There are many negative externalities stemming from our consumption that aren’t being paid for and are being left for future generations to deal with. Some of them are being covered by the governments and producing companies, but far from all. Hence to be able to consume with a clear conscience, an attempt should be made to calculate the residual negative externalities and pay for them individually.
The externalities here covered can be split into 3 sections - Planetary boundaries violated, human rights violated and animal welfare damaged. Calculations are related to the average UK person unless stated otherwise.
This doesn’t deal with how to do the most good, for that turn to Effective Altruism, Giving What We Can, The Life You Can Save or other organisations. This instead deals with accounting what damage each of us is responsible for and offering ways to try to fix that specifically. It is upon each person’s moral framework whether the correct thing is to offset the specific damages they are responsible for, send the same amount of help into the most effective causes, or something different. It is also upon each individual to decide whether all categories problems they should be offsetting themselves for.
This section calculates the scale of each externality accounted for and the costs of offsetting it for an average UK citizen and lists the donation choices. Where the damage is given as global values, the conversion factor to the average UK citizen is UK per capita GDP over world GDP: - unless further details on accountability are given. If unexplained, high and low estimates don’t have any further explanation and are just one half and double the most likely value.
UK citizen’s average footprint calculated from consumption is [1], world average is and linearly adjusted for UK income is . Hence we get a low, a most likely and a high estimate.
Using data from Gold Standard, the estimates for the cost of offsetting one tonne of are £7.4 (low), £11.1 (most likely) and £12.6 (high). Hence the estimated cost of offsetting is 32£/year (low), 133£/year (most likely) and 217£/year (high).
Nature based offsets Protecting rainforests, planting trees, rewilding [2]. Chosen charities are: 30% Plan Vivo, 10% Gold Standard, 20% WILD Foundation, 20% Cool Earth and 20% Rainforest Alliance. Reducing emissions Efficient cooking and heating equipment, clean energy projects, agricultural methane capture and other projects. Chosen charities are: 60% Gold Standard, 20% Founders Pledge Climate change fund, 20% Clean Air Task Force. Sustainable technology R&D Policy leadership and sustainable energy innovation. Chosen charities are: 70% Founders Pledge Climate change fund, 30% Clean Air Task Force.Not considered as it is directly caused by the climate crisis.
Nitrogen and phosphorus are introduced into ecosystems through fertilisers of which only about 40% is used by the crops and the rest runs off into rivers and ultimately the ocean. The cost of reducing consumption or cleaning up is hard to quantify. As one estimate we take the loss of profit to fertiliser producers caused by a tax imposed to limit consumption. The assumption is that the potential lost profits is the maximum fertiliser producers would spend in lobbying and hence would have to be matched by environmental groups. This is a very approximate calculation but gives us at least an order of magnitude. The global fertiliser market is worth $158B. A 10% tax increase would lead to 1.5% reduction of consumption and most of the cost is born by farmers[3]. The reduction of surplus nitrogen is twice as large as the reduction of usage[4]. The profit margins of the fertiliser industry range from 10% to 70%. Hence we get an estimate of $2.4B to reduce fertiliser use by 10%. We extrapolated nitrogen numbers across phosphorus too since it’s a rather approximate calculation. Should we expect the farmers to join the lobbying but in a less organised fashion, we can take an extreme upper estimate of $10B for a 10% reduction.
As a different estimate we can consider how much fertiliser use would be reduced with one person switching to plant based meat alternatives. The reduction of fertiliser runoff is about 70%[5]. It is likely going to be similar for cell-based meat alternatives. 36% of global arable land is used for animal feed. We are assuming constant fertilisation rate. The average meat consumption in Europe and North America is about twice as much as global average. Hence we get that one European or North American person giving up meat leads to 6.6e-11 reduction in fertiliser use. At $1 per person (see 2.4.1) that leads to $1.5B for a 10% reduction.
There are no charities specialised on reducing fertiliser use so instead ones that have it as one of their activities are chosen - 45% allocation to those. Another 45% goes to charities focusing on reducing meat consumption. The last 10% goes to ones focusing on protecting marine environments as there the damage is greatest. Most likely estimate is 5.8£/year going from the meat-alternatives calculation above. High estimate is 18.3£/year - an average of the 2 higher estimates given above. Low estimate is 2.9£/year.
We can assume that reducing land usage, fertiliser usage, meat consumption etc. will lead to a reduced freshwater use too. As a basic calculation - 92% of freshwater is in agriculture, 29% of that is in livestock production[6], switching to plant-based meat reduces the amount by 80%[5] - hence we get 5.6e-11 reduction. That gives us an estimate of $1.8B for a 10% reduction. It will likely be less due to interacting offsets.
Freshwater use can be addressed by adopting better practices in agriculture and by reducing meat consumption. The amount needed to reduce meat consumption and hence water usage is used as a high estimate since it is a part of other offsets. Estimates are 1.7£/year (low), 3.4£/year (most likely) and 6.9£/year (high).
Not considered as the ozone layer seems to be recovering.
According to Global Forest Watch [7] annual rate of loss of primary forest is
4.3MHa/year (5 year average), and overall net forest loss rate is 14.1MHa/year
(approximate 18 year average), giving annual rate of loss of secondary forest is
9.8MHa/year. The 1990-2015 average rate of loss for different types of wilderness
was [8]:
| Tropical & Subtropical Moist Broadleaf Forests | 5.07MHa/year |
| Deserts & Xeric Shrublands | 2.48MHa/year |
| Tropical & Subtropical Grasslands & Savannas | 1.63MHa/year |
| Boreal Forests/Taiga | 1.27MHa/year |
| Tundra | 898kHa/year |
| Montane Grasslands & Shrublands | 556kHa/year |
| Temperate Broadleaf & Mixed Forests | 234kHa/year |
| Temperate Coniferous Forests | 215kHa/year |
| Temperate Grasslands, Savannas & Shrublands | 166kHa/year |
| Tropical & Subtropical Dry Broadleaf Forests | 117kHa/year |
| Mediterranean Forests Woodlands & Scrub | 68kHa/year |
| Flooded Grasslands & Savannas | 59kHa/year |
| Mangroves | 20kHa/year |
| Tropical & Subtropical Coniferous Forests | 16kHa/year |
Majority of primary forest is tropical (other than that some areas of Siberian and North American taiga are untouched). Primary forest hasn’t been touched by human activity (though that usually excludes native tribes and human-caused mega-fauna extinction millennia ago, which then lead to major biome changes since) and hence cannot be replanted and must be instead protected as is. One of the major drivers of wilderness loss is turning the land into animal pastures, as the land efficiency thereof is much lower than plant farming.
Tropical primary forest loss Estimates for conservation investments needed range between £2 and £6000 per remaining and between £10000 and £2000000 per being lost. As a low value we use the cost of replanting the forest that has been lost (which doesn’t keep it as primary forest so it is unlikely that that would be enough) at 2.9£/year, as the most likely estimate we use £4800 per remaining equivalent to £350000 per lost yearly at 6.8£/year, as a high estimate we use 4x the most likely value. Charities picked are focused on protecting rain-forests but also on reducing meat consumption and hence removing the main driver of wilderness loss: 10% WILD Foundation, 30% Cool Earth, 10% Animal Charity Evaluators’ Recommended Charity Fund, 10% New Harvest, 40% Rainforest alliance. Secondary forest loss Most likely estimate is made as $1 to plant a tree and each tree taking up : 15.6£/year. Chosen charities are focused on tree planting: 90% Plan Vivo, 10% Gold Standard. Other land changes Here we mostly combat the loss of land wilderness though potentially loss of marine wilderness and changing biomes should also be included. Low estimate is £10000 per being lost: 0.9£/year, most likely estimate is at same rate as primary forests, with rate reduced to 1/10 for deserts and tundra: 6.2£/year, high value being 4x that. Chosen charities are similar philosophy as primary forests: 40% WILD Foundation, 20% Animal Charity Evaluators’ Recommended Charity Fund, 20% New Harvest, 20% Oceana.The estimated cost of protecting species is $25.1-76.1 billion annually, with at least $3.41 needed to stop species dieoff. Current spending is at about half the needed amount.[9]
Hence we use estimates of additional funding needed: $3.4 billion (low), $12.6 billion (most-likely), $38.1 billion (high). That then translates into individual offsets of 1.3£/year, 4.9£/year and 14.7£/year respectively. Chosen charities are 40% WILD foundation, 20% Rainforest Alliance and 40% Oceana.
We are unsure whether this is an area that should be offset as the negative externalities caused by particulates are most commonly local and hence already being addressed by local governments, while globally aerosols are partly offsetting the effects of climate change. Hence for now we will be omitting this issue but will reexamine it in the future.
The cost of removing plastics from the ocean once Ocean Cleanup’s system is developed is estimated at about $5 per kg which given the influx would equate to an estimate of $43B per year.
Burning plastics would produce about 2.5kg per kg of plastics[11] - hence the carbon offsetting cost would be $5.5B (based on numbers in section 2.1.1 and counting only discarded plastics) - that will often be less than the methane emissions from landfills but we’ll go with a conservative estimate. The cost of an incineration plant in Europe or US is $1000 or less per a tonne of annual capacity[12] - assuming it runs for 20 years and electricity and heat sales can account for running costs, the cost comes to $7B. Hence a conservative estimate on reducing plastic pollution through building incinerators and offsetting carbon is $12.5B.
From estimates given at various charitable projects on GlobalGiving, upcycling is estimated at $660B[13], supporting recycling and education in Nigeria at $94B[14].
Further estimates are needed - mainly for coastal waste collection, recycling and reducing plastics production.
Then the question of how much we are responsible for comes up. Options are global value distributed equally, distributed by income, or trying to estimate UK values directly. UK per capita annual plastic waste production is 76.5kg (about double the world average) of which 0.9kg is mismanaged and could end in the ocean. We also assume that an extra 2-20% waste is produced in the supply chain and produces oceanward plastic at international average rates.
It seems the most cost effective way to be getting rid of plastic is incineration and carbon offsetting but there aren’t any projects or charities to support in the space, hence those estimates are discarded. Hence we are using the the lower estimate for recycling and the estimate for ocean cleanup. Hence we get low estimate at 2.9£/year, most likely at 6.4£/year and high at 27.3£/year. Chosen charities are 70% OceanCleanup, 20% Environmental Working Group and 10% Sustainable Food Trust.
Persistent organic pollutants For most of the pollutants we will assume governments are on track to end their use soon. The problem comes with DDT, which is the only insecticide poor countries can afford to assist the fight against malaria. It is again questionable whether to account it to ourselves but since it’s a relatively small amount ($350-950M[15]) we’ll assume we should. The estimates are 0.1£/year, 0.4£/year, 0.7£/year and the charities are 50% Against Malaria Foundation and 50% Malaria Consortium. Others We won’t make an exact estimate here but will guess that the remaining chemical pollution sits on the range of $1-50B. Charities are 70% Environmental Working Group and 30% Sustainable Food Trust.To deliver the products we buy, many people working in sweatshops and plantations get a wage too low for their families to get out of extreme poverty. To calculate the amount we are directly responsible for through our consumption we can get a first degree estimate by taking how much we pay to each country for imports, how much of that money goes to people in poverty, and how much more would they need to receive to get above the 5.5$ PPP line. We calculate the per-capita missing income from the poverty headcount ratio at $1.90, $3.20 and $5.50 a day.
From that we can directly get an upper estimate by multiplying that value by each country’s population at $923B, dividing it equally by income amongst the world’s population leaves an average Brit with 360£/year, excluding countries above $15000 GDP per capita we get 302£/year. But that doesn’t link accountability to the consumer so to do that we turn to import information. First we need an estimate for how much extra should be paid to each country for each dollar of imports. We have each country’s per capita missing income so we need to calculate how many people the one dollar of imports employs. Since some higher wage people are likely separated from the industry and agriculture, as a most likely estimate we use that the bottom 90% of people are involved in producing exports, with a high estimate being 50% and a low estimate being 100% (because we use the average income of those groups to divide the dollar for imports into a number of people it employs). Hence the calculation of the extra amount that should be paid:
To get a first degree estimate we just multiply the extra rate by the amount of imports from each country. A higher degree estimate would include countries exporting to manufacturing centres and those exporting to the UK. Our guess is that it would increase the amount of imports by about 10% but shift it towards poorer countries so the extra payment might increase by about 50%. Hence we increase the estimates by 0%, 30%, 80% for each estimate respectively.
Chosen charities are focusing on healthcare, education and other ways to fight poverty. Since the goal is to give a missing income to people in poverty, ones with a high level of evidence and directly supporting people in poverty (so for example not to charities researching and advocating macroeconomic levers which could have a greater expected reward but carry more risk and don’t carry the money directly to the people it should (we’re fixing their missing income, not their government’s missing taxes)). Three offsetting choices are given - most needing people, correct country distribution and direct donations. For the first case a subset of charities recommended by Give Well, Effective Altruism, The Live You Can Save and Giving What We Can are chosen. For the second case charities specifically operating in South Africa, Bangladesh, Uzbekistan and Cambodia are added. For the third case only Village Enterprise and Give Directly are included.
|
| Correct country distribution | Most needing people | Direct |
| Malaria | 0.025338 | 0.090909 |
|
| Against Malaria Foundation | 0.033784 | 0.090909 |
|
| Deworm the World | 0.143581 | 0.090909 |
|
| Helen Keller | 0.059122 | 0.090909 |
|
| New Incentives | 0.054899 | 0.090909 |
|
| GiveDirectly | 0.016892 | 0.090909 | 0.5 |
| The END Fund | 0.025338 | 0.090909 |
|
| SCI Foundation | 0.04223 | 0.090909 |
|
| Sightsavers | 0.118243 | 0.090909 |
|
| Village | 0.016892 | 0.090909 | 0.5 |
| Seva | 0.067568 | 0.090909 |
|
| JAAGO | 0.15625 |
|
|
| UNICEF south africa | 0.15625 |
|
|
| Lola Karimova-Tillyaeva | 0.059122 |
|
|
| Cambodian Children’s Fund | 0.024493 |
|
|
The alignment of the ”Correct country distribution” isn’t perfect, compared to the ”Most needing people” it reduces the country distribution error to 43%. Default choice is given as 40-40-20% among the options above.
Here the calculation is mainly how much does it cost to reduce the world’s meat consumption by one person’s worth. ACE’s recommended charities and cell based meat research have a cost at around 1£/year per person, while plant based meat research is less efficient at about 10£/year [16]. Hence those are used as most likely and high estimates respectively, low estimate is at 0.5£/year. Charities chosen are an equal split between New Harvest (cell based meat) and ACE.
Ethical damage done to wildlife is very hard to quantify so we’ll just assume that it’s a similar amount to farm animals. Chosen charities are 30% WILD Foundation, 10% ACE’s recommended charities, 10% New Harvest, 20% Oceana and 30% Rainforest Alliance.
Below is a list of things that have come to mind as something creating a debt or direct injustice in the society but we haven’t yet been able to quantify or find offsets for. Some are also rather speculative and might not be happening.
It could be asserted that by developing capability to easily cause massive damage, a debt is being created that the society will eventually pay with interest. Hence individual accounting could also be established for those kinds of risks.
We can expect that various offsets would interact together - e.g. protecting wilderness also reduces carbon emissions, advocating the use of plant based meat helps both wilderness and emissions. This is something that should be calculated later.
We expect that the government isn’t doing enough in the areas calculated here. Specifically for planetary boundaries we use the rates at which the situation is deteriorating, so there efforts by governments are already included. For human rights violations and animal welfare damage the picture is less clear. Those might already be offset by aid spending and science grants. That doesn’t mean it’s not a problem, but it’s a problem we might not be accountable for.
[1] Dr Anne Owen, Dr Diana Ivanova, Prof John Barrett, Stephen Cornelius, Angela Francis, Shirley Matheson, Gareth Redmond-King, and Lucy Young. Carbon footprint, exploring the uk’s contribution to climate change. https://www.wwf.org.uk/sites/default/files/2020-04/FINAL-WWF-UK_Carbon_Footprint_Analysis_Report_March_2020%20%28003%29.pdf, March 2020.
[2] Joris P. G. M. Cromsigt, Mariska te Beest, Graham I. H. Kerley, Marietjie Landman, Elizabeth le Roux, and Felisa A. Smith. Trophic rewilding as a climate change mitigation strategy? Philosophical Transactions of the Royal Society B: Biological Sciences, 373(1761):20170440, 2018.
[3] Chang Gil Kim and Arthur Stoecker. Economic effects of environmental taxation on chemical fertilizers. International Association of Agricultural Economists, 2006 Annual Meeting, August 12-18, 2006, Queensland, Australia, 01 2006.
[4] Sue Scott. Environmental economics: Fertiliser taxes – implementation issues. Prepared for the Environmental Protection Agency by The Economic and Social Research Institute, 2005.
[5] The Good Food Institute. Plant-based meat for a growing world. https://gfi.org/images/uploads/2019/08/GFI-Plant-Based-Meat-Fact-Sheet_Environmental-Comparison.pdf?utm_source=blog&utm_medium=website&utm_campaign=pb-meat-sustainability.pdf, 2019.
[6] P.W. Gerbens-Leenes, M.M. Mekonnen, and A.Y. Hoekstra. The water footprint of poultry, pork and beef: A comparative study in different countries and production systems. Water Resources and Industry, 1-2:25–36, 2013. Water Footprint Assessment (WFA) for better water governance and sustainable development.
[7] Global Forest Watch. Global deforestation rates & statistics by country: Gfw. https://www.globalforestwatch.org/dashboards/global/.
[8] James E.M. Watson, Danielle F. Shanahan, Moreno Di Marco, James Allan, William F. Laurance, Eric W. Sanderson, Brendan Mackey, and Oscar Venter. Catastrophic declines in wilderness areas undermine global environment targets. Current Biology, 26(21):2929–2934, 2016.
[9] Donal P. McCarthy, Paul F. Donald, Jörn P. W. Scharlemann, Graeme M. Buchanan, Andrew Balmford, Jonathan M. H. Green, Leon A. Bennun, Neil D. Burgess, Lincoln D. C. Fishpool, Stephen T. Garnett, David L. Leonard, Richard F. Maloney, Paul Morling, H. Martin Schaefer, Andy Symes, David A. Wiedenfeld, and Stuart H. M. Butchart. Financial costs of meeting global biodiversity conservation targets: Current spending and unmet needs. Science, 338(6109):946–949, 2012.
[10] Hannah Ritchie and Max Roser. Plastic pollution. Our World in Data, https://ourworldindata.org/plastic-pollution, September 2018.
[11] Ola Eriksson and Göran Finnveden. Plastic waste as a fuel – co2-neutral or not? Energy & Environmental Science, 2:907–914, 08 2009.
[12] Waste to Energy International. Cost of incineration plant. https://wteinternational.com/cost-of-incineration-plant/.
[13] GlobalGiving. Help us recycle 5,250 pounds of plastic wastes. https://www.globalgiving.org/projects/eco-stores-guatemala/.
[14] GlobalGiving. Support recyclespay for 1000 children in lagos. https://www.globalgiving.org/projects/support-recyclespay-for-1000-children-in-lagos/.
[15] Amir Attaran. International Donor Support for Phasing Out POPs: Recommendations for Poor Countries at INC-5. CID Working Papers 67A, Center for International Development at Harvard University, May 2001.
[16] Stijn Bruers. The extreme cost-effectiveness of cell-based meat r&d. https://stijnbruers.wordpress.com/2020/08/10/the-extreme-cost-effectiveness-of-cell-based-meat-rd/.