How green is blue hydrogen?
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1 INTRODUCTION
Hydrogen is widely viewed as an important fuel for a future energy transition. Currently, hydrogen is used mostly by industry during oil-refining and synthetic nitrogen fertilizer production, and little is used for energy because it is expensive relative to fossil fuels.1 However, hydrogen is increasingly being promoted as a way to address climate change, as indicated by a recent article in the New York Times.2 In this view, hydrogen is to be used not only for hard to decarbonize sectors of the economy such as long-distance transportation by trucks and airplanes but also for heating and cooking, with hydrogen blended with natural gas and distributed to homes and business through existing pipeline systems.2 Utilities are also exploring the use of hydrogen, again blended with natural gas, to power existing electric generating facilities.3 In Europe, a recent report from Gas for Climate, an association of natural gas pipeline companies, envisions large scale use of hydrogen in the future for heating and electricity generation.4 The Hydrogen Council, a group established in 2017 by British Petroleum, Shell, and other oil and gas majors, has called for heating all homes with hydrogen in the future.5
The vast majority of hydrogen (96%) is generated from fossil fuels, particularly from steam methane reforming (SMR) of natural gas but also from coal gasification.6 In SMR, which is responsible for approximately three quarters of all hydrogen production globally,7 heat and pressure are used to convert the methane in natural gas to hydrogen and carbon dioxide. The hydrogen so produced is often referred to as “gray hydrogen,” to contrast it with the “brown hydrogen” made from coal gasification.8 Production of gray hydrogen is responsible for 6% of all natural gas consumption globally.7 Hydrogen can also be generated by electrolysis of water. When such electricity is produced by a clean, renewable source, such as hydro, wind, or solar, the hydrogen is termed “green hydrogen.” In 2019, green hydrogen was not cost competitive with gray hydrogen,9 but that is changing as the cost of renewables is decreasing rapidly and electrolyzers are becoming more efficient. Still, the supply of green hydrogen in the future seems limited for at least the next several decades.2, 5
Greenhouse gas emissions from gray hydrogen are high,10, 11 and so increasingly the natural gas industry and others are promoting “blue hydrogen”.5, 8, 9 Blue hydrogen is a relatively new concept and can refer to hydrogen made either through SMR of natural gas or coal gasification, but with carbon dioxide capture and storage. As of 2021, there were only two blue-hydrogen facilities globally that used natural gas to produce hydrogen at commercial scale, as far as we can ascertain, one operated by Shell in Alberta, Canada, and the other operated by Air Products in Texas, USA.12 Often, blue hydrogen is described as having zero or low greenhouse gas emissions.8, 9 However, this is not true: not all of carbon dioxide emissions can be captured, and some carbon dioxide is emitted during the production of blue hydrogen.1 Further, to date no peer-reviewed analysis has considered methane emissions associated with producing the natural gas needed to generate blue hydrogen.1 Methane is a powerful greenhouse gas. Compared mass-to-mass, it is more than 100-times more powerful as a warming agent than carbon dioxide for the time both gases are in the atmosphere and causes 86-times the warming as carbon dioxide over an integrated 20-year time frame after a pulsed emission of the two gases. Approximately 25% of the net global warming that has occurred in recent decades is estimated to be due to methane.13 In a recent report, the United Nations Environment Programme concluded that methane emissions globally from all sources need to be reduced by 40%-45% by 2030 in order to achieve the least cost pathway for limiting the increase in the Earth's temperature to 1.5°C, the target set by COP 21 in Paris in December 2015.14
Here, we explore the full greenhouse gas footprint of both gray and blue hydrogen, accounting for emissions of both methane and carbon dioxide. For blue hydrogen, we focus on that made from natural gas rather than coal, that is gray hydrogen combined with carbon capture and storage. In China, brown hydrogen from coal now dominates over gray hydrogen from natural gas, due to the relative prices of natural gas and coal, but globally and particular in Europe and North America, gray hydrogen dominates.1
2 ESTIMATING EMISSIONS FROM PRODUCING GRAY HYDROGEN
Greenhouse gas emissions from the production of gray hydrogen can be separated into two parts: (a) the SMR process in which methane is converted to carbon dioxide and hydrogen; and (b) the energy used to generate the heat and high pressure needed for the SMR process. For blue hydrogen, which we discuss later in this paper, emissions from the generation of electricity needed to run the carbon dioxide capture equipment must also be included. In this analysis, we consider emissions of only carbon dioxide and methane, and not of other greenhouse gases such as nitrous oxide that are likely to be much smaller. For methane, we consider the major components of its lifecycle emissions associated with the mining, transport, storage, and use of the natural gas needed to produce the hydrogen and power carbon capture. Emissions are expressed per unit energy produced when combusting the hydrogen, to aid in comparing the greenhouse gas footprint with other fuels.15, 16 In this paper, we use gross calorific values.
We start by estimating how much methane is consumed and how much carbon dioxide is produced in the two aspects of production of gray hydrogen. From this information, we can subsequently below estimate emissions of unburned methane.
2.1 Consumption of methane and production of carbon dioxide in SMR process
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Gray H2 | Blue H2 (w/o flue-gas capture) | Blue H2 (w/flue-gas capture) | |
---|---|---|---|
SMR process | |||
CH4 consumed (g CH4/MJ) | 14.0 | 14.0 | 14.0 |
CO2 produced (g CO2/MJ) | 38.5 | 38.5 | 38.5 |
Fugitive CH4 emissions (g CH4/MJ) | 0.49 | 0.49 | 0.49 |
Fugitive CH4 emissions (g CO2eq/MJ) | 42.1 | 42.1 | 42.1 |
Direct CO2 emissions (g CO2/MJ) | 38.5 | 5.8 | 5.8 |
CO2 capture rate | 0% | 85% | 85% |
Energy to drive SMR | |||
CH4 consumed (g CH4/MJ) | 11.6 | 11.6 | 11.6 |
CO2 produced (g CO2/MJ) | 31.8 | 31.8 | 31.8 |
Fugitive CH4 emissions (g CH4/MJ) | 0.41 | 0.41 | 0.41 |
Fugitive CH4 emissions (g CO2eq/MJ) | 35.3 | 35.3 | 35.3 |
Direct CO2 emissions (g CO2/MJ) | 31.8 | 31.8 | 11.1 |
CO2 capture rate | 0% | 0% | 65% |
Energy to power carbon capture | |||
CH4 consumed (g CH4/MJ) | 0 | 3.0 | 6.0 |
CO2 produced (g CO2/MJ) | 0 | 8.2 | 16.3 |
Fugitive CH4 emissions (g CH4/MJ) | 0 | 0.11 | 0.21 |
Fugitive CH4 emissions (g CO2eq/MJ) | 0 | 9.5 | 1 |
Direct CO2 emissions (g CO2/MJ) | 0 | 8.2 | 16.0 |
Indirect upstream CO2 emissions (g CO2/MJ) |
5.3 |
5.9 |
6.5 |
Total CH4 consumed (g CH4/MJ) |
25.6 |
28.6 |
31.6 |
Total CO2 emitted (g CO2/MJ) |
75.6 | 51.7 | 39.7 |
Total fugitive CH4 emissions (g CO2eq/MJ) | 77.4 | 86.9 | 95.4 |
Total emissions (g CO2eq/MJ) | 153 | 139 | 135 |
Note
- The methane leakage rate is 3.5%.
With a molecular weight of 16.04 g per mole, 14.04 g CH4 per MJ is consumed during the SMR process (Table 1). There is essentially no uncertainty in these estimates of how much methane is consumed, and how much carbon dioxide is produced during the SMR process: the relationship is set by the chemical stoichiometry shown in Equation (1).
2.2 Consumption of methane and production of carbon dioxide from energy needed to drive SMR process
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That is, 0.1814 MJ of energy from burning methane is required per mole of hydrogen produced. When burning natural gas for heat, 50 g CO2 per MJ in emissions are produced, using gross calorific values.19 Note that higher carbon dioxide emission values are reported when using net calorific values.
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See Table 1.
2.3 Total carbon dioxide and methane emissions for gray hydrogen
The sum of the carbon dioxide from the SMR process (38.5 g CO2 per MJ) and from the energy used to generate the heat and electricity for the SMR (31.8 g CO2 per MJ) is 70.3 g CO2 per MJ. Additionally, it takes energy to produce, process, and transport the natural gas used to generate the hydrogen. Using the analysis of Santoro et al.20 as reported in Howarth et al,21 these indirect upstream emissions are approximately 7.5% of the direct carbon dioxide emissions for natural gas, or an additional 5.3 g CO2 per MJ (7.5% of 70.3 g CO2 per MJ). Therefore, the total quantity of carbon dioxide produced is 75.6 g CO2 per MJ (Table 1).
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The sum of emissions of carbon dioxide (75.6.0 g CO2 per MJ) and unburned methane (77.4 g CO2eq per MJ) for the production of gray hydrogen is 153 g CO2eq per MJ (Table 1).
There are remarkably few published peer-reviewed papers with which to compare our estimate. Many non peer-reviewed reports give estimates for carbon dioxide emission from gray hydrogen that are in the range of 10 tons carbon dioxide per ton of hydrogen,1, 7 although data in support of these values are generally absent, perhaps because they are based on confidential information.11 Since the gross calorific heat energy content of hydrogen is 0.286 MJ per mole,17 10 tons of carbon dioxide per ton of hydrogen corresponds to 70 g CO2 per MJ. This is similar to but somewhat lower than our value of 75.6 g CO2 per MJ. Most of these non peer-reviewed reports do not include methane in their estimates,1 or if they do, they provide no detail as to how they do so. The most thorough peer-reviewed analysis of carbon dioxide emissions for gray hydrogen is that of Sun et al11 who obtained data on both rates of hydrogen production and emissions of carbon dioxide from many individual facilities across the United States. They concluded that on average, carbon dioxide emissions for gray hydrogen are 77.8 g CO2 per MJ, remarkably close to our value of 75.6 g CO2 per MJ. They did not estimate methane emissions.
3 ESTIMATING EMISSIONS FOR BLUE HYDROGEN
Blue hydrogen differs from gray hydrogen in that, with blue hydrogen, some of the carbon dioxide released by the SMR process is captured. In another version of the blue-hydrogen process, additional carbon dioxide is removed from the flue gases created from burning natural gas to provide the heat and high pressure needed to drive the SMR process. A third set of emissions, not usually captured, is the carbon dioxide and methane from the energy used to produce the electricity for the carbon-capture equipment.
3.1 How much carbon dioxide is emitted after carbon capture?
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That is, 5.8 g CO2 per MJ are emitted from the SMR process after emissions are treated for carbon capture (Table 1).
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Therefore, total carbon dioxide emissions from the SMR process, including the energy used to drive the process, are in the range of 16.9 g CO2 per MJ if the combustion flue is captured (5.8 g CO2 per MJ plus 11.1 g CO2 per MJ) to 37.6 g CO2 per MJ (5.8 g CO2 per MJ plus 31.8 g CO2 per MJ) if the flue gases are not treated (Table 1).
3.2 Consumption of methane and production of carbon dioxide from electricity used to capture carbon dioxide
Energy is required to capture the carbon dioxide, and often this is provided by electricity generated from burning additional natural gas.7 The existing blue-hydrogen facilities make no effort to capture the carbon dioxide from the fuel burned to generate this electricity, nor has there been any effort to do so in the case of carbon capture from coal-burning power plants.31 Often, an energy penalty of 25% is assumed for this additional electricity.34-36 However, this estimate is based on very little publicly available, verifiable information and may be optimistically low. A recent analysis of carbon capture from the flue gases of a coal-burning power plant, where the electricity for carbon capture came from a dedicated natural gas plant, found that the carbon dioxide emissions from the natural gas were 39% of the carbon dioxide captured from the coal-flue gases.31 Carbon dioxide is more concentrated in the gases produced through SMR than in the flue exhaust from combustion, suggesting that it can be captured more easily.
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That is, emissions from the energy used to drive the carbon captured from the SMR process are themselves an additional 8.2 g CO2 per MJ (Table 1).
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Therefore, the carbon dioxide emissions from the energy used to drive the carbon capture is between 8.2 g CO2 per MJ if only emissions from the SMR process are captured or an additional 8.1 g CO2 per MJ for a total of 16.3 g CO2 per MJ if emissions from the energy source used for heat and pressure are also captured (Table 1).
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Therefore, the quantify of methane used to drive carbon capture when the flue gases from the combustion of the gas used to generate heat and pressure for the SMR process are 3.0 g CH4 per MJ plus 3.0 g CH4 per MJ, for a total of 6.0 g CH4 per MJ when carbon capture is applied both to SMR and exhaust flue gases (Table 1).
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Therefore, upstream emissions of unburned methane from the energy used to drive carbon capture are between 9.5 g CO2eq per MJ if only the SMR carbon is captured and 18 g CO2eq per MJ if the flue-gas emissions are also captured (Table 1).
3.3 Total carbon dioxide and methane emissions for blue hydrogen
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To summarize, when only the carbon from the SMR process itself is captured, total emissions of carbon dioxide are 51.7 g CO2 per MJ. When efforts are also taken to capture the carbon dioxide from the flue exhaust from the energy driving the reforming process, total carbon dioxide emissions are 39.7 g CO2 per MJ (Table 1). Treating the exhaust flue gases for carbon capture reduces total lifecycle emissions of carbon dioxide by 23%, less than might have been expected. This is due both to a relatively low efficiency for the carbon capture of flue gases31 and to the increased combustion of natural gas needed to provide the electricity for the carbon capture.
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We are aware of no previously published, peer-reviewed analyses on either total carbon dioxide or methane emissions associated with producing blue hydrogen. Several non peer-reviewed reports suggest that it may be possible to reduce carbon dioxide emissions for blue hydrogen by 56% (when only the SMR process is treated) to 90% (when exhaust flue gases are also treated) relative to gray hydrogen.1, 7 However, no data have been presented to support these estimates, and they apparently do not include emissions associated with the energy needed to drive carbon capture. Our results using a full lifecycle assessment show the 56% to 90% assumptions are too optimistic.
In Figure 1, we compare the greenhouse gas footprint of gray hydrogen with blue hydrogen where only the SMR process is captured and with blue hydrogen where carbon capture is also used for the exhaust flue gases. Because of the increased methane emissions from increased use of natural gas when flue gases are treated for carbon capture, total greenhouse gas emissions are only very slightly less than when just the carbon dioxide from the stream reforming process is treated, 135 vs 139 g CO2eq per MJ. In both cases, total emissions from producing blue hydrogen are only 9% to 12% less than for gray hydrogen, 135 or 139 g CO2eq per MJ compared with 153 g CO2eq per MJ. Blue hydrogen is hardly “low emissions.” The lower, but nonzero, carbon dioxide emissions from blue hydrogen compared with gray hydrogen are partially offset by the higher methane emissions. We further note that blue hydrogen as a strategy only works to the extent it is possible to store carbon dioxide long term indefinitely into the future without leakage back to the atmosphere.
![Details are in the caption following the image Details are in the caption following the image](https://onlinelibrary.wiley.com/cms/asset/563a021f-348a-448a-8fba-dc703d0bfd9b/ese3956-fig-0001-m.png)
4 COMPARISON OF EMISSIONS WITH OTHER FUELS AND SENSITIVITY ANALYSES
4.1 Emissions for fossil fuels
In Figure 1, we also compare greenhouse gas emissions from gray and blue hydrogen with those for other fuels per unit of energy produced when burned. The carbon dioxide emissions shown for coal, diesel oil, and natural gas include both direct and indirect emissions. The direct emissions are based on gross calorific values from EIA.19 Indirect emissions are those required to develop and process the fuels and are based on Howarth et al.21 These indirect carbon dioxide emissions are 4 g CO2 per MJ for coal, 8 g CO2 per MJ, and 3.8 g CO2 per MJ for natural gas. Upstream fugitive emissions of unburned methane are assumed to be 3.5% for natural gas, as we have assumed for the hydrogen estimates. Methane emissions for coal and diesel oil are as presented in Howarth24: 0.185 g CH4 per MJ for coal and 0.093 g CH4 per MJ for diesel oil, corresponding to 8.0 and 15.9 4 g CO2eq per MJ respectively based on a 20-year GWP of 86.
Combined emissions of carbon dioxide and methane are greater for gray hydrogen and for blue hydrogen (whether or not exhaust flue gases are treated for carbon capture) than for any of the fossil fuels (Figure 1). Methane emissions are a major contributor to this, and methane emissions from both gray and blue hydrogen are larger than for any of the fossil fuels. This reflects the large quantities of natural gas consumed in the production of hydrogen. Carbon dioxide emissions are less from either gray or blue hydrogen than from coal or diesel oil. Carbon dioxide emissions from blue hydrogen are also less than from using natural gas directly as a fuel, but not substantially so. Carbon dioxide emissions from gray hydrogen are somewhat larger than from natural gas (Figure 1).
4.2 Sensitivity analyses for methane emissions
Given the importance of methane emissions to the greenhouse gas footprints of gray and blue hydrogen, we here present sensitivity analyses on our estimates. We separately consider different rates of fugitive methane emissions and different assigned GWP values.
Our default value for methane emissions used above for gray hydrogen, blue hydrogen, and natural gas is 3.5% of consumption. As noted above, this is based on top–down estimates for emissions from 20 different studies in 10 different gas fields plus a top–down estimate for emissions from gas transport and storage.16 This is very close to an independent estimate of emissions from shale gas production and consumption estimated from global trends in the 13C stable isotopic composition of methane in the atmosphere since 2005.37 For the sensitivity analysis, we also evaluate one higher rate and two lower rates of methane emission. The higher rate is from the high-end sensitivity analysis for shale gas emissions based on the global 13C data, or 4.3% of consumption.37 The lower rates we analyze are 2.54% and 1.45% of consumption. The 2.54% value is based on Alvarez et al22 who used “bottom–up” approaches to estimate the upstream and midstream methane emissions for natural gas in the United States as 12.7 Tg per year in 2015. This is 2.54% of consumption, based on annual gas consumption for 2015 of 771 billion m3 of natural gas in the United States,26 assuming methane comprises 93% of the volume of gas.38 The bottom–up approach presented by Alvarez et al22 likely underestimates methane emissions.24, 39, 40 We also consider an even lower estimate based on Maasakkers et al.41 Using an inverse model in combination with satellite data and the US EPA methane emissions inventory, they concluded that methane emissions from natural gas operations in the United States were 8.5 T per year in 2012. This is 1.45% of gas consumption, based on again assuming methane is 93% of gas and a national US consumption of gas of 723 billion m3 in 2012.26
Our baseline analysis is based on a 20-year GWP value of 86.13 There is uncertainty in this estimate, so here we also explore the higher 20-year GWP value of 105 presented in Shindell et al.42 Most traditional greenhouse gas inventories use a 100-year GWP, so we explore that as well, using the latest value from the IPCC13 synthesis report of 34. However, the IPCC13 noted that the use of a 100-year time period is arbitrary. We prefer the use of 20-year GWP, since it better captures the role of methane as a driver of climate change over the time period of the next several decades, and the 100-year time frame discounts the importance of methane over these shorter time frames.15, 24
In our sensitivity analyses, we substitute emission rates of 4.3%, 2.54%, and 1.54% for our baseline value of 3.5% in Equations 9, 17, and 18 for gray and blue hydrogen and in our estimate for natural gas presented in Figure 1. We also substitute a 20-year GWP value of 105 and a 100-year GWP value of 34 for the 20-year GWP of 86 used in Equations 10, 19, and 20. The sensitivity estimates are shown in Table 2. Across the full set of assumptions, both gray hydrogen and blue hydrogen without flue-gas capture (where only the carbon dioxide from SMR is captured) always have greater emissions than natural gas. The differences between the greenhouse gas footprint of blue hydrogen with or without the capture of carbon dioxide from the exhaust flue gases are generally small across all assumptions concerning fugitive methane emissions, with the total greenhouse gas emissions without the flue-gas treatment usually higher. The emissions from blue hydrogen with full carbon capture including the exhaust flue gases are higher than for natural gas across all set of assumptions except for the analysis with the 100-year GWP of 34 and low methane emissions, 2.54% or less (Table 2).
Gray H2 | Blue H2 (w/o flue-gas capture) | Blue H2 (w/flue-gas capture) | Natural gas | |
---|---|---|---|---|
Fugitive CH4 = 3.5% | ||||
GWP20 = 8 | 153 | 139 | 135 | 111 |
GWP20 = 105 | 170 | 158 | 155 | 123 |
GWP100 = 34 | 106 | 86 | 77 | 76 |
Fugitive CH4 = 4.3% | ||||
GWP20 = 86 | 171 | 159 | 156 | 124 |
GWP20 = 105 | 192 | 182 | 181 | 139 |
GWP100 = 34 | 113 | 94 | 86 | 81 |
Fugitive CH4 = 2.54% | ||||
GWP20 = 86 | 133 | 115 | 109 | 95 |
GWP20 = 105 | 144 | 129 | 124 | 104 |
GWP100 = 34 | 98 | 76 | 67 | 70 |
Fugitive CH4 = 1.54% | ||||
GWP20 = 86 | 110 | 90 | 82 | 79 |
GWP20 = 105 | 117 | 98 | 91 | 84 |
GWP100 = 34 | 89 | 67 | 57 | 64 |
We also evaluate the sensitivity of our conclusions to the percentage of carbon dioxide that is captured from SMR and from the flue exhaust from the natural gas burned to power the SMR process. Our default values presented above are for 85% capture from the SMR process and 65% capture from the flue gases, if an effort were made to capture those. Our sensitivity analysis includes a low estimate for SMR capture of 78.8% based on actual data from one commercial blue-hydrogen plant30 and a high estimate of 90%, the highest yet reported.31 For capture of the flue gases, we explore carbon dioxide capture efficiencies of 55% at the low end and 90% at the high-end based on actual facility performance for flue gases from coal-burning electric plants.31-33 Note that the 90% rate is the best ever observed and does not reflect likely actual performance under long-term commercial operations. We present the results of this sensitivity analysis in Table 3. Perhaps surprisingly, our conclusions are very insensitive to assumptions about carbon dioxide capture rates. This is because capture is very energy intensive: to capture more carbon dioxide takes more energy, and if this energy comes from natural gas, the emissions of both carbon dioxide and fugitive methane emissions from this increase in such proportion as to offset a significant amount of the reduction in carbon dioxide emission due to the carbon capture.
Total CO2 | Total fugitive CH4 | Total emissions | |
---|---|---|---|
Blue H2 w/o flue-gas capture | |||
85% SMR capture | 51.7 | 86.9 | 139 |
90% SMR capture | 50.2 | 86.9 | 137 |
78.8% SMR capture | 53.5 | 85.7 | 139 |
Blue H2 w/flue-gas capture | |||
85% SMR & 65% flue-gas capture | 39.7 | 95.4 | 135 |
90% SMR & 90% flue-gas capture | 33.3 | 98.9 | 132 |
78.8% SMR & 55% flue-gas capture | 43.4 | 93.2 | 137 |
Note
- The methane leakage rate is 3.5%. The first row in each case is from the baseline case in Table 1.
These sensitivity analyses show that our overall conclusion is robust: the greenhouse gas footprint of blue hydrogen, even with capture of carbon dioxide from exhaust flue gases, is as large as or larger than that of natural gas.
5 IS THERE A PATH FOR TRULY “GREEN” BLUE HYDROGEN?
Some of the CO2eq emissions from blue hydrogen are inherent in the extraction, processing, and use of natural gas as the feedstock source of methane for the SMR process: fugitive methane emissions and upstream emissions of carbon dioxide from the energy needed to produce, process, and transport the natural gas that is reformed into hydrogen are inescapable. On the other hand, the emissions of methane and carbon dioxide from using natural gas to produce the heat and high pressure needed for SMR and to capture carbon dioxide could be reduced if these processes were instead driven by renewable electricity from wind, solar, or hydro. If we assume essentially zero emissions from the renewable electricity, then carbon dioxide emissions from blue hydrogen could be reduced to the 5.8 g CO2 per MJ that is not captured from the SMR process (Equation 11) plus the indirect emissions from extracting and processing the natural gas used as feedstock for the SMR process, estimated as 2.9 g CO2 per M (7.5% of 38.5 g CO2 per MJ; see section on “total carbon dioxide and methane emissions for gray hydrogen”), for a total of 8.7 g CO2 per MJ. This is a substantial reduction compared with using natural gas to power the production of blue hydrogen. However, the fugitive methane emissions associated with the natural gas that is reformed to hydrogen would remain if the process is powered by 100% renewable energy. These emissions are substantial: 3.5% of 14 g CH4 per MJ (Equation 3). Using the 20-year GWP value of 86, these methane emissions equal 43 g CO2eq per MJ of hydrogen produced. The total greenhouse gas emissions, then, for this scenario of blue hydrogen produced with renewable electricity are 52 g (8.7 g plus 43 g) CO2eq per MJ. This is not a low-emissions strategy, and emissions would still be 47% of the 111 g CO2eq per MJ for burning natural gas as a fuel, using the same methane emission estimates and GWP value (Table 1). Seemingly, the renewable electricity would be better used to produce green hydrogen through electrolysis.
This best-case scenario for producing blue hydrogen, using renewable electricity instead of natural gas to power the processes, suggests to us that there really is no role for blue hydrogen in a carbon-free future. Greenhouse gas emissions remain high, and there would also be a substantial consumption of renewable electricity, which represents an opportunity cost. We believe the renewable electricity could be better used by society in other ways, replacing the use of fossil fuels.
Similarly, we see no advantage in using blue hydrogen powered by natural gas compared with simply using the natural gas directly for heat. As we have demonstrated, far from being low emissions, blue hydrogen has emissions as large as or larger than those of natural gas used for heat (Figure 1; Table 1; Table 2). The small reduction in carbon dioxide emissions for blue hydrogen compared with natural gas are more than made up for by the larger emissions of fugitive methane. Society needs to move away from all fossil fuels as quickly as possible, and the truly green hydrogen produced by electrolysis driven by renewable electricity can play a role. Blue hydrogen, though, provides no benefit. We suggest that blue hydrogen is best viewed as a distraction, something than may delay needed action to truly decarbonize the global energy economy, in the same way that has been described for shale gas as a bridge fuel and for carbon capture and storage in general.43 We further note that much of the push for using hydrogen for energy since 2017 has come from the Hydrogen Council, a group established by the oil and gas industry specifically to promote hydrogen, with a major emphasis on blue hydrogen.5 From the industry perspective, switching from natural gas to blue hydrogen may be viewed as economically beneficial since even more natural gas is needed to generate the same amount of heat.
We emphasize that our analysis in this paper is a best-case scenario for blue hydrogen. It assumes that the carbon dioxide that is captured can indeed be stored indefinitely for decades and centuries into the future. In fact, there is no experience at commercial scale with storing carbon dioxide from carbon capture, and most carbon dioxide that is currently captured is used for enhanced oil recovery and is released back to the atmosphere.44 Further, our analysis does not consider the energy cost and associated greenhouse gas emissions from transporting and storing the captured carbon dioxide. Even without these considerations, though, blue hydrogen has large climatic consequences. We see no way that blue hydrogen can be considered “green.”
ACKNOWLEDGMENTS
This research was supported by a grant from the Park Foundation and by an endowment given by David R. Atkinson to Cornell University that supports Robert Howarth. We thank Dominic Eagleton, Dan Miller, and two anonymous reviewers for their valuable feedback on earlier drafts of this paper.
Fonte: https://onlinelibrary.wiley.com/doi/full/10.1002/ese3.956