日韩福利电影在线_久久精品视频一区二区_亚洲视频资源_欧美日韩在线中文字幕_337p亚洲精品色噜噜狠狠_国产专区综合网_91欧美极品_国产二区在线播放_色欧美日韩亚洲_日本伊人午夜精品

Search

Thermal Power

Wednesday
13 Nov 2019

Comparing 10 Carbon Capture Methods on Costs,Scalability,Permanence,Cleanness

13 Nov 2019  by Ella Adlen and Cameron Hepburn   

We need to understand carbon capture, storage and utilisation (CCUS) better. To do so, this article looks at 10 methods and estimates how much CO2 each will take out of the atmosphere by 2050, and the cost per tonne. In their list the authors, Ella Adlen and Cameron Hepburn at the University of Oxford, cover the industrial (e.g. CO2-EOR, synfuels) to the biological (e.g. forestry, soil carbon sequestration). They say there are six that can be cost competitive and profitable soon, even now: CO2 chemicals, concrete building materials, CO2- EOR, forestry, soil carbon sequestration, biochar. Four are not (yet?!): CO2 fuels, microalgae, bioenergy with CCS (BECCS), enhanced weathering. It matters because the closer each is to becoming a profitable business the sooner it will happen. The authors point out their costs are likely to be overestimates: predicting technological breakthroughs over future decades is far from easy. But, in a similar vein, there are large uncertainties too over scalability, the permanence of the capture, and the cleanness of the future energy mix being used to power certain methods. These uncertainties need to be resolved fast as there will be no successful Transition without successful CCUS.

Can we turn CO2, the waste gas largely responsible for global warming, into a valuable feedstock? The question first emerged in the oil crisis of the 1970s, when alternatives to scarce oil were being sought.

The idea has resurfaced on the wave of circular economic thinking, triggered by climate concerns and with a view towards incentivising carbon capture. But opinions on CO2 utilisation veer between scepticism and enthusiasm.

Poor understanding means poor strategy

New approaches are constantly arising. Claims of “CO2 avoided”, “CO2 removed” or “reduced CO2 emissions” are easily confusable, and corporations and governments are starting to invest in various candidate technologies without having the big picture to hand.

In a new Nature perspective, we set out to pin down what CO2 utilisation is, how it might relate to CO2 removals and emission reductions, and whether such technologies are profitable or scalable.

As a team, we represent economists, engineers, chemists, soil scientists and climate modellers – the whole spectrum of views on utilisation. Our study is the most comprehensive to date on the relative scale and costs of different ways to use CO2.

What is CO2 utilisation?

Conventionally, “CO2 utilisation” is an industrial process that makes an economically valuable product using CO2 at concentrations above atmospheric levels. CO2 is either transformed using chemical reactions into materials, chemicals and fuels, or it is used directly in processes such as enhanced oil recovery.

This definition has its historical reasons, but it is not the only kind of CO2 utilisation. For a long time, people have also been thinking about how to use natural carbon – carbon made by plants from atmospheric CO2 – as a feedstock to make valuable products. And CO2-using techniques, such as soil carbon sequestration, through their ability to enhance crop yields, can also make an economic product.

In our paper we look at 10 specific pathways of CO2 utilisation, best categorised by considerations of how easily the carbon flows around the Earth’s spheres and where it ends up, as shown in the figure below.

CO2 storage: Open, Closed and Cycling

This shows “open” utilisation pathways (purple arrows) that store CO2 in leaky natural systems, such as forests, which can turn from sink to source very quickly. “Closed” pathways (red), such as building materials, offer near permanent storage of CO2. Finally “cycling” utilisation (yellow), such as CO2-based fuels, which moves carbon around over short timescales.

Stocks and net flows (large light blue arrows) of CO2 around the human and natural world, including 10 numbered potential utilisation and removal pathways. These are marked with coloured arrows that denote whether carbon is stored in open systems (purple arrows) that can be sources or sinks of CO2, closed systems (red) for near-permanent storage or cycling pathways (yellow) that only temporarily shift carbon. Source: Hepburn et al. (2019).

Climate mitigation + economic gain

All ten CO2 utilisation pathways in our figure offer some kind of economic motivation, together with some degree of climate mitigation potential.

CO2 utilisation can help in two main ways: the removal and long-term storage of atmospheric CO2; and the reduction of CO2 emissions to the atmosphere. Potentially, using CO2 to make valuable products might also offset some of the costs of climate change mitigation.

Our estimates show that at the top end, over 10 billion tonnes of CO2 (GtCO2) a year could be utilised – compared to global emissions of 40GtCO2 – for less than $100 per tonne.

Most of that utilisation is associated with medium- or long- term storage in open and closed pathways. However, there are several problems and challenges to overcome before such large utilisation could be achieved.

CO2 utilisation doesn’t guarantee mitigation

Furthermore, even if CO2 utilisation were successful, that does not necessarily mean it would be beneficial for the climate. If done without due consideration, CO2 utilisation – in common with other approaches that remove and/or store CO2 – might not contribute to mitigation at all.

Possible problems include not just direct CO2 emissions, but also other greenhouse gas emissions; direct and indirect land-use change; emissions from other parts of the process; leakage (when emissions subsequently increase in other parts of the wider system); and impermanent displacement (when emissions are only delayed rather than avoided for good).

Because of these issues, whether the implementation of a CO2 utilisation technology will be climate-beneficial will depend on a host of factors. The most important of these are:

Energy source: CO2 utilisation technologies can be energy-intensive. This energy needs to be renewable: either directly from the sun, or via renewable technologies.

Broader decarbonisation context: Some of these technologies only make sense as mitigation strategies at certain points of the global decarbonisation process. For example, using enhanced oil recovery to sequester CO2 could be used in the short term before the energy and transport systems are decarbonised.

Scale: In order to make an appreciable difference to the global flows of CO2, pathways need to have the potential to scale quickly. The window for climate action is small and building an entirely new CO2 utilisation industry in the time needed is a non-trivial challenge.

Permanence: The most impactful technologies will be the ones that permanently remove atmospheric CO2 or permanently displace CO2 emissions.

The 10 pathways and their prospects…

Below, we compare the potential scale and cost of different CO2 utilisation pathways. Overall, CO2 utilisation has the potential to operate at large scale and at low cost, meaning it could be big business in the future.

The scale evaluations for 2050 come from a process of structured estimates, expert consultation and large scoping reviews. Our cost estimates are breakeven costs – meaning they take into account revenue – and are presented as the interquartile ranges from techno-economic studies collected from scoping reviews. This means that the costs are backward-looking and likely to underestimate the ability of the pathways to achieve economies of scale. Negative costs mean that the process is profitable under present day assumptions.

CO2 chemicals

Reducing CO2 to its constituent components using catalysts and using chemical reactions to build products, such as methanol, urea (to use as fertiliser) or polymers (for use as durable products in buildings or cars), could utilise 0.3 to 0.6GtCO2 a year in 2050, at costs of between -$80 to $300 per tonne of CO2.

CO2 fuels

Combining hydrogen with CO2 to produce hydrocarbon fuels, including methanol, synfuels, and syngas could address a huge market – for example, across existing transport infrastructure – but the present-day costs are high. Together, CO2 fuels could utilise 1 to 4.2GtCO2 a year in 2050, but costs are up to $670 per tonne of CO2.

Microalgae

Using microalgae to fix CO2 at high efficiencies and then processing the biomass to make products, such as fuels and high-value chemicals, has been the focus of research efforts for many years. With complex production economics, costs are between $230 and $920 per tonne of CO2, and 2050 utilisation rates could be 0.2 to 0.9GtCO2 per year.

Concrete building materials

CO2 can be used to “cure” cement, or in the manufacture of aggregates. Doing so stores some CO2 for the long term and could displace emissions-intensive conventional cement. With accelerating global urbanisation, but a challenging regulatory environment, we estimate a utilisation and storage potential of 0.1 to 1.4GtCO2 in 2050, with present day costs of between -$30 and $70 per tonne of CO2.

CO2-enhanced oil recovery (EOR)

Injecting CO2 into oil wells can increase the production of oil. Normally, operators maximise oil and CO2 recovered from the well, but, critically, it is possible to operate EOR so that more CO2 is injected and stored than is produced on consumption of the final oil product. We estimate that 0.1 to 1.8GtCO2 per year could be utilised and stored this way in 2050, at costs that are between -$60 and -$40 per tonne of CO2.

Bioenergy with carbon capture and storage (BECCS)

In bioenergy with carbon capture, the operator captures CO2 by growing trees, produces electricity through bioenergy and sequesters the resulting emissions. With a rough approximation of electricity revenues, we estimate utilisation costs of between $60 and $160 per tonne of CO2. Some 0.5 to 5GtCO2 per year could be utilised and stored this way in 2050. This is lower than some previously published estimates of BECCS and represents a level of deployment that is cognisant of other sustainability aims.

Enhanced weathering

Crushing rocks, such as basalt, and spreading them on land can result in the accelerated formation of stable carbonate from atmospheric CO2. It is likely that doing this on agricultural lands will result in enhanced yields. However, the very early-stage nature of this pathway means that we have not made 2050 estimates for it.

Forestry

Timber from both new and existing forests is an economically valuable product that could potentially store CO2 in buildings and, by doing so, displace cement use. We estimate that up to 1.5GtCO2 could be utilised in 2050 in this way, at costs of between -$40 and $10 per tonne CO2.

Soil carbon sequestration

Land management techniques for soil carbon sequestration can not only store CO2 in the soil but also enhance agricultural yields. We estimate that the CO2 utilised in the form of that increased output might be as much as 0.9 to 1.9GtCO2 per year in 2050, at costs of -$90 to -$20 per tonne CO2.

Biochar

Biochar is “pyrolysed” biomass: plant material that has been burnt at high temperatures under low oxygen levels. Biochar application to agricultural soils has the potential to increase crop yields by 10% – but it is very hard to make a consistent product or predict soil reactions. We estimate between 0.2 and 1GtCO2 could be utilised by biochar in 2050, at costs of around -$65 per tonne of CO2.

Capacity, costs compared

The summary figure below shows an estimate of how much CO2 could be used by each pathway (the width of each column) and the associated breakeven costs (height of the columns).

The low scenario (chart on the left) and the high one (right) reflect the range of outcomes depending on levels of investment, uptake and technological improvements by 2050. The shading refers to technological readiness, ranging from low or variable (pale shades) through to high (darker shades). The asterisks refer to the duration of CO2 storage ranging from days or months (single asterisk) through to centuries or more (triple asterisk).

Estimated CO2 utilisation potential (GtCO2 in 2050) and breakeven cost (2015$/tonne) of different sub-pathways in low (left) and high (right) scenarios. Conventional pathways in grey are industrial utilisation approaches; non-conventional pathways in green are biological utilisation approaches. TRL refers to technological readiness levels, which range between 1 and 9. SCS is soil carbon sequestration; EOR is enhanced oil recovery; BECCS is bioenergy with carbon capture; and DME is dimethyl ether (a type of CO2 fuel). These cost and scale potentials could change substantially with advances in R&D. Source: Hepburn et al. (2019).

The figure above shows that CO2 utilisation could generate significant flows of CO2 in 2050 – and that some pathways can be expected to be profitable in their own right. We think this could be an opportunity to leverage those flows for the purpose of climate change mitigation.

However, the charts also emphasise the large uncertainty over the scale of that potential and the likely costs of tapping into it. In order for CO2 utilisation to be successfully deployed in the fight against climate change, these uncertainties must be resolved alongside potential – and non-trivial – challenges, of which energy intensity and the permanence of carbon storage are just two.

More News

Loading……
欧美日韩一区二区高清| a毛片在线看免费观看| 黄色免费影视| 中文有码在线观看| 69视频在线观看| aaa大片在线观看| av在线小说| 天然素人一区二区视频| 日本一区二区三区电影免费观看 | 欧美日韩一区二区在线播放| 日韩欧美成人免费视频| 91精品国产欧美一区二区18| 男裸体无遮挡网站| 欧美亚洲日本| 超碰高清在线| 亚洲欧美日本国产| 久久久国产精品| 久久一区国产| 久久久精品免费网站| 亚洲超碰97人人做人人爱| 欧美日本韩国一区| 在线天堂日本| 在线观看免费视频你懂的| 成人黄色毛片| 四虎成人精品永久免费av九九| 激情欧美国产欧美| 成人午夜av电影| 午夜伊人狠狠久久| 亚洲成av人在线观看| 亚洲第一会所001| 红杏aⅴ成人免费视频| 99久久夜色精品国产亚洲96| 老司机午夜精品| 亚洲日本在线视频观看| 91精品国产高清一区二区三区蜜臀 | 国产亚洲精品久| 日韩一区电影| 国产精品一区二区黑丝| 亚洲第一狼人社区| 福利视频网站| av手机在线观看| 国产成人影院| 国产成人在线电影| 精品久久久精品| 啦啦啦啦免费高清视频在线观看1| a级片在线免费观看| 欧美精品momsxxx| 国产一区二区三区香蕉 | 男女啪啪在线观看| 91成人短视频| 久久激情五月激情| 欧美日韩久久久久| 天堂在线中文| 超碰cao国产精品一区二区| 一本综合精品| 亚洲精品高清在线| 在线免费看黄色| 欧美成人一二区| 国产精品主播| 五月天欧美精品| аⅴ资源新版在线天堂| 欧美亚洲国产日韩| 国产成人免费视频精品含羞草妖精| 欧美性猛交xxxx黑人| 91啦中文在线| 欧美自拍偷拍| 国产精品成人午夜| 色中色在线视频| 香蕉久久精品| 国产肉丝袜一区二区| 成年人黄视频网站| 韩国一区二区三区视频| 美女视频黄久久| 欧美精品日韩精品| 欧美xxx性| 老司机午夜精品| 欧美一级久久久久久久大片| 免费一二一二在线视频| 香蕉国产精品偷在线观看不卡| 亚洲h精品动漫在线观看| 国产裸舞福利在线视频合集| 九九综合久久| 中文字幕视频一区| 中文字幕一二三区在线观看| 亚瑟一区二区三区四区| 国产精品日韩成人| 国产九九在线| 激情综合激情| 欧美在线免费观看亚洲| 欧美gay视频| 国产精品66部| 116美女写真午夜一级久久| 特黄特色欧美大片| 亚洲欧美日韩国产中文在线| 好了av在线| 久久久久久久波多野高潮日日| 欧美精品亚洲一区二区在线播放| 欧美电影免费看| 福利电影一区二区三区| 日本在线аv| 国模精品一区| 亚洲成人激情av| 自拍偷拍亚洲视频| 国产一区不卡在线| 97影院在线观看| 久久一区91| 欧美三级资源在线| 国产精品igao视频网网址不卡日韩| 成人毛片视频在线观看| 日韩av资源| 国产视频欧美| 黄页在线播放| 欧美电影《轻佻寡妇》| 在线观看区一区二| 成人在线视频国产| 国产精品久久久久久久久快鸭| gogogogo高清视频在线| 黄页视频在线91| 日韩偷拍自拍| 麻豆久久精品| 午夜神马福利影院| 极品少妇一区二区三区| www.天天射| 婷婷激情图片久久| 欧美裸体一区二区三区| 网红女主播少妇精品视频| 精品久久久久久久久久久久| 成人污版视频| 夜夜精品视频一区二区| 成人综合网站| 亚洲猫色日本管| 精品176极品一区| 亚洲黄色性网站| 成人在线精品| 狠狠做深爱婷婷久久综合一区 | 久久久久久久久久看片| 三级网站视频在在线播放| 高清成人在线观看| 国产欧美黑人| 91网站在线观看视频| av电影院在线看| 欧美国产欧美综合| 天天综合网天天| 一二三四区精品视频| 蜜桃精品一区二区三区| 日韩欧美国产视频| 国内精品久久久久久久久电影网| 欧美日韩亚洲综合一区| 99久久这里只有精品| 成人丁香基地| 日韩av在线发布| 自拍视频在线网| 久久久99精品久久| 久久电影天堂| 欧美亚洲国产一区二区三区| 色综合天天爱| 粉嫩欧美一区二区三区| 久草这里只有精品视频| 狂野欧美性猛交xxxxx视频| 国产精品久久久久一区 | 日韩aaa久久蜜桃av| 337p亚洲精品色噜噜狠狠| 亚洲午夜一区| 黄色美女网站在线观看| 成人sese在线| 巨大黑人极品videos精品| 欧美色视频一区| 亚洲激情另类| 蜜桃视频在线观看免费视频网站www | 伊人天天综合| 欧美三级电影一区二区三区| 亚洲国产精品激情在线观看| 9999久久久久| 黄色无遮挡网站| 成人黄色国产精品网站大全在线免费观看 | 日韩美女主播在线视频一区二区三区 | 国产九色porn网址| 国产99精品国产| 日韩久久一区| 先锋影音在av资源看片| 日韩和欧美一区二区三区| 爱情岛亚洲播放路线| 精品久久久中文| 国内精品久久久久久久97牛牛 | 蜜桃特黄a∨片免费观看| 久88久久88久久久| 国产福利91精品一区二区| 欧美一区二区网站| 国产麻豆日韩欧美久久| 99精品女人在线观看免费视频| 精品国产制服丝袜高跟| 国产91在线观看| 国产精品对白| 性视频一区二区三区| 国产精品麻豆网站| 亚洲一区在线| 国产www视频在线观看| 欧美日韩国产区一| 国产凹凸在线观看一区二区| 成人性生交大片免费看96|