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Greenhouse Gas Removal – Summary

It is widely understood that greenhouse gas removal is new and needs research. This is valid for many forms of removal, especially non-CO2 strategies and processes but, there are three, 100-year old processes to remove carbon dioxide (CO2) that are widespread in industry with components that are even more widespread with known scaling factors. The Intergovernmental Panel on Climate Change (IPCC) tells us we need to remove up to 1,250 gigatons of CO2 by the end of the century to achieve a 1.5 degree C above normal warming target. This of course, is not climate restoration to avoid tipping responses by mid-century. The good news is that it is likely that significantly less than 1,250 gigatons of CO2 will need to be removed to restore our climate because a large portion of the removal required by the end of the century is natural feedback emissions from Earth systems warmed beyond their evolutionary boundaries. If we significantly shorten the amount of time our climate is beyond the evolutionary boundaries of our Earth systems, far fewer feedback emissions will occur. This still leaves non-CO2 removal that accounts for about a third of all warming. These strategies are discussed elsewhere.

Atmospheric CO2 removal is very expensive and further research is required to develop the technology.
Reality: Three, shovel ready processes are over 100-years old, are widespread in industry, their components are even more widespread and with known scaling factors, and with costs that industry has been absorbing without detriment, or profiting from for over 100-years. These processes are fundamental to beer and refrigeration (cryoseparation); submarine safety, baking soda and cement production (lime-potash process), and vitamins and bats (amines).

Myth: There are great risks of underground injection of CO2 leaking to the Earth’s surface which is compounded because it will be at great injection pressures forever.
Reality: There are four mechanisms that stabilize CO2 injected into geology that rapidly eliminate pressure and bind CO2 in the geology permanently, eliminating risk of leakage.
Myth: The quantities of removal required are just too large as the amount of removal required is one-million times that amount we are removing today.
Reality: There has been no incentive, rule or law to remove carbon dioxide from our atmosphere making this argument moot. Our engineers create processes to do hundreds of billions of things every year for Earth’s population of eight billion souls.

Our challenge is that we have only a limited amount of time before mid-century to cool (restore) our climate from today, to below 1 degree C warming above normal, so as to avoid tipping responses. Because the task is so large, there is risk that atmospheric removals alone might not be up to the task and therefor engineered cooling solutions are required. This does not mean that engineered cooling is the priority. All three aspects of the Climate Triad must be implemented simultaneously to avoid the untenable risks of irreversible tipping responses. To ensure we do not fail, emergency response is now required. Implementing engineered cooling solutions as an emergency response is mandatory, but we also must use emergency response strategy to implement the three, shovel-ready removal processes to enhance the probability that we will not fail to restore our climate by mid-century. Because natural systems removal is degraded, and will only degrade further and likely nonlinearly until we achieve restoration, and removal solutions other than the three existing 100-year old processes must be developed further to be shovel ready, we have to use these three tools at hand to address an emergency climate response. Once the emergency response pathway is underway, then we address other strategies to ensure the emergency does not recur as in any emergency response in any emergency. Read more about how our engineers will restore our climate in the details of this Greenhouse Gas Removal section.

Learn about the three 100-year old atmospheric CO2 removal processes widespread in industry in this History of Carbon Dioxide Removal. The History of Carbon Dioxide Removal Gigapeople, Gigachickens and Gigashoes is a white paper that shows why our giga task of engineered atmospheric removal solutions will be nothing different than life on Earth every day. Our Giga Culture See more myths and realities on carbon dioxide removal from the atmosphere, and about secure permanent underground storage, in this informational document from the U.S. Department of Energy. Mature CO2 Injection Industry Underground CO2 Injection has been a major part of our world’s industry since the mid-twentieth century. See this presentation by the University of Texas’ engineering geology program to understand the widespread technology, regulations and safety record of this industry. CO2 Injection Presentation History, Regs, Safety and Monitoring

Trust Our Engineers To Keep Us Safe

Greenhouse Gas Removal Details

This section includes two parts: Emergency Response and Restoration Actions. Emergency response is required to ensure we do not incur untenable futures because of degradation-caused climate tipping responses that are now active. Restoration actions are required to finish the job of emergency response, where in an emergency, any emergency, the tools at hand are used to save lives and property, then additional actions are taken to ensure the emergency does not recur.It appears likely that natural systems will play a large role in CDR, especially with the very large capacity of our oceans to change our climate. But the first tenant of emergency response is to implement immediate actions with the tools at hand. We do not yet have the knowledge or mature processes/strategies to utilize natural systems as significant CDR resources. This time when we have this knowledge will likely come, and it is quite plausible that natural systems can assume the heavy lifting of CDR at some point in the future.  To ensure we are doing everything possible to address the climate emergency however, we need to implement shovel-ready solutions in the form of industrial atmospheric removal processes widespread in industry for 100 years, with individual components of these processes even more widespread.

EMERGENCY RESPONSE

The air capture emergency response revolves around three, 100-year old processes that are widespread in industry. Air capture of carbon dioxide is needed so that we do not have to use emergency direct cooling processes indefinitely, and because direct cooling cannot stop ocean acidification. There are three major industrial processes that were developed a hundred years or more ago, that can meet these needs. These processes are shovel ready for emergency response. All that needs done is for our engineers to scale them to the gigasize – no further development research is required. Once an appropriate giga-infrastructure implementation is underway, then we can turn to new atmospheric removal process that need more study, so that we can create a more efficient climate restoration.

Three mature industrial CDR processes have been in use for about a hundred years: recyclable lime/potash, amines, and cryoseparation. Many new processes to remove CO2 and other greenhouse gases from our atmosphere have been discovered since, or are a part of the wide push to seek market share in the coming CDR industrialization of our world. These three mature processes are ready to use with almost all of their process components already widespread in industry. This allows the first principle of emergency action to be implemented, where any emergency requires we use the tools at hand to save lives.
(see a History of Carbon Dioxide Removal for more information.)

RESTORATION ACTIONS

We cannot use direct cooling engineered solutions forever. The risks are too high, increased greenhouse gases in the atmosphere reduce direct cooling efficiency, and our biggest and most important resource, our oceans, do not de-acidify with most direct cooling solutions. Future emissions eliminations with net zero helps a small amount but primarily, carbon dioxide removal (CDR) that is far in excess of emissions reductions is required. These processes are also known as negative emissions. There are two forms of CDR, natural and industrial.

NATURAL CARBON DIOXIDE REMOVAL

Natural CDR is things like our forest, soils, permafrost, wetlands, mangroves, oceans, or different agricultural techniques. The National Academies of Sciences (NAS) and Intergovernmental Panel on Climate Change (IPCC) limit global natural systems sequestration to 5.5 Gt annually fully enhanced and completely healthy, because of sustainability and very importantly, because of equity.

Natural Systems Carbon Dioxide Removal (CDR) Compromised – Permanence

The National Academies of Sciences (NAS) and IPCC limit global natural systems  sequestration to 5.5 Gt annually is significantly lower than others’ because it takes into consideration sustainability and equity issues. Numerous studies show how much greater sequestration is plausible with natural systems but plausibility is not feasibility. Paul Hawken’s Drawdown Project is another example of great promise. Though Hawken’s strategies are certainly plausible, permanence of natural sequestration is compromised because of warming-caused degradation. This compromise will only get worse until that time that we cool our climate’s temperature back to within the evolutionary boundaries of our natural systems so they can self-restore. This concept of compromised sequestration permanence has been demonstrated in academic literature as being ongoing and intensifying. Current natural systems science that tells us natural systems can do a large part of CDR do not incorporate the latest warming degradation science. Some natural systems will certainly remain sequestration resources, but many if not most will not and cannot be relied upon to ensure we do not pass the point of no return of already activated tipping collapses.

Update: Critical work on natural systems sequestration shows they have turned the corner to decline across the globe. This work (Curran and Curran 2025) looked at the response of the Keeling Curve of atmospheric CO2 concentration at Mauna Loa, and how the curve’s cold-season decrease has changed over time, where the cold season decrease is relative to Earth’s natural systems carbon sequestration. What they found was that net, our Earth systems’ carbon sequestration is in decline. What this means is that, if our Earth systems were sequestering greenhouse gases at the same rate they did in the 1960s, the annual atmospheric growth rate would have been 1.9 ppm CO2. Instead, the annual growth rate is 2.5 ppm CO2, a 32 percent decline, and this is the 2010 to 2020 average. In 2023 and 2024, the atmospheric growth rate jumped markedly from previous data at about 3.5 ppm CO2 growth per year, according to the Mauna Loa CO2 records  in Hawai’i. This is a further 40 percent decline in just two years. Carbon dioxide removal by natural systems has been increasing since emissions began, as an effect of greater a greater concentration of CO2 in the atmosphere, and partly because of the CO2 fertilization effect. Natural soil nutrients may now be limiting the CO2 fertilization effect, but most importantly, drought, insects, disease, permafrost thaw, declining ocean absorption, and wildfire are taking their toll and reducing the sequestration capacity of Earth systems. (End Update)

Case Study – West Coast’s Carbon Offset Buffer Burned Already

Permanence is an immense challenge of natural systems sequestration in a climate that is warmer than the evolution of the Earth systems doing the sequestration. As an example, nearly the entire buffer pool for the California carbon credit program has now burned, mostly in 2020 and 2021, a buffer that was supposed to protect the forest carbon credits from fire, insects and disease through 2100. The lightning-caused Lionshead Fire in Oregon in 2020 is one example of many that alone, based on conservative estimates, burned four percent of the buffer pool. Western US fires have recently begun burning much more severely, compromising much more forest area, with an 800 percent increase in high severity fire from 1982 to 2017, where 97 percent of area burned in the 20 years of the study has been high severity fires, with mortality of 95 percent in high severity fires. The result of the California fires in just 2022 are that these fires emitted two and half times more carbon than was reduced by all of California’s emissions reductions actions since they began.

Extreme Fire, Forest Regeneration Failure and Forest Emissions, Not Sequestration

Forest die-off from climate change effects has been observed across the globe, with the results of warming feedbacks  through net forest emissions and reduction of the size of the global forest carbon sink. Extreme fire (≥99.99th percentile) doubled globally, increased 11.1 times in temperate coniferous forests, and 7.3 times in the boreal/tiaga from 2003 to 2023. Drought mortality in forests  has doubled to quadrupled across the globe, where a doubling of forest mortality halves carbon storage. Forest regeneration failure after wildfire has doubled, with half of the remaining forests’ regeneration occuring at only half of the 20th century rate. Management of forest with prescribed burning creates forests that emit greenhouse gases instead of sequestering them because of an additional warming-related feedbacks where more sun hists the former forest floor, increasing soils evaporation and forest floor temperature that limits forest regrowth. These behaviors also broodily represent long-term averages because of large natural variability. This means that it is likely that current responses are double or more the long-term averages. In addition, since these studies were completed, warming has not only continued, but it has accelerated at a pace greater than anything in the record. Finally, enhancing  –or even conserving– most of these forests is not possible until their evolutionary boundary conditions are restored. These responses to warming effects create a natural world that is not only not sequestering, but it is on average a net emitter and not a candidate for CDR.

INDUSTRIAL CARBON DIOXIDE REMOVAL (CDR), DIRECT AIR CAPTURE (DAC), CARBON CAPTURE AND SEQUESTRATION (CCS)

This section comes in two parts: Industrial carbon dioxide removal (air capture or DAC), and carbon capture and sequestration (CCS) from energy generation and industrial processes.

Introduction – Why does IPCC and much academic literature say DAC is too expensive and cannot reach quantities needed?

There are many more reasons than the five listed below that describe why it is that our climate culture wrongly tells us that air capture is infeasible. They come from credible sources and appear to be valid, but “valid” in many cases may not be “valuable.”

Scenario bias… The scenario bias is one reason and it is a big one. Our climate policy is driven almost exclusively by reviews of the Intergovernmental Panel on Climate Change (IPCC). IPCC’s summaries of scientific findings are limited to those findings that follow IPCC’s scenarios. Of the 3,131 scenarios in IPCC’s database of their current report series, they only reviewed 1,202 findings because the rest did not meet their scenario criteria. One of these criteria assume that CDR is only used for cooling back to 1.5 or 2 degrees C warming after temporary overshoot the warming target while we are reducing emissions, and that CDR is used to compensate for net zero emissions for economic sectors that cannot reduce emissions, like industry that requires flame energy for oxidation reactions. IPCC evaluates zero scenarios for climate restoration, or that allow continued emissions with strategies to limit warming or restore our climate using only CDR and or engineered cooling solutions. IPCC reviews are also significantly understated because feedback scenarios in modeling are poorly represented or absent, and the vast majority of IPCC’s summaries are based on modeling outcomes.

Scenario bias – the Moon Shot… Another scenario bias can be labelled the Moon Shot Bias with an argument that, we only remove 10,000 tons of CO2 from air every year and we need to remove 1,000 Gigatons which is 100 million times more and this is all simply infeasible. The same argument was made about human’s travelling to the moon before humans’ travelled to the moon, about electricity, the internet, telephones, transiters, human sewage pollution treatment, and any number of the things we do billions of times a year in our advanced civilization of eight-billion souls. Occidental chemicals alone has six air capture hubs in-design, with the first schedules to begin operations in 2025, with a total capacity of 6 gigatons of CO2. In total, Oxy has 100, 1 million ton per year units committed under the IRS 45Q removal incentive.

Cost bias… this is another scenario bias where academic findings are the product of scenarios and things not defined as a part of the scenario(s) being studied are not represented by the findings of the study. The primary example is Keith 2018’s findings of costs of air capture with the lime-potash process using $0.03 kWh natural gas energy. If renewable energy with a cost of $0.01 kwh is interjected into Keith’s scenarios instead of his $0.03 kWh natural gas energy, costs are far lower, but the media, IPCC and even other scientists findings do not acknowledge the opportunity of any other scenarios and blinding regurgitate the scenario biased findings leading to a false impression of the lower limits of costs of air capture. (See more on Keith 2018 here.)

Moral Hazard… Many view any solution that does not eliminate future emissions as being morally wrong because climate pollution is bad and we have to stop emitting it. This is an upside down argument that does not consider that our advanced human culture almost never eliminates pollution, but we do treat it responsible because the thing that caused the pollution is needed or demanded by our culture. (See more about the Moral Hazard here.)

Nascent technologies that need more research…  Ever present in the DAC disbeliever culture is the concept that air capture technologies are new and not yet up to the task because more research is needed. The reality is that three major industrial processes that are widespread in industry have been in constant use for over 100 years. What is needed is not more research, but for our engineers to scale these processes like they scale countless things to the hundreds of billion units ever year for our advanced civilization of eight billion souls. (See more on giga scaling here.)

HOW OUR TRUSTWORTHY ENGINEERS WILL RESTORE OUR CLIMATE WITH INDUSTRIAL CARBON DIOXIDE REMOVAL (CDR) – DIRECT AIR CAPTURE (DAC)  

Industrial CDR strategies and their components have been in use as a major part of our world’s industrial complex for about a hundred years, with a capacity that is only limited by humanity’s motivation.

The three mature industrial CDR processes are: recyclable lime/potash, amines, and cryoseparation. Many new processes to remove CO2 and other greenhouse gases from our atmosphere have been discovered since, or are a part of the wide push to seek market share in the coming CDR industrialization of our world. These three mature processes are ready to use with almost all of their process components already widespread in industry. This allows the first principle of emergency action to be implemented, where any emergency requires the tools at hand be used to save lives.

Over 200, CO2 capture units are committed under IRS 45Q for completion by 2035. This is an excellent start on industrialization of a climate restoration infrastructure that can finish the job that direct cooling engineered solutions begins. Most of these units use the lime-potash process.

THE THREE, MATURE DAC PROCESSES

Cryoseparation and Beer

Nobel Prize nominee Carl von Linde was the first to remove carbon dioxide from air in a meaningful way. His technology was developed from his high pressure refrigeration discovery that itself was first used in the 1870s to help the brewing industry overcome limitations on summer season brewing and beer storage that was plagued by warm-season bacterial contamination. Literally, brewing beer in the warm season during the 19th century was banned in Bavaria because of this problem. By 1890 Linde had sold 747 of his “ice machines.” In 1892 Guinness contracted with Linde to build a CO2 liquefaction plant to sell excess CO2 from fermentation as a feedstock in the newly industrialized world. This set in motion the ultra-cold, ultra-high pressure refrigeration technology that Linde later used in cryoseparation to distill the components of air into usable products that included, oxygen, nitrogen, carbon dioxide and argon. The cryoseparation technology first supercools and super compresses air to a liquid, then evaporates the liquid in a tall column where the temperature rises upwards in the column, condensing individual components of air as the temperature warms moving upward in the column, much like water vapor condenses in clouds.

Lime-Potash Process for Removing Carbon Dioxide From Air – Submarines, Baking Soda and Cement

The recyclable lime-potash process has been used in various forms to remove CO2 from air since the late 18th Century. It involves two parts – capture with potash and release using lime in the baking soda production process where this baking soda process is part of the process of making cement out of limestone. These two processes have been ubiquitous in industry since the mid- and late-1800s. Sodium bicarbonate (baking soda) has been used for thousands of years as a natural mineral deposited from hot springs among other places. French chemist, Nicolas Leblanc discovered the process to make baking soda (known as soda ash too) in 1791. In the late 18th century, soda ash was first used as a leavening agent in baking by John Dwight and Austin Church, in New York. Its many other uses include: as an animal feed additive, as a bonding agent in dying, as a purifier and catalyst in the plastic industry, in the manufacture of rubber, as a softener in the food industry, as odor control in wastewater treatment, it is widespread in pollution treatment of flue gases (sulfur and nitrogen oxides) using the same chemistry as wastewater odor control, and it is also widespread in the pharmaceutical industry. Potassium carbonate (potash) was first identified in 1742 by Antonio Campanella. It is made by the absorbent reaction with carbon dioxide. Together these things defines the atmospheric carbon capture reaction used in the lime-potash process that kept our submarine sailors safe from carbon dioxide poisoning in World War II.

Vitamines (Note the Spelling) and Amig

Amines are likely going to be the Go to for air capture of CO2 as research into use of this very large chemical family that is extremely important to industry. Trillions of dollars of revenue are at stake and amines are more efficient than the lime/potash and cryosperaration processes. In 1930, Robert Bottoms was awarded a patent for removing CO2 from air with amines. The discovery of amines was first published in 1911 by Kazimierz Funk. Funk was inspired by Christiaan Eijkman work that showed eating brown rice reduced vulnerability to beri-beri, compared to those who at normal milled rice. (Beri-beri is a vitamin B deficiency that causes nerve and heart inflammation.) Funk was able to isolate the substance and because it contained an amine group he called it “vitamine.” It was later to be known as vitamin B3 (niacin),  and described it as “anti-beri-beri-factor”. Amines have gone on to become one of the most important chemical groups in all of industry with processes that include: dyes, nylon, medicines, cooling systems, surfactants, cosmetics, agrochemicals, corrosion inhibitor, machining fluids, powder coatings, polyurethane, and epoxy coatings. Amines are a $32 billion industry in 2023.

The Haber-Bosch Process (Amines) and Bat Guano in World War II

The Haber-Bosch process was a most important piece of chemistry developed just before WWI that allowed nitrogen production for use in explosives and fertilizers, with a key part of the process being the CO2 removal. It was a German invention because the Allies controlled all the bat guano deposits in caves that were the nitrogen source for fertilizers and explosives manufacturing. CO2 is a byproduct of the process produced as waste that must be removed, which is fundamental to the CO2 air capture process. The Haber-Bosch process is responsible for almost all fertilizers on Earth, one of the largest industries on the planet.

Costs of Air Capture CO2

Here is another of the big misinterpretations of science in a mandatory climate restoration world. Not only are air capture CO2 processes widespread and mature, but their costs are nothing like what is suggested in academic literature. Why is this? Academic literature is scenario driven. If the proper scenario criteria are not evaluated, results are not as meaningful as they could be, or simply do not apply.

Case Study – Cost of Industrial CDR, Carbon Engineering (Keith 2018)

Reported excessive costs of industrial CDR are an artifact of science that does not fully consider alternatives; of errors in very credible publishing, of lack of publishing from players as their secrets are worth trillions of dollars in incentives, and from poor interpretation of academic literature by both popular journalism and scientific publications. The Carbon Engineering (Keith 2018) scenario criteria result in a range of $94 to $232 per ton of CO2 captured that reflects the low and high energy costs of natural gas in 2018, or $0.03 kWh and $0.05 kWh, and where 87 percent of process costs are energy related, and costs include upstream emissions and the carbon penalty to remove the carbon emitted from burning the natural gas to create the energy to run the process. Realistically, the lowest cost of of energy will be in these processes. But Keith used $0.03 natural gas energy and the lowest cost today is wind and solar energy at $0.01kWh and not carbon penalty for burning natural gas. so to use a different scenario for Keith’s work, with the latest wind and solar costs , and considering that Keith 2018 allows that 40 percent of process costs can be as electricity, and the rest requires flame energy for oxidation, with $0.01 kWh renewable site-built energy, this reduces total costs to $60 ton. An interesting likelihood with industry is that to energy producers who will likely be doing the lion’s share of atmospheric removal, the costs of natural gas are almost free. this would make using 100% natural gas the go to, as upscaling their removal processes to remove the extra CO2 generated from natural gas powering the process is little money compared to the profits plausible with “almost free” natural gas to the producer.

Utilization of CO2 from Carbon Dioxide Removal (CDR)

It matters not how feasible, plausible or impossible atmospheric carbon capture is perceived to be. If we do not restore our atmosphere to within the boundaries of our Earth systems, untenable futures result. The two big challenges with utilization are quantity and time. Generally, because time is of the essence, utilization cannot create atmospheric removals anywhere close to the quantitates need to reduce Earth’s temperature to a restoration target less than 1 degrees C warming. Nevertheless, utilization is important and has a capacity to help with restoration. One of the most exciting of utilization strategies and or processes is contemporary carbon limestone aggregates made from air capture CO2. One of the leaders in this synthetic limestone production is Blue Planet Aggregates in California where they have synthesized limestone aggregates that are carbon negative for use in airport construction and many other projects, sequestering a net of 500 pounds per ton of concrete, upstream emissions included. Low carbon concrete products that are proliferating in the market today only reduce the carbon footprint of concrete, they do not reverse it like concrete made from synthetic aggregates.

Can We Afford Carbon Dioxide Removal (CDR)?

We have already described the biases in cost assumptions where scenarios rule nad costs are innocently overblow by reports of academic literature that does not look at scenarios that are likely to be used. This discussion addresses the total cost of removing CO2 from the sky that is widely believed to be extremely excessive. Using easy math, removing 1,000 Gt of CO2 at $50 per ton (to use a RAND study costs), is $50 trillion. In 20 years, to restore our climate by mid-century, this is $2.5 trillion per year globally with the US share being a quarter of that or $625 billion per year. At $100 per ton the cost is $5 trillion per year globally and $1.25 trillion for the US. Cost will very likely, before long, fall below $50 per ton, based on iterative process design and Keith 2018 being $60 ton using renewable energy. But the challenge remains that this is a lot of money and when money is always short everywhere, where does the money come from? Simply put, we can find the money as we always find it in an emergency. We realize this is dodging the question, but if motivation is there, the money will be found. What needs to be understood is the scope of this spending. Once it is understood how this very large amount of money (2.5 to 5% of global gross domestic product) relates to life on Earth as we know it, it will be much easier to integrate this spending into our perception of reality. Consider…  In the US alone we spent $4.3 trillion on health care in 2021, $500 billion on clothes, $750 billion on durable goods, $1.3 trillion on nondurable goods, $1.5 trillion on our automobiles, $2.1 trillion on food, $500 billion on water and wastewater treatment, $500 billion on agricultural damages not counting climate change, $500 billion on entertainment, $1 trillion on energy, $600 billion on sick days, and $200 billion disposing of urban waste. Globally we spent $1.9 trillion on fuel subsidies, $2.6 trillion on life insurance, and $1.6 trillion on advertising.

See more details about atmospheric carbon capture below.

CARBON CAPTURE AND SEQUESTRATION (CCS) FROM INDUSTRIAL AND ENERGY GENERATION EXHAUSTS – CATALYZING GIGASCALING

CCS refers to capturing CO2 from exhaust streams in energy generation and industry. Though air capture of CO2 is often referred to as CCS, for this discussion, CSS only includes capture from exhaust streams of energy generation or industry applications. Much literature and IPCC reviews show that to achieve net zero emissions, we must use CDR offsets or carbon captured elsewhere, to compensate for hard to decarbonize sectors. With unlimited time, it is plausible we could decarbonize these sectors but because of the difficulties and short time frames involved with Earth systems degradation, both CDR and CCS are mandatory. WE need CDR to restore our climate, and we need CSS to limit future emissions so as to make CDR easier, and importantly, to catalyze the scaling of CDR. Much has been written about failures of CCS and some is valid because of challenges with emerging technology implementation, but most is misguided. There is no incentive for industry to capture CO2 from their processes and energy generation, but industry can read the writing on the wall and profitability demands they be ready when carbon emissions regulations appear. Therefor they pilot CCS units to determine feasibility, then shut them down because there is no incentive to keep spending money to keep them operating. This process has been misinterpreted by many as failure.

What is the importance of CCS then, with climate restoration? 

CCS alone only limits future emissions by capturing and storing new emissions as they are generated. The importance to climate restoration however, is that CCS serves to catalyze removal and storage process scaling. Most of the CCS process components are identical to air capture components. Storage is identical. CCS engineers scale their components to be able to advance the process to make more money from the sequestration incentives. CCS implementation also considers that soon, there will carbon emissions regulations that do not have positive incentives so their processes for both CCS and air capture need to be maximized through engineering iteration, so that industry’s bottom line does not suffer unduly. These engineering tasks serve not only to safeguard industry profits, but since their components are largely identical, they advance scaling air capture to quantities that are meaningful to climate restoration in time frames that matter.

Case Study – CCS Failures? The Petra Nova Unit

Petra Nova is a first of its kind full-scale demonstration unit for removal of CO2 from coal fired electricity generation in Houston. The CO2 is used for enhanced oil recovery (EOR). Widespread reports of the failure of this unit are unfounded. It was shut down when the price of oil went to near zero during Covid after meeting 85 percent of its design goals – an excellent initial outcome for a full-scale demonstration unit.  Petra Nova is operational again after being refurbished to increase capacity by 30 percent. This is the fate of most of these carbon removal demonstrations. Industry first demonstrates full-scale units to prove concept and then they shut them down after proof awaiting a revenue stream or mandatory regulation as there is no profit in operating the systems (without EOR) and there are no regulations requiring carbon removal from exhaust streams.

Enhanced Oil Recovery (EOR) with CDR, and Carbon Negative Oil

Myth: Enhanced oil recovery cannot be carbon negative because of the greenhouse gas emissions from burning recovered fossil fuels.
Reality: This myth is based on the standard EOR process where all available CO2 is removed from the recovery well to inject into the next well.

Analysis of sequestration efficiency with EOR is based on the industry process of recycling CO2 to the next well where industry removes all the CO2 it can from recovery wells to recycle the process to unrecovered wells. To create carbon negative oil and gas and be awarded incentives from the California Low Carbon Fuels Standard (LCFS) or IRS 45Q Carbon Sequestration Incentive, and as these laws development state – to further the mandatory industrialization and scaling of carbon capture technologies, simply close the valve and leave CO2 in the ground.

EOR produces 10% to 15% of remaining oil or gas in a field where primary and secondary production is no longer feasible after removing half of the product originally in the ground. What must be done to sequester more CO2 is simply close the valve on the well and do not recycle all the CO2 to the next well – or, pump more in the ground, there’s room for it. Why would an oil and gas producer do this? Because the EOR production process to each well already exists and air capture CO2, once the air capture infrastructure is put into place, is cheaper than the LCFS and 45Q incentives creating a revenue windfall. Won’t they just pocket the windfall? Not likely, at least most of it. The reason is that far more revenues will be available from carbon sequestration incentives to the first to market – the first to create the most infrastructure to achieve market share of the 1,000 or so Gt CO2 removal required to restore our climate.

Specifically, How Can Oil From EOR be Carbon Negative?

Half of CO2 injected for EOR is trapped in the formation to start with. It is trapped in kerogens that originally held the oil and gas, it is mineralized in the geology, and it is dissolved in the salty formation water associated with the oil and gas. This sequestration approximately equals the CO2 emissions from burning the recovered product plus the upstream emissions in the process. To make oil and natural gas from EOR carbon negative, leave more CO2 in the ground, the CLCF and 45Q standards pay more than the value of the air capture CO2.<

Incentives for EOR and Non-EOR Air Capture

The Internal Revenue Service’s Carbon Oxide Capture rules (IRS 45Q), pays up to $85 per ton of CO2 sequestered with EOR, if union labor is used. Air capture without EOR, and direct sequestration or sequestration in durable products pays up to $185 a ton if union labor is used. There are many different air capture technologies and most are still in development. The three discussed here are lime/potash, amines and cryosperation.

Occidental Chemicals’ (Oxy) 1PointFive facility in the Permian Basin, Texas. This 500,000 ton per year facility, expandable to 1 million tons per year, is 833 times larger than largest air capture facility in existence today (Orca in Iceland), and expected to go into operation in mid-2025. Oxy has six ongoing air capture projects with a total capacity of six-billion tons storage. Image: Oxy

The Importance of Carbon Dioxide Removal

Carbon dioxide removal (CDR) is required because complete emissions elimination this instant allows further warming and it is current warming that has allowed Earth systems to begin degrading, where once a system begins to degrade, it does not stop unless the thing that caused it to degrade is removed. Engineered cooling is required because once systems’ degradation begins, there is only a limited amount of time before degradation becomes so severe the systems’ cannot self-restore on their own, with time frames of mid-century according to much academic literature. Carbon dioxide removal is required so we do not have to use engineered cooling solutions indefinitely, and because engineered cooling cannot stop ocean acidification and untenable degradation of our planet’s most important system. Decarbonization of as much of our advanced civilization’s infrastructure is also required to create a sustainable future for humankind, but this does not absolve us of the critical path demand for carbon dioxide removal and engineered cooling solutions.

Trust In Engineers to Remove Carbon Dioxide and Other Greenhouse Gasses Too

We trust our engineers to keep us safe from danger, to treat pollution so we can be safe, and to design a world where we can live free from undue risk. Literally, engineering pollution treatment solutions have made our advanced civilization what is is today. Yet, we do not trust geoengineering. Why is this? Why do we trust our engineers to safely deliver extremely deadly electricity to our homes, and to design the plethora of electric appliances that populate our lives so that they do not kill us, and we never give it a second thought? Why do we trust them to design our multiple ton automobiles that travel at 100 feet per second with collision energy of seven million pounds of force? Or, to treat our drinking water to ensure it is free of deadly pathogens, design skyscrapers, dams, and airplanes so they don’t fall down and kill people?

In the US alone, our trustworthy engineers treat 112 gigatons of potable water and human sewage every year, half of which treats extremely dangerous material through a complicated and sensitive process using a biologic reactor. The belief that carbon dioxide pollution treatment is too expensive, too big, and has only limited application is simply a myth, created by those that are unsure, or by those that believe it is morally wrong, or those that believe the scenarios of IPCC are not negotiable; that CDR is only for overshoot and hard to decarbonize sectors. And there is also a huge myth that air capture pilot projects demonstrating CDR have almost all failed, when almost all of them reach their goals and are then shut down because there is no incentive to keep pouring money over them.

Our engineers know what they are about. They have been building processes to remove carbon dioxide from our atmosphere — to treat CO2 like the pollution that it is, for over 100 years. Our engineers  have created our advanced civilization, taking our population from one billion to eight billion, and they have done it safely. They deserve our trust with climate pollution and w once our climate culture understands this fundamental fact of our advanced human civilization, we will sleep a lot easier.

The Moral Hazard – A River That Runs Both Ways; A River of Human Sewage

A primary argument in our climate change culture has been that, pursuing carbon dioxide removal (and direct cooling solutions) constitutes a “moral hazard” because implementation would slow greenhouse gas emissions reduction efforts and this would be “morally wrong.” The rationale continues, “If we can simply remove CO2 from the sky, climate polluters will just keep on polluting.” The simple and effective response to this argument is that, why should we stop emitting only climate pollution? When we discovered that human sewage pollution was killing millions from disease in the 19th century, we did not stop emitting human sewage, we simply started behaving responsibly based on new knowledge that human sewage allows vectors to distribute deadly disease if human sewage pollution is simply dumped in the ditch. Of course decarbonizing our culture will create a sustainable future and of course, limiting emissions reduces the amount of atmospheric removal and direct cooling required. But alone, complete net zero this instant cannot cool, and it is cooling that must occur to avoid untenable futures caused by ongoing ecological degradation that will not self-restore unless we cool our climate to a temperature cooler than today.

Pollution Treatment Theory… We do not as a general rule, stop the emissions of other pollutants when we find out they are deadly, we simply create rules to reduce their emissions and or require treatment to render them moot. Why has our advanced civilization decided that treating climate pollution is different from other forms of pollution? The answer comes from the way our climate change culture was created. In the beginning, in 1990 when the Intergovernmental Panel on Climate Change (IPCC) created their first report, simple emissions reductions from fossil fuels would have solved our human climate sewage pollution problem, if they were responsibly enacted in a timely manner.

Pollution Treatment Responsibility… We did not act responsibly and instead, delayed implementation of emissions limitations regardless of what scientists warned. This delay has now exceeded thirty years and one of the most important things climate scientists warned us about in 1990, was that if we delayed regulations on climate pollution, limiting warming would become more difficult, the rate of warming would rapidly accelerate, and at some point, effects of warming would become so extreme that we would have to use artificial climate cooling strategies to lower our climate temperature or suffer untold mortality from warming related effects. Now, the river of human sewage known as climate pollution has reversed its flow and our advanced civilization as we know is at certain risk of failure.

The repeatedly unprecedented effects from warming can no longer be argued to be natural and their nonlinear increase in extremeness has just begun. Ecological degradation from warming is well underway and does not self-restore unless we cool our climate from today, ultimately leading to ecological collapses across the planet in time frames far sooner than the classic end-of-century, year 2100 time frame. No amount of future emissions reductions can now cool our climate at all, in time frames that matter to ecological collapse, and warming in the pipeline –even with complete emissions cessation this instant, continues to warm because of the great imbalance between our rapidly warming climate and slowly warming oceans and ice sheets. The ultimate fate of climate warming is that, even with complete emissions elimination today, our global temperature will warm another four to five degrees C by the end of the century and a total of eight to ten degrees C after a couple hundred more years — and, there is nothing we can do about it except remove the very long-lived climate pollution from our sky and treat it so we can be safe, and because this takes time, we also must artificially cool our climate with engineered solutions to gives us that extra time to remove the climate pollution from our sky.

The New Moral Hazard… The moral hazard today has been turned upside down because we were irresponsible about our human climate pollution sewage emissions and did not do as our scientists suggested prudent.

The real “moral hazard” then, today, is the failure to pursue cooling approaches that can stop irreversible degradation responses, and reduce ecological and human disasters, and eliminate warming-caused injustice and inequity. It is now morally wrong to only suggest emissions reductions alone can save us. We have caused this reversal of the moral hazard because of our irresponsible delay in action, and now it does not matter what are the costs of carbon removal and engineered cooling solutions, or if there are risks involved. The risk of not cooling our climate; of not restoring our climate so Earth systems degradation can stabilize – the risks are futures that see natural feedback greenhouse gas emissions from failing Earth systems that will dwarf humankind’s climate sewage pollution emissions, will creating a world where even artificial emergency cooling is at risk of failing.

The Limits of Carbon Dioxide Removal

If we delay implementation of a giga-scale air capture infrastructure, natural feedback emissions will vastly increase the amount of removal required. these natural feedback emissions are almost always overlooked in policy and advocacy discussion and in academic findings as well. Even though engineered cooling solutions are the only way we can avoid natural feedback emissions that dwarf humankind’s in the short term, removal is required so we do not have to assume the risks of long term cooling, which does not reduce ocean acidification, where warming degradation is currently creating risks for the viability of humanity’s most important system.

Natural systems have to risks: their capacity fully enhanced and in prime health is only about 5 gigatons annually, considering we can fully enhance all our Earth systems. This consideration however is not possible in most Earth systems because they are currently degrading because of warming. Therefore their restoration so as to apply enhancement is not feasible. this greatly limits the capacity of natural systems to remove greenhouse gases from the atmosphere, let alone remove more than they are removing now because many of them are in fact emitting now, and no longer sequestering.

Delay in action to deploy atmospheric removal solutions, like when we delayed action on reducing emissions, creates a world where removal becomes nonlinearly more difficult, because natural feedback emissions increase nonlinearly with further warming. Combine this with the nonlinear economic effects of warming as it increases and pretty soon there will be a point where removals as well as engineered cooling solutions become infeasible.

Conclusion

The road to climate stability and a sustainable planet will ultimately require a complete transformation of global industrial civilization’s economies, systems, and practices, but if we do not first use engineered cooling solutions to create emergency climate stabilization, and simultaneously implement a gigascale greenhouse gas removal infrastructure, and if we do not do so in time frames relative to point where natural systems degradation becomes so extreme that the systems cannot self-restore, all other actions to create a sustainable human culture will be for naught.

Supporting Literature

Below is a sampling of critical literature about carbon dioxide and greenhouse gas removal, natural and industrial, and the permanence crisis in natural sequestration that is ongoing because of degradation of Earth systems, presented in two parts: Natural and Industrial.

NATURAL SYSTEMS PERMANENCE CRISIS

National Academy of Sciences 2018… Natural systems CDR (carbon dioxide removal) is limited to 5.5 Gt per year globally, fully implemented and fully enhanced.  The National Academies of Sciences Negative Emissions Technologies Report in 2018, referenced by IPPC, says the safe, equitable atmospheric carbon dioxide removal with natural terrestrial Earth Systems enhancements is 5.5 Gt CO2 per year globally… The key with this report that has quantities significantly less than other sources is justice and equity. Other sources do not, or do not fully consider justice and equity, where plausible solutions (example reforestation) create injustice and inequity, and NAS’s feasible quantities consider justice and equity. The Report Highlights summary states with regard to natural systems sequestration, “However, attaining these levels would require unprecedented rates of adoption of agricultural soil conservation practices, forestry management practices, and waste biomass capture. Practically achievable limits are likely substantially less, perhaps half the 1 GtCO2/yr in the US and 10 GtCO2/yr globally.” In addition, NAS’s report does not consider ongoing degradation of natural systems from warming-caused collapses, ocean processes which have a capacity to be very large, but mostly include geoengineering.
“TABLE 1. Cost, Limiting Factors, and Impact Potential of NETs with Current Technology and Understanding. “Safe” rate of CO2 removal means that the deployment would not cause large potential adverse societal, economic, and environmental impacts. Estimated rates assume full adoption of agricultural soil conservation practices, forestry management practices, and waste biomass capture.”

Afforestation/Reforestation       1 Gt/yr
Forest Management                     1.5 Gt/yr
Agricultural Soils                          3 Gt/yr
Total                                                5.5 Gt/yr

Negative Emissions Technologies and Reliable Sequestration, A Research Agenda, Consensus Study Report, Highlights, National Academy of Sciences, October 2018, Summary, page 2, paragraph 2 and 3, and Table 1.
https://www.nap.edu/resource/25259/Negative%20Emissions%20Technologies.pdf

What About Hawken’s “Drawdown”?

Paul Hawken’s book suggests 10 Gt atmospheric CO2 removal is plausible using natural systems and agricultural enhancements… This exhaustive description of advanced drawdown opportunities in Hawken’s book Drawdown—The Most Comprehensive Plan Ever Proposed to Reverse Global Warming, says about 10 Gt negative emissions per year are possible using enhanced natural and agricultural systems. There are several challenge with Hawken’s work: time, justice and equity, feasibility and permanence. Though Hawken’s strategies are certainly plausible, given our culture’s track record of creating sustainable natural systems and agricultural practices, feasibility is questionable, especially in near term time frames associated with collapsing Earth systems points of no return. Some of Hawken’s actions include equity considerations, some do not. Some are wildly beneficial to the commons, but some are obviously not considering justice and equity issues. the most imp[ortant issue with haken’s natural systems work is that our natural systems are already degraded and their sequestration capacity already limited, eliminated or reversed. Hawken does not consider the implications of prematurely activated tipping collapse responses.
Hawken, Drawdown—The Most Comprehensive Plan Ever Proposed to Reverse Global Warming, Penguin Books, 2017.
https://www.drawdown.org/solutions

PERMANENCE OF NATURAL SYSTEMS CARBON SEQUESTRATION

Even if natural systems had the capacity , ongoing degradation from warming has crippled  the current sequestration from natural systems globally. While some systems may be still viable, many others are in various stages of degradation from warming that will only become worse without climate restoration before the degradation becomes so severe the systems cannot self-restore.

Ballard 2023 – Large carbon credit losses of the past decade are likely to become far more frequent in the coming decades as forests become hotter and drier… “One emerging threat to the long-term stability and viability of forest carbon offset projects is wildfires, which can release large amounts of carbon and limit the efficacy of associated offsetting credits… Our results indicate the large wildfire carbon project damages seen in the past decade are likely to become more frequent… Already, wildfires within offset projects in the past decade alone have exhausted nearly all of the carbon credits that California’s cap and trade program set aside for wildfire losses, and that reserve was intended to last 100 years [4]… Large carbon credit losses of the past decade are likely to become far more frequent in the coming decades as forests become hotter and drier.”
Ballard et al., Widespread increases in future wildfire risk to global forest carbon offset projects, ArXiv preprint, May 3, 2023.
https://arxiv.org/abs/2305.02397

Wu 2023 – US forest carbon permanence uncertain – areas most at risk are current carbon offset regions… Abstract, ” Forests have considerable potential to mitigate anthropogenic climate change through carbon sequestration, as well as provide society with substantial co-benefits. However, climate change risks may fundamentally compromise the permanence of forest carbon storage. Here, we conduct a multi-method synthesis of contiguous US forest aboveground carbon storage potential at both regional and species levels through a fusion of historical and future climate projections, extensive forest inventory plots datasets, machine learning/niche models, and mechanistic land surface model ensemble outputs. We find diverging signs and magnitudes of projected future forest aboveground carbon storage potential across contrasting approaches, ranging from an average total gain of 6.7 Pg C to a loss of 0.9 Pg C, in a moderate-emissions scenario. The Great Lakes region and the northeastern United States showed consistent signs of carbon gains across approaches and future scenarios. Substantial risks of carbon losses were found in regions where forest carbon offset projects are currently located. This multi-method assessment highlights the current striking uncertainty in US forest carbon storage potential estimates and provides a critical foundation to guide forest conservation, restoration and nature-based climate solutions.”
(Press Release quotes)
Wu et al., Uncertainty in US forest carbon storage potential due to climate risks, Nature Geoscience, April 6, 2023.
(Paywall) https://www.nature.com/articles/s41561-023-01166-7
(Press Release) Gabrielsen, US forests face an unclear future with climate change, University of Utah, April 6, 2023.
https://www.sciencedaily.com/releases/2023/04/230406113941.htm

Anderegg 2022 – Climate-driven disturbances pose critical risks to the long-term permanence of forest carbon… “Forests are currently a substantial carbon sink globally. Many climate change mitigation strategies leverage forest preservation and expansion, but rely on forests storing carbon for decades to centuries. Yet climate-driven disturbances pose critical risks to the long-term stability of forest carbon. We quantify the climate drivers that influence wildfire and climate stress-driven tree mortality, including a separate insect-driven tree mortality, for the contiguous United States for current (1984–2018) and project these future disturbance risks over the 21st century. We find that current risks are widespread and projected to increase across different emissions scenarios by a factor of >4 for fire and >1.3 for climate-stress mortality. These forest disturbance risks highlight pervasive climate-sensitive disturbance impacts on US forests and raise questions about the risk management approach taken by forest carbon offset policies. Our results provide US-wide risk maps of key climate-sensitive disturbances for improving carbon cycle modeling, conservation and climate policy.”
Anderegg et al., Future climate risks from stress insects and fire across US forests, Ecology Letters, March 26, 2022.
https://onlinelibrary.wiley.com/doi/epdf/10.1111/ele.14018

Anderegg 2020 – Forest carbon sequestration policy does not always consider climate impact risks to forests stability where widespread climate change-induced forest die-offs are creating dangerous feedbacks… “Forests have significant potential to help mitigate human-caused climate change and provide society with a broad range of co-benefits. Local, national, and international efforts have developed policies and economic incentives to protect and enhance forest carbon sinks – ranging from the Bonn Challenge to restore deforested areas to the development of forest carbon offset projects around the world. However, these policies do not always account for important ecological and climate-related risks and limits to forest stability (i.e. permanence). Widespread climate-induced forest die-off has been observed in forests globally and creates a dangerous carbon cycle feedback, both by releasing large amounts of carbon stored in forest ecosystems to the atmosphere and by reducing the size of the future forest carbon sink. Climate-driven risks may fundamentally compromise forest carbon stocks and sinks in the 21st century. Understanding and quantifying climate-driven risks to forest stability is a crucial component needed to forecast the integrity of forest carbon sinks and the extent to which they can contribute towards the Paris Agreement goal to limit warming well below 2 °C. Thus, rigorous scientific assessment of the risks and limitations to widespread deployment of forests as natural climate solutions is urgent.”
Anderegg et al., Climate-driven risks to the climate mitigation potential of forests, Science, June 19, 2020.
https://par.nsf.gov/servlets/purl/10182667

Bernal 2022 – Prescribed burning significantly reduces carbon storage – California Carbon stocks in 2069 modeled at 25 percent of today’s values with 870 megatons net emissions in the next 50 years… With restoration of forests using fuels reductions strategies that reduce the number of trees per acre, in combination with both current and additional warming that favors lower tree density and more pines, total carbon storage in California’s forests in 2069 is only 25 percent of carbon storage today. Abstract, “Restoration of fire-prone forests can promote resiliency to disturbances, yet such activities may reduce biomass stocks to levels that conflict with climate mitigation goals. Using a set of large-scale historical inventories across the Sierra Nevada/southern Cascade region, we identified underlying climatic and biophysical drivers of historical forest characteristics and projected how restoration of these characteristics manifest under future climate. Historical forest conditions varied with climate and site moisture availability but were generally characterized by low tree density (∼53 trees ha−1 ), low live basal area (∼22 m2 ha−1 ), low biomass (∼34 Mg ha−1 ), and high pine dominance. Our predictions reflected broad convergence in forest structure, frequent fire is the most likely explanation for this convergence. Under projected climate (2040–2069), hotter sites become more prevalent, nearly ubiquitously favoring low tree densities, low biomass, and high pine dominance. Based on these projections, this region may be unable to support aboveground biomass >40 Mg ha−1 by 2069, a value approximately 25% of current average biomass stocks. Ultimately, restoring resilient forests will require adjusting carbon policy to match limited future aboveground carbon stocks in this region.” and, “Based on the relationship between AGLB and total biomass (supplementary figure 8), these forests store a total of 1,167 MMT CO2e. We project that the median AGLB in 2069 will be no more than 40 Mg ha−1, which translates to 307 MMT CO2e stored in the total biomass pool. These extrapolations suggest that this region could emit 860 MMT CO2e over the next 50 years (2019–2069). Liang et al (2017a) projected the Sierra Nevada’s carbon carrying capacity under climate-wildfire interactions through the late 21st century and found that the region could lose as much as 78% of current aboveground carbon stocks, which aligns with our projections of climate resilient forests supporting <25% of current AGLB.”
Bernal et al., Biomass stocks in California’s fire-prone forests, mismatch in ecology and policy, Environmental Research Letters, March 25, 2022.
https://iopscience.iop.org/article/10.1088/1748-9326/ac576a/pdf

Maxwell 2022 – Increased frequency of disturbance decreases carbon storage, particularly in management practices that emphasize prescribed fire… “Our results suggest increasing the frequency of disturbances (a lower DRI) would reduce the percentage of high-severity fire on landscape but not the total amount of wildfire in general. However, a higher DRI reduced carbon storage and sequestration, particularly in management strategies that emphasized prescribed fire over hand or mechanical fuel treatments…Climate change is moving the landscape toward becoming a carbon source (Fig. 3, left). This can be moderated or accelerated by the type of management actions taken on the landscape, which is reflected in the different management areas present (see Table 3). Higher removals of biomass (whether from combustion of litter/downed woody material or from higher mortality than other forms of treatment) by prescribed fires in Scenarios 4 and 5 on the landscape affected the carbon balance (Fig. 3, right), where both live and dead C pools decreased through time… Our analysis suggests that, with the management approaches tested, there was a trade-off between C storage and fire severity. Although a lower DRI reduced high-severity fire, the net effect was reduced C storage.”
Maxwell et al., Frequency of disturbance mitigates high-severity fire in the Lake Tahoe basin, Ecology and Society, 2022.
https://www.fs.usda.gov/research/treesearch/63891

Crausbay 2017 – Defining ecological drought  and permanence risk for the twenty-first century… Sequestration permanence is mandatory for nature-based Carbon dioxide removal. If a fire, flood or drought comes along, ever increasing on a warmer planet, it erases all sequestration. There is actually a new type of drought definition that considers ecological collapse because of climate conditions beyond the evolution of an ecosystem. It’s called ecological drought and it is happening worldwide as we have warmed beyond the evolution of many of our global ecologies. “To prepare us for the rising risk of drought in the twenty-first century, we need to reframe the drought conversation by underscoring the value to human communities in sustaining ecosystems and the critical services they provide when water availability dips below critical thresholds. In particular, we need to define a new type of drought—ecological drought—that integrates the ecological, climatic, hydrological, socioeconomic, and cultural dimensions of drought. To this end, we define the term ecological drought as an episodic deficit in water availability that drives ecosystems beyond thresholds of vulnerability, impacts ecosystem services, and triggers feedbacks in natural and/or human systems.”
Crausbay et al, Defining Ecological Drought for the Twenty-First Century BAMS, December 2017.
https://journals.ametsoc.org/doi/pdf/10.1175/BAMS-D-16-0292.1

Crowther 2016 – Soils carbon permanence Soil carbon loss with 1.5 C at 2050 is 5.5 Gt CO2eq loss per year… “If we make the conservative assumption that the full effects of warming are fully realized within a year,  then approximately 30 ± 30 PgC would be lost from the surface soil for 1 °C of warming. Given that global average soil surface temperatures are projected to increase by around 2 °C over the next 35 years under a business-as-usual emissions scenario16, this extrapolation would suggest that warming could drive the net loss of approximately 55 ± 50 PgC from the upper soil horizon. If, as expected, this C entered the atmospheric pool, the atmospheric burden of CO2 would increase by approximately 25 parts per million over this period.”
1.5 C Warming Soil Carbon Loss… 1.5 C by 2050 is about 45 Pg C loss or 165 Gt CO2 in 30 years or 5.5 Gt CO2 per year.
Crowther et al., Quantifying global soil carbon losses in response to warming, Nature, December 1, 2016.
(Researchgate – free subscription) https://www.researchgate.net/publication/311163076_Quantifying_global_soil_carbon_losses_in_response_to_warming

CASE STUDY –  PERMANENCE: CALIFORNIAS 100-YEAR FIRE, INSECT, AND DISEASE CARBON CREDIT OFFSET BUFFER ALREADY BURNED

Badgley 2022 – California’s 100-year carbon credit buffer pool has almost completely burned showing extreme lack of permanence… “Wildfires have depleted nearly one-fifth of the total buffer pool in less than a decade, equivalent to at least 95 percent of the program wide contribution intended to manage all fire risks for 100 years. We also show that potential carbon losses from a single forest disease, sudden oak death, could fully encumber all credits set aside for disease and insect risks. These findings indicate that California’s buffer pool is severely undercapitalized and therefore unlikely to be able to guarantee the environmental integrity of California’s forest offsets program for 100 years.” … “Estimated carbon losses from wildfires within the offset program’s first 10 years have depleted at least 95 percent of the contributions set aside to protect against all fire risks over 100 years.” … “the potential carbon losses associated with a single disease (sudden oak death) and its impacts on a single species (tanoak) is large enough to fully encumber the total credits set aside for all disease- and insect-related mortality over 100 years.” … “From the program’s inception through our study cut-off date of January 5, 2022, a total of 31.0 million credits (13.4 percent) had been contributed to the buffer pool out of a total 231.5 million issued credits, such that the 31.0 million buffer pool credits insure a portfolio of 200.5 million credits against permanence risks.”
Badgley et al., California’s forest carbon offsets buffer pool is severely undercapitalized, Frontiers in Forests and Global Change, August 5, 2022.
https://www.frontiersin.org/articles/10.3389/ffgc.2022.930426/full

Herbert 2020 – Forest carbon credit offset burn example, the Lionshead Fire in Oregon, August 2020…  “The Lionshead Fire in Oregon provides a timely example of the importance of forest carbon offset permanence. Started by a lightning strike on August 16, 2020, the Lionshead Fire merged with nearby fires Beachie Creek and P515. The extent of this fire complex overlaps substantially with the boundaries of the Warm Springs forest offset project in Central Oregon, known as ACR260 in the offsets registry.
Public records from the offset program provide context for the potential scale of carbon loss from this project. ACR260 has received 2,676,483 carbon credits to date — with each credit equal to 1 metric ton of CO₂ — which makes it the largest credited forest offset project in Oregon and among the fifteen largest forest projects in California’s carbon offset market.
Estimate the fraction of carbon lost due to fire-related mortality:  Estimating carbon loss will ultimately require detailed assessment on the ground, which we lack today. As a historical reference point, the 2003 B&B fire, which burned nearby under similar conditions, ultimately killed almost half the trees it encountered. Though the situation in Oregon is still evolving, we can calculate the carbon impacts that would arise from a similar outcome in this incident. At a 50% loss of carbon in the 72% of the ACR260 project area burned through September 17, the Lionshead Fire will have reversed 963,534 credits (about 4% of the total buffer pool). In a worst case scenario in which the entirety of the project burns and all credited carbon is lost, more than 11% of the buffer pool could be depleted.”  It is important to note the 2003 B&B Fire happened a while ago. Recently, Western US fires have begun burning much more severely with an 800 percent increase in high severity fire from 1982 to 2017, where 97 percent of area burned in the last two decades has been high severity fires, with mortality of 95 percent in high severity fires. Without ground-truthing estimates like this one made for the Lionshead fire are likely understated where they assume 50 percent mortality in sever burn area where the modeling assumption was based on the B&B Fire 2003 with 10% mortality in low severity burn areas, 10 to 75% mortality in moderate burn areas and greater than 75% mortality in high severity burn areas, as per USFS Fire Recovery Project Report for the B&B Fire.
Herbert et al., Carbon offsets burning, Carbon Plan, 2020 (accessed May 2023).
https://carbonplan.org/research/offset-project-fire

B&B Fire Recovery Project, Record of Decision, Sisters Ranger District, Deschutes National Forest, USDA, August 2005.
https://scholarsbank.uoregon.edu/xmlui/bitstream/handle/1794/7103/B%26B_Fire_Recovery_Project_ROD.pdf?sequence=1

Badgley 2023 – Klamath East poised for automatic termination in the California Carbon Offset Program… “the Klamath East (ACR273) forest carbon offset project is slated for automatic termination as a result of the catastrophic Bootleg Fire that burned through the project in 2021. New paperwork, filed on Monday, puts total wildfire-induced carbon losses at over 3 million tCO₂. The extent of the damage was so severe that the project’s current standing live carbon stocks are lower than the project’s baseline carbon stocks. As a result, California’s rules require that the entire project be terminated.
Automatic termination means retiring 100 percent of the credits already issued to the project from the program’s buffer pool — totalling at least 1.14 million offset credits. When combined with the estimated 3.95 million credits that have already or are soon to be retired from the buffer pool, total known wildfire losses through the end of the 2021 fire season stand at 5.09 million credits.
We previously estimated that the buffer pool was designed with the assumption that about 6 million credits would be sufficient to cover the wildfire risk of the current portfolio of projects for the next 100 years. The termination of ACR273 would mean about 84 percent of those credits are now gone. And, as we’ve discussed before, that number will continue to grow once we have an official reversal estimate for the 2020 Lionshead fire. Taken together, it seems increasingly likely that the entire wildfire portion of California’s forest carbon buffer pool has already been depleted.”
Badgley, Klamath East poised for automatic termination, Carbon Credit  Blog Post, March 29, 2023.
https://carbonplan.org/blog/bootleg-fire-update

Li and Banerjee 2021 – Extreme wildfires in California are responsible for 97 percent of the area burned in California in the last two decades… have increased significantly in the last two decades with the cause being climate warming related…
“Between 2000 and 2019, compared to 1920 to 1999, the proportion of extreme wildfires larger than 10,000 acres (40.47 km2 ) has increased significantly… The burned area of large wildfires accounted for 97.04 % of the total burned area (13,089.68 out of 13,488.19 thousand acres, that is 52,972.05 out of 54,584.77 km2 ) in the past two decades… The frequency and burned area growth of wildfires in the past two decades are much higher than that during the 80 years in history from 1920 to 1999… The frequency of large wildfires and the burned area of small wildfires in the recent 20 years even have decreased… From 2000 to 2019, the frequency of wildfires in July increased significantly and became much more considerable than in other months. Meanwhile, the start of the wildfire season has also advanced to May (from June) and the duration has increased each month… there has been a major increase in the natural wildfires in July in the past two decades.” Summary: “We found that the frequency and total burned area of all wildfires have increased significantly. The start time and peak months of the wildfire season have been advanced, and the covered months have been lengthened. For large and small wildfires, the annual frequency of large wildfires has remained stable for the last 100 years, but the total burned area has increased rapidly in the past two decades… illustrat[ing] that the comprehensive environmental conditions, such as changes in climate and vegetation, have increased the coverage of potential wildfire ignitions… slope, temperature and maximum vapor pressure deficit have positive correlation with wildfire occurrence… natural factors, especially climate variables, have a greater impact on the density of wildfires.”
Li and Banerjee, Spatial and temporal pattern of wildfires in California from 2000 to 2019, Nature Scientific Reports, April 22, 2021.
https://www.nature.com/articles/s41598-021-88131-9

Parks and Abatzoglou 2020 – An eightfold increase (800 percent) in high-severity fire (95% or greater mortality, Stevens 2017) burned area from 1985 to 2017, implicates increased probability of conversion of forests to alternative vegetation types… “Significant increases in annual area burned at high severity (AABhs) were observed across most ecoregions, with an overall eightfold increase in AABhs across western US forests. The relationships we identified between the annual fire severity metrics and climate, as well as the observed and projected trend toward warmer and drier fire seasons, suggest that climate change will contribute to increased fire severity in future decades where fuels remain abundant. The growing prevalence of high‐severity fire in western US forests has important implications to forest ecosystems, including an increased probability of fire‐catalyzed conversions from forest to alternative vegetation types.”
Parks and Abatzoglou, Warmer and Drier Fire Seasons Contribute to Increases in Area Burned at High Severity in Western US Forests From 1985 to 2017, Geophysical Research Letters, October 22, 2020.
https://agupubs.onlinelibrary.wiley.com/doi/10.1029/2020GL089858

Stevens 2017 – Mortality of 95 percent or greater in high-severity fire…
Stevens et al., Changing spatial patterns of stand-replacing fire in California conifer forests, Forest and Ecology Management, June 23, 2017.
https://www.fs.fed.us/psw/publications/north/psw_2017_north005_stevens.pdf

 

INDUSTRIAL GREENHOUSE GAS REMOVAL COSTS CONTROVERSY

Errors in Academic Findings that Have Biased CDR Costs High

An important note about air capture costs biases: Because the moral hazard is strong, findings that show excessive costs of air capture are leveraged by the moral hazard sector to try and prove their point. These players however, do not recognize the biases inherent in these works and therefore they are creating injustice in our climate culture by advocating that erroneous or scenario overstated  results are valid.

APS 2011 and MIT 2011… The economically infeasible theoretical evaluation of direct air capture (DAC) of carbon dioxide by the American Physical Society (APS) and Massachusetts Institute of Technology’s (MIT) from 2011, only theorizes on the basic physics of CO2 air capture of mature World War II era technology. Because of the outsized capacity for DAC to solve the climate pollution problem, the APS and MIT findings garnered very significant press as they state the costs of DAC to be $600 to $1000 per ton or an order of magnitude greater than what the actual DAC researchers suggest. Their reasoning quotes basic physics and the low concentration of CO2 in air that is supposedly much harder to address than higher flue gas concentrations from power plant and industry smokestacks. But APS and MIT did not evaluate the new technologies, they just hypothesized about the physics involved. Press coverage did not mention that new technologies were not evaluated, or that APS and MIT had made basic physics errors in enthalpy. Several academic rebuttals did not make the news cycle and as a result, climate advocates, the public, and policy makers believe that the APS and MIT work is valid and DAC of carbon dioxide is cost prohibitive. Scientific evaluations are all about scenarios. If a scenario does not evaluate a certain parameter, the study does not speak to that scenario. APS and MIT used poor process assumptions in their scenarios that resulted in the exorbitant costs.

American Physical Society Study… $80 per ton from flue gas, $600 per ton for DAC using “mature technologies.”
Socolow et al., Direct Air Capture of CO2 with Chemicals, The American Physical Society, June 2011.
http://www.aps.org/policy/reports/assessments/upload/dac2011.pdf

MIT Study… $1,000 per ton.
House et al., economic and energetic analysis of capturing CO2 from ambient air, PNAS, September 2011.
http://sequestration.mit.edu/pdf/1012253108full.pdf

Rebuttals…

APS research revealed as significantly incomplete by Nature… Socolow 2011 [APS] evaluated existing WWII Era atmospheric removal technology and not surprisingly found them economically infeasible to address climate pollution.
Van Norden, Sucking carbon dioxide from air too costly, say physicists, Nature, May 11, 2011. http://blogs.nature.com/news/2011/05/sucking_carbon_dioxide_from_ai.html

Further rebuttal of APS and MIT (Holmes and Keith 2012)…Holmes and Keith identify short fallings of MIT and APS work calling out different design choices, insufficient optimization, and use of higher cost processes. When new DAC technologies are evaluated, costs are at or below those of mature DAC removal technology.
Holmes and Keith, An air-liquid contactor for large-scale capture of CO2 from air, Philosophical transactions of the Royal Society A, 370, 4380-4403, 2012.
http://rsta.royalsocietypublishing.org/content/370/1974/4380

Flawed analysis of the basic physics of enthalpy (Realff and Eisenberger 2012)… These researchers point out a fundamental flaw in the work of APS and MIT showing direct air capture takes more energy than flue capture because of CO2 concentration: “The notion of minimum work does not apply to the capture of CO2, because the capture process is exothermic.” When CO2 is reacted with something to remove it from air or flue gas, the reaction creates heat, “is exothermic.” So instead of 400 kJ or work per mole CO2 energy required the actual energy required involves moving air over whatever process is used to remove the CO2 from the air. This is 6 kJ per mole CO2. This relationship of the actual costs of removal of CO2 from the atmosphere being 1.5 percent of the costs suggested by APS and MIT corresponds very well to the costs assumed by research evaluating new technologies of +/- $20 per ton. It is important to note that the cost of regenerating the chemicals used to capture the CO2, whether for flue gas or atmospheric capture, is identical.
Realff and Eisenberger, Flawed analysis of the possibility of air capture, June 19, 2012.
http://sequestration.mit.edu/pdf/2012_PNAS_StorageCapacity_LetterToEditor.pdf

Response to Realff and Eisenberg… Herzog et al. (House 2012) responded to Realff and Eisenberger’s circular argument by declaring that the excess energy from the exothermic reaction was not used as an input into the process because it was considered an inefficiency. This is not the point. The enthalpy was used backwards, and required heat be delivered to this portion of the process when none was required, significantly biasing the results. See the discussion in the link below—scroll down for the rebuttal rebuttal by Herzog et al.
http://sequestration.mit.edu/pdf/2012_PNAS_StorageCapacity_LetterToEditor.pdf

Cruetzig 2019… “DACCS technologies enable the filtering of ambient air to then direct CO2 underground, requiring substantial energy, possibly up to 12% of electric and 60% of non-electric energy in 2100.” Assumes APS 2011 energy requirements.
Cruetzig et al., The mutual dependence of negative emission technologies and energy systems, Energy and Enviro Science, Royal Society of Chemistry, February 27, 2019.
https://pubs.rsc.org/en/content/articlepdf/2019/ee/c8ee03682a

Cruetzig 2021… “The cost of the DAC facility alone contributes $310/tCO2 for a conventional process-based design and $150/tCO2 for a more novel design. When the decomposition of calcium carbonate occurs within a natural-gas-heated calciner, the energy system adds only $80/tCO2 to these costs, assuming $3.25/GJ ($3.43/MMBtu) gas. However, leakage in the natural gas supply chain  increases the cost of net capture dramatically: with 2.3% leakage (U.S. national average) and a 20-year Global Warming Potential of 86, costs are about 50% higher.” and “As currently envisioned, DAC requires such a large amount of energy (Creutzig et al., 2019) that it is essential to investigate the full implications…”  Creutzig 2019 (above) uses APS 2011 energy.

Mayer, Hausfather et al., 2025 – CDR cooling with two-step strategy of Ag/air capture – uses poor costs… This preprint uses McQueen 2021 for costs, “The future cost of DACS is highly uncertain, with current cost estimates ranging from $600$1000 Mg1 CO2e (McQueen, et al., 2021).” These costs are significantly greater than McQueen 2021 and do not reflect real world costs, only scenarios that include APS 2011 errors. Scenarios of Mayer, Hausfather 2025: reversible patchworks of agricultural CDR to start with, transitioning to air capture and geologic storage. Findings obviously are costs are less using ag strategies since too-high DAC costs were used, but they also conclude that ag removals are reversible based on politics whereas geologic storage is not reversible. the too-high costs scenarios are described in this quote, “In this analysis, we assumed three DACS cost trajectories consistent with estimates starting at $500, $750, and $1000 Mg-1 CO2-e in 2025 and declining to $150, $250, and $500 Mg-1 CO2-e.”
Mayer, Hausfather et al., Cost of cooling – The value of reversible carbon storage in a zero-emissions world, CDRXIBV, April 29, 2025.
https://cdrxiv.org/preprint/348

April 16, 2021 – Lit review of air capture costs… Includes APS 2011. IPCC scenarios 1.5 C, 10 Gt by 2050, 20 Gt thereafter. Includes learning by doing that drives down costs. Details on Carbon Engineering, Climeworks and Global Thermostat, plus solid sorbents. this review makes no assumptions about costs, it just reviews them. But they include APS 2011 and MIT 2011, which biases the interpretation of costs high.
McQueen et al., A review of direct air capture DAC scaling up commercial technologies and innovating for the future, Progress in Energy, April 16, 2021.
https://iopscience.iop.org/article/10.1088/2516-1083/abf1ce/pdf

 

Hansen’s 2.2 to $4.5 trillion dollar per year atmospheric removal costs are overestimated by 3.67 times…

Hansen’s Error… James Hansen has made a critical error in his assumptions about the cost of air capture. Because Hasnen is such a powerful authority figure in climate science, this biases our climate culture negatively, into believing that air capture costs are much greater than they actually are.  the proof is in industry’s embracing air capture to receive the IRS 45Q carbon capture incentive, where over 200, 1-million ton per year removal units have been committed.  The details of Hansen’s error are presented below:

Hansen’s  says carbon capture costs are four times greater than reality at “$2.2-4.5 trillion dollars per year” – Reference 116, Hansen 2025… Hansen  assumes the evaluation of air capture costs of Keith 2018 is nearly four times higher than Keith 2018 says it is based on a simple error. Hansen assumed Keith’s numbers were for capture of carbon (C). They were not. Keith 2018 appropriately assumed capture of CO2. This resulting misinterpretation in Hansen’ costs citation for Keith 2018 as being 3.667 times higher than Keith 2018.
Hansen et al., Global Warming Has Accelerated: Are the United Nations and the Public Well-Informed?, Environment, Science an Policy for Sustainable Dev, February 3, 2025.
https://www.tandfonline.com/doi/full/10.1080/00139157.2025.2434494

Hansen 2025 cost of air capture error quote… “The estimated annual cost of CO2 extraction is now $2.2- 4.5 trillion dollars per year,116” Reference 116 is from a Hansen and Kharecha 2018 quote, “Assuming empirical cost estimates of 451-924 TnUS$/tC, based on a pilot direct-air CO2 capture plant.
Hansen and Kharecha, “Cost of carbon capture: Can young people bear the burden?, Joule, August 15, 2018.
https://www.sciencedirect.com/science/article/pii/S2542435118303465 

Here is Hansen and Kharecha’s Errored Explanation…
“Keith et al.6 built a pilot plant capturing CO2, which provides the best basis so far for estimating the cost of CO2 extraction. Their estimated cost range is $94–$232/tCO2, where tCO2 is metric tons of CO2. This cost appears to be much lower than estimates in an earlier study.7 However, it would be a grave misconception to think that the Keith study provides hope for a ‘‘get out of jail free card’’ for the climate problem. First, note that the $94/tCO2 estimate applied only to a case in which CO2 was processed to a point of being ready for use in production of a carbon-based fuel. That use of the CO2 does not result in negative emissions when the fuel is burned. Keith’s cost estimate for cases in which extracted CO2 is prepared for storage is $113–$232/tCO2. the range is based on cost of energy of natural gas at $0.03 kWh and $0.05 kWh. This creates a scenario bias its own as the lowest cost energy today is renewables at $0.01kWh with no carbon penalty for burning natural gas as fuel. SEe the Scenario Evaluationj of Keith 2018 in the next section for more.

Second, note that Keith does not include the cost of CO2 storage, which has been estimated 7 as $10–$20/ tCO2. Inclusion of storage makes the cost estimate for carbon capture and storage (CCS) $123–$252/tCO2. Finally, note that costs are often discussed in units of $/tC, where tC is tons of carbon.

Keith 2018 does not use cost per ton C. The following are quotes refuting this claim…
– From Keith 2018, summary image, “When CO2 is delivered at 15 MPa, the design requires either 8.81 GJ of natural gas, or 5.25 GJ of gas and 366 kWhr of electricity, per ton of CO2 captured. Levelized cost per t-CO2 from atmosphere ranges from 94 to 232 $/t-CO2.”
– From Keith 2018 summary, “When CO2 is delivered at 15 MPa, the design requires either 8.81 GJ of natural gas, or 5.25 GJ of gas and 366 kWhr of electricity, per ton of CO2 captured. Levelized cost per t-CO2 from atmosphere ranges from 94 to 232 $/t-CO2.”
– Table 2 also shows inputs and outputs with consts ranging from $94 to $232 “levelized ($/t-CO2)”
– $94 to $232 ton CO2 is also mentioned in the Comparison with Prior Estimates section, “The most influential prior estimate of DAC costs was provided by a 2011 American Physical Society (APS) study.4 The study estimated the cost of an aqueous Calooping technology like that presented here. The APS ‘‘realistic’’ case had costs of 780 $/t-CO2-avoided and 550 $/t-CO2-captured, where the ‘‘avoided’’ value includes emission from electricity supply outside the plant boundary. Our cost range is 94–232 $/t-CO2 captured, and if we use the financial and gas price assumptions of the APS (CRF = 12% and 6 $/GJ), then our costs would be 107–249 $/t-CO2 for the A and B variants in Table 2.”

Keith 2018’s scenario bias

David Keith’s paper evaluates the 1,000 ton per year Carbon Engineering direct air capture (DAC) process in Squamish British Columbia, where he scaled the process using existing industrial components with known scaling factors to 1 million tons per year, and includes upstream and process emissions. This recyclable lime-potash process is what is being used for the majority of the 200+, 1 million ton per year DAC units committed under the Inflation Reduction Act’s IRS 45Q’s carbon sequestration incentive of $85 ton for enhanced oil recovery and $180 ton for direct sequestration. Keith’s costs of $94 to $232 per ton CO2 captured are biased high because of energy choice assumptions. A researcher cannot evaluate all possible scenarios, so they chose a few and move on. The challenge then is that interpreters of research often do not take into consideration that scenarios different than those in any particular piece of research, produce different outcomes. The cost of renewable energy today is $0.01 kWh and one third of Keith’s $0.03 kWh natural gas scenario.  With energy being 87 percent of Keith’s process costs, a renewable energy scenario creates a huge difference in cost per ton of removal.

  • Keith’s 2018 is based on scaling the 1Kt annual Squamish British Columbia demonstration to 1 Mt using existing industrial components with known scaling factors and includes capital costs.
  • The $94 to $232 per ton range reflects the low and high energy costs of natural gas at the time of $0.03 kWh to $0.06 kWh.
  • 87 percent of process costs are energy.
  • Costs include upstream emissions and the carbon penalty to remove the carbon emitted from burning the natural gas to create the energy to run the process.
  • Latest wind and solar costs at utility scale are now at $0.01 kWh.
  • Lowest natural gas price is $2/GJ.
  • With lowest cost natural gas and renewable energy today, of $2/GJ natural gas and $0.01 kWh renewable electricity, costs are $44.64 per ton.
    Process refinements reduce costs further.
  • Scaling beyond 1 Mt per year reduces costs further dependent upon the amount of scaling.

Cost reduction for cheaper energy with $94/ton Scenario
60/40 natural gas/electricity energy requirement
60% natural gas is $56.4 *($2.0 per GJ/$3.5 per GJ = 0.57)  = $32.22
40% electricity $37.6**($0.01 kWh/$0.03 kWh = 0.33)        = $12.40
Total per ton with cheapest energy = $44.64

What will likely happen with costs? Because almost all air capture will be done by the fossil fuel industrial complex, their energy costs with natural gas -to them as producers- is almost free. So all the energy for air capture will come from natural gas, where the 10 percent carbon penalty for burning additional fossil fuels will be made up scaling the process another 10 percent.

Keith et al., A Process for Capturing CO2 from the Atmosphere, Joule, August 15, 2018.
https://www.sciencedirect.com/science/article/pii/S2542435118302253

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