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Climate change futures: health, ecological and economic dimensions

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68 | NATURAL AND MANAGED SYSTEMS<br />

CASE STUDIES<br />

THE 1997/98 EL NIÑO EVENT<br />

Concerns over the fire-related consequences of global<br />

warming were rekindled in 1998 by the impacts of the<br />

El Niño of 1997/98, the strongest of the 20th century.<br />

This was part of the anomalous period from 1976-98<br />

with an increased frequency, intensity <strong>and</strong> duration of El<br />

Niño events, based on records dating back to 1887.<br />

The powerful impact that climatic anomalies can have<br />

was demonstrated after droughts linked to El Niño were<br />

followed by widespread, devastating fires in Southeast<br />

Asia <strong>and</strong> Brazil, each taking enormous tolls in terms of<br />

acute <strong>and</strong> chronic respiratory diseases. In the US,<br />

Florida experienced a rash of wildfires.<br />

• In Malaysia, there was a two-to-threefold increase in<br />

outpatient visits for respiratory diseases, as winds<br />

carried plumes thous<strong>and</strong>s of miles.<br />

• In Indonesia, 40,000 were hospitalized <strong>and</strong> losses<br />

in terms of property, agriculture <strong>and</strong> disrupted transport<br />

were estimated to be US $9.3 billion (Arnold<br />

2005).<br />

• In Alta Floresta, Brazil, there was a twentyfold<br />

increase in outpatient visits for respiratory diseases.<br />

• In Florida, US, there was a 91% increase in emergency<br />

visits for asthma, 132% increase in bronchitis<br />

<strong>and</strong> 37% increase in chest pain.<br />

– P.E.<br />

THE FUTURE<br />

CCF-I: ESCALATING IMPACTS<br />

Continued warming favors more fungal <strong>and</strong> insect of<br />

forests, <strong>and</strong> more harsh weather will further weaken<br />

tree defenses against pests. Meanwhile, l<strong>and</strong>-use<br />

<strong>change</strong>s as a result of human activities <strong>and</strong> spreading<br />

wildfires can disrupt communities of predators <strong>and</strong> prey<br />

(for example, birds <strong>and</strong> leaf-eating caterpillars) that<br />

have co-evolved <strong>and</strong> keep populations of pests in<br />

check. The <strong>ecological</strong> implications for essential forest<br />

habitat <strong>and</strong> forest functions (water supplies for consumption,<br />

agriculture <strong>and</strong> energy; absorbing pollutants;<br />

drawing down carbon; <strong>and</strong> producing oxygen) will<br />

continue to deteriorate.<br />

Figure 2.26 Rising CO 2<br />

<strong>and</strong> Wildfires<br />

Change<br />

140%<br />

120%<br />

100%<br />

80%<br />

60%<br />

40%<br />

20%<br />

0%<br />

-20%<br />

Acreage Burned<br />

Escapes<br />

Santa Clara Amador-El Dorado Humbolt<br />

Firefighting Region<br />

Chart shows results for contained wildfires (acres burned) as well as<br />

catastrophic “escaped” fires (number of fires) under a double CO 2<br />

scenario for three major climate <strong>and</strong> vegetation zones in California.<br />

Some subregions exhibited up to a four fold increase in damages.<br />

Results calculated by coupling climate models with California<br />

Department of Forestry wildfire models, assuming full deployment of<br />

existing suppression resources.<br />

Source: Tom et al.1998<br />

Northern California forestry services have coupled<br />

California Department of Forestry wildfire models with<br />

the Goddard Institute for Space Sciences general circulation<br />

model of global climate (Torn et al. 1998; Fried et<br />

al. 2004). The regions studied include substantial areas<br />

of wildl<strong>and</strong>s that interface with urban areas on the margins<br />

of the San Francisco Bay area, the Sacramento metropolitan<br />

area, <strong>and</strong> the redwood region's urban center<br />

in Eureka. According to this analysis, climate <strong>change</strong> will<br />

be associated with faster burning fires in most vegetation<br />

types, resulting in more than a doubling of catastrophic<br />

escaped fires under a doubled CO 2<br />

environment. (see<br />

figure 2.25). The results include full use of existing fire<br />

suppression resources, but exclude the impacts of several<br />

important factors, such as beetle infestations, increased<br />

lightning activity (the primary cause of wildfire ignitions)<br />

<strong>and</strong> shifts in post-fire plant regimes towards more flammable<br />

vegetation types (typically grasses).<br />

Empirical data combined with predictive modeling in<br />

British Columbia, performed by the Canadian Forest<br />

Service, demonstrate that climate <strong>change</strong> is eroding the<br />

<strong>ecological</strong> barriers (non-forested prairies <strong>and</strong> the high<br />

elevations of the Rocky Mountains) that once prevented<br />

northward expansion of the mountain pine beetle.<br />

Adjacent boreal forests in northern Alberta <strong>and</strong><br />

Saskatchewan, which are populated by susceptible<br />

jack pine (Pinus banksiana, Lamb) may serve as the<br />

next large-scale emergence zone of the beetle advance<br />

(Furniss <strong>and</strong> Schenk 1969; Safranyik <strong>and</strong> Linton 1982;<br />

Cerezke 1995; Carroll et al. 2003; Alberta<br />

Sustainable Resource Development 2003).

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