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Carrying capacity

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Not to be confused with Biocapacity.

The carrying capacity of an environment is the maximum population size of a biological species that can be sustained by that specific environment, given the food, habitat, water, and other resources available. The carrying capacity is defined as the environment's maximal load,[clarification needed] which in population ecology corresponds to the population equilibrium, when the number of deaths in a population equals the number of births (as well as immigration and emigration). Carrying capacity of the environment implies that the resources extraction is not above the rate of regeneration of the resources and the wastes generated are within the assimilating capacity of the environment. The effect of carrying capacity on population dynamics is modelled with a logistic function. Carrying capacity is applied to the maximum population an environment can support in ecology, agriculture and fisheries. The term carrying capacity has been applied to a few different processes in the past before finally being applied to population limits in the 1950s.[1] The notion of carrying capacity for humans is covered by the notion of sustainable population.

An early detailed examination of global limits was published in the 1972 book Limits to Growth, which has prompted follow-up commentary and analysis, including much criticism.[2] A 2012 review in Nature by 22 international researchers expressed concerns that the Earth may be "approaching a state shift" in which the biosphere may become less hospitable to human life and in which human carrying capacity may diminish.[3] This concern that humanity may be passing beyond "tipping points" for safe use of the biosphere has increased in subsequent years.[4][5] Recent estimates of Earth's carrying capacity run between two billion and four billion people, depending on how optimistic researchers are about international cooperation to solve collective action problems.[6]

Origins

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In terms of population dynamics, the term 'carrying capacity' was not explicitly used in 1838 by the Belgian mathematician Pierre François Verhulst when he first published his equations based on research on modelling population growth.[7]

The origins of the term "carrying capacity" are uncertain, with sources variously stating that it was originally used "in the context of international shipping" in the 1840s,[8][9] or that it was first used during 19th-century laboratory experiments with micro-organisms.[10] A 2008 review finds the first use of the term in English was an 1845 report by the US Secretary of State to the US Senate. It then became a term used generally in biology in the 1870s, being most developed in wildlife and livestock management in the early 1900s.[9] It had become a staple term in ecology used to define the biological limits of a natural system related to population size in the 1950s.[8][9]

Neo-Malthusians and eugenicists popularised the use of the words to describe the number of people the Earth can support in the 1950s,[9] although American biostatisticians Raymond Pearl and Lowell Reed had already applied it in these terms to human populations in the 1920s.[citation needed]

Hadwen and Palmer (1923) defined carrying capacity as the density of stock that could be grazed for a definite period without damage to the range.[11][12]

It was first used in the context of wildlife management by the American Aldo Leopold in 1933, and a year later by the American Paul Lester Errington, a wetlands specialist. They used the term in different ways, Leopold largely in the sense of grazing animals (differentiating between a 'saturation level', an intrinsic level of density a species would live in, and carrying capacity, the most animals which could be in the field) and Errington defining 'carrying capacity' as the number of animals above which predation would become 'heavy' (this definition has largely been rejected, including by Errington himself).[11][13] The important and popular 1953 textbook on ecology by Eugene Odum, Fundamentals of Ecology, popularised the term in its modern meaning as the equilibrium value of the logistic model of population growth.[11][14]

Mathematics

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The specific reason why a population stops growing is known as a limiting or regulating factor.[15]

Reaching carrying capacity through a logistic growth curve

The difference between the birth rate and the death rate is the natural increase. If the population of a given organism is below the carrying capacity of a given environment, this environment could support a positive natural increase; should it find itself above that threshold the population typically decreases.[16] Thus, the carrying capacity is the maximum number of individuals of a species that an environment can support in long run.[17]

Population size decreases above carrying capacity due to a range of factors depending on the species concerned, but can include insufficient space, food supply, or sunlight. The carrying capacity of an environment varies for different species.[citation needed]

In the standard ecological algebra as illustrated in the simplified Verhulst model of population dynamics, carrying capacity is represented by the constant K:

where

Thus, the equation relates the growth rate of the population N to the current population size, incorporating the effect of the two constant parameters r and K. (Note that decrease is negative growth.) The choice of the letter K came from the German Kapazitätsgrenze (capacity limit).

This equation is a modification of the original Verhulst model:

[18]

In this equation, the carrying capacity K, , is

This is a graph of population change utilizing the logistic curve model. When the population is above the carrying capacity it decreases, and when it is below the carrying capacity it increases.

When the Verhulst model is plotted into a graph, the population change over time takes the form of a sigmoid curve, reaching its highest level at K. This is the logistic growth curve and it is calculated with:

where

  • e is the natural logarithm base (also known as Euler's number),
  • x0 is the x value of the sigmoid's midpoint,
  • L is the curve's maximum value,
  • K is the logistic growth rate or steepness of the curve [19] and

The logistic growth curve depicts how population growth rate and carrying capacity are inter-connected. As illustrated in the logistic growth curve model, when the population size is small, the population increases exponentially. However, as population size nears carrying capacity, the growth decreases and reaches zero at K.[20]

What determines a specific system's carrying capacity involves a limiting factor; this may be available supplies of food or water, nesting areas, space, or the amount of waste that can be absorbed without degrading the environment and decreasing carrying capacity.

Population ecology

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Main articles: Population ecology and Population dynamics
See also: Ecological overshoot

Carrying capacity is a commonly used concept for biologists when trying to better understand biological populations and the factors which affect them.[1] When addressing biological populations, carrying capacity can be seen as a stable dynamic equilibrium, taking into account extinction and colonization rates.[16] In population biology, logistic growth assumes that population size fluctuates above and below an equilibrium value.[21]

Numerous authors have questioned the usefulness of the term when applied to actual wild populations.[11][12][22] Although useful in theory and in laboratory experiments, carrying capacity as a method of measuring population limits in the environment is less useful as it sometimes oversimplifies the interactions between species.[16]

Agriculture

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It is important for farmers to calculate the carrying capacity of their land so they can establish a sustainable stocking rate.[23] For example, calculating the carrying capacity of a paddock in Australia is done in Dry Sheep Equivalents (DSEs). A single DSE is 50 kg Merino wether, dry ewe or non-pregnant ewe, which is maintained in a stable condition. Not only sheep are calculated in DSEs, the carrying capacity for other livestock is also calculated using this measure. A 200 kg weaned calf of a British style breed gaining 0.25 kg/day is 5.5DSE, but if the same weight of the same type of calf were gaining 0.75 kg/day, it would be measured at 8DSE. Cattle are not all the same, their DSEs can vary depending on breed, growth rates, weights, if it is a cow ('dam'), steer or ox ('bullock' in Australia), and if it weaning, pregnant or 'wet' (i.e. lactating).

In other parts of the world different units are used for calculating carrying capacities. In the United Kingdom the paddock is measured in LU, livestock units, although different schemes exist for this.[24][25] New Zealand uses either LU,[26] EE (ewe equivalents) or SU (stock units).[27] In the US and Canada the traditional system uses animal units (AU).[28] A French/Swiss unit is Unité de Gros Bétail (UGB).[29][30]

Summering of milk cows in the Swiss Alps in Valais Canton

In some European countries such as Switzerland the pasture (alm or alp) is traditionally measured in Stoß, with one Stoß equaling four Füße (feet). A more modern European system is Großvieheinheit (GV or GVE), corresponding to 500 kg in liveweight of cattle. In extensive agriculture 2 GV/ha is a common stocking rate, in intensive agriculture, when grazing is supplemented with extra fodder, rates can be 5 to 10 GV/ha.[citation needed] In Europe average stocking rates vary depending on the country, in 2000 the Netherlands and Belgium had a very high rate of 3.82 GV/ha and 3.19 GV/ha respectively, surrounding countries have rates of around 1 to 1.5 GV/ha, and more southern European countries have lower rates, with Spain having the lowest rate of 0.44 GV/ha.[31]

This system can also be applied to natural areas. Grazing megaherbivores at roughly 1 GV/ha is considered sustainable in central European grasslands, although this varies widely depending on many factors. In ecology it is theoretically (i.e. cyclic succession, patch dynamics, Megaherbivorenhypothese) taken that a grazing pressure of 0.3 GV/ha by wildlife is enough to hinder afforestation in a natural area. Because different species have different ecological niches, with horses for example grazing short grass, cattle longer grass, and goats or deer preferring to browse shrubs, niche differentiation allows a terrain to have slightly higher carrying capacity for a mixed group of species, than it would if there were only one species involved.[citation needed]

Some niche market schemes mandate lower stocking rates than can maximally be grazed on a pasture. In order to market ones' meat products as 'biodynamic', a lower Großvieheinheit of 1 to 1.5 (2.0) GV/ha is mandated, with some farms having an operating structure using only 0.5 to 0.8 GV/ha.[citation needed]

The Food and Agriculture Organization has introduced three international units to measure carrying capacity: FAO Livestock Units for North America,[32][33] FAO Livestock Units for sub-Saharan Africa,[32][33] and Tropical Livestock Units.[34]

Another rougher and less precise method of determining the carrying capacity of a paddock is simply by looking objectively at the condition of the herd. In Australia, the national standardized system for rating livestock conditions is done by body condition scoring (BCS). An animal in a very poor condition is scored with a BCS of 0, and an animal which is extremely healthy is scored at 5: animals may be scored between these two numbers in increments of 0.25. At least 25 animals of the same type must be scored to provide a statistically representative number, and scoring must take place monthly -if the average falls, this may be due to a stocking rate above the paddock's carrying capacity or too little fodder. This method is less direct for determining stocking rates than looking at the pasture itself, because the changes in the condition of the stock may lag behind changes in the condition of the pasture.[23]

Fisheries

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A fishery at sunset in Cochin, Kerala, India
Main article: Population dynamics of fisheries

In fisheries, carrying capacity is used in the formulae to calculate sustainable yields for fisheries management.[35] The maximum sustainable yield (MSY) is defined as "the highest average catch that can be continuously taken from an exploited population (=stock) under average environmental conditions". MSY was originally calculated as half of the carrying capacity, but has been refined over the years,[36] now being seen as roughly 30% of the population, depending on the species or population.[37][38] Because the population of a species which is brought below its carrying capacity due to fishing will find itself in the exponential phase of growth, as seen in the Verhulst model, the harvesting of an amount of fish at or below MSY is a surplus yield which can be sustainably harvested without reducing population size at equilibrium, keeping the population at its maximum recruitment. However, annual fishing can be seen as a modification of r in the equation -i.e. the environment has been modified, which means that the population size at equilibrium with annual fishing is slightly below what K would be without it.

Note that mathematically and in practical terms, MSY is problematic. If mistakes are made and even a tiny amount of fish are harvested each year above the MSY, populations dynamics imply that the total population will eventually decrease to zero. The actual carrying capacity of the environment may fluctuate in the real world, which means that practically, MSY may actually vary from year to year[39][40][41] (annual sustainable yields and maximum average yield attempt to take this into account).[citation needed] Other similar concepts are optimum sustainable yield and maximum economic yield; these are both harvest rates below MSY.[42][43]

These calculations are used to determine fishing quotas.[citation needed]

Humans

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Human carrying capacity is a function of how people live and the technology at their disposal. The two great economic revolutions that marked human history up to 1900—the agricultural and industrial revolutions—greatly increased the Earth's human carrying capacity, allowing human population to grow from 5 to 10 million people in 10,000 BCE to 1.5 billion in 1900.[44] The immense technological improvements of the past 100 years—in applied chemistry, physics, computing, genetic engineering, and more—have further increased Earth's human carrying capacity, at least in the short term. Without the Haber-Bosch process for fixing nitrogen, modern agriculture could not support 8 billion people.[45] Without the Green Revolution of the 1950s and 60s, famine might have culled large numbers of people in poorer countries during the last three decades of the twentieth century.[46]

Recent technological successes, however, have come at grave environmental costs. Climate change, ocean acidification, and the huge dead zones at the mouths of many of world's great rivers, are a function of the scale of contemporary agriculture[47] and the many other demands 8 billion people make on the planet.[48] Scientists now speak of humanity exceeding or threatening to exceed 9 planetary boundaries for safe use of the biosphere.[49] Humanity's unprecedented ecological impacts threaten to degrade the ecosystem services that people and the rest of life depend on—potentially decreasing Earth's human carrying capacity.[50] The signs that we have crossed this threshold are increasing.[51][52]  

The fact that degrading Earth's essential services is obviously possible, and happening in some cases, suggests that 8 billion people may be above Earth's human carrying capacity. But human carrying capacity is always a function of a certain number of people living a certain way.[53][54] This was encapsulated by Paul Ehrlich and James Holdren's (1972) IPAT equation: environmental impact (I) = population (P) x affluence (A) x the technologies used to accommodate human demands (T).[55] IPAT has found spectacular confirmation in recent decades within climate science, where the Kaya identity for explaining changes in CO2 emissions is essentially IPAT with two technology factors broken out for ease of use.[56]

This suggests to technological optimists that new technological discoveries (or the deployment of existing ones) could continue to increase Earth's human carrying capacity, as it has in the past.[57] Yet technology has unexpected side effects, as we have seen with stratospheric ozone depletion, excessive nitrogen deposition in the world's rivers and bays, and global climate change.[50][5] This suggests that 8 billion people may be sustainable for a few generations, but not over the long term, and the term ‘carrying capacity’ implies a population that is sustainable indefinitely. It is possible, too, that efforts to anticipate and manage the impacts of powerful new technologies, or to divide up the efforts needed to keep global ecological impacts within sustainable bounds among more than 200 nations all pursuing their own self-interest, may prove too complicated to achieve over the long haul.[58]

One issue with applying carrying capacity to any species is that ecosystems are not constant and change over time, therefore changing the resources available. Research has shown that sometimes the presence of human populations can increase local biodiversity, demonstrating that human habitation does not always lead to deforestation and decreased biodiversity. Another issue to consider when applying carrying capacity, especially to humans, is that measuring food resources is arbitrary. This is due to choosing what to consider (e.g., whether or not to include plants that are not available every year), how to classify what is considered (e.g., classifying edible plants that are not usually eaten as food resources or not), and determining if caloric values or nutritional values are privileged. Additional layers to this for humans are their cultural differences in taste (e.g., some consume flying termites) and individual choices on what to invest their labor into (e.g., fishing vs. farming), both of which vary over time. This leads to the need to determine whether or not to include all food resources or only those the population considered will consume. Carrying capacity measurements over large areas also assumes homogeneity in the resources available but this does not account for how resources and access to them can greatly vary within regions and populations. They also assume that the populations in the region only rely on that region’s resources even though humans exchange resources with others from other regions and there are few, if any, isolated populations. Variations in standards of living which directly impact resource consumption are also not taken into account. These issues show that while there are limits to resources, a more complex model of how humans interact with their ecosystem needs to be used to understand them.[59]

Recent warnings that humanity may have exceeded Earth's carrying capacity

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Between 1900 and 2020, Earth's human population increased from 1.6 billion to 7.8 billion (a 390% increase).[60] These successes greatly increased human resource demands, generating significant environmental degradation.[61]

Millennium ecosystem assessment

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The Millennium Ecosystem Assessment (MEA) of 2005 was a massive, collaborative effort to assess the state of Earth's ecosystems, involving more than 1,300 experts worldwide.[61] Their first two of four main findings were the following. The first finding is:

Over the past 50 years, humans have changed ecosystems more rapidly and extensively than in any comparable period of time in human history, largely to meet rapidly growing demands for food, fresh water, timber, fiber, and fuel. This has resulted in a substantial and largely irreversible loss in the diversity of life on Earth.[62]

The second of the four main findings is:

The changes that have been made to ecosystems have contributed to substantial net gains in human well-being and economic development, but these gains have been achieved at growing costs in the form of the degradation of many ecosystem services, increased risks of nonlinear changes, and the exacerbation of poverty for some groups of people. These problems, unless addressed, will substantially diminish the benefits that future generations obtain from ecosystems.[62]

According to the MEA, these unprecedented environmental changes threaten to reduce the Earth's long-term human carrying capacity. “The degradation of ecosystem services could grow significantly worse during the first half of this [21st] century,” they write, serving as a barrier to improving the lives of poor people around the world.[62]

Critiques of Carrying Capacity with Relation to Humans

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Humans and human culture itself are highly adaptable things that have overcome issues that seemed incomprehensible at the time before. It is not to say that carrying capacity is not something that should be considered and thought about, but it should be taken with some skepticism when presented as a concretely evidenced proof of something. Many biologists, ecologists, and social scientists have disposed of the term altogether due to the generalizations that are made that gloss over the complexity of interactions that take place on the micro and macro level. Carrying capacity in a human environment is subject to change at any time due to the highly adaptable nature of human society and culture. If resources, time, and energy are put into an issue, there very well may be a solution that exposes itself. This also should not be used as an excuse to overexploit or take advantage of the land or resources that are available. Nonetheless, it is possible to not be pessimistic as technological, social, and institutional adaptions could be accelerated, especially in a time of need, to solve problems, or in this case, increase carrying capacity. There are also of course resources on this Earth that are limited that most certainly will run out if overused or used without proper oversight/ checks and balances. If things are left without remaining checked then overconsumption and exploitation of land and resources is likely to occur.[63]

Ecological footprint accounting

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Ecological Footprint accounting measures the demands people make on nature and compares them to available supplies, for both individual countries and the world as a whole.[64] Developed originally by Mathis Wackernagel and William Rees, it has been refined and applied in a variety of contexts over the years by Global Footprint Network (GFN). On the demand side, the Ecological Footprint measures how fast a population uses resources and generates wastes, with a focus on five main areas: carbon emissions (or carbon footprint), land devoted to direct settlement, timber and paper use, food and fiber use, and seafood consumption.[65] It converts these into per capita or total hectares used. On the supply side, national or global biocapacity represents the productivity of ecological assets in a particular nation or the world as a whole; this includes “cropland, grazing land, forest land, fishing grounds, and built-up land.”[65] Again the various metrics to capture biocapacity are translated into the single term of hectares of available land. As Global Footprint Network (GFN) states:

Each city, state or nation’s Ecological Footprint can be compared to its biocapacity, or that of the world. If a population’s Ecological Footprint exceeds the region’s biocapacity, that region runs a biocapacity deficit. Its demand for the goods and services that its land and seas can provide—fruits and vegetables, meat, fish, wood, cotton for clothing, and carbon dioxide absorption—exceeds what the region’s ecosystems can regenerate. In more popular communications, this is called “an ecological deficit.” A region in ecological deficit meets demand by importing, liquidating its own ecological assets (such as overfishing), and/or emitting carbon dioxide into the atmosphere. If a region’s biocapacity exceeds its Ecological Footprint, it has a biocapacity reserve.[65]

According to the GFN's calculations, humanity has been using resources and generating wastes in excess of sustainability since approximately 1970: currently humanity use Earth's resources at approximately 170% of capacity.[66][67] This implies that humanity is well over Earth's human carrying capacity for our current levels of affluence and technology use. According to Global Footprint Network:

In 2024, [Earth Overshoot Day] fell on August 1. Earth Overshoot Day marks the date when humanity has exhausted nature’s budget for the year. For the rest of the year, we are maintaining our ecological deficit by drawing down local resource stocks and accumulating carbon dioxide in the atmosphere. We are operating in overshoot.[68]

The concept of ‘ecological overshoot’ can be seen as equivalent to exceeding human carrying capacity.[69][64] According to the most recent calculations from Global Footprint Network, most of the world's residents live in countries in ecological overshoot (see the map on the right).

Nations living within their ecological means (shaded green) or in ecological overshoot (shaded red) in 2022.

This includes countries with dense populations (such as China, India, and the Philippines), countries with high per capita consumption and resource use (France, Germany, and Saudi Arabia), and countries with both high per capita consumption and large numbers of people (Japan, the United Kingdom, and the United States).[65]

Planetary Boundaries Framework

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According to its developers, the planetary boundaries framework defines “a safe operating space for humanity based on the intrinsic biophysical processes that regulate the stability of the Earth system.”[49] Human civilization has evolved in the relative stability of the Holocene epoch; crossing planetary boundaries for safe levels of atmospheric carbon, ocean acidity, or one of the other stated boundaries could send the global ecosystem spiraling into novel conditions that are less hospitable to life—possibly reducing global human carrying capacity. This framework, developed in an article published in 2009 in Nature[70] and then updated in two articles published in 2015 in Science[49] and in 2018 in PNAS,[71]  identifies nine stressors of planetary support systems that need to stay within critical limits to preserve stable and safe biospheric conditions (see figure below). Climate change and biodiversity loss are seen as especially crucial, since on their own, they could push the Earth system out of the Holocene state: “transitions between time periods in Earth history have often been delineated by substantial shifts in climate, the biosphere, or both.” [49]

Estimates of how the different control variables for seven of nine planetary boundaries have changed from 1950 to present. The green shaded polygon represents the safe operating space.

The scientific consensus is that humanity has exceeded three to five of the nine planetary boundaries for safe use of the biosphere and is pressing hard on several more.[71] By itself, crossing one of the planetary boundaries does not prove humanity has exceeded Earth's human carrying capacity; perhaps technological improvements or clever management might reduce this stressor and bring us back within the biosphere's safe operating space. But when several boundaries are crossed, it becomes harder to argue that carrying capacity has not been breached.[72] Because fewer people helps reduce all nine planetary stressors, the more boundaries are crossed, the clearer it appears that reducing human numbers is part of what is needed to get back within a safe operating space.[73][74] Population growth regularly tops the list of causes of humanity's increasing impact on the natural environment in Earth system science literature.[75] Recently, planetary boundaries developer Will Steffen and co-authors ranked global population change as the leading indicator of the influence of socio-economic trends on the functioning of the Earth system in the modern era, post-1750.[76]

See also

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Further reading

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References

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  1. ^ a b Chapman, Eric J.; Byron, Carrie J. (January 2018). "The flexible application of carrying capacity in ecology". Global Ecology and Conservation. 13: e00365. doi:10.1016/j.gecco.2017.e00365.
  2. ^ Turner, Graham (2008) "A comparison of The Limits to Growth with thirty years of reality" Archived 28 November 2010 at the Wayback Machine Commonwealth Scientific and Industrial Research Organisation (CSIRO) Sustainable Ecosystems.
  3. ^ Barnosky, AD; Hadly, EA; et al. (2012). "Approaching a state shift in Earth's biosphere". Nature. 486 (7401): 52–58. Bibcode:2012Natur.486...52B. doi:10.1038/nature11018. hdl:10261/55208. PMID 22678279. S2CID 4788164.
  4. ^ Armstrong McKay, David I.; Staal, Arie; Abrams, Jesse F.; Winkelmann, Ricarda; Sakschewski, Boris; Loriani, Sina; Fetzer, Ingo; Cornell, Sarah E.; Rockström, Johan; Lenton, Timothy M. (2022-09-09). "Exceeding 1.5°C global warming could trigger multiple climate tipping points". Science. 377 (6611): eabn7950. doi:10.1126/science.abn7950. hdl:10871/131584. ISSN 0036-8075. PMID 36074831. S2CID 252161375.
  5. ^ a b Bradshaw, Corey J. A.; Ehrlich, Paul R.; Beattie, Andrew; Ceballos, Gerardo; Crist, Eileen; Diamond, Joan; Dirzo, Rodolfo; Ehrlich, Anne H.; Harte, John; Harte, Mary Ellen; Pyke, Graham; Raven, Peter H.; Ripple, William J.; Saltré, Frédérik; Turnbull, Christine (2021-01-13). "Underestimating the Challenges of Avoiding a Ghastly Future". Frontiers in Conservation Science. 1: 615419. doi:10.3389/fcosc.2020.615419. ISSN 2673-611X.
  6. ^ Examples include Lianos, T. P., & Pseiridis, A. (2016). Sustainable welfare and optimum population size. Environment, Development and Sustainability, 18(6), 1679-1699; Tucker, C. K. (2019). A Planet of 3 Billion: Mapping Humanity's Long History of Ecological Destruction and Finding Our Way to a Resilient Future: a Global Citizen's Guide to Saving the Planet. Atlas Observatory Press; Dasgupta, P. (2019). Time and the generations: population ethics for a diminishing planet. Columbia University Press; Tamburino, L., & Bravo, G. (2021). Reconciling a positive ecological balance with human development: A quantitative assessment. Ecological Indicators, 129, 107973.
  7. ^ Verhulst, Pierre-François (1838). "Notice sur la loi que la population poursuit dans son accroissement" (PDF). Correspondance Mathématique et Physique. 10: 113–121. Retrieved 3 December 2014.
  8. ^ a b Berkshire encyclopedia of sustainability. Great Barrington, MA: Berkshire Publishing Group. 2010–2012. ISBN 978-1-933782-01-0. OCLC 436221172.
  9. ^ a b c d Sayre, N. F. (2008). "The Genesis, History, and Limits of Carrying Capacity". Annals of the Association of American Geographers. 98 (1): 120–134. doi:10.1080/00045600701734356. JSTOR 25515102. S2CID 16994905.
  10. ^ Zimmerer, Karl S. (1994). "Human Geography and the "New Ecology": The Prospect and Promise of Integration" (PDF). Annals of the Association of American Geographers. 84: 108–125. doi:10.1111/j.1467-8306.1994.tb01731.x. Archived (PDF) from the original on 2011-07-19.
  11. ^ a b c d Dhondt, André A. (January 1988). "Carrying capacity - a confusing concept". Acta Oecologica. 9 (4): 337–346. Retrieved 19 March 2021.
  12. ^ a b McLeod, Steven R. (September 1997). "Is the Concept of Carrying Capacity Useful in Variable Environments?". Oikos. 79 (3): 529–542. Bibcode:1997Oikos..79..529M. doi:10.2307/3546897. JSTOR 3546897.
  13. ^ Leopold, Aldo (1933). Game Management. New York: Charles Sccribener's Sons. p. 51.
  14. ^ Odum, Eugene P. (1959). Fundamentals of Ecology (2nd ed.). Philadelphia and London: W. B. Saunders Co. pp. 183-188. ISBN 9780721669410. OCLC 554879.
  15. ^ "Limiting Factors". education.nationalgeographic.org. Retrieved 2023-12-01.
  16. ^ a b c Storch, David; Okie, Jordan G. (October 2019). "The carrying capacity for species richness". Global Ecology and Biogeography. 28 (10): 1519–1532. Bibcode:2019GloEB..28.1519S. doi:10.1111/geb.12987. S2CID 202026304.
  17. ^ Rees, William E. (October 1992). "Ecological footprints and appropriated carrying capacity: what urban economics leaves out". Environment and Urbanization. 4 (2): 121–130. Bibcode:1992EnUrb...4..121R. doi:10.1177/095624789200400212.
  18. ^ Verhulst, Pierre-François (1838). "Notice sur la loi que la population poursuit dans son accroissement" (PDF). Correspondance Mathématique et Physique. 10: 113–121. Retrieved 3 December 2014.
  19. ^ Verhulst, Pierre-François (1845). "Recherches mathématiques sur la loi d'accroissement de la population" [Mathematical Researches into the Law of Population Growth Increase]. Nouveaux Mémoires de l'Académie Royale des Sciences et Belles-Lettres de Bruxelles. 18: 1–42. doi:10.3406/marb.1845.3438. S2CID 157536237. Retrieved 2013-02-18.
  20. ^ Swafford, Angela Lynn. "Logistic Population Growth: Equation, Definition & Graph." Study.com. N.p., 30 May 2015. Web. 21 May 2016. "Logistic Population Growth - Boundless Open Textbook." Boundless. N.p., n.d. Web. 21 May 2016.
  21. ^ Seidl, Irmi; Tisdell, Clem A (December 1999). "Carrying capacity reconsidered: from Malthus' population theory to cultural carrying capacity" (PDF). Ecological Economics. 31 (3): 395–408. Bibcode:1999EcoEc..31..395S. doi:10.1016/S0921-8009(99)00063-4. Archived (PDF) from the original on 2017-08-21.
  22. ^ Hui, C (2006). "Carrying capacity, population equilibrium, and environment's maximal load". Ecological Modelling. 192 (1–2): 317–320. Bibcode:2006EcMod.192..317H. doi:10.1016/j.ecolmodel.2005.07.001.
  23. ^ a b "4 - Determine carrying capacity and stocking rate". More Beef from Pastures. Meat & Livestock Australia Limited. 2019. Retrieved 14 March 2021.
  24. ^ Chesterton, Chris, Revised Calculation of Livestock Units for Higher Level Stewardship Agreements, Technical Advice Note 33 (Second edition), Rural Development Service, 2006 Archived June 26, 2007, at the Wayback Machine
  25. ^ Nix, J. 2009. Farm Management Pocketbook. 39th Ed. Corby: The Andersons Centre.
  26. ^ New Zealand Livestock Units on Ruralfind Archived 2010-05-25 at the Wayback Machine
  27. ^ Cornforth, I S and Sinclair, A G, Fertiliser Recommendations for Pastures and Crops in New Zealand, 2nd Ed (New Zealand Ministry of Agriculture, Wellington, New Zealand, 1984), quoted in A History of the Stock Unit System, New Zealand Ministry of Agriculture Archived 2010-05-23 at the Wayback Machine
  28. ^ Jasper Womach, Report for Congress: Agriculture: A Glossary of Terms, Programs, and Laws, 2005 Edition "Archived copy" (PDF). Archived from the original (PDF) on 2011-02-12. Retrieved 2011-12-10.{{cite web}}: CS1 maint: archived copy as title (link)
  29. ^ Coefficients de conversion des animaux en unités de gros bétail (French): Conversion factors for livestock units.
  30. ^ La Commission Européen: Agriculture et Environnement (French) Archived 2010-01-02 at the Wayback Machine European Commission, Agriculture and Environment (English version).
  31. ^ top agrar 11/2001, o.n.A.
  32. ^ a b "P Chilonda and J Otte, Indicators to monitor trends in livestock production at national, regional and international levels, Livestock Research for Rural Development, 18 (8), 2006, Article #117".
  33. ^ a b "Compendium of Agricultural-Environmental Indicators, Annexe 2: Definitions, Food and Agriculture Organization of the United Nations (includes different values for various regions)" (PDF).[permanent dead link]
  34. ^ FAO paper about Tropical Livestock Units Archived 2011-02-23 at the Wayback Machine
  35. ^ Quinn, Terrance J. (28 June 2008). "Ruminations on the development and future of population dynamics models in fisheries". Natural Resource Modeling. 16 (4): 341–392. doi:10.1111/j.1939-7445.2003.tb00119.x. S2CID 153420994.
  36. ^ Tsikliras, Athanassios C.; Froese, Rainer (2019). "Maximum Sustainable Yield". Encyclopedia of Ecology (2nd ed.). Elsevier. pp. 108–115. doi:10.1016/B978-0-12-409548-9.10601-3. ISBN 9780444641304. S2CID 150025979.
  37. ^ Bousquet, N.; Duchesne, T.; Rivest, L.-P. (2008). "Redefining the maximum sustainable yield for the Schaefer population model including multiplicative environmental noise" (PDF). Journal of Theoretical Biology. 254 (1): 65–75. Bibcode:2008JThBi.254...65B. doi:10.1016/j.jtbi.2008.04.025. PMID 18571675.[permanent dead link]
  38. ^ Thorpe, R.B.; LeQuesne, W.J.F.; Luxford, F.; Collie, J.S.; Jennings, S. (2015). "Evaluation and management implications of uncertainty in a multispecies size-structured model of population and community responses to fishing". Methods in Ecology and Evolution. 6 (1): 49–58. Bibcode:2015MEcEv...6...49T. doi:10.1111/2041-210X.12292. PMC 4390044. PMID 25866615.
  39. ^ Milner-Gulland, E.J., Mace, R. (1998), Conservation of biological resources Wiley-Blackwell. ISBN 978-0-86542-738-9
  40. ^ Larkin, P. A. (1977). "An epitaph for the concept of maximum sustained yield". Transactions of the American Fisheries Society. 106 (1): 1–11. Bibcode:1977TrAFS.106....1L. doi:10.1577/1548-8659(1977)106<1:AEFTCO>2.0.CO;2.
  41. ^ Botsford, L.W.; Castilla, J.C.; Peterson, C.H. (1997). "The management of fisheries and marine ecosystems". Science. 277 (5325): 509–515. doi:10.1126/science.277.5325.509.
  42. ^ Clark, C.W. (1990), Mathematical Bioeconomics: The Optimal Management of Renewable Resources, 2nd ed. Wiley-Interscience, New York
  43. ^ National Marine Fisheries Service (NMFS). 1996. Our Living Oceans: Report on the Status of U.S. Living Marine Resources 1995. NOAA Technical Memorandum NMFS0F/SPO-19. NMFS, Silver Springs, Md.
  44. ^ "Historical Estimates of World Population". Census.gov.
  45. ^ Smil, Vaclav (1999). "Detonator of the population explosion". Nature. 400 (6743): 415. Bibcode:1999Natur.400..415S. doi:10.1038/22672. ISSN 0028-0836. S2CID 4301828.
  46. ^ Gollin, Douglas; Hansen, Casper Worm; Wingender, Asger Mose (2021). "Two Blades of Grass: The Impact of the Green Revolution". Journal of Political Economy. 129 (8): 2344–2384. doi:10.1086/714444. ISSN 0022-3808. S2CID 53401811.
  47. ^ Crist, Eileen; Mora, Camilo; Engelman, Robert (2017-04-21). "The interaction of human population, food production, and biodiversity protection". Science. 356 (6335): 260–264. Bibcode:2017Sci...356..260C. doi:10.1126/science.aal2011. ISSN 0036-8075. PMID 28428391. S2CID 12770178.
  48. ^ Ripple, William J.; Wolf, Christopher; Newsome, Thomas M.; Galetti, Mauro; Alamgir, Mohammed; Crist, Eileen; Mahmoud, Mahmoud I.; Laurance, William F. (2017-11-13). "World Scientists' Warning to Humanity: A Second Notice". BioScience. 67 (12): 1026–1028. doi:10.1093/biosci/bix125. hdl:11336/71342. ISSN 0006-3568.
  49. ^ a b c d Steffen, Will; Richardson, Katherine; Rockström, Johan; Cornell, Sarah E.; Fetzer, Ingo; Bennett, Elena M.; Biggs, Reinette; Carpenter, Stephen R.; de Vries, Wim; de Wit, Cynthia A.; Folke, Carl; Gerten, Dieter; Heinke, Jens; Mace, Georgina M.; Persson, Linn M. (2015-02-13). "Planetary boundaries: Guiding human development on a changing planet". Science. 347 (6223). doi:10.1126/science.1259855. hdl:1885/13126. ISSN 0036-8075. PMID 25592418. S2CID 206561765.
  50. ^ a b (Program), Millennium Ecosystem Assessment (2005). Ecosystems and human well-being : synthesis. Island Press. ISBN 1-59726-039-8. OCLC 1264940723.
  51. ^ IPCC, 2014: Summary for Policymakers. In: Climate Change 2014: Mitigation of Climate Change. Contribution of Work- ing Group III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change [Edenhofer, O., R. Pichs-Madruga, Y. Sokona, E. Farahani, S. Kadner, K. Seyboth, A. Adler, I. Baum, S. Brunner, P. Eickemeier, B. Kriemann, J. Savolainen, S. Schlömer, C. von Stechow, T. Zwickel and J.C. Minx (eds.)]. Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA.
  52. ^ IPBES. (2019). Summary for policymakers. Global assessment report on biodiversity and ecosystem services. Intergovernmental Panel on Biodiversity and Ecosystem Services Secretariat.
  53. ^ Pimentel, David; Harman, Rebecca; Pacenza, Matthew; Pecarsky, Jason; Pimentel, Marcia (1994). "Natural resources and an optimum human population". Population and Environment. 15 (5): 348. doi:10.1007/BF02208317. ISSN 0199-0039. S2CID 153634463.
  54. ^ S., Dasgupta, Partha (2019). Time and the generations : population ethics for a diminishing planet. Columbia University Press. ISBN 978-0-231-16012-4. OCLC 1097199008.{{cite book}}: CS1 maint: multiple names: authors list (link)
  55. ^ P.R. Ehrlich and J.P. Holdren. One-dimensional ecology. Bulletin of the Atomic Scientists, May 1972: 16-27
  56. ^ Environment, energy, and economy : strategies for sustainability. Yōichi Kaya, Keiichi Yokobori, Energy, and Economic Development" Tokyo Conference on "Global Environment. Tokyo: United Nations University Press. 1997. ISBN 0-585-22996-1. OCLC 45731212.{{cite book}}: CS1 maint: others (link)
  57. ^ Simon, Julian Lincoln (1981). The ultimate resource. Princeton, N.J.: Princeton University Press. ISBN 0-691-09389-X. OCLC 7177304.
  58. ^ Mark., Gardiner, Stephen (2011). A perfect moral storm : understanding the ethical tragedy of climate change. Oxford University Press. ISBN 978-0-19-537944-0. OCLC 753470941.{{cite book}}: CS1 maint: multiple names: authors list (link)
  59. ^ Cliggett, Lisa (2001). "Carrying Capacity's New Guise: Folk Models for Public Debate and Longitudinal Study of Environmental Change". Africa Today. 48 (1): 3–19. doi:10.1353/at.2001.0003. ISSN 1527-1978.
  60. ^ "World Population Prospects - Population Division - United Nations". population.un.org. UN Department of Economic and Social Affairs. 2022.
  61. ^ a b Reid, W. V., et al. (2005). The millennium ecosystem assessment: Ecosystems and human well-being. Washington, DC: Island Press.
  62. ^ a b c Reid, W. V., et al. (2005). The millennium ecosystem assessment: Ecosystems and human well-being. Washington, DC: Ecosystems and Human Well-Being: A Synthesis, p. 1.
  63. ^ Cliggett, L., 2001. Carrying capacity's new guise: folk models for public debate and longitudinal study of environmental change. Africa Today, pp.3-19.
  64. ^ a b Mathis Wackernagel and Bert Beyers, 2019. Ecological Footprint: Managing Our Biocapacity Budget. New Society Publishers.
  65. ^ a b c d "Global Footprint". Global Footprint Network.
  66. ^ "Footprint Data Platform". Global Footprint Network.
  67. ^ ,"LIVING PLANET REPORT 2020: BENDING THE CURVE OF BIODIVERSITY LOSS". Climate Change and Law Collection. doi:10.1163/9789004322714_cclc_2020-0074-0399. Retrieved 2023-06-30.
  68. ^ "Earth Overshoot Day". Global Footprint Network.
  69. ^ Catton, W. R. (1982). Overshoot: The ecological basis of revolutionary change. University of Illinois Press.
  70. ^ Rockström, Johan; Steffen, Will; Noone, Kevin; Persson, Åsa; Chapin, F. Stuart III; Lambin, Eric; Lenton, Timothy M.; Scheffer, Marten; Folke, Carl; Schellnhuber, Hans Joachim; Nykvist, Björn; de Wit, Cynthia A.; Hughes, Terry; van der Leeuw, Sander; Rodhe, Henning (2009). "Planetary Boundaries: Exploring the Safe Operating Space for Humanity". Ecology and Society. 14 (2). doi:10.5751/es-03180-140232. hdl:10535/5421. ISSN 1708-3087. S2CID 15182169.
  71. ^ a b Steffen, Will; Rockström, Johan; Richardson, Katherine; Lenton, Timothy M.; Folke, Carl; Liverman, Diana; Summerhayes, Colin P.; Barnosky, Anthony D.; Cornell, Sarah E.; Crucifix, Michel; Donges, Jonathan F.; Fetzer, Ingo; Lade, Steven J.; Scheffer, Marten; Winkelmann, Ricarda (2018). "Trajectories of the Earth System in the Anthropocene". Proceedings of the National Academy of Sciences. 115 (33): 8252–8259. Bibcode:2018PNAS..115.8252S. doi:10.1073/pnas.1810141115. ISSN 0027-8424. PMC 6099852. PMID 30082409.
  72. ^ Higgs, Kerryn (2017). "Limits to growth: human economy and planetary boundaries". The Journal of Population and Sustainability. 2 (1). doi:10.3197/jps.2017.2.1.15. ISSN 2398-5496.
  73. ^ Coole, Diana H. (2018). Should we control world population ?. Political theory today. Cambridge, UK Medford, MA: Polity press. ISBN 978-1-5095-2340-5.
  74. ^ Conly, Sarah (2016). One Child. Oxford University Press. doi:10.1093/acprof:oso/9780190203436.001.0001. ISBN 978-0-19-020343-6.
  75. ^ Bourban, Michel (2019). "Croissance démographique et changement climatique: repenser nos politiques dans le cadre des limites planétaires". La Pensée écologique. 3 (1): 19–37. doi:10.3917/lpe.003.0019. ISSN 2558-1465. S2CID 203184072.
  76. ^ Steffen, Will; Broadgate, Wendy; Deutsch, Lisa; Gaffney, Owen; Ludwig, Cornelia (2015). "The trajectory of the Anthropocene: The Great Acceleration". The Anthropocene Review. 2 (1): 84. Bibcode:2015AntRv...2...81S. doi:10.1177/2053019614564785. hdl:1885/66463. ISSN 2053-0196. S2CID 131524600.
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