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| The '''Lotka–Volterra equations''', also known as the ''predator–prey equations'', are a pair of first-order, [[non-linear]], [[differential equation]]s frequently used to describe the [[dynamical system|dynamics]] of [[Systems biology|biological systems]] in which two species interact, one as a predator and the other as prey. The populations change through time according to the pair of equations: | | Choosing the right web hosting service is necessary. The last thing you wish to do is get a website released with a hosting service (after discovering to use that hosting service), then be dissatisfied with the service and need to mess around with moving your internet site to an additional hosting service.<br><br>I'm a pleased HostGator client. I make use of both HostGator and Bluehost. I recommend both. This article is an extensive HostGator evaluation.<br><br>I'll begin with among the most vital factors to consider: Cost<br><br>HostGator has several pricing plans. 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| :<math>\frac{dx}{dt} = x(\alpha - \beta y)</math> | |
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| :<math>\frac{dy}{dt} = - y(\gamma - \delta x)</math> | |
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| where,
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| *''x'' is the number of prey (for example, [[rabbit]]s);
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| *''y'' is the number of some [[Predation|predator]] (for example, [[fox]]es);
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| *<math>\tfrac{dy}{dt}</math> and <math>\tfrac{dx}{dt}</math> represent the growth rates of the two populations over time;
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| *''t'' represents time; and
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| * <math>\alpha</math>'', ''<math>\beta</math>'', ''<math>\gamma</math>'' and ''<math>\delta</math>'' are [[parameter]]s describing the interaction of the two [[species]].
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| The Lotka–Volterra system of equations is an example of a [[Kolmogorov]] model,<ref>Freedman, H.I., ''Deterministic Mathematical Models in Population Ecology'', [[Marcel Dekker]], (1980)</ref><ref>Brauer, F. and Castillo-Chavez, C., ''Mathematical Models in Population Biology and Epidemiology'', [[Springer-Verlag]], (2000)</ref><ref name="scholarpedia">Hoppensteadt, F., [http://www.scholarpedia.org/article/Predator-prey_model "Predator-prey model"], ''[[Scholarpedia]]'', '''1'''(10), 1563, (2006)</ref> which is a more general framework that can model the dynamics of ecological systems with predator-prey interactions, competition, disease, and mutualism.
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| ==History==
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| The Lotka–Volterra predator–prey [[mathematical model|model]] was initially proposed by [[Alfred J. Lotka]] “in the theory of autocatalytic chemical reactions” in 1910.<ref>Lotka, A.J., "Contribution to the Theory of Periodic Reaction", ''[[Journal of Physical Chemistry A|J. Phys. Chem.]]'', '''14''' (3), pp 271–274 (1910)</ref><ref name="Goelmany">Goel, N.S. et al., “On the Volterra and Other Non-Linear Models of Interacting Populations”, ''Academic Press Inc.'', (1971)</ref> This was effectively the [[Logistic function#In ecology: modeling population growth|logistic equation]],<ref>Berryman, A.A., [http://entomology.wsu.edu/profiles/06BerrymanWeb/Berryman%2892%29Origins.pdf "The Origins and Evolution of Predator-Prey Theory"], [[Ecology (journal)|''Ecology'']], '''73'''(5), 1530–1535, (1992)</ref> which was originally derived by [[Pierre François Verhulst]].<ref>Verhulst, P.H., [http://books.google.com/books?hl=fr&id=8GsEAAAAYAAJ&jtp=113#v=onepage&q=&f=false "Notice sur la loi que la population poursuit dans son accroissement"]. ''Corresp. mathématique et physique'' '''10''', 113–121, (1838)</ref> In 1920 Lotka extended, via Kolmogorov (see above), the model to "organic systems" using a plant species and a herbivorous animal species as an example <ref>Lotka, A.J., [http://www.ncbi.nlm.nih.gov/pmc/articles/PMC1084562/pdf/pnas01916-0016.pdf "Analytical Note on Certain Rhythmic Relations in Organic Systems”], ''[[PNAS|Proc. Natl. Acad. Sci. U.S.]]'', '''6''', 410–415, (1920)</ref> and in 1925 he utilised the equations to analyse predator-prey interactions in his book on [[biomathematics]] <ref>Lotka, A.J., ''Elements of Physical Biology'', [[Williams and Wilkins]], (1925)</ref> arriving at the equations that we know today. [[Vito Volterra]], who made a statistical analysis of fish catches in the Adriatic <ref name="Goelmany"/> independently investigated the equations in 1926.<ref>Volterra, V., “Variazioni e fluttuazioni del numero d’individui in specie animali conviventi”, ''[[Accademia dei Lincei|Mem. Acad. Lincei Roma]]'', '''2''', 31–113, (1926)</ref><ref>Volterra, V., ''Variations and fluctuations of the number of individuals in animal species living together'' in Animal Ecology, Chapman, R.N. (ed), [[McGraw–Hill]], (1931)</ref>
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| [[C.S. Holling]] extended this model yet again, in two 1959 papers, in which he proposed the idea of [[functional response]].<ref>Holling, C.S., "The components of predation as revealed by a study of small mammal predation of the European Pine Sawfly", [[Canadian Entomologist|''Can. Ent'']], '''91''', 293–320, (1959a)</ref><ref>Holling, C.S., “Some characteristics of simple types of predation and parasitism”, ''Can. Ent'', '''91''', 385–398, (1959b)</ref> Both the Lotka–Volterra model and Holling's extensions have been used to model the moose and wolf populations in [[Isle Royale National Park]],<ref>Jost, C., Devulder, G., Vucetich, J.A., Peterson, R., and Arditi, R., [http://www.isleroyalewolf.org/techpubs/techpubs/ISROpubs_files/Jost%20et%20al.pdf "The wolves of Isle Royale display scale-invariant satiation and density dependent predation on moose"], ''J. Anim. Ecol.'', '''74'''(5), 809–816 (2005)</ref> which with over 50 published papers is one of the best studied predator-prey relationships.
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| In the late 1980s, a credible, simple alternative to the Lotka-Volterra predator-prey model (and its common prey dependent generalizations) emerged, the ratio dependent or Arditi-Ginzburg model.<ref>Arditi, R. and Ginzburg, L.R. (1989) [http://life.bio.sunysb.edu/ee/ginzburglab/Coupling%20in%20Predator-Prey%20Dynamics%20-%20Arditi%20and%20Ginzburg,%201989.pdf "Coupling in predator-prey dynamics: ratio dependence"] ''Journal of Theoretical Biology'', '''139''': 311–326.</ref> The two are the extremes of the spectrum of predator interference models. According to the authors of the alternative view, the data show that true interactions in nature are so far from the Lotka-Volterra extreme on the interference spectrum that the model can simply be discounted as wrong. They are much closer to the ratio dependent extreme, so if a simple model is needed one can use the Arditi-Ginzburg model as the first approximation.<ref>Arditi, R. and Ginzburg, L.R. (2012) [http://books.google.co.nz/books?hl=en&lr=&id=c2m6XspGs-cC&oi=fnd&pg=PP2&dq=%22How+Species+Interact:+Altering+the+Standard+View+on+Trophic+Ecology%22&ots=CLPI8KgYU5&sig=5WWhmaSEbWpX9jESMJFI9r2VWsI ''How Species Interact: Altering the Standard View on Trophic Ecology''] Oxford University Press. ISBN 9780199913831.</ref>
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| ===In economics===
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| The Lotka–Volterra equations have a long history of use in economic theory; their initial application is commonly credited to [[Richard M. Goodwin|Richard Goodwin]] in 1965<ref>Gandolfo, G., "Giuseppe Palomba and the Lotka–Volterra equations", ''Rendiconti Lincei'', '''19'''(4), 347–257, (2008)</ref> or 1967.<ref>Goodwin, R.M. , "A Growth Cycle", ''Socialism, Capitalism and Economic Growth'', Feinstein, C.H. (ed.), [[Cambridge University Press]], (1967)</ref><ref>Desai, M. and Ormerod, P. [http://www.paulormerod.com/pdf/economicjournal1998.pdf "Richard Goodwin: A Short Appreciation"], ''[[The Economic Journal]]'', '''108'''(450), 1431–1435 (1998)</ref> In economics, links are between many if not all industries; a proposed way to model the dynamics of various industries has been by introducing trophic functions between various sectors,<ref>Nasritdinov, G. and Dalimov, R.T., [http://www.maxwellsci.com/print/crjet/v2-32-40.pdf "Limit cycle, trophic function and the dynamics of intersectoral interaction"], ''Current Research J. of Economic Theory'', '''2'''(2), 32–40, (2010)</ref> and ignoring smaller sectors by considering the interactions of only two industrial sectors.<ref>Haken, H., [http://books.google.co.uk/books?hl=en&lr=&id=0bc6cLK0w7YC&oi=fnd&pg=PA1&dq=Haken,+Synergetics,+Springer-Verlag,+2004&ots=dw6IC1rdLp&sig=_IIHtwt-Lxsi4694w2jFUhbGWoY#v=onepage&q=Haken%2C%20Synergetics%2C%20Springer-Verlag%2C%202004&f=false ''Synergetics: introduction and advanced topics''], Springer-Verlag, (2004)</ref>
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| ==Physical meanings of the equations==
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| The Lotka–Volterra model makes a number of assumptions about the environment and evolution of the predator and prey populations:
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| # The prey population finds ample food at all times.
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| # The food supply of the predator population depends entirely on the size of the prey population.
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| # The rate of change of population is proportional to its size.
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| # During the process, the environment does not change in favour of one species and the genetic adaptation is sufficiently slow.
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| # Predators have limitless appetite
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| As differential equations are used, the solution is [[determinism|deterministic]] and [[Continuous function|continuous]]. This, in turn, implies that the generations of both the predator and prey are continually overlapping.<ref>Cooke, D. and Hiorns, R.W. et al., ''The Mathematical Theory of the Dynamics of Biological Populations II'', Academic Press Inc., (1981)</ref>
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| ===Prey===
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| When multiplied out, the prey equation becomes:
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| :<math>\frac{dx}{dt} = \alpha x - \beta x y.</math>
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| The prey are assumed to have an unlimited food supply, and to reproduce exponentially unless subject to predation; this [[exponential growth]] is represented in the equation above by the term ''αx''. The rate of predation upon the prey is assumed to be proportional to the rate at which the predators and the prey meet; this is represented above by ''βxy''. If either ''x'' or ''y'' is zero then there can be no predation.
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| With these two terms the equation above can be interpreted as: the change in the prey's numbers is given by its own growth minus the rate at which it is preyed upon.
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| ===Predators===
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| The predator equation becomes:
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| :<math>\frac{dy}{dt} = \delta xy - \gamma y.</math>
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| In this equation, ''<math> \displaystyle \delta xy</math>'' represents the growth of the predator population. (Note the similarity to the predation rate; however, a different constant is used as the rate at which the predator population grows is not necessarily equal to the rate at which it consumes the prey). ''<math>\displaystyle \gamma y</math>'' represents the loss rate of the predators due to either natural death or emigration; it leads to an exponential decay in the absence of prey.
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| Hence the equation expresses the change in the predator population as growth fueled by the food supply, minus natural death.
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| ==Solutions to the equations==
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| The equations have [[periodic function|periodic]] solutions and do not have a simple expression in terms of the usual [[Trigonometric functions|trigonometric function]]s. However, a [[linearization]] of the equations yields a solution similar to [[simple harmonic motion]]<ref>Tong, H., ''Threshold Models in Non-linear Time Series Analysis'', Springer–Verlag, (1983)</ref> with the population of predators following that of prey by 90°.
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| <center>[[Image:Volterra lotka dynamics.PNG]]</center>
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| ===An example problem===
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| Suppose there are two species of animals, a baboon (prey) and a cheetah (predator). If the initial conditions are 80 baboons and 40 cheetahs, one can plot the progression of the two species over time. The choice of time interval is arbitrary.
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| <center>[[Image:Cheetah Baboon LV.jpg]]</center>
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| One can also plot solutions without representing time, but with one axis representing the number of prey and the other axis representing the number of predators. The solutions are closed curves, and there is a quantity ''V'' which is conserved on each curve:
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| <math>V = -\delta \, x + \gamma \, \log(x) - \beta \, y + \alpha \, \log(y)</math>
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| <center>[[Image:CentralTendencyLV.jpg]]</center>
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| These graphs clearly illustrate a serious problem with this as a biological model: in each cycle, the baboon population is reduced to extremely low numbers yet recovers (while the cheetah population remains sizeable at the lowest baboon density). With chance fluctuations, discrete numbers of individuals, and the family structure and lifecycle of baboons, the baboons actually go extinct and by consequence the cheetahs as well. This modelling problem has been called the "atto-fox problem",<ref>Mollison, D., [http://www.ma.hw.ac.uk/~denis/epi/velocities.pdf "Dependence of epidemic and population velocities on basic parameters"], ''Math. Biosci.'', '''107''', 255-287, (1991)</ref> an [[atto-]]<nowiki>fox</nowiki> being an imaginary 10<sup>−18</sup> of a fox, in relation to rabies modelling in the UK.
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| ==Dynamics of the system==
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| In the model system, the predators thrive when there are plentiful prey but, ultimately, outstrip their food supply and decline. As the predator population is low the prey population will increase again. These dynamics continue in a cycle of growth and decline.
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| ===Population equilibrium===
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| Population equilibrium occurs in the model when neither of the population levels is changing, i.e. when both of the derivatives are equal to 0.
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| :<math>x(\alpha - \beta y) = 0\,</math>
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| :<math>-y(\gamma - \delta x) = 0\,</math>
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| When solved for ''x'' and ''y'' the above system of equations yields
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| :<math>\left\{ y = 0 , x = 0 \right\}\,</math>
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| and
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| :<math>\left\{ y = \frac{\alpha}{\beta}, x = \frac{\gamma}{\delta} \right\},\,</math>
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| Hence, there are two equilibria.
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| The first solution effectively represents the extinction of both species. If both populations are at 0, then they will continue to be so indefinitely. The second solution represents a fixed point at which both populations sustain their current, non-zero numbers, and, in the simplified model, do so indefinitely. The levels of population at which this equilibrium is achieved depend on the chosen values of the parameters, α, β, γ, and δ.
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| ===Stability of the fixed points===
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| The stability of the fixed point at the origin can be determined by performing a [[linearization]] using [[partial derivative]]s, while the other fixed point requires a slightly more sophisticated method.
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| The [[Jacobian matrix]] of the predator-prey model is
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| :<math>J(x,y) = \begin{bmatrix}
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| \alpha - \beta y & -\beta x \\
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| \delta y & \delta x - \gamma \\
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| \end{bmatrix}.</math>
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| ====First fixed point (extinction)====
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| When evaluated at the steady state of (0, 0) the Jacobian matrix ''J'' becomes
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| :<math>J(0,0) = \begin{bmatrix}
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| \alpha & 0 \\
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| 0 & -\gamma \\
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| \end{bmatrix}.</math>
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| The [[eigenvalue]]s of this matrix are
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| :<math>\lambda_1 = \alpha,\quad \lambda_2 = -\gamma.\,</math>
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| In the model ''α'' and ''γ'' are always greater than zero, and as such the sign of the eigenvalues above will always differ. Hence the fixed point at the origin is a [[saddle point]].
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| The stability of this fixed point is of importance. If it were stable, non-zero populations might be attracted towards it, and as such the dynamics of the system might lead towards the extinction of both species for many cases of initial population levels. However, as the fixed point at the origin is a saddle point, and hence unstable, we find that the extinction of both species is difficult in the model. (In fact, this can only occur if the prey are artificially completely eradicated, causing the predators to die of starvation. If the predators are eradicated, the prey population grows without bound in this simple model).
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| ====Second fixed point (oscillations)====
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| Evaluating ''J'' at the second fixed point we get
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| :<math>J\left(\frac{\gamma}{\delta},\frac{\alpha}{\beta}\right) = \begin{bmatrix}
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| 0 & -\frac{\beta \gamma}{\delta} \\
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| \frac{\alpha \delta}{\beta} & 0 \\
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| \end{bmatrix}.</math>
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| The eigenvalues of this matrix are
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| :<math>\lambda_1 = i \sqrt{\alpha \gamma},\quad \lambda_2 = -i \sqrt{\alpha \gamma}.\,
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| </math>
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| As the eigenvalues are both purely imaginary, this fixed point is not [[hyperbolic equilibrium point|hyperbolic]], so no conclusions can be drawn from the linear analysis. However, the system admits a [[constant of motion]]
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| :<math> K = y^\alpha e^{-\beta y} \, x^\gamma e^{-\delta x}, </math>
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| and the level curves, where ''K'' = const, are closed trajectories surrounding the fixed point.
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| Consequently, the levels of the predator and prey populations cycle, and oscillate around this fixed point.
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| The largest value of the constant ''K'' can be obtained by solving the optimization problem
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| :<math> y^\alpha e^{-\beta y} \, x^\gamma e^{-\delta x}=\frac{y^\alpha x^\gamma}{e^{\delta x+\beta y}}\longrightarrow \max\limits_{x,y>0}.</math>
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| The maximal value of ''K'' is attained at the stationary point <math>\left(\frac{\gamma}{\delta},\frac{\alpha}{\beta}\right) </math> and it is given by
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| :<math> K^*=\left(\frac{\alpha}{\beta e}\right)^\alpha\left(\frac{\gamma}{\delta e}\right)^\gamma, </math>
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| where ''e'' is [[e (mathematical constant)|Euler's Number]].
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| ==Cellular automata==
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| A rule-based [[Cellular automata|automaton]] model is equivalent to a Lotka–Volterra system and introduces 2D space, with either periodic or fixed boundaries.
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| Each site has three states, fox, bare, rabbit.
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| Rules are as follows:
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| # Pick a site (only stochastic updates allowed), and a neighbour.
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| # If fox is adjacent to rabbit, rabbit gets eaten (becomes fox with probability ''r''). Else fox dies with probability ''p''.
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| # If rabbit is adjacent to bare ground, reproduces with probability ''q''.
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| # If bare ground is adjacent to anything, the thing moves into bare ground.
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| [https://web.archive.org/web/20120710022422/http://www2.ph.ed.ac.uk/nania/lv/lv.html These rules give a model like Lotka–Volterra], but the additional feature of a correlation length between regions oscillating differently. The correlation length is very long, and the model develops a wave structure.
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| ==See also==
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| * [[Competitive Lotka–Volterra equations]]
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| * [[Generalized Lotka–Volterra equation]]
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| * [[Mutualism and the Lotka–Volterra equation]]
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| * [[Community matrix]]
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| * [[Population dynamics]]
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| * [[Population dynamics of fisheries]]
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| * [[Nicholson–Bailey model]]
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| ==Notes==
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| {{reflist|2}}
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| ==References==
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| * E. R. Leigh (1968) The ecological role of Volterra's equations, in ''Some Mathematical Problems in Biology'' – a modern discussion using [[Hudson's Bay Company]] data on [[lynx]] and [[hare]]s in [[Canada]] from 1847 to 1903.
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| * Understanding Nonlinear Dynamics. Daniel Kaplan and [[Leon Glass]].
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| * J.D. Murray. Mathematical Biology I: An Introduction. Springer-Verlag, 2003
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| ==External links==
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| * [http://insightmaker.com/insight/2068 Interactive Lotka-Volterra Predator-Prey Model] (Based on historical Isle Royale Data)
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| * [http://www.egwald.ca/nonlineardynamics/twodimensionaldynamics.php#predatorpreymodel Lotka–Volterra Predator-Prey Model] by Elmer G. Wiens
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| * [http://www.ahahah.eu/trucs/pp/ Lotka–Volterra Predator-Prey Model] as a multi-agents system.
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| *[http://math.fullerton.edu/mathews/n2003/Lotka-VolterraMod.html Lotka-Volterra Model]
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| * [https://web.archive.org/web/20120710022422/http://www2.ph.ed.ac.uk/nania/lv/lv.html NANIA Lotka-Volterra applet] Archived from the [http://www.ph.ed.ac.uk/nania/lv/lv.html Original] on 2012-07-10.
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| * [http://jseed.sourceforge.net/lotka/index.html Lotka Algorithmic Simulation] Similar program, in Javascript (requires an HTML5 browser).
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| * From the ''[[Wolfram Demonstrations Project]]'' — requires [http://demonstrations.wolfram.com/download-cdf-player.html CDF player (free)]:
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| ** [http://demonstrations.wolfram.com/PredatorPreyEquations/ Predator-Prey Equations]
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| ** [http://demonstrations.wolfram.com/PredatorPreyModel/ Predator-Prey Model]
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| ** [http://demonstrations.wolfram.com/PredatorPreyDynamicsWithTypeTwoFunctionalResponse/ Predator-Prey Dynamics with Type-Two Functional Response]
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| ** [http://demonstrations.wolfram.com/PredatorPreyEcosystemARealTimeAgentBasedSimulation/ Predator-Prey Ecosystem: A Real-Time Agent-Based Simulation]
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| {{modelling ecosystems|expanded=other}}
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| {{DEFAULTSORT:Lotka-Volterra Equation}}
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| [[Category:Predation]]
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| [[Category:Differential equations]]
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| [[Category:Fixed points (mathematics)]]
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| [[Category:Population models]]
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