|
The Pacific Northwest
encompasses extensive forests, topography that creates abrupt
changes in
climate and ecosystems over short distances, and mountain and
marine
environments in close proximity. The Cascade Mountains divide the
region
climatically, ecologically, economically, and culturally. Three
quarters
of the region's population live west of the Cascades, concentrated
in the
metropolitan areas of Seattle and Portland, where the aerospace
and
computer industries have largely supplanted the traditional
resource
sectors of forestry, fishing, and agriculture. The Northwest
provides a
quarter of the nation's softwood lumber and plywood. The fertile
lowlands
of eastern Washington produce 60% of the nation's apples and large
fractions of its other tree fruit.
The region has seen several
decades of population and economic growth nearly twice the
national rate,
with population nearly doubling since 1970. The region's moderate
climate, quality of life, and outdoor recreational opportunities
contribute to its continuing attraction to newcomers. The same
environmental attractions that draw people to the region are
increasingly
stressed by rapid development. Stresses arise from dam operation,
forestry, and land-use conversion from natural ecosystems to
metropolitan
areas, intensively managed forests, agriculture, and grazing. The
consequences include loss of old-growth forests, wetlands, and
native
grasslands; urban air pollution; extreme reduction of salmon runs;
and
increasing numbers of threatened and endangered species.
Observed Climate Trends
Over the 20th century, the
region has grown warmer and wetter. Annual-average temperature has
increased 1 to 3F (0.5-1.5C) over most of the region, with
nearly
equal warming in summer and winter. Annual precipitation has also
increased across the region, by 10% on average, with increases
reaching 30
to 40% in eastern Washington and Northern Idaho. The region's
climate also
shows significant recurrent patterns of year-to-year variability.
Warm
years tend to be relatively dry with low streamflow and light
snowpack,
while cool ones tend to be relatively wet with high streamflow and
heavy
snowpack. Though the differences in temperature and precipitation
are
small, they have clearly discernible effects on important regional
resources. Warmer drier years tend to have summer water shortages,
less
abundant salmon, and increased probability of forest fires. These
variations in the region's climate show clear correlations with
two
large-scale patterns of climate variation over the Pacific: the El
Niño/Southern
Oscillation (ENSO) on scales of a few years; and the more recently
discovered Pacific Decadal Oscillation (PDO) on scales of a few
decades.
The observed effects of these patterns provide powerful
illustrations of
regional sensitivities to climate, but how they might interact
with future
climate change is not yet understood.
Scenarios of Future
Climate
Model scenarios project
regional warming in the 21st century to be much greater than
observed
during the 20th century, with average warming over the region of
about 3F
(1.5C) by the 2030s and 5F (3C) by the 2050s. By the 2090s,
average
summer temperatures are projected to rise by 7-8F (4-4.5C),
while
winter temperatures rise by 8-11F (4.5-6C). Through 2050,
average
precipitation is projected to increase, although some locations
have small
decreases. Precipitation increases would be concentrated in
winter, with
little change or a decrease in summer. Because of this seasonal
pattern of
wetter winters and drier summers, even the projections that show
annual
precipitation increasing, show water availability decreasing,
especially
in the Hadley model. By the 2090s, projected annual average
precipitation
increases range from a few percent to 20% in the Hadley model, and
from 20
to 50% in the Canadian model.
|

|
Precipitation has
increased over most of the Pacific Northwest since 1900.
Both
climate models project continued precipitation increases,
with the
largest increases in the southern part of the region.
Warming since 1900 in
the Pacific Northwest ranges from 0F to 4F. By 2100, both
models project warming near 5F west of the Cascades, with
much
larger warming further east in the Canadian model. |
|
Over the 21st century,
both models project increases in annual average
precipitation and in
extreme precipitation events. As the graphs for both models
show,
the largest precipitation increases are projected to occur
on days
already receiving the most. |

|
Changes in Timing of Freshwater Resources
Despite its reputation as a
wet place, most of the Northwest receives less than 20 inches (0.5
meter)
of precipitation a year, and dry summers make freshwater a
limiting
resource for many ecosystems and human activities. Water resources
are
already stressed by multiple growing demands. The projected warmer
wetter
winters will likely increase flooding in rainfed rivers, because
there is
more precipitation, and because more of it falls as rain.
Projected
year-round warming and drier summers will likely increase summer
water
shortages in both rainfed and snowfed rivers, including the
Columbia,
because there would be less snowpack and because it would melt
earlier. In
the Columbia, allocation conflicts are already acute, and the
system is
vulnerable to shortages.
Adaptations: Adapting
to projected increases in summer shortages will likely require a
combination of reducing demand, increasing supply, and reforming
institutions to increase flexibility and regional problem-solving
capacity. In the Colombia Basin, current infrastructure and
institutions
are inflexible and inadequate to deal with the projected scarcity.
|

|
Relative to present
flows (dashed), the wetter winters and drier summers
simulated by
climate models are very likely to shift peak streamflow
earlier in
the year, increasing the risk of late-summer shortages.
Though the
Columbia system is only moderately sensitive to climate
change,
allocation conflicts and a cumbersome network of
interlocking
authorities restrict its ability to adapt, producing
substantial
vulnerability to these shortages. |
|
Learning
from Water Shortages |
|
In response, the City
developed a plan with four levels of response to anticipated
shortage: advising the public of potential shortages and
monitoring
use; requesting voluntary use reductions; mandatory
prohibitions of
certain uses (such as watering lawns and washing cars); and
rationing. Another drought came in 1992, following a winter
with low
snowpack but in which SPU had followed standard
flood-control rules
by spilling water from their reservoirs. With a small
snowmelt,
reservoirs were low by the spring, and SPU invoked mandatory
restrictions during the hot dry summer that followed. Water
quality
declined sharply, prompting a decision to begin building a
costly
ozone-purification plant.
The ill-advised
spilling of early 1992 alerted SPU to the danger of
following rigid
reservoir rule curves, and they have since taken a more
flexible
approach, projecting annual supply and demand using a model
including probabilistic predictions based on ENSO and PDO.
During
the strong El Niño of 1997-1998, SPU took early conservation
education measures and allowed higher than normal reservoir
fill.
When 1998 brought a small snowmelt and a hot dry summer,
these
measures allowed the drought to pass with the public
experiencing no
shortage.
In integrating
seasonal forecasts into its operations, SPU is an uncommonly
adaptable resource-management agency. But it still has a
long way to
go in adapting to longer-term climate variability and
change. SPU
presently projects that new conservation measures will keep
demand
at or below present levels until at least 2010, while
conservation
measures and planned system expansion (including a
connection with a
neighboring system) will maintain adequate supply until at
least
2030. Over this period, climate change is likely to have
significant
effects on both supply and demand, but is not yet included
in
planning.
The warmer drier
summers projected under climate change are likely to stress
both
supply and demand, requiring earlier capacity expansion, and
triggering the more restrictive conservation measures more
often.
Moreover, the recent shift to cool PDO phase that has been
suggested
could well mask this effect for a couple of decades, risking
sudden
appearance of shortages when PDO next shifts back to its
warm phase.
Seattle Public
Utilities (SPU) experienced summer droughts and potential
shortages
in 1987, 1992, and 1998. Their responses to the three events
illustrate institutional flexibility and learning. Summer
1987 began
with full reservoirs, but a hot dry summer and a late return
of
autumn rains created a serious shortage in which water
quality
declined, inadequate flows were maintained for fish, and the
main
reservoir fell so low that an emergency pumping station had
to be
installed. |
|
Regional Impacts: Climate Change Projected for 2050 vs. Observed 20th Century Variability |
|
 |
The pink bars show
projected impacts expected by the 2050s, based on the
Hadley and
Canadian scenarios. Projected regional warming by this
time is
much larger than variations experienced in the 20th
century. This
warming is projected to be associated with a small
increase in
precipitation, a sharp reduction in snowpack, a reduction
in
streamflow, and an increase in area burned by forest
fires.
Although quite uncertain, large reductions in salmon
abundance
ranging from 25 to 50%, are judged to be possible based on
projected changes in temperature and streamflow.
This chart compares
possible Northwest impacts from climate change by the
2050s with
the effects of natural climate variations during the 20th
century.
The orange bars show the effects of the warm phase of the
Pacific
Decadal Oscillation (PDO), relative to average 20th
century
values. During warm-PDO years, the Northwest is warmer,
there is
less rain and snow, stream flow and salmon catch are
reduced, and
forest fires increase. The blue bars show the
corresponding
effects of cool-phase years of the PDO, during which
opposite
tendencies occurred.
|

Added Stresses on Salmon
While non-climatic stresses
on Northwest salmon presently overwhelm climatic ones, salmon
abundances
have shown a clear correlation with 20th century variations in
climate
from decade to decade. Climate models cannot yet project the most
important oceanic conditions for salmon, but the likely effects on
their
freshwater habitat all appear unfavorable. Increased winter
flooding,
reduced summer and fall flows, and rising stream and estuary
temperatures
are all harmful for salmon. In addition, it is possible that
earlier
snowmelt and peak spring streamflow will deliver juveniles to the
ocean
before there is adequate food for them. Climate change is
consequently
very likely to hamper efforts to restore already depleted salmon
stocks,
and to stress presently healthy stocks.
Adaptations: It is
possible that operational changes on managed rivers would reduce
current
stream warming and slow future warming, although such measures
will very
likely be overwhelmed by continued climate warming. Measures to
reduce
general stress on fish, such as changing dam operations to provide
adequate late-summer streamflows, might possibly increase salmon's
resilience to other stresses, including climate. It is very likely
that
maintaining such flows will become increasingly difficult,
however, under
the projected regional warming that will very likely shift peak
streamflows to earlier in the year. Other options include
maintaining the
diversity of salmon by increasing preservation of their habitat,
or
removing existing dams and accepting reduced ability to manage
summer
shortages.

CO2 and Summer Drought Effects on Forests
Evergreen coniferous forests
dominate the landscape of much of the Northwest. West of the
Cascades,
coniferous forests cover about 80% of the land, and include about
half the
world's temperate rainforest. Northwest forests have been
profoundly
altered by timber management and land-use conversion. These
forests are
quite sensitive to climate variation because warm dry summers
stress them
directly, by limiting seedling establishment and summer
photosynthesis, as
well as indirectly, by creating conditions favorable to pests and
fire.
The extent, species mix, and productivity of Northwest forests are
likely
to change under projected 21st century climate change, but the
specifics
of these changes are not known with confidence at present. They
are very
likely to depend on interactions between the timing and amount of
precipitation, the seasonal water-storage capacity of forest
soils, and
changes in trees' water-use efficiency under elevated CO2. It is
very
likely that these factors will jointly determine the consequences
of the
likely increase in summer moisture stress, which will also depend
on
interactions with forest management practices, land-use
conversion, and
other pressures from development.
Adaptations: Options
include planting species adapted to projected climate rather than
present
climate; managing forest density to reduce susceptibility to
drought
stress and fire risk; and using prescribed burning to reduce the
risk of
large, high-intensity fires. Increased capacity for long-term
monitoring
and planning would likely help with management. Reduced tree
cutting,
reduced road construction, and establishment of large buffers
around
streams are some of the ways to promote diversity of plant and
animal
species and the services provided by forest ecosystems (such as
purifying
air and water). Improved seasonal forecasts, and knowledge of the
typical
effects of ENSO and PDO, could possibly assist in decision making
on
timing and species of planting, and use and timing of prescribed
burning.
Sea-Level Rise Impacts on Coastal Erosion
Sea-level rise is likely to
require substantial investments in order to avoid coastal
inundation,
especially in the low-lying communities of southern Puget Sound
where
coastal subsidence is occurring. Other likely effects include
increases in
winter landslides, and increased erosion on sandy

stretches of the
Pacific
Coast. Severe storm surges and erosion are presently associated
with El Niño
events, which raise sea level for several months and change the
direction
of prevailing winds. Climate change is projected to bring similar
shifts.
Projected heavier winter rainfall is likely to increase soil
saturation,
landsliding, and winter flooding. All these changes would likely
increase
the danger to property and infrastructure on bluffs and
beachfronts, and
beside rivers.
Adaptations: The
current coastal management system is not particularly adaptable,
even to
current climate variability and risks, and there is little
inclination to
restrict development in vulnerable locations. Adaptation
strategies would
involve conserving remaining natural coastal areas, placing less
property
at risk in low-lying or flood- or slide-prone areas, assigning
more of the
associated risk to property owners through insurance rates, and
more
effective transfer of climate change information to local
governments,
where most planning authority lies.
|