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Analyses of the Effects of Global Change on - US Climate Change ...

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The U.S. <strong>Climate</strong> <str<strong>on</strong>g>Change</str<strong>on</strong>g> Science Program Chapter 2<br />

50<br />

development <str<strong>on</strong>g>of</str<strong>on</strong>g> chr<strong>on</strong>ic br<strong>on</strong>chitis, heart attack,<br />

and arrhythmias (Dockery et al., 1993; Samet<br />

et al., 2000; Pope et al., 1995, 2002, 2004;<br />

Pope and Dockery, 2006; Dominici et al, 2006;<br />

Laden et al., 2006). Associati<strong>on</strong>s have also been<br />

reported for increased school absences, hospital<br />

admissi<strong>on</strong>s, emergency room visits, and<br />

premature mortality. Susceptible individuals<br />

include people with existing heart and lung<br />

disease, and diabetics, children, and older<br />

adults. Because <str<strong>on</strong>g>the</str<strong>on</strong>g> mortality risks <str<strong>on</strong>g>of</str<strong>on</strong>g> PM2.5<br />

appear to be mediated through narrowing <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

arteries and resultant heart impacts (Künzli<br />

et al., 2005), pers<strong>on</strong>s or populati<strong>on</strong>s with<br />

high blood pressure and/or pre-existing heart<br />

c<strong>on</strong>diti<strong>on</strong>s may be at increased risk. In a study<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> mortality in relati<strong>on</strong> to l<strong>on</strong>g-term PM2.5<br />

c<strong>on</strong>centrati<strong>on</strong>s in 50 U.S. cities, individuals<br />

without a high school educati<strong>on</strong> dem<strong>on</strong>strated<br />

higher c<strong>on</strong>centrati<strong>on</strong>/resp<strong>on</strong>se functi<strong>on</strong>s than<br />

those with more educati<strong>on</strong> (Pope et al., 2002).<br />

This result suggests that low educati<strong>on</strong> was a<br />

proxy for increased likelihood <str<strong>on</strong>g>of</str<strong>on</strong>g> engaging in<br />

outdoor labor with an associated increase in<br />

exposure to ambient air.<br />

Using a coupled climate-air polluti<strong>on</strong> threedimensi<strong>on</strong>al<br />

model, Jacobs<strong>on</strong> (2008) compared<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> health effects <str<strong>on</strong>g>of</str<strong>on</strong>g> pre-industrial vs. present<br />

day atmospheric c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> CO 2. The<br />

results suggest that increasing c<strong>on</strong>centrati<strong>on</strong>s<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> CO 2 increased tropospheric oz<strong>on</strong>e and<br />

PM2.5, which increased mortality by about 1.1<br />

percent per degree temperature increase over<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> baseline rate. Jacobs<strong>on</strong> estimated that about<br />

40 percent <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> increase was due to oz<strong>on</strong>e and<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> rest to particulate matter. The estimated<br />

mortality increase was higher in locati<strong>on</strong>s with<br />

poorer air quality.<br />

2.2.4.6 Aeroallergens and<br />

Allergenic Diseases<br />

<strong>Climate</strong> change has caused an earlier <strong>on</strong>set <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

spring pollen seas<strong>on</strong> for several species in North<br />

America (Casassa et al., 2007). Although data<br />

are limited, it is reas<strong>on</strong>able to infer that allergenic<br />

diseases caused by pollen, such as allergic rhinitis,<br />

also have experienced c<strong>on</strong>comitant changes in<br />

seas<strong>on</strong>ality (Emberlin et al., 2002; Burr et al.,<br />

2003). Several laboratory studies suggest that<br />

increasing CO 2 c<strong>on</strong>centrati<strong>on</strong>s and temperatures<br />

could increase ragweed pollen producti<strong>on</strong> and<br />

prol<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> ragweed pollen seas<strong>on</strong> (Wan et al.,<br />

2002; Wayne et al., 2002; Singer et al., 2005;<br />

Ziska et al., 2005; Rogers et al., 2006) and<br />

increase some plant metabolites that can affect<br />

human health (Ziska et al., 2005; Mohan et al.,<br />

2006). Although <str<strong>on</strong>g>the</str<strong>on</strong>g>re are suggesti<strong>on</strong>s that <str<strong>on</strong>g>the</str<strong>on</strong>g><br />

abundance <str<strong>on</strong>g>of</str<strong>on</strong>g> a few species <str<strong>on</strong>g>of</str<strong>on</strong>g> air-borne pollens<br />

has increased due to climate change, it is unclear<br />

whe<str<strong>on</strong>g>the</str<strong>on</strong>g>r <str<strong>on</strong>g>the</str<strong>on</strong>g> allergenic c<strong>on</strong>tent <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g>se pollen<br />

types has changed (Huynen and Menne, 2003;<br />

Beggs and Bambrick, 2005). The introducti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

regi<strong>on</strong>ally new invasive species associated with<br />

climatic and o<str<strong>on</strong>g>the</str<strong>on</strong>g>r changes, such as ragweed and<br />

pois<strong>on</strong> ivy, may increase current health risks.<br />

There are no projecti<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> possible impacts<br />

<str<strong>on</strong>g>of</str<strong>on</strong>g> climate change <strong>on</strong> allergenic diseases.<br />

2.3 PROjECTED HEALTH<br />

IMPACTS OF CLIMATE<br />

CHANGE IN THE UNITED<br />

STATES<br />

2.3.1 Heat-Related Mortality<br />

Determinants <str<strong>on</strong>g>of</str<strong>on</strong>g> how climate change could alter<br />

heat-related mortality include actual changes in<br />

<str<strong>on</strong>g>the</str<strong>on</strong>g> mean and variance <str<strong>on</strong>g>of</str<strong>on</strong>g> future temperatures;<br />

factors affecting temperature variability<br />

at <str<strong>on</strong>g>the</str<strong>on</strong>g> local scale; demographic and health<br />

characteristics <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> populati<strong>on</strong>; and policies<br />

that affect <str<strong>on</strong>g>the</str<strong>on</strong>g> social and ec<strong>on</strong>omic structure <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

communities, including urban design, energy<br />

policy, water use, and transportati<strong>on</strong> planning.<br />

Barring an unexpected and catastrophic<br />

ec<strong>on</strong>omic decline, residential and industrial<br />

development will increase over <str<strong>on</strong>g>the</str<strong>on</strong>g> coming

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