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Emissions Scenarios - IPCC

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136 Scenario Driving Forces<br />

Table 3-6: Global renewable energy potentials for 2020 to 2025, maximum technical potentials, and annual flows, in EJ. Data<br />

sources: Watson et al.. 1996; Enquete-Kommission, 1990?<br />

Consumption Potentials by Long-term Technical Annual<br />

1860-1990 1990 2020-2025 Potentials Flows<br />

Hydro 560 21 35-55 >130 >400<br />

Geothermal - 20 >800<br />

Wind - - 7-10 >130 >200,000<br />

Ocean - - 2 >20 >300<br />

Solar - - 16-22 >2,600 >3,000,000<br />

Biomass 1,150 55 72-137 > 1,300 >3,000<br />

Total 1,710 76 130-230 >4,200 >3,000,000<br />

(Nakicenovic etal., 1996) and shown in Table 3-6. A summary<br />

of the literature of renewable resource development potentials<br />

consistent with <strong>IPCC</strong> WGII SAR, including a detailed regional<br />

breakdown, is given in Christiansson (1995) and Neij (1997).<br />

Hydropower cun'ently provides some of the cheapest electricity<br />

available in the world, although the potential for new capacity<br />

is limited in some regions. WEC (1994, 1995a) estimates the<br />

gross world potential for hydroelectric schemes at about 144 EJ<br />

per year, of which about 47 EJ per year is technically feasible<br />

for development, about 32 EJ per year is economically feasible<br />

at present, and about 8 EJ per year is currently in operation.<br />

<strong>IPCC</strong> WGII SAR (Nakicenovic etal, 1996) gives a comparable<br />

medium-teiTn potential of between 13 and 55 EJ, and a<br />

maximum technical potential above 130 EJ.<br />

Other important renewable energy resources are wind and<br />

solar, as well as modem forms of biomass use. Biomass<br />

resources are potentially the largest renewable global energy<br />

source, with an annual primary production of 220 billion oven<br />

dry tons (ODT) or 4500 EJ (Hall and Rosillo-Calle, 1998).<br />

The annual bioenergy potential is estimated to be in the order<br />

of 2900 EJ, of which 270 EJ could currently be considered<br />

available on a sustainable basis (Hall and Rosillo-Calle, 1998).<br />

Hall and Rao (1994) conclude that the biomass challenge is<br />

not one of availability but of the sustainable management,<br />

conversion, and delivery to the market place in the form of<br />

modem and affordable energy services. It is also important to<br />

distinguish between harvesting and deforestation; the fonner<br />

results in afforestation, and the latter in conversion of forest<br />

land for other uses, such as agriculture or urban development.<br />

The use of biomass as an energy source necessitates the use of<br />

land. Based on estimates by IIASA-WEC (1995), by 2100<br />

about 690-1350 million hectares of additional land would be<br />

needed to support future biomass energy requirements for a<br />

high-growth scenario. However, the additional land<br />

requirement for agriculture is estimated to reach 1700 million<br />

hectares during the same period. These land requirements can<br />

^ All estimates, excluding biomass, have been converted into thermal<br />

equivalents with an average factor of 38.5%.<br />

be fulfilled if the potential additiofial arable land is taken into<br />

account (at present this is mostly covered by forest). Hence,<br />

land-use conflicts could arise, and particularly for Asia which<br />

is projected to require its entire potential of arable land by<br />

2100. Africa and Latin America may have sufficient land to<br />

support an expanded biomass program. One estimate (WEC,<br />

1994) shows that Africa can support the production of biomass<br />

energy equivalent to 115% of its current energy consumption<br />

(8.6 EJ).<br />

Some authors stress that increased demand for bioenergy could<br />

compete with food production (Azar and Bemdes, 1999). They<br />

note that the competitiveness between food and bioenergy<br />

production is not realistic in most energy-economy models;<br />

rather it is treated in an ad hoc fashion with the assumption that<br />

enough land is secured for food production. In reality an<br />

increasing competitiveness of bioenergy plantations may cause<br />

food prices to jump. Some developing regions, in particular<br />

Africa, are often assumed in scenarios to become major<br />

importers of food (Azar and Bemdes, 1999).<br />

Unlike hydropower, most of the technologies that could<br />

harness these renewable energy fonns are in their infancy and<br />

are generally still high cost (although wind power is becoming<br />

increasingly competitive in some areas). Conversely, the<br />

potential for improvement in technical performance and costs<br />

is substantial. Thus, the future resource potential of these<br />

renewables is lai'gely determined by advances in technologies<br />

and economics (discussed in Section 3.4.4).<br />

Advances in renewable energy technologies could materialize<br />

to a significant extent even in the absence of climate policies,<br />

albeit conventional wisdom holds that such policies could<br />

accelerate their dilfusion considerably. According to <strong>IPCC</strong><br />

WGII SAR (Nakicenovic et al, 1996), in the medium-term (to<br />

2025) the largest renewable energy potentials lie in the<br />

development of modem biomass (70 to 140 EJ), solar (16 to 22<br />

EJ), and wind energy (7 to 10 EJ) as indicated in Table 3-6. In<br />

the long term the maximum technical energy supply potential<br />

for renewable energy is evidently solar (>2,600 EJ), followed<br />

by biomass (>1,300EJ).

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