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Table 2.2. Land-use and afforestation summary evaluation table. The ratings given (refer Table 5.1) are according to the<br />

criteria explained in Chapter 1<br />

Land use and afforestation<br />

Effectiveness Limited potential for carbon removal Low<br />

Affordability Cheap to deploy Very high<br />

Timeliness<br />

Safety<br />

Ready for immediate deployment and starts CO 2 reductions immediately<br />

Slow to reduce global temperatures (CDR method)<br />

Few undesirable side effects except for potential land use conflicts and biodiversity<br />

implications<br />

Medium<br />

High<br />

management regimes, often exceeding national<br />

jurisdictions in order to gain the benefits of scale.<br />

As summarised in Table 2.2 these methods are feasible and<br />

are low risk, but are long-term and can achieve only small<br />

to medium effects on atmospheric CO 2 concentrations<br />

(see also Table 5.1). Several regional scale studies have<br />

demonstrated that overall benefits to the economy and<br />

to other ecosystem services such as water regulation,<br />

amenities, biodiversity conservation and agriculture can<br />

result from integrated land-use planning that would deliver<br />

enhanced CO 2 draw-down and storage. However, carbon<br />

stored in vegetation is not securely sequestered in the<br />

long-term, as it can easily be released by fire, drought or<br />

deliberate deforestation (<strong>Royal</strong> <strong>Society</strong> 2001).<br />

2.2.2 Biochar and biomass-related methods<br />

As terrestrial vegetation grows it removes large quantities<br />

of carbon from the atmosphere during photosynthesis.<br />

When the organisms die and decompose, most of the carbon<br />

they stored is returned to the atmosphere. There are four<br />

ways in which the growth of biomass may be harnessed<br />

to slow the increase in atmospheric CO 2 (<strong>Keith</strong> 2001).<br />

1. Land Carbon Sinks. Carbon may be sequestered in situ<br />

in soil or as standing biomass, as discussed above in<br />

Section 2.2.1.<br />

2. Bioenergy & Biofuels. Biomass may be harvested and<br />

used as fuel so that CO 2 emissions from the fuel’s use<br />

are (roughly) balanced by CO 2 captured in growing<br />

the energy crops. The use of bioenergy and biofuels<br />

(<strong>Royal</strong> <strong>Society</strong> 2008a) is considered to be a means of<br />

reducing emissions, rather than geoengineering and<br />

is not considered further here.<br />

3. Bioenergy with CO 2 capture and sequestration (BECS).<br />

Biomass may be harvested and used as fuel, with<br />

capture and sequestration of the resulting CO 2 ; for<br />

example, one may use biomass to make hydrogen or<br />

electricity and sequester the resulting CO 2 in geological<br />

formations.<br />

4. Biomass for sequestration. Biomass may be harvested<br />

and sequestered as organic material, for example, by<br />

burying trees or crop wastes, or as charcoal (biochar).<br />

Bioenergy with CO 2 sequestration (BECS) builds directly<br />

on existing technology for bioenergy/biofuels and for CCS,<br />

and inherits the advantages and dis advantages of both of<br />

these technologies. There is no doubt that it is technically<br />

feasible, and there are already some small real-world<br />

examples (<strong>Keith</strong> 2001; Obersteiner et al. 2001; IPCC 2005).<br />

It is again not necessarily or normally regarded as<br />

geoengineering, and has been reviewed in some detail<br />

by the IPCC (2005). However, BECS has much in common<br />

with some other methods considered here, and has<br />

therefore been included for comparison purposes,<br />

but is not reviewed in detail (see Table 2.3).<br />

Sequestration of biomass and biochar have been<br />

proposed as a method for intervening in the natural<br />

cycle so that some or all of the carbon fixed by organic<br />

matter can be stored in soils or elsewhere for hundreds<br />

or thousands of years. For example, it has been proposed<br />

to bury wood and agricultural waste both on land and<br />

in the deep ocean to store the carbon rather than<br />

allow decomposition to return it to the atmosphere<br />

(Submission: Mark Capron; Submission: Newcastle<br />

University; Submission: Ning Zeng; Strand & Benford<br />

2009). In contrast to bioenergy with CO 2 sequestration,<br />

there is relatively little peer-reviewed literature about<br />

biomass for sequestration, though there appears to be<br />

growing interest in the biochar process (discussed later<br />

in this section).<br />

Methods involving burying biomass in the land or deep<br />

ocean will require additional energy consumption for<br />

transport, burying and processing. Most seriously, the<br />

processes involved may disrupt growth, nutrient cycling<br />

and viability of the ecosystems involved. In the deep<br />

ocean, for example, organic material would be<br />

decomposed and the carbon and nutrients returned to<br />

shallow waters, since oxygen is generally present (unless<br />

sufficient material were deposited to create anoxic<br />

conditions, which would constitute a major ecosystem<br />

perturbation). Full assessments are not yet available to<br />

assess the costs and benefits involved but it seems unlikely<br />

that this will be a viable technique at any scale that could<br />

usefully reduce atmospheric carbon.<br />

Biochar (charcoal) is created when organic matter<br />

decomposes, usually through heating, in a low- or zero<br />

The <strong>Royal</strong> <strong>Society</strong><br />

Geoengineering the Climate I September 2009 I 11

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