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2018/12/30

Agroecology - Wikipedia



Agroecology - Wikipedia

Agroecology
From Wikipedia, the free encyclopedia

Agroecology
A community-supported agriculture share of crops
Product(s) agriculture


Agroecology is the study of ecological processes applied to agriculturalproduction systems. 

Bringing ecological principles to bear in agroecosystemscan suggest novel management approaches that would not otherwise be considered. The term is often used imprecisely and may refer to "a science, a movement, [or] a practice".[1]Agroecologists study a variety of agroecosystems

The field of agroecology is not associated with any one particular method of farming, whether it be organic, integrated, or conventional, intensive or extensive
However, it has much more in common with organic and integrated farming.[2]


Contents
1Ecological strategy


2Approaches
2.1Agro-population ecology
2.2Indigenous agroecology
2.3Inclusive agroecology



9External links
9.1Topic
9.2Courses
Ecological strategy[edit]

Agroecologists do not unanimously oppose technology or inputs in agriculture but instead assess how, when, and if technology can be used in conjunction with natural, social and human assets.[3] 

Agroecology proposes a context- or site-specific manner of studying agroecosystems, and as such, it recognizes that there is no universal formula or recipe for the success and maximum well-being of an agroecosystem. Thus, agroecology is not defined by certain management practices, such as the use of natural enemies in place of insecticides, or polyculture in place of monoculture.

Instead, agroecologists may study questions related to the four system properties of agroecosystems: 




As opposed to disciplines that are concerned with only one or some of these properties, agroecologists see all four properties as interconnected and integral to the success of an agroecosystem. Recognizing that these properties are found on varying spatial scales, agroecologists do not limit themselves to the study of agroecosystems at any one scale: 

gene-organism-population-community-ecosystem-landscape-biome, 
field-farm-community-region-state-country-continent-global.

Agroecologists study these four properties through an interdisciplinary lens, using natural sciences to understand elements of agroecosystems such as soil properties and 
plant-insect interactions, as well as 
using social sciences to understand the effects of farming practices on rural communities, economic constraints to developing new production methods, or
cultural factors determining farming practices.

Approaches

Agroecologists do not always agree about what agroecology is or should be in the long-term. Different definitions of the term agroecology can be distinguished largely by the specificity with which one defines the term "ecology", as well as the term's potential political connotations. Definitions of agroecology, therefore, may be first grouped according to the specific contexts within which they situate agriculture. Agroecology is defined by the OECD as "the study of the relation of agricultural crops and environment."[5] 

This definition refers to the "-ecology" part of "agroecology" narrowly as the natural environment. Following this definition, an agroecologist would study agriculture's various relationships with soil health, water quality, air quality, meso- and micro-fauna, surrounding flora, environmental toxins, and other environmental contexts.

A more common definition of the word can be taken from Dalgaard et al., who refer to agroecology as the study of the interactions between plants, animals, humans and the environment within agricultural systems. Consequently, agroecology is inherently multidisciplinary, including factors from agronomy, ecology, sociology, economics and related disciplines.[6] In this case, the "-ecology" portion of "agroecology is defined broadly to include social, cultural, and economic contexts as well. Francis et al. also expand the definition in the same way, but put more emphasis on the notion of food systems.[7]

Agroecology is also defined differently according to geographic location. In the global south, the term often carries overtly political connotations. Such political definitions of the term usually ascribe to it the goals of social and economic justice; special attention, in this case, is often paid to the traditional farming knowledge of indigenous populations.[8] North American and European uses of the term sometimes avoid the inclusion of such overtly political goals. In these cases, agroecology is seen more strictly as a scientific discipline with less specific social goals.

Agro-population ecology[edit]

This approach is derived from the science of ecology primarily based on population ecology, which over the past three decades has been displacing the ecosystems biology of Odum. Buttel explains the main difference between the two categories, saying that "the application of population ecology to agroecology involves the primacy not only of analyzing agroecosystems from the perspective of the population dynamics of their constituent species, and their relationships to climate and biogeochemistry, but also there is a major emphasis placed on the role of genetics."[9]

Indigenous agroecology[edit]

This concept was proposed by political ecologist Josep Garí to recognise and uphold the integrated agro-ecological practices of many indigenous peoples, who simultaneously and sustainably safeguard, manage and use ecosystems for agricultural, food, biodiversity and cultural purposes at the same time.[10] Indigenous agroecologies are not systems and practices halted in time, but keep co-evolving with new knowledge and resources, such as that provided by development projects, research initiatives and agro-biodiversity exchanges. In fact, the first agro-ecologists were indigenous peoples that advocated development policies and programmes to support their systems, rather than replacing them.[11]

Inclusive agroecology[edit]

Rather than viewing agroecology as a subset of agriculture, Wojtkowski[12][13] takes a more encompassing perspective. In this, natural ecology and agroecology are the major headings under ecology. Natural ecology is the study of organisms as they interact with and within natural environments. Correspondingly, agroecology is the basis for the land-use sciences. Here humans are the primary governing force for organisms within planned and managed, mostly terrestrial, environments.

As key headings, natural ecology and agroecology provide the theoretical base for their respective sciences. These theoretical bases overlap but differ in a major way. Economics has no role in the functioning of natural ecosystems whereas economics sets direction and purpose in agroecology.

Under agroecology are the three land-use sciences, agriculture, forestry, and agroforestry. Although these use their plant components in different ways, they share the same theoretical core.

Beyond this, the land-use sciences further subdivide. The subheadings include agronomy, organic farming, traditional agriculture, permaculture, and silviculture. Within this system of subdivisions, agroecology is philosophically neutral. The importance lies in providing a theoretical base hitherto lacking in the land-use sciences. This allows progress in biocomplex agroecosystems including the multi-species plantations of forestry and agroforestry.

Applications[edit]

To arrive at a point of view about a particular way of farming, an agroecologist would first seek to understand the contexts in which the farm(s) is(are) involved. Each farm may be inserted in a unique combination of factors or contexts. Each farmer may have their own premises about the meanings of an agricultural endeavor, and these meanings might be different from those of agroecologists. 

Generally, farmers seek a configuration that is viable in multiple contexts, such as family, financial, technical, political, logistical, market, environmental, spiritual. Agroecologists want to understand the behavior of those who seek livelihoods from plant and animal increase, acknowledging the organization and planning that is required to run a farm.

Views on organic and non-organic milk production[edit]

Because organic agriculture proclaims to sustain the health of soils, ecosystems, and people,[14] it has much in common with Agroecology;[citation needed] this does not mean that Agroecology is synonymous with organic agriculture, nor that Agroecology views organic farming as the 'right' way of farming.[citation needed] Also, it is important to point out that there are large differences in organic standards among countries and certifying agencies.
Three of the main areas that agroecologists would look at in farms, would be: the environmental impacts, animal welfare issues, and the social aspects.

Environmental impacts caused by organic and non-organic milk production can vary significantly. For both cases, there are positive and negative environmental consequences.

Compared to conventional milk production, organic milk production tends to have lower eutrophication potential per ton of milk or per hectare of farmland, because it potentially reduces leaching of nitrates (NO3−) and phosphates (PO4−) due to lower fertilizer application rates. Because organic milk production reduces pesticides utilization, it increases land use per ton of milk due to decreased crop yields per hectare. Mainly due to the lower level of concentrates given to cows in organic herds, organic dairy farms generally produce less milk per cow than conventional dairy farms. Because of the increased use of roughage and the, on-average, lower milk production level per cow, some research has connected organic milk production with increases in the emission of methane.[15]

Animal welfare issues vary among dairy farms and are not necessarily related to the way of producing milk (organically or conventionally).

A key component of animal welfare is freedom to perform their innate (natural) behavior, and this is stated in one of the basic principles of organic agriculture. Also, there are other aspects of animal welfare to be considered – such as freedom from hunger, thirst, discomfort, injury, fear, distress, disease and pain. Because organic standards require loose housing systems, adequate bedding, restrictions on the area of slatted floors, a minimum forage proportion in the ruminant diets, and tend to limit stocking densities both on pasture and in housing for dairy cows, they potentially promote good foot and hoof health. Some studies show lower incidence of placenta retention, milk fever, abomasums displacement and other diseases in organic than in conventional dairy herds.[16] However, the level of infections by parasites in organically managed herds is generally higher than in conventional herds.[17]

Social aspects of dairy enterprises include life quality of farmers, of farm labor, of rural and urban communities, and also includes public health.

Both organic and non-organic farms can have good and bad implications for the life qualityof all the different people involved in that food chain. Issues like labor conditions, labor hours and labor rights, for instance, do not depend on the organic/non-organic characteristic of the farm; they can be more related to the socio-economical and cultural situations in which the farm is inserted, instead.

As for the public health or food safety concern, organic foods are intended to be healthy, free of contaminations and free from agents that could cause human diseases. Organic milk is meant to have no chemical residues to consumers, and the restrictions on the use of antibiotics and chemicals in organic food production has the purpose to accomplish this goal. Although dairy cows in both organic and conventional farming practices can be exposed to pathogens, it has been shown that, because antibiotics are not permitted as a preventative measure in organic practices, there are far fewer antibiotic resistant pathogens on organic farms. This dramatically increases the efficacy of antibiotics when/if they are necessary.

In an organic dairy farm, an agroecologist could evaluate the following:
Can the farm minimize environmental impacts and increase its level of sustainability, for instance by efficiently increasing the productivity of the animals to minimize waste of feed and of land use?
Are there ways to improve the health status of the herd (in the case of organics, by using biological controls, for instance)?
Does this way of farming sustain good quality of life for the farmers, their families, rural labor and communities involved?
Views on no-till farming[edit]

No-tillage is one of the components of conservation agriculture practices and is considered more environmental friendly than complete tillage.[18][19] There is a general consensus that no-till can increase carbon content of topsoils, especially when combined with cover crops, but whether this improves the function of soils as a carbon sink is contested.[18][20] [21][22]

No-till can contribute to higher soil organic matter and organic carbon content in soils,[23][24] though reports of no-effects of no-tillage in organic matter and organic carbon soil contents also exist, depending on environmental and crop conditions.[25] In addition, no-till can indirectly reduce CO2 emissions by decreasing the use of fossil fuels.[23][26]

Most crops can benefit from the practice of no-till, but not all crops are suitable for complete no-till agriculture.[27][28] Crops that do not perform well when competing with other plants that grow in untilled soil in their early stages can be best grown by using other conservation tillage practices, like a combination of strip-till with no-till areas.[28] Also, crops which harvestable portion grows underground can have better results with strip-tillage,[citation needed] mainly in soils which are hard for plant roots to penetrate into deeper layers to access water and nutrients.

The benefits provided by no-tillage to predators may lead to larger predator populations,[29] which is a good way to control pests (biological control), but also can facilitate predation of the crop itself. In corn crops, for instance, predation by caterpillars can be higher in no-till than in conventional tillage fields.[30]

In places with rigorous winter, untilled soil can take longer to warm and dry in spring, which may delay planting to less ideal dates.[31][32] Another factor to be considered is that organic residue from the prior year's crops lying on the surface of untilled fields can provide a favorable environment to pathogens, helping to increase the risk of transmitting diseases to the future crop. And because no-till farming provides good environment for pathogens, insects and weeds, it can lead farmers to a more intensive use of chemicals for pest control.[citation needed] Other disadvantages of no-till include underground rot, low soil temperatures and high moisture.[citation needed]

Based on the balance of these factors, and because each farm has different problems, agroecologists will not attest that only no-till or complete tillage is the right way of farming.[citation needed] Yet, these are not the only possible choices regarding soil preparation, since there are intermediate practices such as strip-till, mulch-till and ridge-till, all of them – just as no-till – categorized as conservation tillage. Agroecologists, then, will evaluate the need of different practices for the contexts in which each farm is inserted.

In a no-till system, an agroecologist could ask the following:
Can the farm minimize environmental impacts and increase its level of sustainability; for instance by efficiently increasing the productivity of the crops to minimize land use?
Does this way of farming sustain good quality of life for the farmers, their families, rural labor and rural communities involved?


History[edit]
Pre-WWII[edit]

The notions and ideas relating to crop ecology have been around since at least 1911 when F.H. King released Farmers of Forty Centuries. King was one of the pioneers as a proponent of more quantitative methods for characterization of water relations and physical properties of soils.[7] In the late 1920s the attempt to merge agronomy and ecology was born with the development of the field of crop ecology. Crop ecology's main concern was where crops would be best grown.[33] Actually, it was only in 1928 that agronomy and ecology were formally linked by Klages.[7][34]

The first mention of the term agroecology was in 1928, with the publication of the term by Bensin in 1928.[35] The book of Tischler (1965), was probably the first to be actually titled 'agroecology'.[36] He analysed the different components (plants, animals, soils and climate) and their interactions within an agroecosystem as well as the impact of human agricultural management on these components. Other books dealing with agroecology, but without using the term explicitly were published by the German zoologist Friederichs (1930) with his book on agricultural zoology and related ecological/environmental factors for plant protection,[37] and by American crop physiologist Hansen in 1939[38] when both used the word as a synonym for the application of ecology within agriculture.[6][clarification needed]
Post-WWII[edit]

Gliessman mentions that post-WWII, groups of scientists with ecologists gave more focus to experiments in the natural environment, while agronomists dedicated their attention to the cultivated systems in agriculture.[33] According to Gliessman,[33] the two groups kept their research and interest apart until books and articles using the concept of agroecosystems and the word agroecology started to appear in 1970.[35] Dalgaard[6]explains the different points of view in ecology schools, and the fundamental differences, which set the basis for the development of agroecology. The early ecology school of Henry Gleason investigated plant populations focusing in the hierarchical levels of the organism under study.

Friederich Clement's ecology school, however included the organism in question as well as the higher hierarchical levels in its investigations, a "landscape perspective". However, the ecological schools where the roots of agroecology lie are even broader in nature. The ecology school of Tansley, whose view included both the biotic organism and their environment, is the one from which the concept of agroecosystems emerged in 1974 with Harper.[6][39]

In the 1960s and 1970s the increasing awareness of how humans manage the landscape and its consequences set the stage for the necessary cross between agronomy and ecology. Even though, in many ways the environmental movement in the US was a product of the times, the Green Decade,[clarification needed] spread an environmental awareness of the unintended consequences of changing ecological processes. Works such as Silent Spring, and The Limits to Growth, and changes in legislation such as the Clean Air Act, Clean Water Act, and the National Environmental Policy Act caused the public to be aware of societal growth patterns, agricultural production, and the overall capacity of the system.[6]


Fusion with ecology[edit]

After the 1970s, when agronomists saw the value of ecology and ecologists began to use the agricultural systems as study plots, studies in agroecology grew more rapidly.[33]Gliessman describes that the innovative work of Prof. Efraim Hernandez X., who developed research based on indigenous systems of knowledge in Mexico, led to education programs in agroecology.[40] In 1977 Prof. Efraim Hernandez X. explained that modern agricultural systems had lost their ecological foundation when socio-economicfactors became the only driving force in the food system.[7] The acknowledgement that the socio-economic interactions are indeed one of the fundamental components of any agroecosystems came to light in 1982, with the article Agroecologia del Tropico Americano by Montaldo. The author argues that the socio-economic context cannot be separated from the agricultural systems when designing agricultural practices.[7]

In 1995 Edens et al. in Sustainable Agriculture and Integrated Farming Systems solidified this idea proving his point by devoting special sections to economics of the systems, ecological impacts, and ethics and values in agriculture.[7] Actually, 1985 ended up being a fertile and creative year for the new discipline. For instance in the same year, Miguel Altieriintegrated how consolidation of the farms, and cropping systems impact pest populations. In addition, Gliessman highlighted that socio-economic, technological, and ecological components give rise to producer choices of food production systems.[7] These pioneering agroecologists have helped to frame the foundation of what we today consider the interdisciplinary field of agroecology and have led to advances in a number of farming systems. In Asian rice, for example, crop diversification by growing flowering crops in strips beside rice fields has recently been demonstrated to reduce pests so effectively (by the flower nectar attracting and supporting parasitoids and predators) that insecticide spraying is reduced by 70%, yields increase by 5%, together resulting in an economic advantage of 7.5% (Gurr et al., 2016).


By region[edit]

The principles of agroecology are expressed differently depending on local ecological and social contexts.
Latin America[edit]
Main article: Agroecology in Latin America

Latin America's experiences with North American Green Revolution agricultural techniques have opened space for agroecologists. Traditional or indigenous knowledge represents a wealth of possibility for agroecologists, including "exchange of wisdoms". See Miguel Alteiri's Enhancing the Productivity of Latin American Traditional Peasant Farming Systems Through an Agroecological Approach for information on agroecology in Latin America.

Agroecological techniques and knowledge played an important role in solving the severe food crisis in Cuba following the dissolution of the Soviet Union.[41] As part of Cuba's urban agricultural movement, agroecology is integral to production in Cuban organopónicos.[42]


Africa[edit]

Historically, agroecology has had low traction in Africa, as governments, international organisations, extension services and farmers' organisations tended to focus on issues of inputs and outputs as the defining factors to deal with recurrent food crises and chronic malnutrition in the continent. Agrocecology was only a minor proposal from a few, non-governmental, small-scale projects and a sort of "experimental" idea of the Farmer Field Schools programme.

In the early 2000s, when the AIDS pandemic was creating a major rural crisis across Africa, Josep Garí proposed FAO to consider an agroecological approach as the most effective way to empower farmers cope with the impacts of the AIDS pandemic on agriculture and food production: in particular, he proposed agro-biodiversity as a key resource and knowledge for farmers to address the labour and malnutrition crisis.[43] The proposal was rapidly adopted by the Farmer Field Schools scheme across the world, and even presented and translated in China.[44]

Most recently, agroecology has started to permeate projects and discourses on farming and natural-resource management in Africa. In 2011, the 1st encounter of agroecology trainers took place in Zimbabwe and issued the Shashe Declaration.


Madagascar[edit]
Main article: Agroecology in Madagascar

Most of the historical farming in Madagascar has been conducted by indigenous peoples. The French colonial period disturbed a very small percentage of land area, and even included some useful experiments in Sustainable forestry. Slash-and-burn techniques, a component of some shifting cultivation systems have been practised by natives in Madagascar for centuries. As of 2006 some of the major agricultural products from slash-and-burn methods are wood, charcoal and grass for Zebu grazing. These practices have taken perhaps the greatest toll on land fertility since the end of French rule, mainly due to overpopulation pressures.


See also[edit]

Agriculture and agronomy portal
Ecology portal


Agricultural biodiversity
Agriculture in Concert with the Environment
Agrobiodiversity
Agroecological restoration
Agroecosystem
Agrophysics
Aquaculture
Climate change and agriculture
Community development
Community-supported agriculture
Conventional agriculture
Climate change and agriculture
Climate change adaptation
Dynamic equilibrium
Edaphology
Ecological economics
Ecology of contexts
Ecosystem services
Environmental economics
Environmental engineering
Environmental impact assessment
Environmental impact of agriculture
Farmer-managed Natural Regeneration
Forest gardening
Food desert
Food-feed system
Food politics
Food sovereignty
Food security
Genetic erosion
Human ecology
International development
Intercropping
Integrated pest management
Land degradation
Landscape ecology
Life cycle analysis
Malnutrition
Managed intensive grazing
Nutrient management
Political ecology
Pollinator decline
Regenerative agriculture
Rural development
Secondary succession
Small-scale agriculture
Social metabolism
Socio-ecological system
Soil science
Sustainable agriculture
Sustainable development

References[edit]

  1. ^ Wezel, A., Bellon, S., Doré, T., Francis, C., Vallod, D., David, C. (2009). Agroecology as a science, a movement or a practice. A review. Agronomy for Sustainable Development (published online)
  2. ^ Wibblemann et al. (2013) Mainstreaming Agroecology: Implications for Global Food and Farming Systems. "Archived copy" (PDF). Archived from the original (PDF) on 2016-05-22. Retrieved 2015-05-19.
  3. ^ Pretty, Jules. 2008. Agricultural sustainability: concepts, principles and evidence. Philosophical Transactions of the Royal Society, 363, 447-465.
  4. ^ Conway, Gordon R. 1985. Agroecosystem analysis. Agricultural Administration, 20, 31-55.
  5. ^ Agroecology, Glossary of Statistical Terms
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  8. ^ Agroecology.org Archived 2006-04-22 at the Wayback Machine.
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  10. ^ Garí, Josep A. (2001). Biodiversity and Indigenous Agroecology in Amazonia. Etnoecologica 5 (7): 21-37
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  14. ^ IFOAM (International Federation for Organic Agriculture Movements)
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  17. ^ Bennedsgaard, T.W. et al. 2003. Eleven years of organic dairy production in Denmark: herd health and production related to time of conversion and compared to conventional production. Livestock production science. Vol 80, p 121-131.
  18. ^ Jump up to:a b Garcia-Torres, L. et al. 2002. Summary of the Workshop on Soil Protection and Sustainable Agriculture organized by the EU Commission DG Environment and the DG Environmental Quality of the Spanish Ministry of Environment (Soria, Spain)
  19. ^ Branco, H. and Lal, R. 2008. Principles of Conservation Management. No Tillage-Farming (Ch.8). Springer Verlag. Netherlands. P. 195
  20. ^ Bolliger, A. et al. 2006. Taking stock of the Brazilian "Zero Till Revolution": A review of landmark research and farmers' practice. Adv. Agron. Vol 91, p 47–110
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  22. ^ Powlson, D. S., Stirling, C. M., Jat, M. L., Gerard, B. G., Palm, C. A., Sanchez, P. A., & Cassman, K. G. (2014). Limited potential of no-till agriculture for climate change mitigation. Nature Climate Change, 4(8), 678.
  23. ^ Jump up to:a b Calegari, A. et al. 2008. Impact of Long-Term No-Tillage and Cropping System Management on Soil Organic Carbon in an Oxisol: A Model for Sustainability. Agronomy Journal. Vol 100, Issue 4, p 1013-1019
  24. ^ West, T. and Post, W. 2002. Soil Organic Carbon Sequestration Rates by Tillage and Crop Rotation: A Global Data Analysis. Soil Sci. Soc. Am. J. 66:1930–1946
  25. ^ Machado, P.L.O.A. and Silva, C.A. 2001. Soil management under no-tillage systems in the tropics with special reference to Brazil. Nutr. Cycling Agroecosyst. Vol 61, p 119–130
  26. ^ Koga, N. et al. 2003. Fuel consumption-derived CO2 emissions under conventional and reduced tillage cropping systems in northern Japan. Agriculture, Ecosystems and Environment. Vol 99, p 213–219.
  27. ^ Fleizo et al. 2002
  28. ^ Jump up to:a b Koller, K. 2003. Techniques of soil tillage. Ed. Adel El Titi (CRC Press)
  29. ^ Pavuk, D.M. 1994. Influence of weeds within Zea mays crop plantings on populations of adult Diabrotica barberi and Diabrotica virgifera virgifera. Agriculture, Ecosystems & Environment. Vol 50, p 165-175
  30. ^ G. E. Brust, B. Stinner & D. McCartney. 1986. Predator activity and predation in corn agroecosystems. Environmental Entomology 15:1017-1021
  31. ^ Randall, G.W., and P.R. Hill. 2000. Fall strip-tillage systems. p. 193–199. In R.C. Reeder (ed.) Conservation tillage systems and management. MWPS-45, 2nd ed. Iowa State Univ., Ames.
  32. ^ Licht, M.A. and Al-Kaisi, M. 2005. Strip-tillage effect on seedbed soil temperature and other soil physical properties. Soil and Tillage Research. Vol 80, p 233-249
  33. ^ Jump up to:a b c d Gliessman, Stephen. R Agroecology: Ecological Processes in Sustainable Agriculture. Ann Arbor: Sleeping Bear Press, 1998.
  34. ^ Klages, K.H.W. 1928. Crop ecology and ecological crop geography in the agronomic curriculum. J. Amer. Soc. Agron. 20:336-353.
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  36. ^ Tischler, W. (1965). Agrarökologie. Gustav Fischer Verlag, Jena, Germany, 499 pp.
  37. ^ Friederichs, K. (1930) Die Grundfragen und Gesetzmäßigkeiten der land- und forstwirtschaftlichen Zoologie. Vol. 1: Ökologischer Teil, Vol. 2: Wirtschaftlicher Teil. Verlagsbuchhandlung Paul Parey, Berlin, Germany, 417 and 443 pp.
  38. ^ Hansen, B., Alrøe, H.F., Kristensen, E.S., 2001. Approaches to assess the environmental impact of organic farming with particular regard to Denmark. Agric. Ecosys. Environ. 83, 11–26.
  39. ^ Harper, J.L., 1974. Agric. Ecosyst. Agroecosyst. 1, 1–6.
  40. ^ qtd. in Francis et al. 2003.
  41. ^ Funes, Fernando; García, Luis; Bourque, Martin; Pérez, Nilda; Rosset, Peter. Sustainable Agriculture and Resistance: Transforming Food Production in Cuba. Oakland, CA: Food First Books. ISBN 0-935028-87-0.
  42. ^ Cederlöf, Gustav (2016). "Low-carbon food supply: The ecological geography of Cuban urban agriculture and agroecological theory". Agriculture and Human Values. 33 (4): 771–784. doi:10.1007/s10460-015-9659-y.
  43. ^ Garí, Josep A. (2003). Agrobiodiversity strategies to combat food insecurity and HIV/AIDS impact in rural Africa. FAO / Population and Development Service, Rome.
  44. ^ Garí, Josep A. (2004). Plant diversity, sustainable rural livelihoods and the HIV/AIDS crisis. Bangkok: UNDP & FAO, 2004. Published in English and Chinese. ISBN 974-92021-4-7.



Further reading[edit]

Altieri, M.A. 1987. Agroecology: the scientific basis of alternative agriculture. Boulder: Westview Press.
Altieri, M.A. 1992. Agroecological foundations of alternative agriculture in California. Agriculture, Ecosystems and Environment 39: 23-53.
Buttel, F.H. and M.E. Gertler 1982. Agricultural structure, agricultural policy and environmental quality. Agriculture and Environment 7: 101-119.
Carrol, C. R., J.H. Vandermeer and P.M. Rosset. 1990. Agroecology. McGraw Hill Publishing Company, New York.
Paoletti, M.G., B.R. Stinner, and G.G. Lorenzoni, ed. Agricultural Ecology and Environment. New York: Elsevier Science Publisher B.V., 1989.
Robertson, Philip, and Scott M Swinton. "Reconciling agricultural productivity and environmental integrity: a grand challenge for agriculture." Frontiers in Ecology and the Environment 3.1 (2005): 38-46.
Savory, Allan; Jody Butterfield (1998-12-01) [1988]. Holistic Management: A New Framework for Decision Making (2nd ed.). Washington, D.C.: Island Press. ISBN 1-55963-487-1.
The Power of Community: How Cuba Survived Peak Oil. Yellow Springs,Ohio 45387: The Community Solution.
Vandermeer, J. 1995. The ecological basis of alternative agriculture. Annu. Rev. Ecol. Syst. 26: 201-224
Wojtkowski, P.A. 2002. Agroecological perspectives in agronomy, forestry and agroforestry. Science Publishers Inc., Enfield, New Hampshire.

Advances in Agroecology Book Series

Soil Organic Matter in Sustainable Agriculture (Advances in Agroecology) by Fred Magdoff and Ray R. Weil (Hardcover - May 27, 2004)
Agroforestry in Sustainable Agricultural Systems (Advances in Agroecology) by Louise E. Buck, James P. Lassoie, and Erick C.M. Fernandes (Hardcover - Oct 1, 1998)
Agroecosystem Sustainability: Developing Practical Strategies (Advances in Agroecology) by Stephen R. Gliessman (Hardcover - Sep 25, 2000)
Interactions Between Agroecosystems and Rural Communities (Advances in Agroecology) by Cornelia Flora (Hardcover - Feb 5, 2001)
Landscape Ecology in Agroecosystems Management (Advances in Agroecology) by Lech Ryszkowski (Hardcover - Dec 27, 2001)
Integrated Assessment of Health and Sustainability of Agroecosystems (Advances in Agroecology) by Thomas Gitau, Margaret W. Gitau, David Waltner-ToewsClive A. Edwards June 2008 | Hardback: 978-1-4200-7277-8 (CRC Press)
Multi-Scale Integrated Analysis of Agroecosystems (Advances in Agroecology) by Mario Giampietro 2003 | Hardback: 978-0-8493-1067-6 (CRC Press)
Soil Tillage in Agroecosystems (Advances in Agroecology) edited by Adel El Titi 2002 | Hardback: 978-0-8493-1228-1 (CRC Press)
Tropical Agroecosystems (Advances in Agroecology) edited by John H. Vandermeer 2002 | Hardback: 978-0-8493-1581-7 (CRC Press)
Structure and Function in Agroecosystem Design and Management (Advances in Agroecology) edited by Masae Shiyomi, Hiroshi Koizumi 2001 | Hardback: 978-0-8493-0904-5 (CRC Press)
Biodiversity in Agroecosystems (Advances in Agroecology) edited by Wanda W. Collins, Calvin O. Qualset 1998 | Hardback: 978-1-56670-290-4 (CRC Press)
Sustainable Agroecosystem Management: Integrating Ecology, Economics and Society. (Advances in Agroecology) edited by Patrick J. Bohlen and Gar House 2009 | Hardback: 978-1-4200-5214-5 (CRC Press)


External links[edit]
Topic[edit]
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Permaculture - Wikipedia

Permaculture - Wikipedia 

Permaculture
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Permaculture is a set of design principles centered around whole systems thinking simulating or directly utilizing the patterns and resilientfeatures observed in natural ecosystems. It uses these principles in a growing number of fields from regenerative agriculture, rewilding to community and organizational design and development.
With its
 system of applied education, research and citizen- led design permaculture has grown a popular web of global networks and developed into a global social movement[citation needed].

The term permaculture was developed and coined by David Holmgren, then a graduate student at the Tasmanian College of Advanced Education's Department of Environmental Design, and Bill Mollison, senior lecturer in Environmental Psychology at University of Tasmania, in 1978. [1] The word permaculture originally referred to "permanent agriculture",[2][3] but was expanded to stand also for "permanent culture", as it was understood that social aspects were integral to a truly sustainable system as inspired by Masanobu Fukuoka’s natural farming philosophy.

It has many branches that include, but are not limited to, ecological design, ecological engineering, regenerative design, environmental design, and construction

Permaculture also includes integrated water resources managementthat develops sustainable architecture, and regenerative and self-maintained habitatand agricultural systems modelled from natural ecosystems.[4][5]

Mollison has said: "Permaculture is a philosophy of working with, rather than against nature; of protracted and thoughtful observation rather than protracted and thoughtless labor; and of looking at plants and animals in all their functions, rather than treating any area as a single product system."[6]

The 12 principles of permaculture most commonly referred to are first described by David Holmgren in his book Permaculture: Principles and Pathways Beyond Sustainability (2002). They include: 


  1. Observe and Interact, 
  2. Catch and Store Energy, 
  3. Obtain a Yield, 
  4. Apply Self Regulation and Accept Feedback, 
  5. Use and Value Renewable Resources and Services, 
  6. Produce No Waste, 
  7. Design From Patterns to Details, 
  8. Integrate Rather Than Segregate, 
  9. Use Small and Slow Solutions, 
  10. Use and Value Diversity, 
  11. Use Edges and Value the Marginal, and 
  12. Creatively Use and Respond to Change.



Contents
1History
2Core tenets and principles of design


3Theory
3.1Twelve design principles
3.2Layers
3.3Guilds
3.4Edge effect
3.5Zones
3.6People and permaculture
3.7Domesticated animals


4Common practices
4.1Agroforestry
4.2Hügelkultur
4.3Natural building
4.4Rainwater harvesting
4.5Sheet mulching
4.6Intensive rotational grazing
4.7Keyline design
4.8Fruit tree management


5Trademark and copyright issues


6Criticisms
6.1General criticisms
6.2Agroforestry


7See also


8References
8.1Bibliography
9External links


History[edit]

Several individuals revolutionized the branch of permaculture. In 1929, Joseph Russell Smith added an antecedent term as the subtitle for Tree Crops: A Permanent Agriculture, a book which sums up his long experience experimenting with fruits and nuts as crops for human food and animal feed.[7] Smith saw the world as an inter-related whole and suggested mixed systems of trees and crops underneath. This book inspired many individuals intent on making agriculture more sustainable, such as Toyohiko Kagawa who pioneered forest farming in Japan in the 1930s.[8]

In Australian P.A. Yeomans' 1964 book Water for Every Farm, he supports the definition of permanent agriculture, as one that can be sustained indefinitely. Yeomans introduced both an observation-based approach to land use in Australia in the 1940s and the Keyline Design as a way of managing the supply and distribution of water in the 1950s.

Holmgren noted Stewart Brand’s works as an early influence to permaculture.[9] Other early influences include Ruth Stout and Esther Deans, who pioneered no-dig gardening, and Masanobu Fukuoka who, in the late 1930s in Japan, began advocating no-till orchards and gardens and natural farming.[10]

Bill Mollison in 2008.

In the late 1960s, Bill Mollison and David Holmgren started developing ideas about stable agricultural systems on the southern Australian island state of Tasmania. Dangers of the rapidly growing use of industrial-agricultural methods sparked these ideas.[11]In their view, these methods were highly dependent on non-renewable resources, and were additionally poisoning land and water, reducing biodiversity, and removing billions of tons of topsoil from previously fertile landscapes. They responded with a design approach called permaculture. This term was first made public with their publication of their 1978 book Permaculture One.[11]

Among some of the more recognizable names who received their original training within Mollison's PDC system would include Geoff Lawton and Toby Hemenway, each of whom have more than 25 years experience teaching and promoting permaculture as a sustainable way of growing food. Simon J Fjell was a Founding Director of the Permaculture Institute in late 1979 and a teacher of the first Permaculture Design Course, having first met Mollison in 1976. He has since worked internationally and is currently listing a major social enterprise on NASDAQ.

By the early 1980s, the concept had broadened from agricultural systems design towards sustainable human habitats. After Permaculture One, Mollison further refined and developed the ideas by designing hundreds of permaculture sites and writing more detailed books, such as Permaculture: A Designers Manual. Mollison lectured in over 80 countries and taught his two-week Permaculture Design Course (PDC) to hundreds of students.[citation needed] Mollison "encouraged graduates to become teachers themselves and set up their own institutes and demonstration sites. This multiplier effect was critical to permaculture’s rapid expansion."[12]

The permaculture movement also spread throughout Asia and Central America, with Hong Kong-based Asian Institute of Sustainable Architecture (AISA),[13] Rony Lec leading the foundation of the Mesoamerican Permaculture Institute (IMAP)[14] in Guatemala and Juan Rojas co-founding the Permaculture Institute of El Salvador.[15]

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Core tenets and principles of design[edit]

The three core tenets of permaculture are:[16][17][18]


Care for the earth: Provision for all life systems to continue and multiply. This is the first principle, because without a healthy earth, humans cannot flourish.


Care for the people: Provision for people to access those resources necessary for their existence


Fair share: By governing our own needs, we can set resources aside to further the above principles.[19] This includes returning waste back into the system to recycle into usefulness.[20] The third ethic is referred to as Fair Share, which reflects that each of us should take no more than what we need before we reinvest the surplus.
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Permaculture design emphasizes patterns of landscape, function, and species assemblies. It determines where these elements should be placed so they can provide maximum benefit to the local environment. Permaculture maximizes useful connections between components and synergy of the final design. The focus of permaculture, therefore, is not on each separate element, but rather on the relationships created among elements by the way they are placed together; the whole becomes greater than the sum of its parts. Permaculture design therefore seeks to minimize waste, human labor, and energy input by building systems, and maximizes benefits between design elements to achieve a high level of synergy. Permaculture designs evolve over time by taking into account these relationships and elements and can evolve into extremely complex systems that produce a high density of food and materials with minimal input.[21]

The design principles, which are the conceptual foundation of permaculture, were derived from the science of systems ecology and study of pre-industrial examples of sustainable land use. Permaculture draws from several disciplines including organic farming, agroforestry, integrated farming, sustainable development, and applied ecology.[22] Permaculture has been applied most commonly to the design of housing and landscaping, integrating techniques such as agroforestry, natural building, and rainwater harvesting within the context of permaculture design principles and theory.[citation needed]


Theory[edit]


Twelve design principles[edit]

Twelve Permaculture design principles articulated by David Holmgren in his Permaculture: Principles and Pathways Beyond Sustainability:[23]



  1. Observe and interact: By taking time to engage with nature we can design solutions that suit our particular situation.
  2. Catch and store energy: By developing systems that collect resources at peak abundance, we can use them in times of need.
  3. Obtain a yield: Ensure that you are getting truly useful rewards as part of the work that you are doing.
  4. Apply self-regulation and accept feedback: We need to discourage inappropriate activity to ensure that systems can continue to function well.
  5. Use and value renewable resources and services: Make the best use of nature's abundance to reduce our consumptive behavior and dependence on non-renewable resources.
  6. Produce no waste: By valuing and making use of all the resources that are available to us, nothing goes to waste.
  7. Design from patterns to details: By stepping back, we can observe patterns in nature and society. These can form the backbone of our designs, with the details filled in as we go.
  8. Integrate rather than segregate: By putting the right things in the right place, relationships develop between those things and they work together to support each other.
  9. Use small and slow solutions: Small and slow systems are easier to maintain than big ones, making better use of local resources and producing more sustainable outcomes.
  10. Use and value diversity: Diversity reduces vulnerability to a variety of threats and takes advantage of the unique nature of the environment in which it resides.
  11. Use edges and value the marginal: The interface between things is where the most interesting events take place. These are often the most valuable, diverse and productive elements in the system.
  12. Creatively use and respond to change: We can have a positive impact on inevitable change by carefully observing, and then intervening at the right time.
Layers[edit]


Suburban permaculture garden in Sheffield, UK with different layers of vegetation
---
Layers are one of the tools used to design functional ecosystems that are both sustainable and of direct benefit to humans. A mature ecosystem has a huge number of relationships between its component parts: trees, understory, ground cover, soil, fungi, insects, and animals. Because plants grow to different heights, a diverse community of life is able to grow in a relatively small space, as the vegetation occupies different layers. There are generally seven recognized layers in a food forest, although some practitioners also include fungi as an eighth layer.[24]
The canopy: the tallest trees in the system. Large trees dominate but typically do not saturate the area, i.e. there exist patches barren of trees.
Understory layer: trees that flourish in the dappled light under the canopy.
Shrub layer: a diverse layer of woody perennials of limited height. Includes most berry bushes.
Herbaceous layer: Plants in this layer die back to the ground every winter (if winters are cold enough, that is). They do not produce woody stems as the Shrub layer does. Many culinary and medicinal herbs are in this layer. A large variety of beneficial plants fall into this layer. May be annuals, biennials or perennials.
Soil surface/Groundcover: There is some overlap with the Herbaceous layerand the Groundcover layer; however plants in this layer grow much closer to the ground, grow densely to fill bare patches of soil, and often can tolerate some foot traffic. Cover crops retain soil and lessen erosion, along with green manures that add nutrients and organic matter to the soil, especially nitrogen.
Rhizosphere: Root layers within the soil. The major components of this layer are the soil and the organisms that live within it such as plant roots and rhizomes (including root crops such as potatoes and other edible tubers), fungi, insects, nematodes, worms, etc.
Vertical layer: climbers or vines, such as runner beans and lima beans (vine varieties).[24][25]


Guilds[edit]

A guild is a group of species where each provides a unique set of diverse functions that work in conjunction or harmony. There are many forms of guilds, including guilds of plants with similar functions that could interchange within an ecosystem, but the most common perception is that of a mutual support guild. Mutual support guilds are groups of plants, animals, insects, etc. that work well together. Plants may be grown for food production, draw nutrients from deep in the soil through tap roots, are nitrogen-fixing legumes, attract beneficial insects, and repel harmful insects. When grouped together in a mutually beneficial arrangement, these plants form a guild. See Dave Jacke's work on edible forest gardens for more information on other guilds, specifically resource-partitioning and community-function guilds.[26][27][28]
Edge effect[edit]

The edge effect in ecology is the effect of the juxtaposition, or placing contrasting environments on an ecosystem. Permaculturists argue that where vastly differing systems meet, there is an intense area of productivity and useful connections. An example of this is the coast; where the land and the sea meet, there is a particularly rich area that meets a disproportionate percentage of human and animal needs. This idea is played out in permacultural designs by using spirals in herb gardens, or creating ponds that have wavy undulating shorelines rather than a simple circle or oval (thereby increasing the amount of edge for a given area).[29]


Zones[edit]

Permaculture zones 0-5

Zones intelligently organize design elements in a human environment based on the frequency of human use and plant or animal needs. Frequently manipulated or harvested elements of the design are located close to the house in zones 1 and 2. Manipulated elements located further away are used less frequently. Zones are numbered from 0 to 5 based on positioning.[30]Zone 0The house, or home center. Here permaculture principles would be applied in terms of aiming to reduce energy and water needs, harnessing natural resources such as sunlight, and generally creating a harmonious, sustainable environment in which to live and work. Zone 0 is an informal designation, which is not specifically defined in Bill Mollison’s book.


Zone 1The zone nearest to the house, the location for those elements in the system that require frequent attention, or that need to be visited often, such as salad crops, herb plants, soft fruit like strawberries or raspberries, greenhouse and cold frames, propagation area, worm compost bin for kitchen waste, etc. Raised bedsare often used in zone 1 in urban areas.

Zone 2This area is used for siting perennial plants that require less frequent maintenance, such as occasional weed control or pruning, including currant bushes and orchards, pumpkins, sweet potato, etc. This would also be a good place for beehives, larger scale composting bins, etc.

Zone 3The area where main-crops are grown, both for domestic use and for trade purposes. After establishment, care and maintenance required are fairly minimal (provided mulches and similar things are used), such as watering or weed control maybe once a week.

Zone 4A semi-wild area. This zone is mainly used for forage and collecting wild food as well as production of timber for construction or firewood.

Zone 5A wilderness area. There is no human intervention in zone 5 apart from the observation of natural ecosystems and cycles. Through this zone we build up a natural reserve of bacteria, moulds and insects that can aid the zones above it.[31]
People and permaculture[edit]

Permaculture uses observation of nature to create regenerative systems, and the place where this has been most visible has been on the landscape. There has been a growing awareness though that firstly, there is the need to pay more attention to the peoplecare ethic, as it is often the dynamics of people that can interfere with projects, and secondly that the principles of permaculture can be used as effectively to create vibrant, healthy and productive people and communities as they have been in landscapes.
Domesticated animals[edit]

Domesticated animals are often incorporated into site design, ensuring the efficiency and productivity of the system.[32]Animals, domestic or wild are a critical component of any wild or designed sustainable ecosystem. Research indicates that without the animal’s participation and contribution, ecological integrity is diminished or impossible.[33] Some of the activities that contribute to the system include: foraging to cycle nutrients, clear fallen fruit, weed maintenance, spreading seeds, and pest maintenance. The nutrients are cycled by animals, transformed from their less digestible form (such as grass or twigs) into more nutrient-dense manure.[33]

Several animals can be incorporated into a permaculture system, including cows, goats, chickens, geese, turkey, rabbits, and worms. A more specific explanation of how the animals can be used is seen in the chicken design. Chickens can be used to scratch over the soil, thus breaking down the top soil and using the fecal matter as manure creating a sustainable system. However, in the domestication of these animals, the complexity and elegance lie in an effectiveness and efficiency of the design, including factors like timing and habits to specific areas of a farm. For example, animals require daily attention in a way that is much more demanding than plants.[34]
Common practices[edit]
Agroforestry[edit]

Agroforestry is an integrated approach of permaculture, which uses the interactive benefits from combining trees and shrubs with crops or livestock. It combines agricultural and forestry technologies to create more diverse, productive, profitable, healthy and sustainable land-use systems.[35] In agroforestry systems, trees or shrubs are intentionally used within agricultural systems, or non-timber forest products are cultured in forest settings.[36]

Forest gardening is a term permaculturalists use to describe systems designed to mimic natural forests. Forest gardens, like other permaculture designs, incorporate processes and relationships that the designers understand to be valuable in natural ecosystems. The terms forest garden and food forest are used interchangeably in the permaculture literature. Numerous permaculturists are proponents of forest gardens, such as Graham Bell, Patrick Whitefield, Dave Jacke, Eric Toensmeier and Geoff Lawton. Bell started building his forest garden in 1991 and wrote the book The Permaculture Garden in 1995, Whitefield wrote the book How to Make a Forest Garden in 2002, Jacke and Toensmeier co-authored the two volume book set Edible Forest Gardening in 2005, and Lawton presented the film Establishing a Food Forestin 2008.[21][37][38]

Tree Gardens, such as Kandyan tree gardens, in South and Southeast Asia, are often hundreds of years old. It is not self-evident whether these tree gardens derived initially from experiences of cultivation and forestry, as is the case in agroforestry, or whether they derived from an understanding of forest ecosystems, as is the case for permaculture systems. Many studies of these systems, especially those that predate the term permaculture, consider these systems to be forms of agroforestry. Permaculturalists may obscure the distinction of permaculture and agroforestry when they include existing and ancient systems of polycropping as examples of food forests.

Food forests and agroforestry are parallel approaches that sometimes lead to similar designs.


Hügelkultur[edit]

Hügelkultur is the practice of burying large volumes of wood to increase soil water retention. The porous structure of wood acts as a sponge when decomposing underground. During the rainy season, masses of buried wood can absorb enough water to sustain crops through the dry season.[39] This technique has been used by permaculturalists Sepp Holzer, Toby Hemenway, Paul Wheaton, and Masanobu Fukuoka.[40][41]


Natural building[edit]

A natural building involves a range of building systems and materials that place major emphasis on sustainability. Ways of achieving sustainability through natural building focus on durability and the use of minimally processed, plentiful or renewable resources, as well as those that, while recycled or salvaged, produce healthy living environments and maintain indoor air quality.

The basis of natural building is the need to lessen the environmental impact of buildings and other supporting systems, without sacrificing comfort, health, or aesthetics. Natural building primarily utilizes abundantly available natural materials (e.g., clay, rock, sand, straw, wood, reeds), and draws heavily on traditional architectural strategies from various climates across the world. In addition to relying on natural building materials, the emphasis on the architectural design is heightened. The orientation of a building, the utilization of local climate and site conditions, the emphasis on natural ventilation through design, fundamentally lessen operational costs and positively impact the environment. Building compactly and minimizing the ecological footprint is common, as are on-site handling of energy acquisition, on-site water capture, alternate sewage treatment, and water reuse.[citation needed] Most materials are sourced regionally, locally, or even on-site. Straw bales, and various earthen masonry techniques such as adobe bricks, cob (or monolithic adobe), rammed earth and clay-straw infill are common choices for wall material. Roofing coverings often used include sod or "living" roofs, thatch, and wooden shakes or shingles. Rubble trench foundations are popular, as they do not require concrete; likewise, dry-stacked or lime mortared stem walls are common. Natural builders also regularly combine different wall systems in a single building, making best use of different materials' thermal or water resistant properties, for example, where they are most needed in the structure.
Rainwater harvesting[edit]

Rainwater harvesting is the accumulating and storing of rainwater for reuse before it reaches the aquifer.[42] It has been used to provide drinking water, water for livestock, water for irrigation, as well as other typical uses. Rainwater collected from the roofs of houses and local institutions can make an important contribution to the availability of drinking water. It can supplement the subsoil water level and increase urban greenery. Water collected from the ground, sometimes from areas which are especially prepared for this purpose, is called stormwater harvesting.[citation needed]

Greywater is wastewater generated from domestic activities such as laundry, dishwashing, and bathing, which can be recycled on-site for uses such as landscape irrigation and constructed wetlands. Greywater is largely sterile, but not potable (drinkable). Greywater differs from water from the toilets, which is designated sewageor blackwater to indicate it contains human waste. Blackwater is septic or otherwise toxic and cannot easily be reused. There are, however, continuing efforts to make use of blackwater or human waste. The most notable is for composting through a process known as humanure; a combination of the words human and manure. Additionally, the methane in humanure can be collected and used similar to natural gas as a fuel, such as for heating or cooking, and is commonly referred to as biogas. Biogas can be harvested from the human waste and the remainder still used as humanure. Some of the simplest forms of humanure use include a composting toilet or an outhouse or dry bog surrounded by trees that are heavy feeders which can be coppiced for wood fuel. This process eliminates the use of a standard toilet with plumbing.[citation needed]


Sheet mulching[edit]

In agriculture and gardening, mulch is a protective cover placed over the soil. Any material or combination can be used as mulch, such as stones, leaves, cardboard, wood chips, gravel, etc., though in permaculture mulches of organic material are the most common because they perform more functions. These include absorbing rainfall, reducing evaporation, providing nutrients, increasing organic matter in the soil, feeding and creating habitat for soil organisms, suppressing weed growth and seed germination, moderating diurnal temperature swings, protecting against frost, and reducing erosion. Sheet mulching is an agricultural no-dig gardening technique that attempts to mimic natural processes occurring within forests. Sheet mulching mimics the leaf cover that is found on forest floors. When deployed properly and in combination with other Permacultural principles, it can generate healthy, productive and low maintenance ecosystems.[43][44][page needed]

Sheet mulch serves as a "nutrient bank," storing the nutrients contained in organic matter and slowly making these nutrients available to plants as the organic matter slowly and naturally breaks down. It also improves the soil by attracting and feeding earthworms, slaters and many other soil micro-organisms, as well as adding humus. Earthworms "till" the soil, and their worm castings are among the best fertilizers and soil conditioners. Sheet mulching can be used to reduce or eliminate non-desired plants by starving them of light, and can be more advantageous than using herbicideor other methods of control. [45]


Intensive rotational grazing[edit]

Grazing has long been blamed for much of the destruction we see in the environment. However, it has been shown that when grazing is modeled after nature, the opposite effect can be seen.[46][47] Also known as cell grazing, managed intensive rotational grazing (MIRG) is a system of grazing in which ruminant and non-ruminant herds or flocks are regularly and systematically moved to fresh pasture, range, or forest with the intent to maximize the quality and quantity of forage growth. This disturbance is then followed by a period of rest which allows new growth. MIRG can be used with cattle, sheep, goats, pigs, chickens, rabbits, geese, turkeys, ducks, and other animals depending on the natural ecological community that is being mimicked. Sepp Holzerand Joel Salatin have shown how the disturbance caused by the animals can be the spark needed to start ecological succession or prepare ground for planting. Allan Savory's holistic management technique has been likened to "a permaculture approach to rangeland management".[48][49] One variation on MIRG that is gaining rapid popularity is called eco-grazing. Often used to either control invasives or re-establish native species, in eco-grazing the primary purpose of the animals is to benefit the environment and the animals can be, but are not necessarily, used for meat, milk or fiber.[50][51][52][53][54][55][56]


Keyline design[edit]

Keyline design is a technique for maximizing the beneficial use of water resources of a piece of land developed in Australia by farmer and engineer P. A. Yeomans. The Keyline refers to a specific topographic feature linked to water flow which is used in designing the drainage system of the site.[57] The essential factor in this system, the Keyline, is a level or sloping line extending in both directions from a point or divides the two types of relationship, always in the same vertical interval, that a valley bears to its ridges.[58]
Fruit tree management[edit]

Some proponents of permaculture advocate no, or limited, pruning. One advocate of this approach is Sepp Holzer who used the method in connection with Hügelkulturberms. He has successfully grown several varieties of fruiting trees at altitudes (approximately 9,000 feet (2,700 m)) far above their normal altitude, temperature, and snow load ranges. He notes that the Hügelkultur berms kept or generated enough heat to allow the roots to survive during alpine winter conditions. The point of having unpruned branches, he notes, was that the longer (more naturally formed) branches bend over under the snow load until they touched the ground, thus forming a natural arch against snow loads that would break a shorter, pruned, branch.[citation needed]

Masanobu Fukuoka, as part of early experiments on his family farm in Japan, experimented with no-pruning methods, noting that he ended up killing many fruit trees by simply letting them go, which made them become convoluted and tangled, and thus unhealthy.[59][60][page needed] Then he realised this is the difference between natural-form fruit trees and the process of change of tree form that results from abandoning previously-pruned unnatural fruit trees.[59][61][page needed] He concluded that the trees should be raised all their lives without pruning, so they form healthy and efficient branch patterns that follow their natural inclination. This is part of his implementation of the Tao-philosophy of Wú wéi translated in part as no-action (against nature), and he described it as no unnecessary pruning, nature farming or "do-nothing" farming, of fruit trees, distinct from non-intervention or literal no-pruning. He ultimately achieved yields comparable to or exceeding standard/intensive practices of using pruning and chemical fertilisation.[59][61][page needed][62]

Permaculture Action

Permaculture helps generate plans that are easy and cheap when it comes to production. Permaculture allows creativity and innovation in farming. The action of permaculture looks and all becoming consciously involved in the process of producing and ensuring abundant food nearby, problem on malnutrition caused by the world hunger problem will inevitably lessen.[63] Permaculture principles in action are powerful forces to help right the environmental wrongs of the last two centuries.[64]
Trademark and copyright issues[edit]

There has been contention over who, if anyone, controls legal rights to the word permaculture: is it trademarked or copyrighted? If so, who holds the legal rights to the use of the word? For a long time Bill Mollison claimed to have copyrighted the word, and his books said on the copyright page, "The contents of this book and the word PERMACULTURE are copyright." These statements were largely accepted at face value within the permaculture community. However, copyright law does not protect names, ideas, concepts, systems, or methods of doing something; it only protects the expression or the description of an idea, not the idea itself. Eventually Mollison acknowledged that he was mistaken and that no copyright protection existed for the word permaculture.[65]

In 2000, Mollison's US based Permaculture Institute sought a service mark (a form of trademark) for the word permaculture when used in educational services such as conducting classes, seminars, or workshops.[66] The service mark would have allowed Mollison and his two Permaculture Institutes (one in the US and one in Australia) to set enforceable guidelines regarding how permaculture could be taught and who could teach it, particularly with relation to the PDC, despite the fact that he had instituted a system of certification of teachers to teach the PDC in 1993. The service mark failed and was abandoned in 2001. Also in 2001 Mollison applied for trademarks in Australia for the terms "Permaculture Design Course"[67] and "Permaculture Design".[67] These applications were both withdrawn in 2003. In 2009 he sought a trademark for "Permaculture: A Designers’ Manual"[67] and "Introduction to Permaculture",[67] the names of two of his books. These applications were withdrawn in 2011. There has never been a trademark for the word permaculture in Australia.[67]


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Criticisms[edit]


General criticisms[edit]

In 2011, Owen Hablutzel argued that "permaculture has yet to gain a large amount of specific mainstream scientific acceptance," and that "the sensitiveness to being perceived and accepted on scientific terms is motivated in part by a desire for permaculture to expand and become increasingly relevant."

In his books Sustainable Freshwater Aquaculture and Farming in Ponds and Dams, Nick Romanowski expresses the view that the presentation of aquaculture in Bill Mollison's books is unrealistic and misleading.[68]


Agroforestry[edit]

Greg Williams argues that forests cannot be more productive than farmland because the net productivity of forests declines as they mature due to ecological succession.[69] 


Proponents of permaculture respond that this is true only if one compares data between woodland forest and climax vegetation, but not when comparing farmland vegetation with woodland forest.[citation needed] For example, ecological succession generally results in a forest's productivity rising after its establishment only until it reaches the woodland state (67% tree cover), before declining until full maturity.[21]

See also[edit]

Agrarianism
Agroecology
Agroforestry
Aquaponics
Biodynamics
Bill Mollison
Geoff Lawton
Willie Smits
Biointensive agriculture
Biomimicry
Climate-friendly gardening
David Holmgren
Ecoagriculture
Food-feed system
Forest gardening
Holzer Permaculture
Hügelkultur
List of permaculture projects
Microponics
Paul Wheaton
Permaforestry
Regenerative agriculture
Seed saving
Sepp Holzer
Zaï


References[edit]

  1. ^ Holmgren and Mollison (1978). Permaculture One. Transworld Publishers. p. 128. ISBN 0552980757.
  2. ^ King 1911.
  3. ^ Paull , John (2011) The making of an agricultural classic: Farmers of Forty Centuries or Permanent Agriculture in China, Korea and Japan, 1911-2011, Agricultural Sciences, 2 (3), pp. 175-180.
  4. ^ Hemenway 2009, p. 5.
  5. ^ Mars, Ross (2005). The Basics of Permaculture Design. Chelsea Green. p. 1. ISBN 978-1-85623-023-0.
  6. ^ Mollison, B. (1991). Introduction to permaculture. Tasmania, Australia: Tagari.
  7. ^ Smith, Joseph Russell; Smith, John (1987). Tree Crops: A permanent agriculture. Island Press. ISBN 978-1-59726873-8.
  8. ^ Hart 1996, p. 41.
  9. ^ Holmgren, David (2006). "The Essence of Permaculture". Holmgren Design Services. Archived from the original on 26 May 2008. Retrieved 10 September 2011.
  10. ^ Mollison, Bill (15–21 September 1978). "The One-Straw Revolution by Masanobu Fukuoka". Nation Review. p. 18.
  11. ^ Jump up to:a b Introduction to Permaculture, 1991, Mollison, p.v
  12. ^ Lillington, Ian; Holmgren, David; Francis, Robyn; Rosenfeldt, Robyn. "The Permaculture Story: From 'Rugged Individuals' to a Million Member Movement"(PDF). Pip Magazine. Retrieved 9 July 2015.
  13. ^ Asian Institute of Sustainable Architecture (AISA)
  14. ^ Mesoamerican Permaculture Institute (IMAP)
  15. ^ Permaculture Institute of El Salvador
  16. ^ Greenblott, Kara; Nordin, Kristof (2012), Permaculture Design for Orphans and Vulnerable Children Programming: Low-Cost, Sustainable Solutions for Food and Nutrition Insecure Communities, AIDS Support and Technical Assistance Resources, AIDSTAR-One (Task Order 1), Arlington, VA: USAID.
  17. ^ Mollison 1988, p. 2.
  18. ^ Holmgren, David (2002). Permaculture: Principles & Pathways Beyond Sustainability. Holmgren Design Services. p. 1. ISBN 0-646-41844-0.
  19. ^ Mollison, Bill (1988). Permaculture: a Designer's Manual. Tagari Press. p. 2. ISBN 0-908228-01-5.
  20. ^ Mollison, Bill. "Permaculture: A Quiet Revolution". Scott London (interview). Retrieved 17 May 2013.
  21. ^ Jump up to:a b c "Edible Forest Gardening".
  22. ^ Holmgren, David (1997). "Weeds or Wild Nature" (PDF). Permaculture International Journal. Retrieved 10 September 2011.
  23. ^ "Permaculture: Principles and Pathways Beyond Sustainability". Holmgren Design. Retrieved 21 October 2013.
  24. ^ Jump up to:a b Nine layers of the edible forest garden, TC permaculture, 27 May 2013.
  25. ^ "Seven layers of a forest", Food forests, CA: Permaculture school.
  26. ^ Simberloff, D; Dayan, T (1991). "The Guild Concept and the Structure of Ecological Communities". Annual Review of Ecology and Systematics. 22: 115. doi:10.1146/annurev.es.22.110191.000555.
  27. ^ "Guilds". Encyclopædia Britannica. Retrieved 21 October 2011.
  28. ^ Williams, SE; Hero, JM (1998). "Rainforest frogs of the Australian Wet Tropics: guild classification and the ecological similarity of declining species". Proceedings: Biological Sciences. The Royal Society. 265 (1396): 597–602. doi:10.1098/rspb.1998.0336. PMC 1689015. PMID 9881468.
  29. ^ "10. Edge Effect". Deep Green Permaculture. 3 April 2013. Retrieved 19 January2017.
  30. ^ Burnett, Graham, Permaculture A Beginners Guide', Spiralseed, 2001 p.26.
  31. ^ Permacultuur course, NL: WUR.
  32. ^ Mollison 1988, p. 5: ‘Deer, rabbits, sheep, and herbivorous fish are very useful to us, in that they convert unusable herbage to acceptable human food. Animals represent a valid method of storing inedible vegetation as food.’
  33. ^ Jump up to:a b "Backyard Animals | Permaculture Institute". www.permaculture.org. Archived from the original on 17 December 2014. Retrieved 6 April 2017.
  34. ^ "Permaculture Animals as a Discipline to the System". The Permaculture Research Institute. 7 March 2016. Retrieved 6 April 2017.
  35. ^ "USDA National Agroforestry Center (NAC)". UNL. 1 August 2011. Retrieved 21 October 2011.
  36. ^ "USDA Agroforestry Strategic Framework" (PDF). United States Department of Agriculture. 1 August 2011. Retrieved 19 January 2017.
  37. ^ "Graham Bell's Forest Garden". Permaculture. Media mice. Archived from the original on 8 March 2012.
  38. ^ "Establishing a Food Forest" (film review). Transition culture. 11 February 2009.
  39. ^ Wheaton, Paul. "Raised garden beds: hugelkultur instead of irrigation" Richsoil. Retrieved 15 July 2012.
  40. ^ Hemenway 2009, pp. 84–85.
  41. ^ Feineigle, Mark. "Hugelkultur: Composting Whole Trees With Ease". Permaculture Research Institute of Australia. Retrieved 15 July 2012.
  42. ^ "Rainwater harvesting". DE: Aramo. 2012. Archived from the original on 6 June 2013. Retrieved 19 August 2015.
  43. ^ "Sheet Mulching: Greater Plant and Soil Health for Less Work". Agroforestry. 3 September 2011. Archived from the original on 10 December 2002. Retrieved 21 October 2011.
  44. ^ Mason, J (2003), Sustainable Agriculture, Landlinks.
  45. ^ Stratton, Margie Lynn; Barker, Allen; Ragsdale, James (April 2000). "Sheet composting overpowers weeds in restoration project". BioCycle. 41 (4): 57.
  46. ^ "Prince Charles sends a message to IUCN's World Conservation Congress". International Union for Conservation of Nature. Archived from the original on 15 March 2013. Retrieved 6 April 2013.
  47. ^ Undersander, Dan; et al. "Grassland birds: Fostering habitat using rotational grazing" (PDF). University of Wisconsin-Extension. Retrieved 5 April 2013.
  48. ^ Fairlie, Simon (2010). Meat: A Benign Extravagance. Chelsea Green. pp. 191–93. ISBN 978-1-60358325-1.
  49. ^ Bradley, Kirsten. "Holistic Management: Herbivores, Hats, and Hope". Milkwood. Retrieved 25 March 2014.
  50. ^ "Munching sheep replace lawn mowers in Paris". The Sunday Times. 4 April 2013. Retrieved 7 April 2013.
  51. ^ Ash, Andrew, The Ecograze Project – developing guidelines to better manage grazing country (PDF), et al., CSIRO, ISBN 0-9579842-0-0, archived from the original(PDF) on 10 April 2012, retrieved 7 April 2013
  52. ^ McCarthy, Caroline. "Things to make you happy: Google employs goats". CNET. Retrieved 7 April 2013.
  53. ^ Gordon, Ian. "A systems approach to livestock/resource interactions in tropical pasture systems" (PDF). The James Hutton Institute. Archived from the original (PDF) on 3 February 2014. Retrieved 7 April 2013.
  54. ^ Littman, Margaret. "Getting your goat: Eco-friendly mowers". Chicago Tribune News. Retrieved 7 April 2013.
  55. ^ Stevens, Alexis. "Kudzu-eating sheep take a bite out of weeds". The Atlanta Journal-Constitution. Retrieved 7 April 2013.
  56. ^ Klynstra, Elizabeth. "Hungry sheep invade Candler Park". CBS Atlanta. Retrieved 7 April 2013.
  57. ^ Tipping, Don (4 January 2013). "Creating Permaculture Keyline Water Systems"(video). UK: Beaver State Permaculture.
  58. ^ Yeomas, P.A (1954). The Keyline plan. Australia: Authour. p. 120.
  59. ^ Jump up to:a b c Masanobu, Fukuoka (1987) [1985], The Natural Way of Farming – The Theory and Practice of Green Philosophy (rev ed.), Tokyo: Japan Publications, p. 204
  60. ^ Fukuoka 1978, pp. 13, 15–18, 46, 58–60.
  61. ^ Jump up to:a b Fukuoka 1978.
  62. ^ "Masanobu Fukuoka", Public Service (biography), PH: The Ramon Magsaysay Award Foundation, 1988.
  63. ^ Kasarinlan (2011). "Permaculture as Alternative Agriculture". Philippine. 26: 422–434.
  64. ^ "Permaculture and Sustainability - Solscape". Solscape. Retrieved 6 April 2017.
  65. ^ Grayson, Russ (2011). "The Permaculture Papers 5: time of change and challenge — 2000-2004". Pacific edge. Retrieved 8 September 2011.
  66. ^ United States Patent and Trademark Office (2011). "Trademark Electronic Search System (TESS)". US Department of Commerce. Retrieved 8 September 2011.
  67. ^ Jump up to:a b c d e "Result". IP Australia. 2011. Retrieved 8 September 2011.
  68. ^ Nick Romanowski (2007). Sustainable Freshwater Aquaculture: The Complete Guide from Backyard to Investor. UNSW Press. p. 130. ISBN 978-0-86840-835-4.
  69. ^ Williams, Greg (2001). "Gaia's Garden: A Guide to Home-Scale Permaculture". Whole Earth.

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Bibliography[edit]



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External links[edit]
Wikimedia Commons has media related to Permaculture.

Ferguson, Rafter Sass; Lovell, Sarah Taylor (2013), "Permaculture for agroecology: design, movement, practice, and worldview", Agronomy for Sustainable Development (review), Springer, 34(2): 251, doi:10.1007/s13593-013-0181-6 – The first systematic review of the permaculture literature, from the perspective of agroecology.


Noosa Forest Retreat - one of the world's oldest permaculture communities located at Noosa, Queensland, Australia (founded by Ian Trew) - formerly "Mothar Mountain Ashram".


Permaculture Online Community - Permaculture Online Community & Online Permaculture Education, run independently by Noosa Forest Retreat.


The Permaculture Research Institute – Permaculture Forums, Courses, Information, News and Worldwide Reports.


The Worldwide Permaculture Network – Database of permaculture people and projects worldwide.


The Permaculture Association, UK.
The 15 pamphlets based on the 1981 Permaculture Design Course given by Bill Mollison (co-founder of permaculture) all in 1 PDF file.


David Holmgren's web site (co-founder of permaculture)


Ethics and principles of permaculture (Holmgren’s)


Permaculture a Beginners Guide – a 'pictorial walkthrough'


Permaculture – Sustainability and sustainable development


Urban Permaculture Design – a city lot with over a hundred perennial edible varieties. Permaculture land acquisition discussion.


A quarter acre suburban property in Eugene, Oregon – grass to garden, reclaim automobile space, elevated/edible landscape, rain water catchment, passive solar design, education


The Permaculture Activist is a co-evolving quarterly produced by a dedicated handful of entirely part-time folks


Permaculture Commons is a collection of permaculture material under free licenses

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