A low-carbon diet refers to making lifestyle choices to reduce the greenhouse gas emissions (GHGe) resulting from consumption decisions. It is estimated that the U.S. food system is responsible for at least 20 percent of U.S. greenhouse gases. This estimate may be low, as it counts only direct sources of GHGe. Indirect sources, such as demand for products from other countries, are often not counted. A low-carbon diet minimizes the emissions released from the production, packaging, processing, transport, preparation and waste of food. Major tenets of a low-carbon diet include eating less industrial meat and dairy, eating less industrially produced food in general, eating food grown locally and seasonally, eating less processed and packaged foods and reducing waste from food by proper portion size, recycling or composting.
- 7.19 for high meat-eaters (≥100 g/day)
- 5.63 for medium meat-eaters (50–99 g/day)
- 4.67 for low meat-eaters (<50 g/day)
- 3.91 for fish-eaters
- 3.81 for vegetarians
- 2.89 for vegans
Background on diet and greenhouse gas emissions
In the U.S., the food system emits four of the greenhouse gases associated with climate change: carbon dioxide, methane, nitrous oxide, and chlorofluorocarbons. The burning of fossil fuels (such as oil and gasoline) to power vehicles that transport food for long distances by air, ship, truck and rail releases carbon dioxide (CO2), the primary gas responsible for global warming. Chlorofluorocarbons (CFCs) are emitted from mechanical refrigerating and freezing mechanisms – both staples in food shipment and storage. Anthropogenic methane emission sources include agriculture (ruminants, manure management, wetland rice production), various other industries and landfills. Anthropogenic nitrous oxide sources include fertilizer, manure, crop residues and nitrogen-fixing crops production. Methane and nitrous oxide are also emitted in large amounts from natural sources. The 100-year global warming potentials of methane and nitrous oxide are recently estimated at 25 and 298 carbon dioxide equivalents, respectively.
Steinfeld et al. estimate that livestock production accounts for 18 percent of anthropogenic GHG emissions expressed as carbon dioxide equivalents. Of this amount, 34 percent is carbon dioxide emission from deforestation, principally in Central and South America, that they assigned to livestock production. However, deforestation associated with livestock production is not an issue in many regions. In the US, the land area occupied by forest increased between 1990 and 2009 and a net increase in forest land area was also reported in Canada.
Of emissions they attribute to livestock production, Steinfeld et al. estimate that globally, methane accounts for 30.2 percent. Like other greenhouse gases, methane contributes to global warming when its atmospheric concentration rises. Although methane emission from agriculture and other anthropogenic sources has contributed substantially to past warming, it is of much less significance for current and recent warming. This is because there has been relatively little increase in atmospheric methane concentration in recent years  The anomalous increase in methane concentration in 2007, discussed by Rigby et al., has since been attributed principally to anomalous methane flux from natural wetlands, mostly in the tropics, rather than to anthropogenic sources.
Livestock sources (including enteric fermentation and manure) account for about 3.1 percent of US anthropogenic GHG emissions expressed as carbon dioxide equivalents. This EPA estimate is based on methodologies agreed to by the Conference of Parties of the UNFCCC, with 100-year global warming potentials from the IPCC Second Assessment Report used in estimating GHG emissions as carbon dioxide equivalents.
A 2016 study published in Nature Climate Change concludes that climate taxes on meat and milk would simultaneously produce substantial cuts in greenhouse gas emissions and lead to healthier diets. Such taxes would need to be designed with care: exempting and subsidising some food groups, selectively compensating for income loss, and using part of the revenue for health promotion. The study analyzed surcharges of 40% on beef and 20% on milk and their effects on consumption, climate emissions, and distribution. An optimum plan would reduce emissions by 1 billion tonnes per year – similar in amount to those from aviation globally.
High-carbon and low-carbon food choices
Certain foods require more fossil fuel inputs than others, making it possible to go on a low-carbon diet and reduce one’s carbon footprint by choosing foods that need less fossil fuel and therefore emit less carbon dioxide and other greenhouse gases.
Cundiff and Harris write: "The American Dietetic Association (ADA) and Dietitians of Canada position paper officially recognizes that well-planned vegan and other vegetarian diets are appropriate for infancy and childhood. The American Academy of Pediatrics concurs." However, care is essential to ensure adequate nutrition with a vegetarian diet. For example, there is evidence of higher frequencies of non-anemic iron deficiency among vegetarians versus omnivores and lower zinc status of vegetarian children, in addition to the need for vitamin B12 supplementation with vegan diets. Statistically, a higher risk of dietary deficiency has been reported with vegan diets. Risks associated with such diets for children are discussed by Jacobs and Dwyer. Also, some studies indicate higher frequency of hypospadias among children of vegetarian mothers.
China introduced new dietary guidelines in 2016 which aim to cut meat consumption by 50% and thereby reduce greenhouse gas emissions by 1 billion tonnes by 2030.
Industrial versus pastured livestock
Beef and dairy cattle can be particularly high in their levels of greenhouse gas emissions. Feed is a significant contributor to emissions from animals raised in Confined Animal Feeding Operations (CAFOs) or factory farms, as corn or soy beans must be fertilised, irrigated, processed into animal feed, packaged and then transported to the CAFO. In 2005, CAFOs accounted for 74% of the world's poultry production, 50% of pork, 43% of beef, and 68% of eggs, according to the Worldwatch Institute. Proportions are significantly higher in developed countries, but are growing rapidly in developing countries, where demand is also growing fast. However, in the US, only about 11 percent of soybean acres and 14 percent of corn acres are irrigated; in contrast, about 66 percent of vegetable acres and 79 percent of orchard acres are irrigated. In 1995, commercial fertilizer inputs averaged 11 pounds per acre for US soybean production, versus 157 pounds per acre for US potato production. Soybean meal for livestock feed is commonly produced after extraction of soybean oil (used for cooking, food products, biodiesel, etc., so that only a fraction of processing is assignable to feed. Such examples illustrate that issues relating to irrigation, fertilization and processing for meat production should also be of concern with regard to production of other foods.
In one study, grass-fed cattle were estimated to account for 40% less greenhouse emissions than CAFO cattle However, comparative effects on emissions can vary. in a US study, lower GHG emissions were associated with feedlot-finished beef production than with beef production on pasture and hay. Similarly, a study in New Zealand concluded that environmental emissions per kilogram of beef produced can be reduced by incorporating feedlot finishing in a beef production system. Another factor to be considered is the role of a healthy pastoral ecosystem in carbon sequestration. Rotational grazing of ruminants (cattle, sheep, goats, etc.) and birds (chickens, turkeys, etc.) on untilled pasture land promotes rapid topsoil accumulation, representing a major carbon sink.
Because CAFO production is highly centralised, the transport of animals to slaughter and then to distant retail outlets is a further source of greenhouse gas emissions. However, this can be more or less compensated by reduced transport of feed, where CAFOs are located in feed-producing areas.
In livestock production, emissions are reduced by feeding human-inedible materials that might otherwise by wasted. Elferink et al. state that "Currently, 70 % of the feedstock used in the Dutch feed industry originates from the food processing industry." Among several US examples is the feeding of distillers grains remaining from biofuel production. For the marketing year 2009/2010, the amount of dried distillers grains used as livestock feed (and residual) in the US amounted to 25.0 million tonnes.
Distance traveled and method of transit
Carbon emissions from transport account for 11% of the total carbon emissions of food, of which the transportation from producer to consumer accounts for 4%. However, "food miles" are a very misleading measure; in many cases food imported from the other side of the world may have a lower carbon footprint than a locally produced equivalent, due to differences in farming methods; "local food" campaigns may be motivated by protectionism rather than genuine environmentalism.
When looking at total greenhouse gases (not just carbon dioxide), 83% of emissions come from the actual production of the food because of the methane released by livestock and the nitrous oxide due to fertilizer.
The word locavore describes a person attempting to eat a diet consisting of foods harvested from within a 100-mile radius.
Some studies have criticized the emphasis on local food, claiming that it romanticizes local production, but does not produce very much environmental benefit. Transportation accounts for a relatively small portion of overall energy consumption in food production, and locally produced food may be much more energy intensive than food produced in a better area. Additionally the emphasis on "inefficient" local producers over more efficient ones further away may be damaging.
Processing, packaging and waste
Highly processed foods such as granola bars come in individual packaging, demanding high energy inputs and resulting in packaging waste. These products contribute up to a third of total energy inputs for food consumption, as their ingredients are shipped from all over, processed, packaged, trucked to storage, then transported to retail outlets. Bottled water is another example of a highly packaged, wasteful food product. It is estimated that Americans throw away 40 million plastic water bottles every day, and bottled water is often shipped trans-continentally. Carbonated water must be chilled and kept under pressure during storage and transport so as to keep the carbon dioxide dissolved. This factor contributes greater energy usage for products shipped longer distances.
- Stukin, Stacie (30 October 2006). "The Low Carbon Diet". Time Magazine. Retrieved 21 June 2016.
- 20% of GHGe from food industry
- "'Low Carbon Diet' Aims to Take Bite Out of Global Warming". CNS News. 7 July 2008. Retrieved 25 January 2019.
- Scarborough, Peter; Appleby, Paul N.; Mizdrak, Anja; Briggs, Adam D.M.; Travis, Ruth C.; Bradbury, Kathryn E.; Key, Timothy J. (July 2014). "Dietary greenhouse gas emissions of meat-eaters, fish-eaters, vegetarians and vegans in the UK". Climatic Change. 125 (2): 179–192. doi:10.1007/s10584-014-1169-1. PMC 4372775. PMID 25834298.
- STAT saying that those four are emitted
- CFC STAT
- EPA. 2011. Inventory of U.S. greenhouse gas emissions and sinks: 1990-2009. United States Environmental Protection Agency. EPA 430-R-11-005. 459 pp.
- IPCC. 2007. Fourth Assessment Report. The Scientific Basis. Intergovernmental Panel on Climate Change. Sec. 2.10.2.
- Steinfeld, H. et al. 2006, Livestock’s Long Shadow: Environmental Issues and Options. Livestock, Environment and Development, FAO.
- US EPA. 2011. Inventory of U.S. greenhouse gas emissions and sinks: 1990-2009. United States Environmental Protection Agency. EPA 430-R-11-005. 459 pp.
- Environment Canada. 2010. National Inventory Report 1990-2008. Greenhouse Gas Sources and Sinks in Canada. Part 1. 221 pp.
- Dlugokencky, E. J.; et al. (1998). "Continuing decline in the growth rate of the atmospheric methane burden". Nature. 393 (6684): 447–450. Bibcode:1998Natur.393..447D. doi:10.1038/30934.
- Dlugokencky, E.J.; et al. (2011). "Global atmospheric methane: budget, changes and dangers". Phil. Trans. R. Soc. 369 (1943): 2058–2072. Bibcode:2011RSPTA.369.2058D. doi:10.1098/rsta.2010.0341. PMID 21502176.
- IPCC. 2007. Fourth Assessment Report. Intergovernmental Panel on Climate Change.
- Rigby, M.; et al. (2008). "Renewed growth of atmospheric methane" (PDF). Geophys. Res. Lett. 35 (22): L22805. Bibcode:2008GeoRL..3522805R. doi:10.1029/2008GL036037.
- Bousquet, P.; et al. (2011). "Source attribution of the changes in atmospheric methane for 2006-2008". Atmos. Chem. Phys. 11: 3689–3700.
- Carrington, Damian (7 November 2016). "Tax meat and dairy to cut emissions and save lives, study urges". The Guardian. London, United Kingdom. ISSN 0261-3077. Retrieved 7 November 2016.
- Springmann, Marco; Mason-D'Croz, Daniel; Robinson, Sherman; Wiebe, Keith; Godfray, H Charles J; Rayner, Mike; Scarborough, Peter (7 November 2016). "Mitigation potential and global health impacts from emissions pricing of food commodities". Nature Climate Change (1): 69. Bibcode:2017NatCC...7...69S. doi:10.1038/nclimate3155. ISSN 1758-678X.
- Stephen Clune; Enda Crossin; Karli Verghese (1 January 2017). "Systematic review of greenhouse gas emissions for different fresh food categories" (PDF). Journal of Cleaner Production. 140 (2): 766–783. doi:10.1016/j.jclepro.2016.04.082. Retrieved 28 July 2017.
- Felicity Carus UN urges global move to meat and dairy-free diet, The Guardian, 2 June 2010
- Also see "Energy and Agriculture Top Resource Panel's Priority List for Sustainable 21st Century", United Nations Environment Programme (UNEP), Brussels, 2 June 2010.
- Cundiff, David K.; Harris, William (2006). "Case report of 5 siblings: malnutrition? Rickets? DiGeorge syndrome? Developmental delay?". Nutrition Journal. 5: 1. doi:10.1186/1475-2891-5-1. PMC 1363354. PMID 16412249.
- "Position of the American Dietetic Association and Dietitians of Canada: Vegetarian diets". Journal of the American Dietetic Association. 103 (6): 748–765. 2003. doi:10.1053/jada.2003.50142. PMID 12778049.
- "Pediatric Nutrition Handbook". American Academy Of Pediatrics. Retrieved 19 May 2005.
- Mangels, A.; Messina, V. (2001). "Considerations in planning vegan diets infants". Journal of the American Dietetic Association. 101 (6): 670–677. doi:10.1016/S0002-8223(01)00169-9. PMID 11424546.
- Barr, S. I.; Rideout, C. A. (2004). "Nutritional considerations for vegetarian athletes". Nutrition. 20 (7–8): 696–703. doi:10.1016/j.nut.2004.04.015. PMID 15212753.
- Gibson, R. S. (1 May 1994). "Content and bioavailability of trace elements in vegetarian diets". The American Journal of Clinical Nutrition. 59 (5): 1223S–1232S. doi:10.1093/ajcn/59.5.1223S. ISSN 0002-9165.
- Rauma, A.-L.; Tőrrönen, R.; Hänninen, O.; Mykkänen, H. (1995). "Vitamin B12 status of long-term adherents of a strict uncooked vegan diet ("living food diet") is compromised". J. Nutr. 125: 2511–2515.
- Dwyer, J. T. (1988). "Health aspects of vegetarian diets". Am. J. Clin. Nutr. 48: 712–738. doi:10.1093/ajcn/48.3.712.
- Jacobs, C.; Dwyer, J. T. (1988). "Vegetarian children: appropriate and inappropriate diets". Am. J. Clin. Nutr. 48: 811–818. doi:10.1093/ajcn/48.3.811.
- North, K. and J. Golding. 2000. A maternal vegetarian diet in pregnancy is associated with hypospadias. BJU Int. 85: 107–113
- Akre, O.; et al. (2008). "Maternal and gestational risk factors for hypospadias". Environ. Health Perspect. 116 (8): 1071–1076. doi:10.1289/ehp.10791. PMC 2516569. PMID 18709149.
- Milman, Oliver (20 June 2016). "China's plan to cut meat consumption by 50% cheered by climate campaigners". The Guardian. Retrieved 20 June 2016.
- Danielle Nierenberg, Lisa Mastny, 2005, Worldwatch Paper #171: Happier Meals: Rethinking the Global Meat Industry, p. 11-12
- 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.
- USDA. 2009. 2007 Census of agriculture. Farm and ranch irrigation survey (2008). Volume 3. Special Studies. Part 1. AC-07-SS-1. 177 pp. + appendices.
- Anderson, M. and R. Magleby. 1997. Agricultural resources and environmental indicators, 1996-1997. USDA Ag. Handbook AH712. 356 pp.
- Soyatech: http://soyatech.com/soy_facts.htm
- USDA. 2011. Agricultural Statistics 2010. 505 pp.
- Brian Halweil and Danielle Nierenberg, 2008, Meat and Seafood: The Global Diet’s Most Costly Ingredients, in The Worldwatch Institute's State of the World 2008, p. 65
- Pelletier, N.; Pirog, R.; Rasmussen, R. (2010). "Comparative life cycle environmental impacts of three beef production strategies in the Upper Midwestern United States". Agric. Systems. 103 (6): 380–389. doi:10.1016/j.agsy.2010.03.009.
- White, T. A.; Snow, V. A.; King, W. M. (2010). "Intensification of New Zealand beef farming systems". Agric. Systems. 103: 21–36. doi:10.1016/j.agsy.2009.08.003.
- Elferink, E. V., S. Nonhebel and H. C. Moll. 2008. Feeding livestock food residue and the consequences for the environmental impact of meat. J. Cleaner Prod. 16: 1227-1233
- Hoffman, L. and A. Baker. 2010. Market issues and prospects for U.S. distillers' grains supply, use, and price relationships. USDA FDS-10k-01).
- Bijal Trevedi (11 September 2008). "What Is Your Dinner Doing to the Climate". New Scientist.
- "Food politics: Voting with your trolley". The Economist. 7 December 2006. Retrieved 23 April 2012.
- Hiroku Shimozu; Pierre Desrochers (24 October 2008). "Yes We Have No Bananas: A Critique of the 'Food Miles' Perspective". Mercatus Policy Series (8). SSRN 1315986.
- Annika Carlsson-Kanyama, Marianne Ekstrom, Helena Pipping Shanahan, "Food and life cycle energy inputs: consequences of diet and ways to increase efficiency," Ecological Economics, 2003
- Miguel Llanos, "Plastic bottles pile up as mountains of waste," (2005), MSNBC