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0.4
Wetter
0.2
0.0
-0.2
-0.4
-0.6
Drier
1600
1650
1700
1750
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2000
3.0
12
2.5
10
2.0
8
1.5
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1.0
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0.5
2
0.0
0
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1650
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Year
Fig. 9.10 Composite age structure data from a network of 12 ponderosa pine stands and recon-
structed summer Palmer Drought Severity Index (PDSI) from corresponding grid points in the
southwestern United States (Cook et al. 1999 , 2004 )
other surface fuels. Hence, it seems quite likely that historically, the favorable germi-
nation and establishment periods of ponderosa pine in the Southwest corresponded
with wetter conditions for the reasons described above; i.e., more successful ger-
mination and survival during these periods, and relatively longer intervals between
fires during these wet periods (see also Fig. 9.8 ) . It is likely that climate affected
recruitment in many of these forests both through direct effects on demographic
processes (seed production, germination, and seedling growth) as well as by mod-
ifying fire frequency and timing (and perhaps other disturbances, such as insect
outbreaks; e.g., Fig. 9.6 ) . In a later section of this chapter, we will discuss timing
of longer fire-free intervals, and their relationships to both climate and patterns of
regional tree recruitment shown in Fig. 9.10 .
As in most dendrochronological studies involving networks of chronologies,
regional-scale emergent patterns of ecological synchrony may be reasonably inter-
preted to reflect, at least in part, the important role of climatic variability. This
is not to discount the important role of local factors in causing unique distur-
bances or demographic peculiarities at the tree or stand level. Interactions between
 
 
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