Environmental impacts of animal agriculture

Last updated
Los Llanos, Venezuela (12832335223).jpg
Hog confinement barn interior.jpg
CSIRO ScienceImage 1898 Testing Sheep for Methane Production.jpg
NRCSNC00012 - North Carolina (5133)(NRCS Photo Gallery).jpg
Examples of environmental impacts of animal agriculture: Meat production is a main driver of deforestation in Venezuela; Pigs in intensive farming; Testing Australian sheep for exhaled methane production to reduce greenhouse gas emissions from agriculture; Farms often pump their animal waste directly into a large lagoon, which has environmental consequences.

The environmental impacts of animal agriculture vary because of the wide variety of agricultural practices employed around the world. Despite this, all agricultural practices have been found to have a variety of effects on the environment to some extent. Animal agriculture, in particular meat production, can cause pollution, greenhouse gas emissions, biodiversity loss, disease, and significant consumption of land, food, and water. Meat is obtained through a variety of methods, including organic farming, free-range farming, intensive livestock production, and subsistence agriculture. The livestock sector also includes wool, egg and dairy production, the livestock used for tillage, and fish farming.

Contents

Animal agriculture is a significant contributor to greenhouse gas emissions. Cows, sheep, and other ruminants digest their food by enteric fermentation, and their burps are the main source of methane emissions from land use, land-use change, and forestry. Together with methane and nitrous oxide from manure, this makes livestock the main source of greenhouse gas emissions from agriculture. [1] A significant reduction in meat consumption is essential to mitigate climate change, especially as the human population increases by a projected 2.3 billion by the middle of the century. [2] [3]

Total annual meat consumption by type of meat Total annual meat consumption by type of meat.png
Total annual meat consumption by type of meat
Cereal-use statistic show an estimated large fraction of crops used as fodder Cereals allocated to food, animal feed and fuel, World.png
Cereal-use statistic show an estimated large fraction of crops used as fodder
Nutritional value and environmental impact of animal products, compared to agriculture overall [4]
CategoriesContribution of farmed animal product [%]
Calories
18
Proteins
37
Land use
83
Greenhouse gases
58
Water pollution
57
Air pollution
56
Freshwater withdrawals
33

Multiple studies have found that increases in meat consumption are currently associated with human population growth and rising individual incomes or GDP, and therefore, the environmental impacts of meat production and consumption will increase unless current behaviours change. [5] [6] [7] [2]

Changes in demand for meat will influence how much is produced, thus changing the environmental impact of meat production. It has been estimated that global meat consumption may double from 2000 to 2050, mostly as a consequence of the increasing world population, but also partly because of increased per capita meat consumption (with much of the per capita consumption increase occurring in the developing world). [8] The human population is projected to grow to 9 billion by 2050, and meat production is expected to increase by 40%. [9] Global production and consumption of poultry meat have been growing recently at more than 5% annually. [8] Meat consumption typically increases as people and countries get richer. [10] Trends also vary among livestock sectors. For example, global pork consumption per capita has increased recently (almost entirely due to changes in consumption within China), while global consumption per capita of ruminant meats has been declining. [8]

Per capita annual meat consumption by region Per capita annual meat consumption by region.png
Per capita annual meat consumption by region
Total annual meat consumption by region Total annual meat consumption by region.png
Total annual meat consumption by region

Resource use

Food production efficiency

About 85% of the world's soybean crop is processed into meal and vegetable oil, and virtually all of that meal is used in animal feed. [11] Approximately 6% of soybeans are used directly as human food, mostly in Asia. [11]

For every 100 kilograms of food made for humans from crops, 37 kilograms byproducts unsuitable for direct human consumption are generated. [12] Many countries then repurpose these human-inedible crop byproducts as livestock feed for cattle. [13] Raising animals for human consumption accounts for approximately 40% of total agricultural output in industrialized nations. [14] Moreover, the efficiency of meat production varies depending on the specific production system, as well as the type of feed. It may require anywhere from 0.9 and 7.9 kilograms of grain to produce 1 kilogram of beef, between 0.1 to 4.3 kilograms of grain to produce 1 kilogram of pork, and 0 to 3.5 kilograms of grains to produce 1 kilogram of chicken. [15] [16]

Field of crops for animal consumption. These fields occupy a large amount of land. This limits the land available for local people to grow crops for their own consumption. Bridleway past Crop Field - geograph.org.uk - 1874041.jpg
Field of crops for animal consumption. These fields occupy a large amount of land. This limits the land available for local people to grow crops for their own consumption.

FAO estimates, however, that about 2 thirds of the pasture area used by livestock is not convertible to crop-land. [15] [16]

Major corporations purchase land in different developing nations in Latin America and Asia to support large-scale production of animal feed crops, mainly corn and soybeans. This practice reduces the amount of land available for growing crops that are fit for human consumption in these countries, putting the local population at risk of food security. [17]

According to a study conducted in Jiangsu, China, individuals with higher incomes tend to consume more food than those with lower incomes and larger families. Consequently, it is unlikely that those employed in animal feed production in these regions do not consume the animals that eat the crops they produce. The lack of space for growing crops for consumption, coupled with the need to feed larger families, only exacerbates their food insecurity. [18]

According to FAO, crop-residues and by-products account for 24% of the total dry matter intake of the global livestock sector. [15] [16] A 2018 study found that, "Currently, 70% of the feedstock used in the Dutch feed industry originates from the food processing industry." [19] Examples of grain-based waste conversion in the United States include feeding livestock the distillers grains (with solubles) remaining from ethanol production. For the marketing year 2009–2010, dried distillers grains used as livestock feed (and residual) in the US was estimated at 25.5 million metric tons. [20] Examples of waste roughages include straw from barley and wheat crops (edible especially to large-ruminant breeding stock when on maintenance diets), [21] [22] [23] and corn stover. [24] [25]

Land use

Mean land use of different foods [26]
Food TypesLand Use (m2year per 100g protein)
Lamb and mutton
185
Beef
164
Cheese
41
Pork
11
Poultry
7.1
Eggs
5.7
Farmed fish
3.7
Groundnuts
3.5
Peas
3.4
Tofu
2.2

Permanent meadows and pastures, grazed or not, occupy 26% of the Earth's ice-free terrestrial surface. [15] [16] Feed crop production uses about one-third of all arable land. [15] [16] More than one-third of U.S. land is used for pasture, making it the largest land-use type in the contiguous United States. [27]

The amount of globally needed agricultural land would be reduced by almost half if no beef or mutton would be eaten. Land-use-of-different-diets-Poore-Nemecek.png
The amount of globally needed agricultural land would be reduced by almost half if no beef or mutton would be eaten.

In many countries, livestock graze from the land which mostly cannot be used for growing human-edible crops, as seen by the fact that there is three times as much agricultural land [28] as arable land. [29]

A 2023 study found that a vegan diet reduced land use by 75%. [30]

Free-range animal production, particularly beef production, has also caused tropical deforestation because it requires land for grazing. [31] The livestock sector is also the primary driver of deforestation in the Amazon, with around 80% of all deforested land being used for cattle farming. [32] [33] Additionally, 91% of deforested land since 1970 has been used for cattle farming. [34] [35] Research has argued that a shift to meat-free diets could provide a safe option to feed a growing population without further deforestation, and for different yields scenarios. [36] However, according to FAO, grazing livestock in drylands “removes vegetation, including dry and flammable plants, and mobilizes stored biomass through depositions, which is partly transferred to the soil, improving fertility. Livestock is key to creating and maintaining specific habitats and green infrastructures, providing resources for other species and dispersing seeds”. [37]

Water use

Globally, the amount of water used for agricultural purposes exceeds any other industrialized purpose of water consumption. [38] About 80% of water resources globally are used for agricultural ecosystems. In developed countries, up to 60% of total water consumption can be used for irrigation; in developing countries, it can be up to 90%, depending on the region's economic status and climate. According to the projected increase in food production by 2050, water consumption would need to increase by 53% to satisfy the world population's demands for meat and agricultural production. [38]

Groundwater depletion is a concern in some areas because of sustainability issues (and in some cases, land subsidence and/or saltwater intrusion). [39] A particularly important North American example of depletion is the High Plains (Ogallala) Aquifer, which underlies about 174,000 square miles in parts of eight states of the USA and supplies 30 percent of the groundwater withdrawn for irrigation there. [40] Some irrigated livestock feed production is not hydrologically sustainable in the long run because of aquifer depletion. Rainfed agriculture, which cannot deplete its water source, produces much of the livestock feed in North America. Corn (maize) is of particular interest, accounting for about 91.8% of the grain fed to US livestock and poultry in 2010. [41] :table 1–75 About 14 percent of US corn-for-grain land is irrigated, accounting for about 17% of US corn-for-grain production and 13% of US irrigation water use, [42] [43] but only about 40% of US corn grain is fed to US livestock and poultry. [41] :table 1–38 Irrigation accounts for about 37% of US withdrawn freshwater use, and groundwater provides about 42% of US irrigation water. [44] Irrigation water applied in the production of livestock feed and forage has been estimated to account for about 9 percent of withdrawn freshwater use in the United States. [45]

Almost one-third of the water used in the western United States goes to crops that feed cattle. [46] This is despite the claim that withdrawn surface water and groundwater used for crop irrigation in the US exceeds that for livestock by about a ratio of 60:1. [44] This excessive use of river water distresses ecosystems and communities, and drives scores of species of fish closer to extinction during times of drought. [47]

A 2023 study found that a vegan diet reduced water usage by 54%. [30]

A study in 2019 focused on linkages between water usage and animal agricultural practices in China. [48] The results of the study showed that water resources were being used primarily for animal agriculture; the highest categories were animal husbandry, agriculture, slaughtering and processing of meat, fisheries, and other foods. Together they accounted for the consumption of over 2400 billion m3 embodied water, roughly equating to 40% of total embodied[ clarification needed ] water by the whole system. [48] This means that more than one-third of China's entire water consumption is being used for food processing purposes, and mostly for animal agricultural practices.

Estimated water requirements for various foods [49]
FoodstuffLitres per
kilocaloriegram of
protein
kg of
foodstuff
gram of
fat
Sugar crops0.69N/A197N/A
Vegetables1.3426322154
Starchy roots0.4731387226
Fruits2.09180962348
Cereals0.51211644112
Oil crops0.8116236411
Pulses1.19194055180
Nuts3.63139906347
Milk1.8231102033
Eggs2.2929326533
Chicken meat3.0034432543
Butter0.72N/A55536.4
Pig meat2.1557598823
Sheep/goat meat4.2563876354
Bovine meat10.1911215415153

Water pollution

Water pollution due to animal waste is a common problem in both developed and developing nations. [14] The USA, Canada, India, Greece, Switzerland and several other countries are experiencing major environmental degradation due to water pollution via animal waste. [50] :Table I-1 Concerns about such problems are particularly acute in the case of CAFOs (concentrated animal feeding operations). In the US, a permit for a CAFO requires the implementation of a plan for the management of manure nutrients, contaminants, wastewater, etc., as applicable, to meet requirements under the Clean Water Act. [51] There were about 19,000 CAFOs in the US as of 2008. [52] In fiscal 2014, the United States Environmental Protection Agency (EPA) concluded 26 enforcement actions for various violations by CAFOs. [53]

A 2023 study found that a vegan diet reduced water pollution by 75%. [30]

A green algae bloom has been observed in Sichuan, China. In normal conditions, river water is transparent, but algae blooms result in green algae covering the surface. This prevents other plants at the bottom of the river from getting sunlight, causing them to lose their ability to photosynthesise. Oxygen levels in rivers fall when there is no other vegetation, resulting in the death of other species. River algae Sichuan.jpg
A green algae bloom has been observed in Sichuan, China. In normal conditions, river water is transparent, but algae blooms result in green algae covering the surface. This prevents other plants at the bottom of the river from getting sunlight, causing them to lose their ability to photosynthesise. Oxygen levels in rivers fall when there is no other vegetation, resulting in the death of other species.

Effective use of fertilizer is crucial to accelerate the growth of animal feed production, which in turn increases the amount of feed available for livestock. [54] However, excess fertilizer can enter water bodies via runoff after rainfall, resulting in eutrophication. [55] The addition of nitrogen and phosphorus can cause the rapid growth of algae, also known as an algae bloom. The reduction of oxygen and nutrients in the water caused by the growth of algae ultimately leads to the death of other species in the ecosystem. This ecological harm has consequences not only for the native animals in the affected water body but also for the water supply for people. [54]

To dispose of animal waste and other pollutants, animal production farms often spray manure (often contaminated with potentially toxic bacteria) onto empty fields, called "spray-fields", via sprinkler systems. The toxins within these spray-fields oftentimes run into creeks, ponds, lakes, and other bodies of water, contaminating bodies of water. This process has also led to the contamination of drinking water reserves, harming the environment and citizens alike. [56]

Air pollution

Mean acidifying emissions (air pollution) of different foods per 100g of protein [26]
Food TypesAcidifying Emissions (g SO2eq per 100g protein)
Beef
343.6
Cheese
165.5
Pork
142.7
Lamb and Mutton
139.0
Farmed Crustaceans
133.1
Poultry
102.4
Farmed Fish
65.9
Eggs
53.7
Groundnuts
22.6
Peas
8.5
Tofu
6.7

Animal agriculture is a cause of harmful particulate matter pollution in the atmosphere. This type of production chain produces byproducts; endotoxin, hydrogen sulfide, ammonia, and particulate matter (PM), such as dust, [57] [58] all of which can negatively impact human respiratory health. [59] Furthermore, methane and CO2—the primary greenhouse gas emissions associated with meat production—have also been associated with respiratory diseases like asthma, bronchitis, and COPD. [60]

A study found that concentrated animal feeding operations (CAFOs) could increase perceived asthma-like symptoms for residents within 500 meters. [61] Concentrated hog feeding operations release air pollutants from confinement buildings, manure holding pits, and land application of waste. Air pollutants from these operations have caused acute physical symptoms, such as respiratory illnesses, wheezing, increased breath rate, and irritation of the eyes and nose. [62] [63] [64] That prolonged exposure to airborne animal particulate, such as swine dust, induces a large influx of inflammatory cells into the airways. [65] Those in close proximity to CAFOs could be exposed to elevated levels of these byproducts, which may lead to poor health and respiratory outcomes. [66] Additionally, since CAFOs tend to be located in primarily rural and low-income communities, low-income people are disproportionately affected by these environmental health consequences.

Especially when modified by high temperatures, air pollution can harm all regions, socioeconomic groups, sexes, and age groups. Approximately seven million people die from air pollution exposure every year. Air pollution often exacerbates respiratory disease by permeating into the lung tissue and damaging the lungs. [67]

Despite the wealth of environmental consequences listed above, local US governments tend to support the harmful practices of the animal production industry due to its strong economic benefits. Due to this protective legislature, it is extremely difficult for activists to regulate industry practices and diminish environmental impacts. [68]

Climate change aspects

Energy consumption

Energy efficiency of meat and dairy production Energy efficiency of meat and dairy production, OWID.svg
Energy efficiency of meat and dairy production

An important aspect of energy use in livestock production is the energy consumption that the animals contribute. Feed Conversion Ratio is an animal's ability to convert feed into meat. The Feed Conversion Ratio (FCR) is calculated by taking the energy, protein, or mass input of the feed divided by the output of meat provided by the animal. A lower FCR corresponds with a smaller requirement of feed per meat output, and therefore the animal contributes less GHG emissions. Chickens and pigs usually have a lower FCR compared to ruminants. [69]

Intensification and other changes in the livestock industries influence energy use, emissions, and other environmental effects of meat production. [70]

Manure can also have environmental benefits as a renewable energy source, in digester systems yielding biogas for heating and/or electricity generation. Manure biogas operations can be found in Asia, Europe, [71] [72] North America, and elsewhere. [73] System cost is substantial, relative to US energy values, which may be a deterrent to more widespread use. Additional factors, such as odour control and carbon credits, may improve benefit-to-cost ratios. [74] Manure can be mixed with other organic wastes in anaerobic digesters to take advantage of economies of scale. Digested waste is more uniform in consistency than untreated organic wastes, and can have higher proportions of nutrients that are more available to plants, which enhances the utility of digestate as a fertiliser product. [75] This encourages circularity in meat production, which is typically difficult to achieve due to environmental and food safety concerns.

Greenhouse gas emissions

Livestock produces the majority of greenhouse gas emissions from agriculture and demands around 30% of agricultural fresh water needs, while only supplying 18% of the global calorie intake. Animal-derived food plays a larger role in meeting human protein needs, yet is still a minority of supply at 39%, with crops providing the rest. [76] :746–747

Out of the Shared Socioeconomic Pathways used by the Intergovernmental Panel on Climate Change, only SSP1 offers any realistic possibility of meeting the 1.5 °C (2.7 °F) target. [77] Together with measures like a massive deployment of green technology, this pathway assumes animal-derived food will play a lower role in the global diets relative to now. [78] As a result, there have been calls for phasing out subsidies currently offered to livestock farmers in many places worldwide, [79] and net zero transition plans now involve limits on total livestock headcounts, including substantial reductions of existing stocks in some countries with extensive animal agriculture sectors like Ireland. [80] Yet, an outright end to human consumption of meat and/or animal products is not currently considered a realistic goal. [81] Therefore, any comprehensive plan of adaptation to effects of climate change, particularly the present and future effects of climate change on agriculture, must also consider livestock.

Livestock activities also contribute disproportionately to land-use effects, since crops such as corn and alfalfa are cultivated in order to feed the animals.

In 2010, enteric fermentation accounted for 43% of the total greenhouse gas emissions from all agricultural activity in the world. [82] The meat from ruminants has a higher carbon equivalent footprint than other meats or vegetarian sources of protein based on a global meta-analysis of lifecycle assessment studies. [83] Small ruminants such as sheep and goats contribute approximately 475 million tons of carbon dioxide equivalent to GHG emissions, which constitutes around 6.5% of world agriculture sector emissions. [84] Methane production by animals, principally ruminants, makes up an estimated 15-20% global production of methane. [85] [86]

Mitigation options

Per capita meat consumption and GDP 1990-2017 Development of per capita meat consumption and gross domestic product (GDP) over time (1990-2017).png
Per capita meat consumption and GDP 1990–2017

Mitigation options for reducing methane emission from livestock include a change in diet, that is consuming less meat and dairy. [87] A significant reduction in meat consumption will be essential to mitigate climate change, especially as the human population increases by a projected 2.3 billion by the middle of the century. [2] A 2019 report in The Lancet recommended that global meat consumption be halved to mitigate climate change. [88] A study quantified climate change mitigation potentials of 'high-income' nations shifting diets – away from meat-consumption – and restoration of the spared land, finding that if these were combined they could "reduce annual agricultural production emissions of high-income nations' diets by 61%". [89] [90]

In addition to reduced consumption, emissions can also be reduced by changes in practice. One study found that shifting compositions of current feeds, production areas, and informed land restoration could enable greenhouse gas emissions reductions of 34–85% annually (612–1,506 megatons CO2 equivalent per year) without increasing costs or changing diets. [91]

Producers can reduce ruminant enteric fermentation using genetic selection, [92] [93] immunization, rumen defaunation, competition of methanogenic archaea with acetogens, [94] introduction of methanotrophic bacteria into the rumen, [95] [96] diet modification and grazing management, among others. [97] [98] [99] The principal mitigation strategies identified for reduction of agricultural nitrous oxide emissions are avoiding over-application of nitrogen fertilizers and adopting suitable manure management practices. [100] [101] Mitigation strategies for reducing carbon dioxide emissions in the livestock sector include adopting more efficient production practices to reduce agricultural pressure for deforestation (such as in Latin America), reducing fossil fuel consumption, and increasing carbon sequestration in soils. [102]

Measures that increase state revenues from meat consumption/production could enable the use of these funds for related research and development and "to cushion social hardships among low-income consumers". Meat and livestock are important sectors of the contemporary socioeconomic system, with livestock value chains employing an estimated >1.3 billion people. [5]

Sequestering carbon into soil is currently not feasible to cancel out planet-warming emissions caused by the livestock sector. The global livestock annually emits 135 billion metric tons of carbon, way more than can be returned to the soil. [103] Despite of this the idea of sequestering carbon to the soil is currently advocated by livestock industry as well as grassroots groups. [104]

Effects on ecosystems

Soils

Grazing can have positive or negative effects on rangeland health, depending on management quality, [105] and grazing can have different effects on different soils [106] and different plant communities. [107] Grazing can sometimes reduce, and other times increase, biodiversity of grassland ecosystems. [108] [109] In beef production, cattle ranching helps preserve and improve the natural environment by maintaining habitats that are well suited for grazing animals. [110] Lightly grazed grasslands also tend to have higher biodiversity than overgrazed or non-grazed grasslands. [111]

Overgrazing can decrease soil quality by constantly depleting it of necessary nutrients. [112] By the end of 2002, the US Bureau of Land Management (BLM) found that 16% of the evaluated 7,437 grazing allotments had failed to meet rangeland health standards because of their excessive grazing use. [113] Overgrazing appears to cause soil erosion in many dry regions of the world. [14] However, on US farmland, soil erosion is much less on land used for livestock grazing than on land used for crop production. According to the US Natural Resources Conservation Service, on 95.1% of US pastureland, sheet and rill erosion are within the estimated soil loss tolerance, and on 99.4% of US pastureland, wind erosion is within the estimated soil loss tolerance. [114]

Dryland grazing on the Great Plains in Colorado Two cows grazing.jpg
Dryland grazing on the Great Plains in Colorado

Grazing can affect the sequestration of carbon and nitrogen in the soil. This sequestration helps mitigate the effects of greenhouse gas emissions, and in some cases, increases ecosystem productivity by affecting nutrient cycling. [115] A 2017 meta-study of the scientific literature estimated that the total global soil carbon sequestration potential from grazing management ranges from 0.3–0.8 gigatons CO2eq per year, which is equivalent to 4–11% of total global livestock emissions, but that "Expansion or intensification in the grazing sector as an approach to sequestering more carbon would lead to substantial increases in methane, nitrous oxide and land use change-induced CO2 emissions". [116] Project Drawdown estimates the total carbon sequestration potential of improved managed grazing at 13.72–20.92 gigatons CO2eq between 2020–2050, equal to 0.46–0.70 gigatons CO2eq per year. [117] A 2022 peer-reviewed paper estimated the carbon sequestration potential of improved grazing management at a similar level of 0.15–0.70 gigatons CO2eq per year. [118] A 2021 peer-reviewed paper found that sparsely grazed and natural grasslands account for 80% of the total cumulative carbon sink of the world’s grasslands, whereas managed grasslands have been a net greenhouse gas source over the past decade. [119] Another peer-reviewed paper found that if current pastureland was restored to its former state as wild grasslands, shrublands, and sparse savannas without livestock this could store an estimated 15.2–59.9 gigatons additional carbon. [120] A study found that grazing in US virgin grasslands causes the soil to have lower soil organic carbon but higher soil nitrogen content. [121] In contrast, at the High Plains Grasslands Research Station in Wyoming, the soil in the grazed pastures had more organic carbon and nitrogen in the top 30 cm than the soil in non-grazed pastures. [122] Additionally, in the Piedmont region of the US, well-managed grazing of livestock on previously eroded soil resulted in high rates of beneficial carbon and nitrogen sequestration compared to non-grazed grass. [123]

In Canada, a review highlighted that the methane and nitrous oxide emitted from manure management comprised 17% of agricultural greenhouse gas emissions, while nitrous oxide emitted from soils after application of manure, accounted for 50% of total emissions. [124]

Manure provides environmental benefits when properly managed. Deposition of manure on pastures by grazing animals is an effective way to preserve soil fertility. Many nutrients are recycled in crop cultivation by collecting animal manure from barns and concentrated feeding sites, sometimes after composting. For many areas with high livestock density, manure application substantially replaces the application of synthetic fertilizers on surrounding cropland. [125] Manure is also spread on forage-producing land that is grazed, rather than cropped. [43]

Also, small-ruminant flocks in North America (and elsewhere) are sometimes used on fields for removal of various crop residues inedible by humans, converting them to food. Small ruminants, such as sheep and goats, can control some invasive or noxious weeds (such as spotted knapweed, tansy ragwort, leafy spurge, yellow starthistle, tall larkspur, etc.) on rangeland. [126] Small ruminants are also useful for vegetation management in forest plantations and for clearing brush on rights-of-way. Other ruminants, like Nublang cattle, are used in Bhutan to help remove a species of bamboo, Yushania microphylla, which tends to crowd out indigenous plant species. [127] These represent alternatives to herbicide use. [128]

Biodiversity

Biomass of mammals on Earth [129] [130]

   Livestock, mostly cattle and pigs (60%)
   Humans (36%)
   Wild mammals (4%)

Meat production is considered one of the prime factors contributing to the current biodiversity loss crisis. [131] [132] [133] The 2019 IPBES Global Assessment Report on Biodiversity and Ecosystem Services found that industrial agriculture and overfishing are the primary drivers of the extinction, with the meat and dairy industries having a substantial impact. [134] [135] The global livestock sector contributes a significant share to anthropogenic GHG emissions, but it can also deliver a significant share of the necessary mitigation effort. [136] FAO estimates that the adoption of already available best practices can reduce emissions by up to 30%. [136]

Grazing (especially overgrazing) may detrimentally affect certain wildlife species, e.g. by altering cover and food supplies. The growing demand for meat is contributing to significant biodiversity loss as it is a significant driver of deforestation and habitat destruction; species-rich habitats, such as significant portions of the Amazon region, are being converted to agriculture for meat production. [137] [131] [138] World Resource Institute (WRI) website mentions that "30 percent of global forest cover has been cleared, while another 20 percent has been degraded. Most of the rest has been fragmented, leaving only about 15 percent intact." [139] WRI also states that around the world there is "an estimated 1.5 billion hectares (3.7 billion acres) of once-productive croplands and pasturelands – an area nearly the size of Russia – are degraded. Restoring productivity can improve food supplies, water security, and the ability to fight climate change." [140] Around 25% to nearly 40% of global land surface is being used for livestock farming. [135] [141]

A 2022 report from World Animal Protection and the Center for Biological Diversity found that, based on 2018 data, some 235 million pounds (or 117,500 tons) of pesticides are used for animal feed purposes annually in the United States alone, in particular glyphosate and atrazine. The report emphasizes that 100,000 pounds of glyphosate has the potential to harm or kill some 93% of species listed under the Endangered Species Act. Atrazine, which is banned in 35 countries, could harm or kill at least 1,000 listed species. Both groups involved in the report advocate for consumers to reduce their consumption of animal products and to transition towards plant-based diets in order to reduce the growth of factory farming and protect endangered species of wildlife. [142]

A 2023 study found that a vegan diet reduced wildlife destruction by 66%. [30]

In North America, various studies have found that grazing sometimes improves habitat for elk, [143] blacktailed prairie dogs, [144] sage grouse, [145] and mule deer. [146] [147] A survey of refuge managers on 123 National Wildlife Refuges in the US tallied 86 species of wildlife considered positively affected and 82 considered negatively affected by refuge cattle grazing or haying. [148] The kind of grazing system employed (e.g. rest-rotation, deferred grazing, HILF grazing) is often important in achieving grazing benefits for particular wildlife species. [149]

The biologists Rodolfo Dirzo, Gerardo Ceballos, and Paul R. Ehrlich write in an opinion piece for Philosophical Transactions of the Royal Society B that reductions in meat consumption "can translate not only into less heat, but also more space for biodiversity." They insist that it is the "massive planetary monopoly of industrial meat production that needs to be curbed" while respecting the cultural traditions of indigenous peoples, for whom meat is an important source of protein. [150]

Aquatic ecosystems

Mean eutrophying emissions (water pollution by phosphates) of different foods per 100g of protein [26]
Food typeEutrophying emissions
(g PO43-eq per 100g protein)
Beef
301.4
Farmed Fish
235.1
Farmed Crustaceans
227.2
Cheese
98.4
Lamb and Mutton
97.1
Pork
76.4
Poultry
48.7
Eggs
21.8
Groundnuts
14.1
Peas
7.5
Tofu
6.2

Global agricultural practices are known to be one of the main reasons for environmental degradation. Animal agriculture worldwide encompasses 83% of farmland (but only accounts for 18% of the global calorie intake), and the direct consumption of animals as well as over-harvesting them is causing environmental degradation through habitat alteration, biodiversity loss, climate change, pollution, and trophic interactions. [151] These pressures are enough to drive biodiversity loss in any habitat, however freshwater ecosystems are showing to be more sensitive and less protected than others and show a very high effect on biodiversity loss when faced with these impacts. [151]

In the Western United States, many stream and riparian habitats have been negatively affected by livestock grazing. This has resulted in increased phosphates, nitrates, decreased dissolved oxygen, increased temperature, turbidity, and eutrophication events, and reduced species diversity. [152] [153] Livestock management options for riparian protection include salt and mineral placement, limiting seasonal access, use of alternative water sources, provision of "hardened" stream crossings, herding, and fencing. [154] [155] In the Eastern United States, a 1997 study found that waste release from pork farms has also been shown to cause large-scale eutrophication of bodies of water, including the Mississippi River and Atlantic Ocean (Palmquist, et al., 1997). [156] In North Carolina, where the study was done, measures have since been taken to reduce the risk of accidental discharges from manure lagoons, and since then there has been evidence of improved environmental management in US hog production. [157] Implementation of manure and wastewater management planning can help assure low risk of problematic discharge into aquatic systems. [157]

In Central-Eastern Argentina, a 2017 study found large quantities of metal pollutants (chromium, copper, arsenic and lead) in their freshwater streams, disrupting the aquatic biota. [158] The level of chromium in the freshwater systems exceeded 181.5× the recommended guidelines necessary for survival of aquatic life, while lead was 41.6×, copper was 57.5×, and arsenic exceeded 12.9×. The results showed excess metal accumulation due to agricultural runoff, the use of pesticides, and poor mitigation efforts to stop the excess runoff. [158]

Animal agriculture contributes to global warming, which leads to ocean acidification. This occurs because as carbon emissions increase, a chemical reaction occurs between carbon dioxide in the atmosphere and ocean water, causing seawater acidification. [159] The process is also known as the dissolution of inorganic carbon in seawater. [160] This chemical reaction creates an environment that makes it difficult for calcifying organisms to produce protective shells and causes seagrass overpopulation. [161] A reduction in marine life can have an adverse effect on people’s way of life, since limited sea life may reduce food availability and reduce coastal protection against storms. [162]

Effects on antibiotic resistance

A CDC infographic on how antibiotic-resistant bacteria have the potential to spread from farm animals Ar-infographic-950px.jpg
A CDC infographic on how antibiotic-resistant bacteria have the potential to spread from farm animals

Antibiotic use in livestock is the use of antibiotics for any purpose in the husbandry of livestock, which includes treatment when ill (therapeutic), treatment of a group of animals when at least one is diagnosed with clinical infection (metaphylaxis [163] ), and preventative treatment (prophylaxis). Antibiotics are an important tool to treat animal as well as human disease, safeguard animal health and welfare, and support food safety. [164] However, used irresponsibly, this may lead to antibiotic resistance which may impact human, animal and environmental health. [165] [166] [167] [168]

While levels of use vary dramatically from country to country, for example some Northern European countries use very low quantities to treat animals compared with humans, [169] [170] worldwide an estimated 73% of antimicrobials (mainly antibiotics) are consumed by farm animals. [171] Furthermore, a 2015 study also estimates that global agricultural antibiotic usage will increase by 67% from 2010 to 2030, mainly from increases in use in developing BRIC countries. [172]

Increased antibiotic use is a matter of concern as antibiotic resistance is considered to be a serious threat to human and animal welfare in the future, and growing levels of antibiotics or antibiotic-resistant bacteria in the environment could increase the numbers of drug-resistant infections in both. [173] Bacterial diseases are a leading cause of death and a future without effective antibiotics would fundamentally change the way modern human as well as veterinary medicine is practised. [173] [174] [175] However, legislation and other curbs on antibiotic use in farm animals are now being introduced across the globe. [176] [177] [178] In 2017, the World Health Organization strongly suggested reducing antibiotic use in animals used in the food industry. [179]

The use of antibiotics for growth promotion purposes was banned in the European Union from 2006, [180] and the use of sub-therapeutic doses of medically important antibiotics in animal feed and water [181] to promote growth and improve feed efficiency became illegal in the United States on 1 January 2017, through regulatory change enacted by the Food and Drug Administration (FDA), which sought voluntary compliance from drug manufacturers to re-label their antibiotics. [182] [183]

There are concerns about meat production's potential to spread diseases as an environmental impact. [184] [185] [186] [187]

Alternatives to meat production and consumption

A study shows that novel foods such as cultured meat and dairy, algae, existing microbial foods, and ground-up insects are shown to have the potential to reduce environmental impacts [5] [188] [189] [190] – by over 80%. [191] [192] Various combinations may further reduce the environmental impacts of these alternatives – for example, a study explored solar-energy-driven production of microbial foods from direct air capture. [193] Alternatives are not only relevant for human consumption but also for pet food and other animal feed.

Meat reduction and health

An insight to a vegetarian diet Soy-whey-protein-diet.jpg
An insight to a vegetarian diet

With care, meat can be substituted in most diets with a wide variety of foods such as fungi [194] [195] [196] or "meat substitutes". However, substantially reducing meat intake could result in nutritional deficiencies if done inadequately, especially for children, adolescents, and pregnant and lactating women "in low-income countries". [5] A review suggests that the reduction of meat in people's diets should be accompanied by an increase in alternative sources of protein and micronutrients to avoid nutritional deficiencies for healthy diets such as iron and zinc. [5] Meats notably also contain vitamin B12, [197] collagen [198] and creatine. [199] This could be achieved with specific types of foods such as iron-rich beans and a diverse variety of protein-rich foods [200] like red lentils, plant-based protein powders [201] and high-protein wraps, and/or dietary supplements. [189] [202] [203] Dairy and fish and/or specific types of other foods and/or supplements contain omega 3, vitamin K2, vitamin D3, iodine, magnesium and calcium, many of which were generally lower in people consuming types of plant-based diets in studies. [204] [205]

Nevertheless, observational studies find beneficial effects from plant-based diets (compared to consumption of meat products) on health and mortality rates. [206] [5] [207] [208] [209]

Meat-reduction strategies

Strategies for implementing meat-reduction among populations include large-scale education and awareness building to promote more sustainable consumption styles. Other types of policy interventions could accelerate these shifts and might include "restrictions or fiscal mechanisms such as [meat] taxes". [5] In the case of fiscal mechanisms, these could be based on forms of scientific calculation of external costs (externalities currently not reflected in any way in the monetary price) [210] to make the polluter pay, e.g. for the damage done by excess nitrogen. [211] In the case of restrictions, this could be based on limited domestic supply or Personal (Carbon) Allowances (certificates and credits which would reward sustainable behavior). [212] [213]

Relevant to such a strategy, estimating the environmental impacts of food products in a standardized way – as has been done with a dataset of more than 57,000 food products in supermarkets – could also be used to inform consumers or in policy, making consumers more aware of the environmental impacts of animal-based products (or requiring them to take such into consideration). [214] [215]

Young adults that are faced with new physical or social environments (for example, moving away from home) are also more likely to make dietary changes and reduce their meat intake. [216] Another strategy includes increasing the prices of meat while also reducing the prices of plant-based products, which could show a significant impact on meat-reduction. [217]

Meat reduction and increased plant-based preferences seen based on social and other life changes. Plant-Based Preferences.png
Meat reduction and increased plant-based preferences seen based on social and other life changes.

A reduction in meat portion sizes could potentially be more beneficial than cutting out meat entirely from ones diet, according to a 2022 study. [216] This study revolved around young Dutch adults, and showed that the adults were more reluctant to cut out meat entirely to make the change to plant-based diets due to habitual behaviours. Increasing and improving plant-based alternatives, as well as the education about plant-based alternatives, proved to be one of the most effective ways to combat these behaviours. The lack of education about plant-based alternatives is a road-block for most people - most adults do not know how to properly cook plant-based meals or know the health risks/benefits associated with a vegetarian diet - which is why education among adults is important in meat-reduction strategies. [216] [217]

In the Netherlands, a meat tax of 15% to 30% could show a reduction of meat consumption by 8% to 16%. [216] as well as reducing the amount of livestock by buying out farmers. [218] In 2022, the city of Haarlem, Netherlands announced that advertisements for factory-farmed meat will be banned in public places, starting in 2024. [219]

A 2022 review concluded that "low and moderate meat consumption levels are compatible with the climate targets and broader sustainable development, even for 10 billion people". [5]

In June 2023, the European Commission's Scientific Advice Mechanism published a review of all available evidence and accompanying policy recommendations to promote sustainable food consumption and reducing meat intake. They reported that the evidence supports policy interventions on pricing (including "meat taxes, and pricing products according to their environmental impacts, as well as lower taxes on healthy and sustainable alternatives"), availability and visibility, food composition, labelling and the social environment. [220] They also stated:

People choose food not just through rational reflection, but also based on many other factors: food availability, habits and routines, emotional and impulsive reactions, and their financial and social situation. So we should consider ways to unburden the consumer and make sustainable, healthy food an easy and affordable choice.

By type of animal

Cattle

Clearings for cattle grazing in the Chaco region of Paraguay ParaguayChaco Clearings for cattle grazing.jpg
Clearings for cattle grazing in the Chaco region of Paraguay

Pigs

The environmental impact of pig farming is mainly driven by the spread of feces and waste to surrounding neighborhoods, polluting air and water with toxic waste particles. [221] Waste from pig farms can carry pathogens, bacteria (often antibiotic resistant), and heavy metals that can be toxic when ingested. [221] Pig waste also contributes to groundwater pollution in the forms of groundwater seepage and waste spray into neighboring areas with sprinklers. The contents in the spray and waste drift have been shown to cause mucosal irritation, [222] respiratory ailment, [223] increased stress, [224] decreased quality of life, [225] and higher blood pressure. [226] This form of waste disposal is an attempt for factory farms to be cost efficient. The environmental degradation resulting from pig farming presents an environmental injustice problem, since the communities do not receive any benefit from the operations, and instead, suffer negative externalities, such as pollution and health problems. [227] The United States Agriculture and Consumer Health Department has stated that the "main direct environmental impact of pig production is related to the manure produced. [228]

See also

Related Research Articles

<span class="mw-page-title-main">Meat</span> Animal flesh eaten as food

Meat is animal tissue, often muscle, that is eaten as food. Humans have hunted and farmed other animals for meat since prehistory. The Neolithic Revolution allowed the domestication of animals, including chickens, sheep, goats, pigs, horses, and cattle, starting around 11,000 years ago. Since then, selective breeding has enabled farmers to produce meat with the qualities desired by producers and consumers.

<span class="mw-page-title-main">Animal husbandry</span> Management of farm animals

Animal husbandry is the branch of agriculture concerned with animals that are raised for meat, fibre, milk, or other products. It includes day-to-day care, management, production, nutrition, selective breeding, and the raising of livestock. Husbandry has a long history, starting with the Neolithic Revolution when animals were first domesticated, from around 13,000 BC onwards, predating farming of the first crops. By the time of early civilisations such as ancient Egypt, cattle, sheep, goats, and pigs were being raised on farms.

<span class="mw-page-title-main">Grazing</span> Feeding livestock on forage

In agriculture, grazing is a method of animal husbandry whereby domestic livestock are allowed outdoors to free range and consume wild vegetations in order to convert the otherwise indigestible cellulose within grass and other forages into meat, milk, wool and other animal products, often on land that is unsuitable for arable farming.

<span class="mw-page-title-main">Concentrated animal feeding operation</span> Type of American intensive animal farming

In animal husbandry, a concentrated animal feeding operation (CAFO), as defined by the United States Department of Agriculture (USDA), is an intensive animal feeding operation (AFO) in which over 1,000 animal units are confined for over 45 days a year. An animal unit is the equivalent of 1,000 pounds of "live" animal weight. A thousand animal units equates to 700 dairy cows, 1,000 meat cows, 2,500 pigs weighing more than 55 pounds (25 kg), 10,000 pigs weighing under 55 pounds, 10,000 sheep, 55,000 turkeys, 125,000 chickens, or 82,000 egg laying hens or pullets.

<span class="mw-page-title-main">Ethics of eating meat</span> Food ethics topic

Conversations regarding the ethics of eating meat are focused on whether or not it is moral to eat non-human animals. Ultimately, this is a debate that has been ongoing for millennia, and it remains one of the most prominent topics in food ethics. Individuals who promote meat consumption do so for a number of reasons, such as health, cultural traditions, religious beliefs, and scientific arguments that support the practice. Those who support meat consumption typically argue that making a meat-free diet mandatory would be wrong because it fails to consider the individual nutritional needs of humans at various stages of life, fails to account for biological differences between the sexes, ignores the reality of human evolution, ignores various cultural considerations, or because it would limit the adaptability of the human species.

<span class="mw-page-title-main">Environmental vegetarianism</span> Type of practice of vegetarianism

Environmental vegetarianism is the practice of vegetarianism that is motivated by the desire to create a sustainable diet, which avoids the negative environmental impact of meat production. Livestock as a whole is estimated to be responsible for around 15% of global greenhouse gas emissions. As a result, significant reduction in meat consumption has been advocated by, among others, the Intergovernmental Panel on Climate Change in their 2019 special report and as part of the 2017 World Scientists' Warning to Humanity.

<span class="mw-page-title-main">Animal product</span> Food product derived from non-human animal body

An animal product is any material derived from the body of a non-human animal. Examples are fat, flesh, blood, milk, eggs, and lesser known products, such as isinglass and rennet.

<span class="mw-page-title-main">Intensive animal farming</span> Branch of agriculture

Intensive animal farming, industrial livestock production, and macro-farms, also known as factory farming, is a type of intensive agriculture, specifically an approach to animal husbandry designed to maximize production while minimizing costs. To achieve this, agribusinesses keep livestock such as cattle, poultry, and fish at high stocking densities, at large scale, and using modern machinery, biotechnology, and global trade. The main products of this industry are meat, milk and eggs for human consumption. There are issues regarding whether intensive animal farming is sustainable in the social long-run given its costs in resources. Analysts also raise issues about its ethics.

<span class="mw-page-title-main">Sustainable food system</span> Balanced growth of nutritional substances and their distribution

A sustainable food system is a type of food system that provides healthy food to people and creates sustainable environmental, economic, and social systems that surround food. Sustainable food systems start with the development of sustainable agricultural practices, development of more sustainable food distribution systems, creation of sustainable diets, and reduction of food waste throughout the system. Sustainable food systems have been argued to be central to many or all 17 Sustainable Development Goals.

<i>Livestocks Long Shadow</i> United Nations report

Livestock's Long Shadow: Environmental Issues and Options is a United Nations report, released by the Food and Agriculture Organization (FAO) of the United Nations on 29 November 2006, that "aims to assess the full impact of the livestock sector on environmental problems, along with potential technical and policy approaches to mitigation". It stated that livestock accounts for 18% of anthropogenic greenhouse gas emissions, a figure which FAO changed to 14.5% in its 2013 study Tackling climate change through livestock.

<span class="mw-page-title-main">Low-carbon diet</span> Diet to reduce greenhouse gas emissions

A low-carbon diet is any diet that results in lower greenhouse gas emissions. Choosing a low carbon diet is one facet of developing sustainable diets which increase the long-term sustainability of humanity. Major tenets of a low-carbon diet include eating a plant-based diet, and in particular little or no beef and dairy. Low-carbon diets differ around the world in taste, style, and the frequency they are eaten. Asian countries like India and China feature vegetarian and vegan meals as staples in their diets. In contrast, Europe and North America rely on animal products for their Western diets.

<span class="mw-page-title-main">Sustainable diet</span> Diet that contributes to the broader environmental and social sustainability

Sustainable diets are "dietary patterns that promote all dimensions of individuals’ health and wellbeing; have low environmental pressure and impact; are accessible, affordable, safe and equitable; and are culturally acceptable". These diets are nutritious, eco-friendly, economically sustainable, and accessible to people of various socioeconomic backgrounds. Sustainable diets attempt to address nutrient deficiencies and excesses, while accounting for ecological phenomena such as climate change, loss of biodiversity and land degradation. These diets are comparable to the climatarian diet, with the added domains of economic sustainability and accessiblity.

The environmental impact of agriculture is the effect that different farming practices have on the ecosystems around them, and how those effects can be traced back to those practices. The environmental impact of agriculture varies widely based on practices employed by farmers and by the scale of practice. Farming communities that try to reduce environmental impacts through modifying their practices will adopt sustainable agriculture practices. The negative impact of agriculture is an old issue that remains a concern even as experts design innovative means to reduce destruction and enhance eco-efficiency. Though some pastoralism is environmentally positive, modern animal agriculture practices tend to be more environmentally destructive than agricultural practices focused on fruits, vegetables and other biomass. The emissions of ammonia from cattle waste continue to raise concerns over environmental pollution.

<span class="mw-page-title-main">Agricultural pollution</span> Type of pollution caused by agriculture

Agricultural pollution refers to biotic and abiotic byproducts of farming practices that result in contamination or degradation of the environment and surrounding ecosystems, and/or cause injury to humans and their economic interests. The pollution may come from a variety of sources, ranging from point source water pollution to more diffuse, landscape-level causes, also known as non-point source pollution and air pollution. Once in the environment these pollutants can have both direct effects in surrounding ecosystems, i.e. killing local wildlife or contaminating drinking water, and downstream effects such as dead zones caused by agricultural runoff is concentrated in large water bodies.

<span class="mw-page-title-main">Livestock</span> Animals kept for production of meat, eggs, milk, wool, etc.

Livestock are the domesticated animals raised in an agricultural setting in order to provide labour and produce diversified products for consumption such as meat, eggs, milk, fur, leather, and wool. The term is sometimes used to refer solely to animals who are raised for consumption, and sometimes used to refer solely to farmed ruminants, such as cattle, sheep, and goats. Horses are considered livestock in the United States. The USDA classifies pork, veal, beef, and lamb (mutton) as livestock, and all livestock as red meat. Poultry and fish are not included in the category. The latter is likely due to the fact that fish products are not governed by the USDA, but by the FDA.

<span class="mw-page-title-main">Manure</span> Organic matter, mostly derived from animal feces, which can be used as fertilizer

Manure is organic matter that is used as organic fertilizer in agriculture. Most manure consists of animal feces; other sources include compost and green manure. Manures contribute to the fertility of soil by adding organic matter and nutrients, such as nitrogen, that are utilised by bacteria, fungi and other organisms in the soil. Higher organisms then feed on the fungi and bacteria in a chain of life that comprises the soil food web.

A meat tax is a tax levied on meat and/or other animal products to help cover the health and environmental costs that result from using animals for food. Livestock is known to significantly contribute to global warming, and to negatively impact global nitrogen cycles and biodiversity.

The production of cattle has a significant environmental impact, whether measured in terms of methane emissions, land use, consumption of water, discharge of pollutants, or eutrophication of waterways.

<span class="mw-page-title-main">Climate-smart agriculture</span> System for agricultural productivity

Climate-smart agriculture (CSA) is a set of farming methods that has three main objectives with regards to climate change. Firstly, they use adaptation methods to respond to the effects of climate change on agriculture. Secondly, they aim to increase agricultural productivity and to ensure food security for a growing world population. Thirdly, they try to reduce greenhouse gas emissions from agriculture as much as possible. Climate-smart agriculture works as an integrated approach to managing land. This approach helps farmers to adapt their agricultural methods to the effects of climate change.

<span class="mw-page-title-main">Greenhouse gas emissions from agriculture</span> Agricultures effects on climate change

The amount of greenhouse gas emissions from agriculture is significant: The agriculture, forestry and land use sector contribute between 13% and 21% of global greenhouse gas emissions. Emissions come from direct greenhouse gas emissions. and from indirect emissions. With regards to direct emissions, nitrous oxide and methane make up over half of total greenhouse gas emission from agriculture. Indirect emissions on the other hand come from the conversion of non-agricultural land such as forests into agricultural land. Furthermore, there is also fossil fuel consumption for transport and fertilizer production. For example, the manufacture and use of nitrogen fertilizer contributes around 5% of all global greenhouse gas emissions. Livestock farming is a major source of greenhouse gas emissions. At the same time, livestock farming is affected by climate change.

References

  1. Mitigation of Climate Change: Full report (Report). IPCC Sixth Assessment Report. 2022. 7.3.2.1 page 771.
  2. 1 2 3 Carrington, Damian (October 10, 2018). "Huge reduction in meat-eating 'essential' to avoid climate breakdown". The Guardian . Retrieved October 16, 2017.
  3. Eisen, Michael B.; Brown, Patrick O. (2022-02-01). "Rapid global phaseout of animal agriculture has the potential to stabilize greenhouse gas levels for 30 years and offset 68 percent of CO2 emissions this century". PLOS Climate. 1 (2): e0000010. doi: 10.1371/journal.pclm.0000010 . ISSN   2767-3200. S2CID   246499803.
  4. Damian Carrington, "Avoiding meat and dairy is ‘single biggest way’ to reduce your impact on Earth ", The Guardian, 31 May 2018 (page visited on 19 August 2018).
  5. 1 2 3 4 5 6 7 8 9 Parlasca, Martin C.; Qaim, Matin (5 October 2022). "Meat Consumption and Sustainability". Annual Review of Resource Economics. 14: 17–41. doi: 10.1146/annurev-resource-111820-032340 . ISSN   1941-1340.
  6. Devlin, Hannah (July 19, 2018). "Rising global meat consumption 'will devastate environment'". The Guardian. Retrieved July 21, 2018.
  7. Godfray, H. Charles J.; Aveyard, Paul; et al. (2018). "Meat consumption, health, and the environment". Science. 361 (6399). Bibcode:2018Sci...361M5324G. doi: 10.1126/science.aam5324 . PMID   30026199. S2CID   49895246.
  8. 1 2 3 FAO. 2006. World agriculture: towards 2030/2050. Prospects for food, nutrition, agriculture and major commodity groups. Interim report. Global Perspectives Unit, United Nations Food and Agriculture Organization. 71 pp.
  9. Nibert, David (2011). "Origins and Consequences of the Animal Industrial Complex". In Steven Best; Richard Kahn; Anthony J. Nocella II; Peter McLaren (eds.). The Global Industrial Complex: Systems of Domination. Rowman & Littlefield. p. 208. ISBN   978-0739136980.
  10. Ritchie, Hannah; Roser, Max (2017-08-25). "Meat and Dairy Production". Our World in Data.
  11. 1 2 "Information About Soya, Soybeans". 2011-10-16. Archived from the original on 2011-10-16. Retrieved 2019-11-11.
  12. Fadel, J. G (1999-06-30). "Quantitative analyses of selected plant by-product feedstuffs, a global perspective". Animal Feed Science and Technology. 79 (4): 255–268. doi:10.1016/S0377-8401(99)00031-0. ISSN   0377-8401.
  13. Schingoethe, David J. (1991-07-01). "Byproduct Feeds: Feed Analysis and Interpretation". Veterinary Clinics of North America: Food Animal Practice. 7 (2): 577–584. doi:10.1016/S0749-0720(15)30787-8. ISSN   0749-0720. PMID   1654177.
  14. 1 2 3 Steinfeld, Henning; Gerber, Pierre; Wassenaar, Tom; Castel, Vincent; Rosales, Mauricio; de Haan, Cees (2006), Livestock's Long Shadow: Environmental Issues and Options (PDF), Rome: FAO
  15. 1 2 3 4 5 Mottet, A.; de Haan, C.; Falcucci, A.; Tempio, G.; Opio, C.; Gerber, P. (2022). More fuel for the food/feed debate. FAO.
  16. 1 2 3 4 5 Mottet, Anne; de Haan, Cees; Falcucci, Alessandra; Tempio, Giuseppe; Opio, Carolyn; Gerber, Pierre (2017-09-01). "Livestock: On our plates or eating at our table? A new analysis of the feed/food debate". Global Food Security. Food Security Governance in Latin America. 14: 1–8. doi:10.1016/j.gfs.2017.01.001. ISSN   2211-9124.
  17. Borsari, Bruno; Kunnas, Jan (2020), Leal Filho, Walter; Azul, Anabela Marisa; Brandli, Luciana; özuyar, Pinar Gökçin (eds.), "Agriculture Production and Consumption", Responsible Consumption and Production, Encyclopedia of the UN Sustainable Development Goals, Cham: Springer International Publishing, pp. 1–11, doi:10.1007/978-3-319-95726-5_78, ISBN   978-3-319-95726-5 , retrieved 2023-02-20
  18. Zheng, Zhihao; Henneberry, Shida Rastegari (2010). "The Impact of Changes in Income Distribution on Current and Future Food Demand in Urban China". Journal of Agricultural and Resource Economics. 35 (1): 51–71. ISSN   1068-5502. JSTOR   23243036.
  19. Elferink, E. V.; et al. (2008). "Feeding livestock food residue and the consequences for the environmental impact of meat". J. Clean. Prod. 16 (12): 1227–1233. doi:10.1016/j.jclepro.2007.06.008.
  20. Hoffman, L. and A. Baker. 2010. Market issues and prospects for U.S. distillers' grains supply, use, and price relationships. USDA FDS-10k-01
  21. National Research Council. 2000. Nutrient Requirements of Beef Cattle. National Academy Press.
  22. Anderson, D. C. (1978). "Use of cereal residues in beef cattle production systems". J. Anim. Sci. 46 (3): 849–861. doi:10.2527/jas1978.463849x.
  23. Males, J. R. (1987). "Optimizing the utilization of cereal crop residues for beef cattle". J. Anim. Sci. 65 (4): 1124–1130. doi:10.2527/jas1987.6541124x.
  24. Ward, J. K. (1978). "Utilization of corn and grain sorghum residues in beef cow forage systems". J. Anim. Sci. 46 (3): 831–840. doi:10.2527/jas1978.463831x.
  25. Klopfenstein, T.; et al. (1987). "Corn residues in beef production systems". J. Anim. Sci. 65 (4): 1139–1148. doi:10.2527/jas1987.6541139x.
  26. 1 2 3 Nemecek, T.; Poore, J. (2018-06-01). "Reducing food's environmental impacts through producers and consumers". Science. 360 (6392): 987–992. Bibcode:2018Sci...360..987P. doi: 10.1126/science.aaq0216 . ISSN   0036-8075. PMID   29853680.
  27. Merrill, Dave; Leatherby, Lauren (2018-07-31). "Here's How America Uses Its Land". Bloomberg.com. Retrieved 2019-11-11.
  28. "Agricultural land (% of land area) | Data". data.worldbank.org. Retrieved 2023-01-13.
  29. "Arable land (% of land area) | Data". data.worldbank.org. Retrieved 2023-01-13.
  30. 1 2 3 4 Carrington, Damian (20 July 2023). "Vegan diet massively cuts environmental damage, study shows". The Guardian . Retrieved 20 July 2023.
  31. "How much does eating meat affect nations' greenhouse gas emissions?". Science News. 5 May 2022. Retrieved 27 May 2022.
  32. Wang, George C. (April 9, 2017). "Go vegan, save the planet". CNN . Retrieved August 25, 2019.
  33. Liotta, Edoardo (August 23, 2019). "Feeling Sad About the Amazon Fires? Stop Eating Meat". Vice . Retrieved August 25, 2019.
  34. Steinfeld, Henning; Gerber, Pierre; Wassenaar, T. D.; Castel, Vincent (2006). Livestock's Long Shadow: Environmental Issues and Options. Food and Agriculture Organization of the United Nations. ISBN   978-92-5-105571-7 . Retrieved August 19, 2008.
  35. Margulis, Sergio (2004). Causes of Deforestation of the Brazilian Amazon (PDF). Washington D.C.: The World Bank. p. 9. ISBN   0-8213-5691-7. Archived (PDF) from the original on September 10, 2008. Retrieved September 4, 2008.{{cite book}}: |work= ignored (help)
  36. Erb KH, Lauk C, Kastner T, Mayer A, Theurl MC, Haberl H (19 April 2016). "Exploring the biophysical option space for feeding the world without deforestation". Nature Communications . 7: 11382. Bibcode:2016NatCo...711382E. doi:10.1038/ncomms11382. PMC   4838894 . PMID   27092437.
  37. Grazing with trees. A silvopastoral approach to managing and restoring drylands. Rome: FAO. 2022. doi:10.4060/cc2280en. hdl:2078.1/267328. ISBN   978-92-5-136956-2. S2CID   252636900.
  38. 1 2 Velasco-Muñoz, Juan F. (2018-04-05). "Sustainable Water Use in Agriculture: A Review of Worldwide Research". Sustainability. 10 (4): 1084. doi: 10.3390/su10041084 . hdl: 10835/7355 . ISSN   2071-1050.
  39. Konikow, L. W. 2013. Groundwater depletion in the United States (1900-2008). United States Geological Survey. Scientific Investigations Report 2013-5079. 63 pp.
  40. "HA 730-C High Plains aquifer. Ground Water Atlas of the United States. Arizona, Colorado, New Mexico, Utah". United States Geological Survey . Retrieved 2018-10-13.
  41. 1 2 USDA. 2011. USDA Agricultural Statistics 2011.
  42. USDA 2010. 2007 Census of agriculture. AC07-SS-1. Farm and ranch irrigation survey (2008). Volume 3, Special Studies. Part 1. (Issued 2009, updated 2010.) 209 pp. + appendices. Tables 1 and 28.
  43. 1 2 USDA. 2009. 2007 Census of Agriculture. United States Summary and State Data. Vol. 1. Geographic Area Series. Part 51. AC-07-A-51. 639 pp. + appendices. Table 1.
  44. 1 2 Kenny, J. F. et al. 2009. Estimated use of water in the United States in 2005, US Geological Survey Circular 1344. 52 pp.
  45. Zering, K. D., T. J. Centner, D. Meyer, G. L. Newton, J. M. Sweeten and S. Woodruff.2012. Water and land issues associated with animal agriculture: a U.S. perspective. CAST Issue Paper No. 50. Council for Agricultural Science and Technology, Ames, Iowa. 24 pp.
  46. Richter, Brian D.; Bartak, Dominique; Caldwell, Peter; Davis, Kyle Frankel; Debaere, Peter; Hoekstra, Arjen Y.; Li, Tianshu; Marston, Landon; McManamay, Ryan; Mekonnen, Mesfin M.; Ruddell, Benjamin L. (2020-03-02). "Water scarcity and fish imperilment driven by beef production". Nature Sustainability. 3 (4): 319–328. Bibcode:2020NatSu...3..319R. doi:10.1038/s41893-020-0483-z. ISSN   2398-9629. S2CID   211730442.
  47. Borunda, Alejandra (March 2, 2020). "How beef eaters in cities are draining rivers in the American West". National Geographic . Archived from the original on March 3, 2020. Retrieved April 27, 2020.
  48. 1 2 Xiao, Zhengyan; Yao, Meiqin; Tang, Xiaotong; Sun, Luxi (2019-01-01). "Identifying critical supply chains: An input-output analysis for Food-Energy-Water Nexus in China". Ecological Modelling. 392: 31–37. Bibcode:2019EcMod.392...31X. doi:10.1016/j.ecolmodel.2018.11.006. ISSN   0304-3800. S2CID   92222220.
  49. Fabrique [merken, design & interactie. "Water footprint of crop and animal products: a comparison". waterfootprint.org. Retrieved 2023-01-13.
  50. "Livestock and the Environment". Archived from the original on 2019-01-29. Retrieved 2017-06-07.
  51. the US Code of Federal Regulations 40 CFR 122.42(e)
  52. United States Environmental Protection Agency. Appendix to EPA ICR 1989.06: Supporting Statement for the Information Collection Request for NPDES and ELG Regulatory Revisions for Concentrated Animal Feeding Operations (Final Rule)
  53. the US EPA. National Enforcement Initiative: Preventing animal waste from contaminating surface and groundwater. http://www2.epa.gov/enforcement/national-enforcement-initiative-preventing-animal-waste-contaminating-surface-and-ground#progress Archived 2018-09-10 at the Wayback Machine
  54. 1 2 Zhou, Yuan; Yang, Hong; Mosler, Hans-Joachim; Abbaspour, Karim C. (2010). "Factors affecting farmers' decisions on fertilizer use: A case study for the Chaobai watershed in Northern China". Consilience (4): 80–102. ISSN   1948-3074. JSTOR   26167133.
  55. HERNÁNDEZ, DANIEL L.; VALLANO, DENA M.; ZAVALETA, ERIKA S.; TZANKOVA, ZDRAVKA; PASARI, JAE R.; WEISS, STUART; SELMANTS, PAUL C.; MOROZUMI, CORINNE (2016). "Nitrogen Pollution Is Linked to US Listed Species Declines". BioScience. 66 (3): 213–222. doi: 10.1093/biosci/biw003 . ISSN   0006-3568. JSTOR   90007566.
  56. Berger, Jamie (2022-04-01). "How Black North Carolinians pay the price for the world's cheap bacon". Vox. Retrieved 2023-11-30.
  57. Merchant, James A.; Naleway, Allison L.; Svendsen, Erik R.; Kelly, Kevin M.; Burmeister, Leon F.; Stromquist, Ann M.; Taylor, Craig D.; Thorne, Peter S.; Reynolds, Stephen J.; Sanderson, Wayne T.; Chrischilles, Elizabeth A. (2005). "Asthma and Farm Exposures in a Cohort of Rural Iowa Children". Environmental Health Perspectives. 113 (3): 350–356. doi:10.1289/ehp.7240. PMC   1253764 . PMID   15743727.
  58. Borrell, Brendan (December 3, 2018). "In California's Fertile Valley, a Bumper Crop of Air Pollution". Undark. Retrieved 2019-09-27.
  59. Viegas, S.; Faísca, V. M.; Dias, H.; Clérigo, A.; Carolino, E.; Viegas, C. (2013). "Occupational Exposure to Poultry Dust and Effects on the Respiratory System in Workers". Journal of Toxicology and Environmental Health, Part A. 76 (4–5): 230–239. Bibcode:2013JTEHA..76..230V. doi:10.1080/15287394.2013.757199. PMID   23514065. S2CID   22558834.
  60. George, Maureen; Bruzzese, Jean-Marie; Matura, Lea Ann (2017). "Climate Change Effects on Respiratory Health: Implications for Nursing". Journal of Nursing Scholarship. 49 (6): 644–652. doi: 10.1111/jnu.12330 . PMID   28806469.
  61. Radon, Katja; Schulze, Anja; Ehrenstein, Vera; Van Strien, Rob T.; Praml, Georg; Nowak, Dennis (2007). "Environmental Exposure to Confined Animal Feeding Operations and Respiratory Health of Neighboring Residents". Epidemiology. 18 (3): 300–308. doi: 10.1097/01.ede.0000259966.62137.84 . PMID   17435437. S2CID   15905956.
  62. Schinasi, Leah; Horton, Rachel Avery; Guidry, Virginia T.; Wing, Steve; Marshall, Stephen W.; Morland, Kimberly B. (2011). "Air Pollution, Lung Function, and Physical Symptoms in Communities Near Concentrated Swine Feeding Operations". Epidemiology. 22 (2): 208–215. doi:10.1097/ede.0b013e3182093c8b. PMC   5800517 . PMID   21228696.
  63. Mirabelli, M. C.; Wing, S.; Marshall, S. W.; Wilcosky, T. C. (2006). "Asthma Symptoms Among Adolescents Who Attend Public Schools That Are Located Near Confined Swine Feeding Operations". Pediatrics. 118 (1): e66–e75. doi:10.1542/peds.2005-2812. PMC   4517575 . PMID   16818539.
  64. Pavilonis, Brian T.; Sanderson, Wayne T.; Merchant, James A. (2013). "Relative exposure to swine animal feeding operations and childhood asthma prevalence in an agricultural cohort". Environmental Research. 122: 74–80. Bibcode:2013ER....122...74P. doi:10.1016/j.envres.2012.12.008. PMC   3980580 . PMID   23332647.
  65. Müller-Suur, C.; Larsson, K.; Malmberg, P.; Larsson, P.H. (1997). "Increased number of activated lymphocytes in human lung following swine dust inhalation". European Respiratory Journal. 10 (2): 376–380. doi: 10.1183/09031936.97.10020376 . PMID   9042635.
  66. Carrie, Hribar (2010). "Understanding Concentrated Animal Feeding Operations and Their Impact on Communities" (PDF). 2010 National Association of Local Boards of Health via Centres for Disease Control and Prevention.
  67. Areal, Ashtyn Tracey; Zhao, Qi; Wigmann, Claudia; Schneider, Alexandra; Schikowski, Tamara (2022-03-10). "The effect of air pollution when modified by temperature on respiratory health outcomes: A systematic review and meta-analysis". Science of the Total Environment. 811: 152336. Bibcode:2022ScTEn.811o2336A. doi:10.1016/j.scitotenv.2021.152336. ISSN   0048-9697. PMID   34914983. S2CID   245204902.
  68. Cooke, Christina (2017-05-09). "NC GOP Protects Factory Farms' Right to Pollute". Civil Eats. Retrieved 2023-11-30.
  69. Röös, Elin; Sundberg, Cecilia; Tidåker, Pernilla; Strid, Ingrid; Hansson, Per-Anders (2013-01-01). "Can carbon footprint serve as an indicator of the environmental impact of meat production?". Ecological Indicators. 24: 573–581. Bibcode:2013EcInd..24..573R. doi:10.1016/j.ecolind.2012.08.004.
  70. Capper, J. L. (2011). "The environmental impact of beef production in the United States: 1977 compared with 2007". J. Anim. Sci. 89 (12): 4249–4261. doi: 10.2527/jas.2010-3784 . PMID   21803973.
  71. Erneubare Energien in Deutschland - Rückblick und Stand des Innovationsgeschehens. Bundesministerium fűr Umwelt, Naturschutz u. Reaktorsicherheit. http://www.bmu.de/files/pdfs/allgemin/application/pdf/ibee_gesamt_bf.pdf%5B%5D
  72. Biogas from manure and waste products - Swedish case studies. SBGF; SGC; Gasföreningen. 119 pp. http://www.iea-biogas.net/_download/public-task37/public-member/Swedish_report_08.pdf%5B%5D
  73. "U.S. Anaerobic Digester" (PDF). Agf.gov.bc.ca. 2014-06-02. Retrieved 2015-03-30.
  74. NRCS. 2007. An analysis of energy production costs from anaerobic digestion systems on U.S. livestock production facilities. US Natural Resources Conservation Service. Tech. Note 1. 33 pp.
  75. Ramirez, Jerome; McCabe, Bernadette; Jensen, Paul D.; Speight, Robert; Harrison, Mark; van den Berg, Lisa; O'Hara, Ian (2021). "Wastes to profit: a circular economy approach to value-addition in livestock industries". Animal Production Science. 61 (6): 541. doi: 10.1071/AN20400 . S2CID   233881148.
  76. Kerr R.B., Hasegawa T., Lasco R., Bhatt I., Deryng D., Farrell A., Gurney-Smith H., Ju H., Lluch-Cota S., Meza F., Nelson G., Neufeldt H., Thornton P., 2022: Chapter 5: Food, Fibre and Other Ecosystem Products. In Climate Change 2022: Impacts, Adaptation and Vulnerability [H.-O. Pörtner, D.C. Roberts, M. Tignor, E.S. Poloczanska, K. Mintenbeck, A. Alegría, M. Craig, S. Langsdorf, S. Löschke,V. Möller, A. Okem, B. Rama (eds.)]. Cambridge University Press, Cambridge, United Kingdom and New York, NY, US, pp. 1457–1579 |doi=10.1017/9781009325844.012
  77. Ellen Phiddian (5 April 2022). "Explainer: IPCC Scenarios". Cosmos . Retrieved 12 June 2023.
  78. Roth, Sabrina K.; Hader, John D.; Domercq, Prado; Sobek, Anna; MacLeod, Matthew (22 May 2023). "Scenario-based modelling of changes in chemical intake fraction in Sweden and the Baltic Sea under global change". Science of the Total Environment . 888: 2329–2340. Bibcode:2023ScTEn.888p4247R. doi: 10.1016/j.scitotenv.2023.164247 . PMID   37196966. S2CID   258751271.
  79. "just-transition-meat-sector" (PDF).
  80. Lisa O'Carroll (3 November 2021). "Ireland would need to cull up to 1.3 million cattle to reach climate targets". The Guardian . Retrieved 12 June 2023.
  81. Rasmussen, Laura Vang; Hall, Charlotte; Vansant, Emilie C.; Braber, Bowie den; Olesen, Rasmus Skov (17 September 2021). "Rethinking the approach of a global shift toward plant-based diets". One Earth. 4 (9): 1201–1204. Bibcode:2021OEart...4.1201R. doi: 10.1016/j.oneear.2021.08.018 . S2CID   239376124.
  82. Food and Agriculture Organization of the United Nations (2013) "FAO STATISTICAL YEARBOOK 2013 World Food and Agriculture". See data in Table 49.
  83. Ripple WJ, Smith P, Haberl H, Montzka SA, McAlpine C, Boucher DH (20 December 2013). "Ruminants, climate change and climate policy". Nature Climate Change. 4 (1): 2–5. Bibcode:2014NatCC...4....2R. doi:10.1038/nclimate2081.
  84. Giamouri, Elisavet; Zisis, Foivos; Mitsiopoulou, Christina; Christodoulou, Christos; Pappas, Athanasios C.; Simitzis, Panagiotis E.; Kamilaris, Charalampos; Galliou, Fenia; Manios, Thrassyvoulos; Mavrommatis, Alexandros; Tsiplakou, Eleni (2023-02-24). "Sustainable Strategies for Greenhouse Gas Emission Reduction in Small Ruminants Farming". Sustainability. 15 (5): 4118. doi: 10.3390/su15054118 . ISSN   2071-1050.
  85. Cicerone RJ, Oremland RS (December 1988). "Biogeochemical aspects of atmospheric methane". Global Biogeochemical Cycles. 2 (4): 299–327. Bibcode:1988GBioC...2..299C. doi:10.1029/GB002i004p00299. S2CID   56396847.
  86. Yavitt JB (1992). "Methane, biogeochemical cycle". Encyclopedia of Earth System Science. 3. London, England: Academic Press: 197–207.
  87. Poore, J.; Nemecek, T. (2018-06-01). "Reducing food's environmental impacts through producers and consumers". Science. 360 (6392): 987–992. Bibcode:2018Sci...360..987P. doi: 10.1126/science.aaq0216 . ISSN   1095-9203. PMID   29853680. S2CID   206664954.
  88. Gibbens, Sarah (January 16, 2019). "Eating meat has 'dire' consequences for the planet, says report". National Geographic . Archived from the original on January 17, 2019. Retrieved January 21, 2019.
  89. "How plant-based diets not only reduce our carbon footprint, but also increase carbon capture". Leiden University . Retrieved 14 February 2022.
  90. Sun, Zhongxiao; Scherer, Laura; Tukker, Arnold; Spawn-Lee, Seth A.; Bruckner, Martin; Gibbs, Holly K.; Behrens, Paul (January 2022). "Dietary change in high-income nations alone can lead to substantial double climate dividend" . Nature Food. 3 (1): 29–37. doi:10.1038/s43016-021-00431-5. ISSN   2662-1355. PMID   37118487. S2CID   245867412.
  91. Castonguay, Adam C.; Polasky, Stephen; H. Holden, Matthew; Herrero, Mario; Mason-D’Croz, Daniel; Godde, Cecile; Chang, Jinfeng; Gerber, James; Witt, G. Bradd; Game, Edward T.; A. Bryan, Brett; Wintle, Brendan; Lee, Katie; Bal, Payal; McDonald-Madden, Eve (March 2023). "Navigating sustainability trade-offs in global beef production". Nature Sustainability. 6 (3): 284–294. Bibcode:2023NatSu...6..284C. doi:10.1038/s41893-022-01017-0. ISSN   2398-9629. S2CID   255638753.
  92. "Bovine genomics project at Genome Canada". Archived from the original on 2019-08-10. Retrieved 2018-11-30.
  93. "Canada Is Using Genetics to Make Cows Less Gassy". Wired . 2017-06-09. Archived from the original on 2023-05-24.
  94. Joblin, K. N. (1999). "Ruminal acetogens and their potential to lower ruminant methane emissions". Australian Journal of Agricultural Research. 50 (8): 1307. doi:10.1071/AR99004.
  95. The use of direct-fed microbials for mitigation of ruminant methane emissions: a review
  96. Parmar, N.R.; Nirmal Kumar, J.I.; Joshi, C.G. (2015). "Exploring diet-dependent shifts in methanogen and methanotroph diversity in the rumen of Mehsani buffalo by a metagenomics approach". Frontiers in Life Science. 8 (4): 371–378. doi:10.1080/21553769.2015.1063550. S2CID   89217740.
  97. Boadi, D (2004). "Mitigation strategies to reduce enteric methane emissions from dairy cows: Update review". Can. J. Anim. Sci. 84 (3): 319–335. doi: 10.4141/a03-109 .
  98. Martin, C. et al. 2010. Methane mitigation in ruminants: from microbe to the farm scale. Animal 4 : pp 351-365.
  99. Eckard, R. J.; et al. (2010). "Options for the abatement of methane and nitrous oxide from ruminant production: A review". Livestock Science. 130 (1–3): 47–56. doi:10.1016/j.livsci.2010.02.010.
  100. Dalal, R.C.; et al. (2003). "Nitrous oxide emission from Australian agricultural lands and mitigation options: a review". Australian Journal of Soil Research . 41 (2): 165–195. doi:10.1071/sr02064. S2CID   4498983.
  101. Klein, C. A. M.; Ledgard, S. F. (2005). "Nitrous oxide emissions from New Zealand agriculture – key sources and mitigation strategies". Nutrient Cycling in Agroecosystems. 72 (1): 77–85. Bibcode:2005NCyAg..72...77D. doi:10.1007/s10705-004-7357-z. S2CID   42756018.
  102. Gerber, P. J., H. Steinfeld, B. Henderson, A. Mottet, C. Opio, J. Dijkman, A. Falcucci and G. Tempio. 2013. Tackling climate change through livestock - a global assessment of emissions and mitigation opportunities. Food and Agriculture Organization of the United Nations, Rome. 115 pp.
  103. Wang, Yue; de Boer, Imke J. M.; Persson, U. Martin; Ripoll-Bosch, Raimon; Cederberg, Christel; Gerber, Pierre J.; Smith, Pete; van Middelaar, Corina E. (2023-11-22). "Risk to rely on soil carbon sequestration to offset global ruminant emissions". Nature Communications. 14 (1): 7625. Bibcode:2023NatCo..14.7625W. doi:10.1038/s41467-023-43452-3. ISSN   2041-1723. PMC   10665458 . PMID   37993450.
  104. Fassler, Joe (2024-02-01). "Research Undermines Claims that Soil Carbon Can Offset Livestock Emissions". DeSmog. Retrieved 2024-02-02.
  105. Bilotta, G. S.; Brazier, R. E.; Haygarth, P. M. (2007). The impacts of grazing animals on the quality of soils, vegetation, and surface waters in intensively managed grasslands. Advances in Agronomy. Vol. 94. pp. 237–280. doi:10.1016/s0065-2113(06)94006-1. ISBN   9780123741073.{{cite book}}: |journal= ignored (help)
  106. Greenwood, K. L.; McKenzie, B. M. (2001). "Grazing effects on soil physical properties and the consequences for pastures: a review". Austral. J. Exp. Agr. 41 (8): 1231–1250. doi:10.1071/EA00102.
  107. Milchunas, D. G.; Lauenroth, W. KI. (1993). "Quantitative effects of grazing on vegetation and soils over a global range of environments". Ecological Monographs. 63 (4): 327–366. Bibcode:1993EcoM...63..327M. doi:10.2307/2937150. JSTOR   2937150.
  108. Olff, H.; Ritchie, M. E. (1998). "Effects of herbivores on grassland plant diversity" (PDF). Trends in Ecology and Evolution. 13 (7): 261–265. doi:10.1016/s0169-5347(98)01364-0. hdl:11370/3e3ec5d4-fa03-4490-94e3-66534b3fe62f. PMID   21238294.
  109. Environment Canada. 2013. Amended recovery strategy for the Greater Sage-Grouse (Centrocercus urophasianus urophasianus) in Canada. Species at Risk Act, Recovery Strategy Series. 57 pp.
  110. Food and Agriculture Organization of the United Nations. "The contributions of livestock species and breeds to ecosystem services" (PDF).
  111. Food and Agriculture Organization of the United Nations (2016). "The contributions of livestock species and breeds to ecosystem services" (PDF). FAO . Retrieved 2021-05-15.
  112. National Research Council. 1994. Rangeland Health. New Methods to Classify, Inventory and Monitor Rangelands. Nat. Acad. Press. 182 pp.
  113. US BLM. 2004. Proposed Revisions to Grazing Regulations for the Public Lands. FES 04-39
  114. NRCS. 2009. Summary report 2007 national resources inventory. USDA Natural Resources Conservation Service. 123 pp.
  115. De Mazancourt, C.; Loreau, M.; Abbadie, L. (1998). "Grazing optimization and nutrient cycling: when do herbivores enhance plant production?". Ecology. 79 (7): 2242–2252. doi:10.1890/0012-9658(1998)079[2242:goancw]2.0.co;2. S2CID   52234485.
  116. Garnett, Tara; Godde, Cécile (2017). "Grazed and confused?" (PDF). Food Climate Research Network. p. 64. Retrieved 11 February 2021. The non-peer-reviewed estimates from the Savory Institute are strikingly higher – and, for all the reasons discussed earlier (Section 3.4.3), unrealistic.
  117. "Table of Solutions". Project Drawdown. 2020-02-05. Retrieved 2023-07-23.
  118. Bai, Yongfei; Cotrufo, M. Francesca (2022-08-05). "Grassland soil carbon sequestration: Current understanding, challenges, and solutions". Science. 377 (6606): 603–608. Bibcode:2022Sci...377..603B. doi:10.1126/science.abo2380. ISSN   0036-8075. PMID   35926033. S2CID   251349023.
  119. Chang, Jinfeng; Ciais, Philippe; Gasser, Thomas; Smith, Pete; Herrero, Mario; Havlík, Petr; Obersteiner, Michael; Guenet, Bertrand; Goll, Daniel S.; Li, Wei; Naipal, Victoria; Peng, Shushi; Qiu, Chunjing; Tian, Hanqin; Viovy, Nicolas (2021-01-05). "Climate warming from managed grasslands cancels the cooling effect of carbon sinks in sparsely grazed and natural grasslands". Nature Communications. 12 (1): 118. Bibcode:2021NatCo..12..118C. doi:10.1038/s41467-020-20406-7. ISSN   2041-1723. PMC   7785734 . PMID   33402687.
  120. Hayek, Matthew N.; Harwatt, Helen; Ripple, William J.; Mueller, Nathaniel D. (January 2021). "The carbon opportunity cost of animal-sourced food production on land". Nature Sustainability. 4 (1): 21–24. doi:10.1038/s41893-020-00603-4. ISSN   2398-9629. S2CID   221522148.
  121. Bauer, A.; Cole, C. V.; Black, A. L. (1987). "Soil property comparisons in virgin grasslands between grazed and nongrazed management systems". Soil Sci. Soc. Am. J. 51 (1): 176–182. Bibcode:1987SSASJ..51..176B. doi:10.2136/sssaj1987.03615995005100010037x.
  122. Manley, J. T.; Schuman, G. E.; Reeder, J. D.; Hart, R. H. (1995). "Rangeland soil carbon and nitrogen responses to grazing". J. Soil Water Cons. 50: 294–298.
  123. Franzluebbers, A.J.; Stuedemann, J. A. (2010). "Surface soil changes during twelve years of pasture management in the southern Piedmont USA". Soil Sci. Soc. Am. J. 74 (6): 2131–2141. Bibcode:2010SSASJ..74.2131F. doi:10.2136/sssaj2010.0034.
  124. Kebreab, E.; Clark, K.; Wagner-Riddle, C.; France, J. (2006-06-01). "Methane and nitrous oxide emissions from Canadian animal agriculture: A review". Canadian Journal of Animal Science. 86 (2): 135–157. doi: 10.4141/A05-010 . ISSN   0008-3984.
  125. McDonald, J. M. et al. 2009. Manure use for fertilizer and for energy. Report to Congress. USDA, AP-037. 53pp.
  126. "Livestock Grazing Guidelines for Controlling Noxious weeds in the Western United States" (PDF). University of Nevada. Retrieved 24 April 2019.
  127. Food and Agriculture Organization of the United Nations. "The contributions of livestock species and breeds to ecosystem services" (PDF).
  128. Launchbaugh, K. (ed.) 2006. Targeted Grazing: a natural approach to vegetation management and landscape enhancement. American Sheep Industry. 199 pp.
  129. Damian Carrington, "Humans just 0.01% of all life but have destroyed 83% of wild mammals – study", The Guardian, 21 May 2018 (page visited on 19 August 2018).
  130. Baillie, Jonathan; Zhang, Ya-Ping (2018). "Space for nature". Science. 361 (6407): 1051. Bibcode:2018Sci...361.1051B. doi: 10.1126/science.aau1397 . PMID   30213888.
  131. 1 2 Morell, Virginia (2015). "Meat-eaters may speed worldwide species extinction, study warns". Science. doi:10.1126/science.aad1607.
  132. Woodyatt, Amy (May 26, 2020). "Human activity threatens billions of years of evolutionary history, researchers warn". CNN . Retrieved May 27, 2020.
  133. Hentschl, Moritz; Michalke, Amelie; Pieper, Maximilian; Gaugler, Tobias; Stoll-Kleemann, Susanne (2023-05-11). "Dietary change and land use change: assessing preventable climate and biodiversity damage due to meat consumption in Germany". Sustainability Science. doi: 10.1007/s11625-023-01326-z . ISSN   1862-4057.
  134. McGrath, Matt (6 May 2019). "Humans 'threaten 1m species with extinction'". BBC . Retrieved 3 July 2019. Pushing all this forward, though, are increased demands for food from a growing global population and specifically our growing appetite for meat and fish.
  135. 1 2 Watts, Jonathan (6 May 2019). "Human society under urgent threat from loss of Earth's natural life". The Guardian . Retrieved 3 July 2019. Agriculture and fishing are the primary causes of the deterioration. Food production has increased dramatically since the 1970s, which has helped feed a growing global population and generated jobs and economic growth. But this has come at a high cost. The meat industry has a particularly heavy impact. Grazing areas for cattle account for about 25% of the world's ice-free land and more than 18% of global greenhouse gas emissions.
  136. 1 2 Tackling Climate Change through Livestock. FAO. 2013. ISBN   9789251079201.
  137. Hance, Jeremy (October 20, 2015). "How humans are driving the sixth mass extinction". The Guardian . Retrieved January 10, 2017.
  138. Machovina, B.; Feeley, K. J.; Ripple, W. J. (2015). "Biodiversity conservation: The key is reducing meat consumption". Science of the Total Environment. 536: 419–431. Bibcode:2015ScTEn.536..419M. doi:10.1016/j.scitotenv.2015.07.022. PMID   26231772.
  139. "Forests". World Resources Institute. Retrieved 2020-01-24.
  140. "Tackling Global Challenges". World Resources Institute. 2018-05-04. Retrieved 2020-01-24.
  141. Sutter, John D. (December 12, 2016). "How to stop the sixth mass extinction". CNN . Retrieved January 10, 2017.
  142. Boyle, Louise (February 22, 2022). "US meat industry using 235m pounds of pesticides a year, threatening thousands of at-risk species, study finds". The Independent . Retrieved February 28, 2022.
  143. Anderson, E. W.; Scherzinger, R. J. (1975). "Improving quality of winter forage for elk by cattle grazing". J. Range MGT. 25 (2): 120–125. doi:10.2307/3897442. hdl: 10150/646985 . JSTOR   3897442. S2CID   53006161.
  144. Knowles, C. J. (1986). "Some relationships of black-tailed prairie dogs to livestock grazing". Great Basin Naturalist. 46: 198–203.
  145. Neel. L.A. 1980. Sage Grouse Response to Grazing Management in Nevada. M.Sc. Thesis. Univ. of Nevada, Reno.
  146. Jensen, C. H.; et al. (1972). "Guidelines for grazing sheep on rangelands used by big game in winter". J. Range MGT. 25 (5): 346–352. doi:10.2307/3896543. hdl: 10150/647438 . JSTOR   3896543. S2CID   81449626.
  147. Smith, M. A.; et al. (1979). "Forage selection by mule deer on winter range grazed by sheep in spring". J. Range MGT. 32 (1): 40–45. doi:10.2307/3897382. hdl: 10150/646509 . JSTOR   3897382.
  148. Strassman, B. I. (1987). "Effects of cattle grazing and haying on wildlife conservation at National Wildlife Refuges in the United States" (PDF). Environmental MGT. 11 (1): 35–44. Bibcode:1987EnMan..11...35S. doi:10.1007/bf01867177. hdl:2027.42/48162. S2CID   55282106.
  149. Holechek, J. L.; et al. (1982). "Manipulation of grazing to improve or maintain wildlife habitat". Wildlife Soc. Bull. 10: 204–210.
  150. Dirzo, Rodolfo; Ceballos, Gerardo; Ehrlich, Paul R. (2022). "Circling the drain: the extinction crisis and the future of humanity". Philosophical Transactions of the Royal Society B . 377 (1857). doi:10.1098/rstb.2021.0378. PMC   9237743 . PMID   35757873. The dramatic deforestation resulting from land conversion for agriculture and meat production could be reduced via adopting a diet that reduces meat consumption. Less meat can translate not only into less heat, but also more space for biodiversity . . . Although among many Indigenous populations, meat consumption represents a cultural tradition and a source of protein, it is the massive planetary monopoly of industrial meat production that needs to be curbed
  151. 1 2 Pena-Ortiz, Michelle (2021-07-01). "Linking aquatic biodiversity loss to animal product consumption: A review" (PDF). Freshwater and Marine Biology: 57.
  152. Belsky, A. J.; et al. (1999). "Survey of livestock influences on stream and riparian ecosystems in the western United States". J. Soil Water Cons. 54: 419–431.
  153. Agouridis, C. T.; et al. (2005). "Livestock grazing management impact on streamwater quality: a review" (PDF). Journal of the American Water Resources Association. 41 (3): 591–606. Bibcode:2005JAWRA..41..591A. doi:10.1111/j.1752-1688.2005.tb03757.x. S2CID   46525184.
  154. "Pasture, Rangeland, and Grazing Operations - Best Management Practices | Agriculture | US EPA". Epa.gov. 2006-06-28. Retrieved 2015-03-30.
  155. "Grazing management processes and strategies for riparian-wetland areas" (PDF). US Bureau of Land Management. 2006. p. 105.
  156. Williams, C. M. (July 2008). "Technologies to mitigate enviromental [sic] impact of swine production". Revista Brasileira de Zootecnia. 37 (SPE): 253–259. doi: 10.1590/S1516-35982008001300029 . ISSN   1516-3598.
  157. 1 2 Key, N. et al. 2011. Trends and developments in hog manure management, 1998-2009. USDA EIB-81. 33 pp.
  158. 1 2 Regaldo, Luciana; Gutierrez, María F.; Reno, Ulises; Fernández, Viviana; Gervasio, Susana; Repetti, María R.; Gagneten, Ana M. (2017-12-22). "Water and sediment quality assessment in the Colastiné-Corralito stream system (Santa Fe, Argentina): impact of industry and agriculture on aquatic ecosystems". Environmental Science and Pollution Research. 25 (7): 6951–6968. doi:10.1007/s11356-017-0911-4. hdl: 11336/58691 . ISSN   0944-1344. PMID   29273985. S2CID   3685205.
  159. "Ocean acidification". Journal of College Science Teaching. 41 (4): 12–13. 2012. ISSN   0047-231X. JSTOR   43748533.
  160. DONEY, SCOTT C.; BALCH, WILLIAM M.; FABRY, VICTORIA J.; FEELY, RICHARD A. (2009). "Ocean Acidification". Oceanography. 22 (4): 16–25. doi:10.5670/oceanog.2009.93. hdl: 1912/3181 . ISSN   1042-8275. JSTOR   24861020.
  161. Johnson, Ashanti; White, Natasha D. (2014). "Ocean Acidification: The Other Climate Change Issue". American Scientist. 102 (1): 60–63. doi:10.1511/2014.106.60. ISSN   0003-0996. JSTOR   43707749.
  162. "Fisheries, Food Security, and Climate Change in the Indo-Pacific Region". Sea Change: 111–121. 2014.
  163. Bousquet-Melou, Alain; Ferran, Aude; Toutain, Pierre-Louis (May 2010). "Prophylaxis & Metaphylaxis in Veterinary Antimicrobial Therapy". Conference: 5th International Conference on Antimicrobial Agents in Veterinary Medicine (AAVM)At: Tel Aviv, Israel via ResearchGate.
  164. British Veterinary Association, London (May 2019). "BVA policy position on the responsible use of antimicrobials in food producing animals" (PDF). Retrieved 22 March 2020.
  165. Massé, Daniel; Saady, Noori; Gilbert, Yan (4 April 2014). "Potential of Biological Processes to Eliminate Antibiotics in Livestock Manure: An Overview". Animals. 4 (2): 146–163. doi: 10.3390/ani4020146 . PMC   4494381 . PMID   26480034. S2CID   1312176.
  166. Sarmah, Ajit K.; Meyer, Michael T.; Boxall, Alistair B. A. (1 October 2006). "A global perspective on the use, sales, exposure pathways, occurrence, fate and effects of veterinary antibiotics (VAs) in the environment". Chemosphere. 65 (5): 725–759. Bibcode:2006Chmsp..65..725S. doi:10.1016/j.chemosphere.2006.03.026. PMID   16677683.
  167. Kumar, Kuldip; C. Gupta, Satish; Chander, Yogesh; Singh, Ashok K. (1 January 2005). "Antibiotic Use in Agriculture and Its Impact on the Terrestrial Environment". Advances in Agronomy. 87: 1–54. doi:10.1016/S0065-2113(05)87001-4. ISBN   9780120007851.
  168. Boeckel, Thomas P. Van; Glennon, Emma E.; Chen, Dora; Gilbert, Marius; Robinson, Timothy P.; Grenfell, Bryan T.; Levin, Simon A.; Bonhoeffer, Sebastian; Laxminarayan, Ramanan (29 September 2017). "Reducing antimicrobial use in food animals". Science. 357 (6358): 1350–1352. Bibcode:2017Sci...357.1350V. doi:10.1126/science.aao1495. PMC   6510296 . PMID   28963240. S2CID   206662316.
  169. ESVAC (European Medicines Agency) (October 2019). "Sales of veterinary antimicrobial agents in 31 European countries in 2017: Trends from 2010 to 2017" (PDF). Retrieved 22 March 2020.
  170. Torrella, Kenny (2023-01-08). "Big Meat just can't quit antibiotics". Vox. Retrieved 2023-01-23.
  171. Boeckel, Thomas P. Van; Pires, João; Silvester, Reshma; Zhao, Cheng; Song, Julia; Criscuolo, Nicola G.; Gilbert, Marius; Bonhoeffer, Sebastian; Laxminarayan, Ramanan (20 September 2019). "Global trends in antimicrobial resistance in animals in low- and middle-income countries" (PDF). Science. 365 (6459): eaaw1944. doi:10.1126/science.aaw1944. ISSN   0036-8075. PMID   31604207. S2CID   202699175.
  172. Van Boeckel, Thomas P.; Brower, Charles; Gilbert, Marius; Grenfell, Bryan T.; Levin, Simon A.; Robinson, Timothy P.; Teillant, Aude; Laxminarayan, Ramanan (2015). "Global trends in antimicrobial use in food animals". Proceedings of the National Academy of Sciences. 112 (18): 5649–5654. Bibcode:2015PNAS..112.5649V. doi: 10.1073/pnas.1503141112 . PMC   4426470 . PMID   25792457. S2CID   3861749.
  173. 1 2 Bush, Karen; Courvalin, Patrice; Dantas, Gautam; Davies, Julian; Eisenstein, Barry; Huovinen, Pentti; Jacoby, George A.; Kishony, Roy; Kreiswirth, Barry N.; Kutter, Elizabeth; Lerner, Stephen A.; Levy, Stuart; Lewis, Kim; Lomovskaya, Olga; Miller, Jeffrey H.; Mobashery, Shahriar; Piddock, Laura J. V.; Projan, Steven; Thomas, Christopher M.; Tomasz, Alexander; Tulkens, Paul M.; Walsh, Timothy R.; Watson, James D.; Witkowski, Jan; Witte, Wolfgang; Wright, Gerry; Yeh, Pamela; Zgurskaya, Helen I. (2 November 2011). "Tackling antibiotic resistance". Nature Reviews Microbiology. 9 (12): 894–896. doi:10.1038/nrmicro2693. PMC   4206945 . PMID   22048738. S2CID   4048235.
  174. Tang, Karen L; Caffrey, Niamh P; Nóbrega, Diego; Cork, Susan C; Ronksley, Paul C; Barkema, Herman W; Polachek, Alicia J; Ganshorn, Heather; Sharma, Nishan; Kellner, James D; Ghali, William A (November 2017). "Restricting the use of antibiotics in food-producing animals and its associations with antibiotic resistance in food-producing animals and human beings: a systematic review and meta-analysis". The Lancet Planetary Health. 1 (8): e316–e327. doi:10.1016/S2542-5196(17)30141-9. PMC   5785333 . PMID   29387833.
  175. Shallcross, Laura J.; Howard, Simon J.; Fowler, Tom; Davies, Sally C. (5 June 2015). "Tackling the threat of antimicrobial resistance: from policy to sustainable action". Philosophical Transactions of the Royal Society B: Biological Sciences. 370 (1670): 20140082. doi:10.1098/rstb.2014.0082. PMC   4424432 . PMID   25918440. S2CID   39361030.
  176. European Medicines Agency (4 September 2019). "Implementation of the new Veterinary Medicines Regulation in the EU".
  177. OECD, Paris (May 2019). "Working Party on Agricultural Policies and Markets: Antibiotic Use and Antibiotic Resistance in Food Producing Animals in China" . Retrieved 22 March 2020.
  178. US Food & Drug Administration (July 2019). "Timeline of FDA Action on Antimicrobial Resistance". Food and Drug Administration . Retrieved 22 March 2020.
  179. "WHO guidelines on use of medically important antimicrobials in food-producing animals" (PDF).
  180. European Commission, Brussels (December 2005). "Ban on antibiotics as growth promoters in animal feed enters into effect".
  181. "The Judicious Use of Medically Important Antimicrobial Drugs in Food-Producing Animals" (PDF). Guidance for Industry (#209). 2012.
  182. "Veterinary Feed Directive (VFD) Basics". AVMA. Archived from the original on 15 April 2017. Retrieved 14 March 2017.
  183. University of Nebraska, Lincoln (October 2015). "Veterinary Feed Directive Questions and Answers". UNL Beef. Retrieved 14 March 2017.
  184. Walker, Polly; Rhubart-Berg, Pamela; McKenzie, Shawn; Kelling, Kristin; Lawrence, Robert S. (June 2005). "Public health implications of meat production and consumption". Public Health Nutrition. 8 (4): 348–356. doi: 10.1079/PHN2005727 . ISSN   1475-2727. PMID   15975179. S2CID   59196.
  185. Hafez, Hafez M.; Attia, Youssef A. (2020). "Challenges to the Poultry Industry: Current Perspectives and Strategic Future After the COVID-19 Outbreak". Frontiers in Veterinary Science. 7: 516. doi: 10.3389/fvets.2020.00516 . ISSN   2297-1769. PMC   7479178 . PMID   33005639.
  186. Greger, Michael (September 2021). "Primary Pandemic Prevention". American Journal of Lifestyle Medicine. 15 (5): 498–505. doi:10.1177/15598276211008134. ISSN   1559-8276. PMC   8504329 . PMID   34646097. S2CID   235503730.
  187. Mehdi, Youcef; Létourneau-Montminy, Marie-Pierre; Gaucher, Marie-Lou; Chorfi, Younes; Suresh, Gayatri; Rouissi, Tarek; Brar, Satinder Kaur; Côté, Caroline; Ramirez, Antonio Avalos; Godbout, Stéphane (1 June 2018). "Use of antibiotics in broiler production: Global impacts and alternatives". Animal Nutrition. 4 (2): 170–178. doi:10.1016/j.aninu.2018.03.002. ISSN   2405-6545. PMC   6103476 . PMID   30140756.
  188. Rzymski, Piotr; Kulus, Magdalena; Jankowski, Maurycy; Dompe, Claudia; Bryl, Rut; Petitte, James N.; Kempisty, Bartosz; Mozdziak, Paul (January 2021). "COVID-19 Pandemic Is a Call to Search for Alternative Protein Sources as Food and Feed: A Review of Possibilities". Nutrients. 13 (1): 150. doi: 10.3390/nu13010150 . ISSN   2072-6643. PMC   7830574 . PMID   33466241.
  189. 1 2 Onwezen, M. C.; Bouwman, E. P.; Reinders, M. J.; Dagevos, H. (1 April 2021). "A systematic review on consumer acceptance of alternative proteins: Pulses, algae, insects, plant-based meat alternatives, and cultured meat". Appetite. 159: 105058. doi: 10.1016/j.appet.2020.105058 . ISSN   0195-6663. PMID   33276014. S2CID   227242500.
  190. Humpenöder, Florian; Bodirsky, Benjamin Leon; Weindl, Isabelle; Lotze-Campen, Hermann; Linder, Tomas; Popp, Alexander (May 2022). "Projected environmental benefits of replacing beef with microbial protein". Nature. 605 (7908): 90–96. Bibcode:2022Natur.605...90H. doi:10.1038/s41586-022-04629-w. ISSN   1476-4687. PMID   35508780. S2CID   248526001.
    News article: "Replacing some meat with microbial protein could help fight climate change". Science News. 5 May 2022. Retrieved 27 May 2022.
  191. "Lab-grown meat and insects 'good for planet and health'". BBC News. 25 April 2022. Retrieved 25 April 2022.
  192. Mazac, Rachel; Meinilä, Jelena; Korkalo, Liisa; Järviö, Natasha; Jalava, Mika; Tuomisto, Hanna L. (25 April 2022). "Incorporation of novel foods in European diets can reduce global warming potential, water use and land use by over 80%". Nature Food. 3 (4): 286–293. doi:10.1038/s43016-022-00489-9. hdl: 10138/348140 . PMID   37118200. S2CID   257158726 . Retrieved 25 April 2022.
  193. Leger, Dorian; Matassa, Silvio; Noor, Elad; Shepon, Alon; Milo, Ron; Bar-Even, Arren (29 June 2021). "Photovoltaic-driven microbial protein production can use land and sunlight more efficiently than conventional crops". Proceedings of the National Academy of Sciences. 118 (26): e2015025118. Bibcode:2021PNAS..11815025L. doi: 10.1073/pnas.2015025118 . ISSN   0027-8424. PMC   8255800 . PMID   34155098. S2CID   235595143.
  194. "Plant-based meat substitutes - products with future potential | Bioökonomie.de". biooekonomie.de. Retrieved 25 May 2022.
  195. Berlin, Kustrim CerimiKustrim Cerimi studied biotechnology at the Technical University in; biotechnology, is currently doing his PhD He is interested in the broad field of fungal; Artists, Has Collaborated in Various Interdisciplinary Projects with; Artists, Hybrid (28 January 2022). "Mushroom meat substitutes: A brief patent overview". On Biology. Retrieved 25 May 2022.
  196. Lange, Lene (December 2014). "The importance of fungi and mycology for addressing major global challenges*". IMA Fungus. 5 (2): 463–471. doi:10.5598/imafungus.2014.05.02.10. ISSN   2210-6340. PMC   4329327 . PMID   25734035. S2CID   13755426.
  197. Gille, Doreen; Schmid, Alexandra (February 2015). "Vitamin B12 in meat and dairy products". Nutrition Reviews. 73 (2): 106–115. doi: 10.1093/nutrit/nuu011 . ISSN   1753-4887. PMID   26024497.
  198. Weston, A. R.; Rogers, R. W.; Althen, T. G. (1 June 2002). "Review: The Role of Collagen in Meat Tenderness". The Professional Animal Scientist. 18 (2): 107–111. doi:10.15232/S1080-7446(15)31497-2. ISSN   1080-7446.
  199. Ostojic, Sergej M. (1 July 2020). "Eat less meat: Fortifying food with creatine to tackle climate change". Clinical Nutrition. 39 (7): 2320. doi:10.1016/j.clnu.2020.05.030. ISSN   0261-5614. PMID   32540181. S2CID   219701817.
  200. Mariotti, François; Gardner, Christopher D. (4 November 2019). "Dietary Protein and Amino Acids in Vegetarian Diets—A Review". Nutrients. 11 (11): 2661. doi: 10.3390/nu11112661 . ISSN   2072-6643. PMC   6893534 . PMID   31690027.
  201. Tsaban, Gal; Meir, Anat Yaskolka; Rinott, Ehud; Zelicha, Hila; Kaplan, Alon; Shalev, Aryeh; Katz, Amos; Rudich, Assaf; Tirosh, Amir; Shelef, Ilan; Youngster, Ilan; Lebovitz, Sharon; Israeli, Noa; Shabat, May; Brikner, Dov; Pupkin, Efrat; Stumvoll, Michael; Thiery, Joachim; Ceglarek, Uta; Heiker, John T.; Körner, Antje; Landgraf, Kathrin; Bergen, Martin von; Blüher, Matthias; Stampfer, Meir J.; Shai, Iris (1 July 2021). "The effect of green Mediterranean diet on cardiometabolic risk; a randomised controlled trial". Heart. 107 (13): 1054–1061. doi:10.1136/heartjnl-2020-317802. ISSN   1355-6037. PMID   33234670. S2CID   227130240.
  202. Craig, Winston John (December 2010). "Nutrition concerns and health effects of vegetarian diets". Nutrition in Clinical Practice. 25 (6): 613–620. doi:10.1177/0884533610385707. ISSN   1941-2452. PMID   21139125.
  203. Zelman, Kathleen M.; MPH; RD; LD. "The Truth Behind the Top 10 Dietary Supplements". WebMD. Retrieved 2022-06-18.
  204. Neufingerl, Nicole; Eilander, Ans (January 2022). "Nutrient Intake and Status in Adults Consuming Plant-Based Diets Compared to Meat-Eaters: A Systematic Review". Nutrients. 14 (1): 29. doi: 10.3390/nu14010029 . ISSN   2072-6643. PMC   8746448 . PMID   35010904.
  205. Boston, 677 Huntington Avenue; Ma 02115 +1495‑1000 (2012-09-18). "Vitamin K". The Nutrition Source. Retrieved 2022-06-18.{{cite web}}: CS1 maint: numeric names: authors list (link)
  206. Fadnes, Lars T.; Økland, Jan-Magnus; Haaland, Øystein A.; Johansson, Kjell Arne (8 February 2022). "Estimating impact of food choices on life expectancy: A modeling study". PLOS Medicine. 19 (2): e1003889. doi: 10.1371/journal.pmed.1003889 . ISSN   1549-1676. PMC   8824353 . PMID   35134067.
  207. "Quality of plant-based diet determines mortality risk in Chinese older adults". Nature Aging. 2 (3): 197–198. March 2022. doi:10.1038/s43587-022-00178-z. PMID   37118375. S2CID   247307240 . Retrieved 27 May 2022.
  208. Jafari, Sahar; Hezaveh, Erfan; Jalilpiran, Yahya; Jayedi, Ahmad; Wong, Alexei; Safaiyan, Abdolrasoul; Barzegar, Ali (6 May 2021). "Plant-based diets and risk of disease mortality: a systematic review and meta-analysis of cohort studies". Critical Reviews in Food Science and Nutrition. 62 (28): 7760–7772. doi:10.1080/10408398.2021.1918628. ISSN   1040-8398. PMID   33951994. S2CID   233867757.
  209. Medawar, Evelyn; Huhn, Sebastian; Villringer, Arno; Veronica Witte, A. (12 September 2019). "The effects of plant-based diets on the body and the brain: a systematic review". Translational Psychiatry. 9 (1): 226. doi:10.1038/s41398-019-0552-0. ISSN   2158-3188. PMC   6742661 . PMID   31515473.
  210. Pieper, Maximilian; Michalke, Amelie; Gaugler, Tobias (15 December 2020). "Calculation of external climate costs for food highlights inadequate pricing of animal products". Nature Communications. 11 (1): 6117. Bibcode:2020NatCo..11.6117P. doi:10.1038/s41467-020-19474-6. ISSN   2041-1723. PMC   7738510 . PMID   33323933. S2CID   229282344.
  211. "Have we reached 'peak meat'? Why one country is trying to limit its number of livestock". the Guardian. 2023-01-16. Retrieved 2023-01-16.
  212. Fuso Nerini, Francesco; Fawcett, Tina; Parag, Yael; Ekins, Paul (December 2021). "Personal carbon allowances revisited". Nature Sustainability. 4 (12): 1025–1031. Bibcode:2021NatSu...4.1025F. doi: 10.1038/s41893-021-00756-w . ISSN   2398-9629. S2CID   237101457.
  213. "A blueprint for scaling voluntary carbon markets | McKinsey". www.mckinsey.com. Retrieved 2022-06-18.
  214. "These are the UK supermarket items with the worst environmental impact". New Scientist. Retrieved 14 September 2022.
  215. Clark, Michael; Springmann, Marco; Rayner, Mike; Scarborough, Peter; Hill, Jason; Tilman, David; Macdiarmid, Jennie I.; Fanzo, Jessica; Bandy, Lauren; Harrington, Richard A. (16 August 2022). "Estimating the environmental impacts of 57,000 food products". Proceedings of the National Academy of Sciences. 119 (33): e2120584119. Bibcode:2022PNAS..11920584C. doi: 10.1073/pnas.2120584119 . ISSN   0027-8424. PMC   9388151 . PMID   35939701.
  216. 1 2 3 4 van den Berg, Saskia W.; van den Brink, Annelien C.; Wagemakers, Annemarie; den Broeder, Lea (2022-01-01). "Reducing meat consumption: The influence of life course transitions, barriers and enablers, and effective strategies according to young Dutch adults". Food Quality and Preference. 100: 104623. doi: 10.1016/j.foodqual.2022.104623 . ISSN   0950-3293. S2CID   248742133.
  217. 1 2 Collier, Elizabeth S.; Oberrauter, Lisa-Maria; Normann, Anne; Norman, Cecilia; Svensson, Marlene; Niimi, Jun; Bergman, Penny (2021-12-01). "Identifying barriers to decreasing meat consumption and increasing acceptance of meat substitutes among Swedish consumers". Appetite. 167: 105643. doi: 10.1016/j.appet.2021.105643 . ISSN   0195-6663. PMID   34389377. S2CID   236963808.
  218. "Up to 3,000 'peak polluters' given last chance to close by Dutch government". the Guardian. 2022-11-30. Retrieved 2023-01-16.
  219. Fortuna, Carolyn (2022-09-08). "Is It Time To Start Banning Ads For Meat Products?". CleanTechnica . Retrieved 2022-11-01.
  220. "Towards sustainable food consumption – SAPEA" . Retrieved 2023-06-29.
  221. 1 2 Nicole, Wendee (2017-03-01). "CAFOs and Environmental Justice: The Case of North Carolina". Environmental Health Perspectives. 121 (6): a182–a189. doi:10.1289/ehp.121-a182. ISSN   0091-6765. PMC   3672924 . PMID   23732659.
  222. Wing, S; Wolf, S (2017-03-01). "Intensive livestock operations, health, and quality of life among eastern North Carolina residents". Environmental Health Perspectives. 108 (3): 233–238. doi:10.1289/ehp.00108233. ISSN   0091-6765. PMC   1637983 . PMID   10706529.
  223. Thorne, Peter S. (2017-03-01). "Environmental Health Impacts of Concentrated Animal Feeding Operations: Anticipating Hazards—Searching for Solutions". Environmental Health Perspectives. 115 (2): 296–297. doi:10.1289/ehp.8831. ISSN   0091-6765. PMC   1817701 . PMID   17384781.
  224. Schiffman, S. S.; Miller, E. A.; Suggs, M. S.; Graham, B. G. (1995-01-01). "The effect of environmental odors emanating from commercial swine operations on the mood of nearby residents". Brain Research Bulletin. 37 (4): 369–375. doi:10.1016/0361-9230(95)00015-1. ISSN   0361-9230. PMID   7620910. S2CID   4764858.
  225. Bullers, Susan (2005). "Environmental Stressors, Perceived Control, and Health: The Case of Residents Near Large-Scale Hog Farms in Eastern North Carolina". Human Ecology. 33 (1): 1–16. doi:10.1007/s10745-005-1653-3. ISSN   0300-7839. S2CID   144569890.
  226. Horton, Rachel Avery; Wing, Steve; Marshall, Stephen W.; Brownley, Kimberly A. (2009-11-01). "Malodor as a Trigger of Stress and Negative Mood in Neighbors of Industrial Hog Operations". American Journal of Public Health. 99 (S3): S610–S615. doi:10.2105/AJPH.2008.148924. ISSN   0090-0036. PMC   2774199 . PMID   19890165.
  227. Edwards, Bob (January 2001). "Race, poverty, political capacity and the spatial distribution of swine waste in North Carolina, 1982-1997". NC Geogr.
  228. "FAO's Animal Production and Health Division: Pigs and Environment". www.fao.org. Retrieved 2017-04-23.