature and around the world. One of the earliest descriptions of a food chain was described by a medieval Afro-Arab scholar named Al-Jahiz: "All animals, in short, can not exist without food, neither can the hunting animal escape being hunted in his turn."^[83]:143 The earliest graphical depiction of a food web was by Lorenzo Camerano in 1880, followed independently by those of Pierce and colleagues in 1912 and Victor Shelford in 1913.^[84][85] Two food webs about herring were produced by Victor Summerhayes and Charles Elton^[86] and Alister Hardy^[87] in 1923 and 1924. Charles Elton subsequently pioneered the concept of food cycles, food chains, and food size in his classical 1927 book "Animal Ecology"; Elton's 'food cycle' was replaced by 'food web' in a subsequent ecological text.^[88] After Charles Elton's use of food webs in his 1927 synthesis,^[89] they became a central concept in the field of ecology. Elton^[88] organized species into functional groups, which formed the basis for the trophic system of classification in Raymond Lindeman's classic and landmark paper in 1942 on trophic dynamics.^[16][36][90] The notion of a food web has a historical foothold in the writings of Charles Darwin and his terminology, including an "entangled bank", "web of life", "web of complex relations", and in reference to the decomposition actions of earthworms he talked about "the continued movement of the particles of earth". Even earlier, in 1768 John Bruckner described nature as "one continued web of life".^{[3][91][92][93]}

Interest in food webs increased after Robert Paine's experimental and descriptive study of intertidal shores^[94] suggesting that food web complexity was key to maintaining species diversity and ecological stability. Many theoretical ecologists, including Sir Robert May^[95] and Stuart Pimm,^[96] were prompted by this discovery and others to examine the mathematical properties of food webs.

See also

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• Antipredator adaptations
• Apex predator
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Notes

1. ^ Kormondy, E. J. (1996). Concepts of ecology (4th ed.). New Jersey: Prentice-Hall. pp. 559. ISBN 0134781163. http://books.google.ca/books?id=pJbuAAAAMAAJ&q=kormondy+concepts+of+ecology&dq=kormondy+concepts+of+ecology. 
2. ^ ^{a b} Proulx, S. R.; Promislow, D. E. L.; Phillips, P. 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. http://eeb19.biosci.arizona.edu/Faculty/Dornhaus/courses/materials/papers/Proulx%20Promislow%20Phillips%20networks%20ecol%20evol.pdf. 
3. ^ ^{a b c d e f g} Pimm, S. L.; Lawton, J. H.; Cohen, J. E. (1991). "Food web patterns and their consequences" (PDF). Nature 350 (6320): 669–674. doi:10.1038/350669a0. http://www.nicholas.duke.edu/people/faculty/pimm/publications/pimmreprints/71_Pimm_Lawton_Cohen_Nature.pdf. 
4. ^ ^{a b c d e f g} Odum, E. P.; Barrett, G. W. (2005). Fundamentals of Ecology (5th ed.). Brooks/Cole, a part of Cengage Learning. ISBN 0534420664. http://www.cengage.com/aushed/instructor.do?disciplinenumber=1041&product_isbn=9780534420666&courseid=BI03&codeid=2BF6&subTab=&mainTab=About_the_Book&mailFlag=true&topicName=. 
5. ^ ^{a b} Benke, A. C. (2010). "Secondary production". Nature Education Knowledge 1 (8): 5. http://www.nature.com/scitable/knowledge/library/secondary-production-13234142. 
6. ^ Allesina, S.; Alonso, D.; Pascual, M.. "A general model for food web structure.". Science 320 (5876): 658–661. doi:10.1126/science.1156269. http://cas.bellarmine.edu/tietjen/Secret/PlantGenome/General%20Model%20for%20Food%20WEb%20Structure.pdf. 
7. ^ Azam, F.; Fenche, T.; Field, J. G.; Gra, J. S.; Meyer-Reil, L. A.; Thingstad, F. (1983). "The ecological role of water-column microbes in the sea". Mar. Ecol. Prog. Ser. 10: 257–263. doi:10.3354/meps010257. http://www.soest.hawaii.edu/oceanography/courses/OCN621/Spring2011/Azam%20et%20al_loop.pdf. 
8. ^ Uroz, S.; Calvarus, C.; Turpault, M.; Frey-Klett (2009). "Mineral weathering by bacteria: ecology, actors and mechanisms". Trends in Microbiology 17 (8): 378–387. doi:10.1016/j.tim.2009.05.004. PMID 19660952. http://mycor.nancy.inra.fr/GIteam/wp-content/uploads/2009/11/Uroz-TiM-2009.pdf. 
9. ^ Williams, R. J.; Martinez, N. D. (2000). "Simple rules yield complex food webs.". Nature 404 (6774): 180–183. doi:10.1038/35004572. http://userwww.sfsu.edu/~parker/bio840/pdfs/WilliamsMartinez2000.pdf. 
10. ^ Post, D. M. (2002). "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. http://limnology.wisc.edu/courses/zoo955/Spring2005/food%20web%20seminar%20papers/post02TREE.pdf. 
11. ^ Tavares-Cromar, A. F.; Williams, D. D. (1996). "The importance of temporal resolution in food web analysis: Evidence from a detritus-based stream". Ecological Monographs 66 (1): 91–113. JSTOR 2963482. 
12. ^ ^{a b} Pimm, S. L. (1979). "The structure of food webs". Theoretical population biology 16: 144–158. http://www.nicholas.duke.edu/people/faculty/pimm/publications/pimmreprints/12_Pimm_TPB_1979.pdf. 
13. ^ ^{a b} Cousins, S.. "Ecologists build pyramids again.". New Scientist 1463: 50–54. http://books.google.ca/books?id=NOPpwVvNu44C&pg=PA51&dq=trophic+level#v=onepage&q=trophic%20level&f=false. 
14. ^ McCann, K. (2007). "Protecting biostructure". Nature 446 (7131): 29. doi:10.1038/446029a. PMID 17330028. http://www.bolinfonet.org/pdf/McCann_2007_biostructure.pdf. 
15. ^ ^{a b} Thompson, R. M.; Hemberg, M.; Starzomski, B. M.; Shurin, J. B.. "Trophic levels and trophic tangles: The prevalence of omnivory in real food webs.". Ecology 88: 612–617. doi:10.1890/05-1454. PMID 17503589. http://myweb.dal.ca/br238551/thompson_hem_star_shur_ecology07.pdf. 
16. ^ ^{a b c} Lindeman, R. L. (1942). "The trophic-dynamic aspect of ecology". Ecology 23 (4): 399–417. http://www.fcnym.unlp.edu.ar/catedras/ecocomunidades/Lindman_1942.pdf. 
17. ^ ^{a b} Hairston, N. G.; Hairston, N. G. (1993). "Cause-effect relationships in energy flow, trophic structure, and interspecific interactions.". The American Naturalist 142 (3): 379–411. doi:10.1086/285546. http://limnology.wisc.edu/courses/zoo955/Spring2005/food%20web%20seminar%20papers/hairston93AmNat.pdf. 
18. ^ Fretwell, S. D. (1987). "Food chain dynamics: The central theory of ecology?". Oikos 50: 291–301. http://limnology.wisc.edu/courses/zoo955/Spring2005/food%20web%20seminar%20papers/fretwell_food_chain_dynamics_oikos.pdf. 
19. ^ Polis, G. A.; Strong, D. R. (1996). "Food web complexity and community dynamics.". The American Naturalist 147 (5): 813–846. http://www.seaturtle.org/PDF/Polis_1996_AmerNat.pdf. 
20. ^ Hoekman, D.. "Turning up the head: Temperature influences the relative importance of top-down and bottom-up effects.". Ecology 91 (10): 2819–2825. http://www.nd.edu/~underc/east/publications/documents/Hoekman2010b.pdf. 
21. ^ Schmitz, O. J. (2008). "Herbivory from individuals to ecosystems.". Annual Review of Ecology, Evolution and Systematics 39: 133–152. doi:10.1146/annurev.ecolsys.39.110707.173418. http://www.annualreviews.org/doi/abs/10.1146/annurev.ecolsys.39.110707.173418. 
22. ^ Tscharntke, T.; Hawkins, B., A., eds (2002). Multitrophic Level Interactions. Cambridge: Cambridge University Press. pp. 282. ISBN 0521791103. http://books.google.ca/books?id=_8bHeXvUc08C&printsec=frontcover&dq=Multitrophic+Level+Interactions#v=onepage&q&f=false. 
23. ^ Polis, G.A. et al. (2000). "When is a trophic cascade a trophic cascade?". Trends in Ecology and Evolution 15 (11): 473–5. doi:10.1016/S0169-5347(00)01971-6. PMID 11050351. http://www.cof.orst.edu/leopold/class-reading/Polis%202000.pdf. 
24. ^ Sterner, R. W.; Small, G. E.; Hood, J. M.. "The conservation of mass". Nature Education Knowledge 2 (1): 11. http://www.nature.com/scitable/knowledge/library/the-conservation-of-mass-17395478. 
25. ^ Odum, H. T. (1988). "Self-organization, transformity, and information". Science 242 (4882): 1132–1139. doi:10.1126/science.242.4882.1132. JSTOR 1702630. 
26. ^ Odum, E. P. (1968). "Energy flow in ecosystems: A historical review". American Zoologist 8 (1): 11–18. doi:10.1093/icb/8.1.11. http://icb.oxfordjournals.org/content/8/1/11.short. 
27. ^ Mann, K. H. (1988). "Production and use of detritus in various freshwater, estuarine, and coastal marine ecosystems". Limnol. Oceanogr. 33 (2): 910–930. http://nospam.aslo.org/lo/toc/vol_33/issue_4_part_2/0910.pdf. 
28. ^ ^{a b} Koijman, S. A. L. M.; Andersen, T.; Koo, B. W. (2004). "Dynamic energy budget representations of stoichiometric constraints on population dynamics". Ecology 85 (5): 1230–1243. http://www.bio.vu.nl/thb/research/bib/KooyAnde2004.pdf. 
29. ^ Anderson, K. H.; Beyer, J. E.; Lundberg, P. (2009). "Trophic and individual efficiencies of size-structured communities". Proc Biol Sci. 276 (1654): 109–114. doi:10.1098/rspb.2008.0951. PMC 2614255. PMID 18782750. http://www.pubmedcentral.nih.gov/articlerender.fcgi?tool=pmcentrez&artid=2614255. 
30. ^ Benke, A. C. (2011). "Secondary production, quantitative food webs, and trophic position". Nature Education Knowledge 2 (2): 2. http://www.nature.com/scitable/knowledge/library/secondary-production-quantitative-food-webs-and-trophic-17653963. 
31. ^ Spellman, Frank R. (2008). The Science of Water: Concepts and Applications. CRC Press. p. 165. ISBN 9781420055443. http://books.google.com/?id=Grivqd7tLuAC&pg=PA165&dq=%22is+lost+as+heat+and+wastes%22&cd=2#v=onepage&q=%22is%20lost%20as%20heat%20and%20wastes%22. 
32. ^ Kent, Michael (2000). Advanced Biology. Oxford University Press US. p. 511. ISBN 9780199141951. http://books.google.com/?id=8aw4ZWLABQkC&pg=PA511&dq=%22trophic+efficiency+of+less+than+1%25%22&cd=1#v=onepage&q=%22trophic%20efficiency%20of%20less%20than%201%25%22. 
33. ^ Kent, Michael (2000). Advanced Biology. Oxford University Press US. p. 510. ISBN 9780199141951. http://books.google.com/?id=8aw4ZWLABQkC&pg=PA510&dq=%22by+an+energy+flow+diagram%22&cd=1#v=onepage&q=%22by%20an%20energy%20flow%20diagram%22. 
34. ^ ^{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. 
35. ^ ^{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. 
36. ^ ^{a b c} Paine, R. T. (1980). "Food webs: Linkage, interaction strength and community infrastructure.". Journal of Animal Ecology 49 (3): 666–685. JSTOR 4220. 
37. ^ Raffaelli, D. (2002). "From Elton to mathematics and back again". Science 296 (5570): 1035–1037. doi:10.1126/science.1072080. PMID 12004106. 
38. ^ ^{a b c} Rickleffs, Robert, E. (1996). The Economy of Nature. University of Chicago Press. p. 678. ISBN 0716738473. 
39. ^ Whitman, W. B.; Coleman, D. C.; Wieb, W. J. (1998). "Prokaryotes: The unseen majority". Proc. Natl. Acad. Sci. USA 95 (12): 6578–83. doi:10.1073/pnas.95.12.6578. PMC 33863. PMID 9618454. http://www.pubmedcentral.nih.gov/articlerender.fcgi?tool=pmcentrez&artid=33863. 
40. ^ 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.com/?id=_kHeAXV5-XwC&printsec=frontcover. 
41. ^ Spellman, Frank R. (2008). The Science of Water: Concepts and Applications. CRC Press. p. 167. ISBN 9781420055443. http://books.google.com/?id=Grivqd7tLuAC&pg=PA167&dq=However,+biomass+pyramids+can+sometimes+be+inverted.&cd=1#v=onepage&q=However%2C%20biomass%20pyramids%20can%20sometimes%20be%20inverted.. 
42. ^ Wang, H.; Morrison, W.; Singh, A.; Weiss, H. (2009). "Modeling inverted biomass pyramids and refuges in ecosystems". Ecological Modelling 220 (11): 1376–1382. doi:10.1016/j.ecolmodel.2009.03.005. http://people.math.gatech.edu/~weiss/pub/General_Mechanisms_Final.pdf. 
43. ^ Pomeroy, L. R.. "The strategy of mineral cycling". Annual Review of Ecology and Systematics 1: 171–190. JSTOR 2096770. 
44. ^ Elser, J. J.; Fagan, W. F.; Donno, R. F.; Dobberfuhl, D. R.; Folarin, A.; Huberty, A.; et al. (2000). "Nutritional constraints in terrestrial and freshwater food webs". Nature 408 (6812): 578–580. doi:10.1038/35046058. http://www.rug.nl/biologie/onderzoek/onderzoekInstituten/cees/colloquia/pdf/elser_et_al2_2000.pdf. 
45. ^ Koch, P. L.; Fox-Dobbs, K.; Newsom, S. D.. Diet; Flessa. eds. The isotopic ecology of fossil vertebrates and conservation paleobiology.. 15. 95–112. http://www.es.ucsc.edu/~pkoch/pdfs/Koch%20papers/2009/Koch%20et%2009%20PSP%2015.pdf. 
46. ^ ^{a b} Moore, J. C.; Berlow, E. L.; Coleman, D. C.; de Ruiter, P. C.; Dong, Q.; Hastings, A.; et al. (2004). "Detritus, trophic dynamics and biodiversity". Ecology Letters 7 (7): 584–600. doi:10.1111/j.1461-0248.2004.00606.x. 
47. ^ H. A., Lowenstam (1981). "Minerals formed by organisms.". Science 211 (4487): 1126–1131. doi:10.1126/science.7008198. JSTOR 1685216. PMID 7008198. 
48. ^ Warren, L. A.; Kauffman, M. E. (2003). "Microbial geoengineers". Science 299 (5609): 1027–1029. doi:10.1126/science.1072076. JSTOR 3833546. PMID 12586932. 
49. ^ González-Muñoz, M. T.; Rodriguez-Navarro, C.; Martínez-Ruiz, F.; Arias, J. M.; Merroun, M. L.; Rodriguez-Gallego, M.. "Bacterial biomineralization: new insights from Myxococcus-induced mineral precipitation.". Geological Society, London, Special Publications 336 (1): 31–50. doi:10.1144/SP336.3. http://sp.lyellcollection.org/content/336/1/31.abstract. 
50. ^ Gonzalez-Acosta, B.; Bashan, Y.; Hernandez-Saavedra, N. Y.; Ascencio, F.; De la Cruz-Agüero, G.. "Seasonal seawater temperature as the major determinant for populations of culturable bacteria in the sediments of an intact mangrove in an arid region.". FEMS Microbiology Ecology 55 (2): 311–321. doi:10.1111/j.1574-6941.2005.00019.x. http://www.bashanfoundation.org/gmaweb/pdfs/mangrovebalandra.pdf. 
51. ^ DeAngelis, D. L.; Mulholland, P. J.; Palumbo, A. V.; Steinman, A. D.; Huston, M. A.; Elwood, J. W. (1989). "Nutrient dynamics and food-web stability.". Annual Review of Ecology and Systematics 20: 71–95. JSTOR 2097085. 
52. ^ Twiss, M. R.; Campbell, P. G. C.; Auclair, J. (1996). "Regeneration, recycling, and trophic transfer of trace metals by microbial food-web organisms in the pelagic surface waters of Lake Erie.". Limnology and Oceanography 41 (7): 1425–1437. http://www.nospam.aslo.org/lo/toc/vol_41/issue_7/1425.pdf. 
53. ^ May, R. M. (1988). "How many species are there on Earth?". Science 241 (4872): 1441–1449. doi:10.1126/science.241.4872.1441. PMID 17790039. http://www.cerium.ca/IMG/pdf/May_2520_281988_29_1_.pdf. 
54. ^ Beattie, A.; Ehrlich, P. (2010). "The missing link in biodiversity conservation.". Science 328 (5976): 307–308. doi:10.1126/science.328.5976.307-c. http://www.sciencemag.org/content/328/5976/307.3.citation. 
55. ^ Ehrlich, P. R.; Pringle, R. M.. "Colloquium Paper: Where does biodiversity go from here? A grim business-as-usual forecast and a hopeful portfolio of partial solutions". Proceedings of the National Academy of Sciences 105 (S1): 11579–11586. doi:10.1073/pnas.0801911105. PMC 2556413. PMID 18695214. http://www.pubmedcentral.nih.gov/articlerender.fcgi?tool=pmcentrez&artid=2556413. 
56. ^ ^{a b} Dunne, J. A.; Williams, R. J.; Martinez, N. D.; Wood, R. A.; Erwin, D. H.; Dobson, Andrew P. (2008). "Compilation and Network Analyses of Cambrian Food Webs.". PlosBiol 6 (4): e102. doi:10.1371/journal.pbio.0060102. http://www.plosbiology.org/article/info%3Adoi%2F10.1371%2Fjournal.pbio.0060102. 
57. ^ ^{a b} Krause, A. E.; Frank, K. A.; Mason, D. M.; Ulanowicz, R. E.; Taylor, W. W. (2003). "Compartments revealed in food-web structure". Nature 426 (6964): 282–285. doi:10.1038/nature02115. PMID 14628050. http://www.glerl.noaa.gov/pubs/fulltext/2003/20030014.pdf. 
58. ^ ^{a b} Bormann, F. H.; Likens, G. E. (1967). "Nutrient cycling". Science 155 (3761): 424–429. doi:10.1126/science.155.3761.424. http://www.biology.duke.edu/upe302/pdf%20files/Emily_BormannLikens1967.pdf. 
59. ^ ^{a b} Polis, G. A.; Anderson, W. B.; Hold, R. D. (1997). "Toward an integration of landscape and food web ecology: The dynamics of spatially subsidized food webs". Annual Review of Ecology and Systematics 28: 289–316. http://limnology.wisc.edu/courses/zoo955/Fall2006/Papers/Polis_1997_Toward.pdf. 
60. ^ ^{a b} O'Neil, R. V. (2001). "Is it time to bury the ecosystem concept? (With full military honors, of course!)". Ecology 82 (12): 3275–3284. doi:10.1890/0012-9658(2001)082[3275:IITTBT]2.0.CO;2. http://ss1.webkreator.com.mx/4_2/000/000/00c/04a/Concepto%20de%20Ecosistema.pdf. 
61. ^ Gönenç, I. Ethem; Koutitonsky, Vladimir G.; Rashleigh, Brenda (2007). Assessment of the Fate and Effects of Toxic Agents on Water Resources. Springer. p. 279. ISBN 9781402055270. http://books.google.com/?id=nBQYnbsUrBQC&pg=PA278&dq=Water+Resources+grazing+detrital+web&cd=1#v=onepage&q=Water%20Resources%20grazing%20detrital%20web. 
62. ^ Gil Nonato C. Santos; Alfonso C. Danac, Jorge P. Ocampo (2003). E-Biology II. Rex Book Store. p. 58. ISBN 9789712335631. http://books.google.com/?id=L9TwLvnIvnkC&pg=PA58&dq=grazing+web+detrital+web#v=onepage&q=grazing%20web%20detrital%20web. 
63. ^ Elser, J.; Hayakawa, K.; Urabe, J. (2001). "Nutrient Limitation Reduces Food Quality for Zooplankton: Daphnia Response to Seston Phosphorus Enrichment.". Ecology 82 (3): 898–903. doi:10.1890/0012-9658(2001)082[0898:NLRFQF]2.0.CO;2. 
64. ^ ^{a b} Paine, R. T.. "Road maps of interactions or grist for theoretical development?". Ecology 69 (6): 1648–1654. doi:10.2307/1941141. http://limnology.wisc.edu/courses/zoo955/Spring2005/food%20web%20seminar%20papers/Paine88Ecol.pdf. 
65. ^ ^{a b c} Williams, R. J.; Berlow, E. L.; Dunne, J. A.; Barabási, A.; Martinez, N. D. (2002). "Two degrees of separation in complex food webs". Proceedings of the National Academy of Sciences 99 (20): 12913–12916. doi:10.1073/pnas.192448799. 
66. ^ Banasek-Richter, C.; Bersier, L. L.; Cattin, M.; Baltensperger, R.; Gabriel, J.; Merz, Y.; et al.. "Complexity in quantitative food webs". Ecology 90 (6): 1470–1477. http://www.unifr.ch/biol/ecology/bersier/publications/Ecology_Banasek-Richter_2009_withAppendices.pdf. 
67. ^ Riede, J. O.; Rall, B. C.; Banasek-Richter, C.; Navarrete, S. A.; Wieters, E. A.; Emmerson, M. C.; et al. (2010). Woodwoard, G.. ed. Scaling of food web properties with diversity and complexity across ecosystems.. 42. Burlington: Academic Press. pp. 139–170. ISBN 978-0-12-381363-3. http://www.bio.puc.cl/caseb/pdf/prog6/Riede%20et%20al._AER%2010.pdf. 
68. ^ Briand, F.; Cohen, J. E. (1987). "Environmental correlates of food chain length.". Science (4829): 956–960. doi:10.1126/science.3672136. http://spider.allegheny.edu/employee/M/mostrofs/mywebfiles/Bio330/Bio330Readings/briand_and_cohen.pdf. 
69. ^ ^{a b} Neutel, A.; Heesterbeek, J. A. P.; de Ruiter, P. D. (2002). "Stability in real food webs: Weak link in long loops". Science 295 (550): 1120–1123. doi:10.1126/science.1068326. http://igitur-archive.library.uu.nl/vet/2006-0321-200233/heesterbeek_02_stability_webs.pdf. 
70. ^ Leveque, C., ed (2003). Ecology: From ecosystem to biosphere. Science Publishers. pp. 490. ISBN 9781578082940. http://books.google.ca/books?id=-h3AFlmGS_kC&printsec=frontcover&dq=Ecology+from+ecosystem+to+biosphere#v=onepage&q&f=false. 
71. ^ ^{a b} Proctor, J. D.; Larson, B. M. H. (2005). "Ecology, complexity, and metaphor". Bioscience 55 (12): 1065–1068. doi:10.1641/0006-3568(2005)055[1065:ECAM]2.0.CO;2. http://media.eurekalert.org/release_graphics/pdf/EcologyComplexity112205.pdf. 
72. ^ ^{a b} Dunne, J. A.; Williams, R. J.; Martinez, N. D. (2002). "Food-web structure and network theory: The role of connectance and size". Proceedings of the National Academy of Sciences 99 (20): 12917–12922. doi:10.1073/pnas.192407699. 
73. ^ Banašek-Richter, C.; Bersier, L.; Cattin, M.; Baltensperger, R.; Gabriel, J.; Merz, J.; et al. (2009). "Complexity in quantitative food webs". Ecology 90: 1470–1477. doi:10.1890/08-2207.1. http://doc.rero.ch/lm.php?url=1000,43,4,20090727160545-QX/Banasek-Richter_Carolin_-_Complexity_in_quantitative_food_webs_20090727.pdf. 
74. ^ ^{a b} Capra, F. (2007). "Complexity and life". Syst. Res. 24: 475–479. doi:10.1002/sres.848. 
75. ^ Peters, R. H. (1988). "Some general problems for ecology illustrated by food web theory". Ecology 69 (6): 1673–1676. JSTOR 1941145. 
76. ^ Michener, W. K.; Baerwald, T. J.; Firth, P.; Palmer, M. A.; Rosenberger, J. L.; Sandlin, E. A.; Zimmerman, H. (2001). "Defining and unraveling biocomplexity". BioScience 51: 1018–1023. http://holisticbiology.stanford.edu/biocomplexity.pdf. 
77. ^ Bascompte, J.; Jordan, P. (2007). "Plant-animal mutualistic networks: The architecture of biodiversity.". Annu. Rev. Ecol. Evol. Syst. 38: 567–569. http://ieg.ebd.csic.es/JordiBascompte/Publications/AREES-07.pdf. 
78. ^ Montoya, J. M.; Pimm, S. L.; Solé, R. V. (2006). "Ecological networks and their fragility". Nature 442 (7100): 259–264. doi:10.1038/nature04927. http://eeb19.biosci.arizona.edu/Faculty/Dornhaus/courses/materials/papers/Montoya%20Pimm%20Sole%20networks%20ecol.pdf. 
79. ^ Michio, K.; Kato, S.; Sakato, Y. (2010). "Food webs are built up with nested subwebs". Ecology 91: 3123–3130. doi:10.1890/09-2219.1. http://www.esajournals.org/doi/pdf/10.1890/09-2219.1. 
80. ^ Montoya, J. M.; Solé, R. V. (2002). "Small world patterns in food webs". Journal of Theoretical Biology 214 (3): 405–412. doi:10.1006/jtbi.2001.2460. http://complex.upf.es/papers/Small_World_Patterns_in_Food_Webs.pdf. 
81. ^ Montoya, J. M.; Blüthgen, N; Brown, L.; Dormann, C. F.; Edwards, F.; Figueroa, D.; et al. (2009). "Ecological networks: beyond food webs". Journal of Animal Ecology 78: 253–269. doi:10.1111/j.1365-2656.2008.01460.x. http://www.higrade.ufz.de/data/Ings2008JAnimEcol942012634.pdf. 
82. ^ 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 (1582): 1–9. doi:10.1098/rspb.2005.3377. PMC 1560001. PMID 16519227. http://rspb.royalsocietypublishing.org/content/273/1582/1.full.pdf+html. 
83. ^ Egerton, F. N.. "A history of the ecological sciences, part 6: Arabic language science: Origins and zoological writings.". Bulletin of the Ecological Society of America 83 (2): 142–146. http://www.esapubs.org/bulletin/current/history_list/history_part6.pdf. 
84. ^ Egerton, FN (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. 
85. ^ Shelford, V (1913) imal+communities&printsec=frontcover&source=bl&ots=XT6Rz02AEZ&sig=hOm3G1CE5r4PYmq2kuR0VNKrxjU&hl=en&ei=mRvzSrCjG4aSMc_-kOgF&sa=X&oi=book_result&ct=result&resnum=2&ved=0CAoQ6AEwAQ#v=onepage&q=&f=false Animal Communities in Temperate America as Illustrated in the Chicago Region. University of Chicago Press.
86. ^ Summerhayes, VS; Elton, CS (1923). "Contributions to the Ecology of Spitsbergen and Bear Island". Journal of Ecology 11: 214–286. 
87. ^ Hardy, AC (1924). "The herring in relation to its animate environment. Part 1. The food and feeding habits of the herring with special reference to the east coast of England". Fisheries Investigation London Series II 7 (3): 1–53. 
88. ^ ^{a b} Elton, C. S. (1927). Animal Ecology. London, UK.: Sidgwick and Jackson. ISBN 0226206394. 
89. ^ Elton CS (1927) Animal Ecology. Republished 2001. University of Chicago Press.
90. ^ Allee, W. C. (1932). Animal life and social growth. Baltimore: The Williams & Wilkins Company and Associates. 
91. ^ Stauffer, R. C. (1960). "Ecology in the long manuscript version of Darwin's "Origin of Species" and Linnaeus' "Oeconomy of Nature"". Proceedings of the American Philosophical Society 104 (2): 235–241. JSTOR 985662. 
92. ^ Darwin, C. R. (1881). The formation of vegetable mould, through the action of worms, with observations on their habits.. London: John Murray. http://darwin-online.org.uk/content/frameset?viewtype=text&itemID=F1357&pageseq=1. 
93. ^ Worster, D. (1994). Nature's economy: A history of ecological ideas (2nd ed.). Cambridge University Press. pp. 423. ISBN 9780521468343. http://books.google.ca/books?id=2Ng-5B5H2wcC&pg=PR9&dq=food+web+history+ecology+linnaeus+economy+of+nature#v=onepage&q&f=false. 
94. ^ Paine, RT (1966). "Food web complexity and species diversity". The American Naturalist 100: 65–75. doi:10.1086/282400. 
95. ^ May RM (1973) Stability and Complexity in Model Ecosystems. Princeton University Press.
96. ^ Pimm SL (1982) Food Webs, Chapman & Hall.