Abstracts
Science in the National Parks
June 23-24, 2006
Padilla Bay Interpretive Center
Mount Vernon, Washington
Friday June 23, 2006
9:00 Welcome
William F. Paleck, Superintendent, North Cascades
National Park Service
Complex
Key 1 Relationships
between mountain climate and Douglas-fir growth patterns in the
North
Cascades
9:30 Jeremy Littell, University of Washington Climate Impacts Group / Fire and Mountain Ecology Lab
Conifer species' growth and biogeography are well known to be
limited by climate in mountain ecosystems.
However, very little is known about the stability of growth/climate
relationships in space and time. In order to put future climate change impacts
to forest ecosystems into context, we need much better quantitative information
on where, when, and how climate mediates tree growth. In this talk, the
researcher describes results from a study of Douglas-fir tree rings in several
North Cascades watersheds. Stands from 100 to 500 years old yielded
chronologies that are sensitive to climate, but the nature and degree of
climate sensitivity varies with the biophysical context of each stand. Common
patterns emerge, however, and nearly all chronologies reflect the influence of
summer precipitation and temperature during the 20th century.
Key 2 Where
Ornament and Function are So Agreeably Combined: A New Look at
Consumer Choice Studies Using
English Ceramic Wares at Hudson’s Bay Company, Fort Vancouver National Historic
Site
10:00 Dr. Bob Cromwell, Ph.D., Fort Vancouver,
National Historic Site
This paper
focuses on data from over 20,000 English-manufactured ceramic ware sherds
excavated from archaeological households at Fort Vancouver National Historic
Site, Vancouver, Washington. The study utilizes the concept
of consumer choice (Spencer Wood 1987) in a setting that effectively integrates
the relationship between consumer behavior and goods consumption within a
capitalist market economy. It expands this relationship, to the choices of the
various socio-economic and job classifications represented by class and ethnic
differentiated archaeological households. Examination of these phenomena
affords a more nuanced approach to consumer choice studies than projected by
Spencer Wood; in part because of the isolation of the setting and the formalized
trading patterns of the Hudson’s
Bay Company. In addition, the well-documented spatial definition of the various
ethnic groups living and working at Fort
Vancouver provides an
ideal setting to explore a consumer choice perspective in relationship to the
complexity of culture, class, and identity.
Key 3
Forest Carnivore Surveys in Washington’s Wilderness Parks
10:30 Patricia
J. Happe, Olympic National Park; Roger Christopherson, North Cascades National
Park; Jim Schaberle, Mount Rainier National Park; and Robert Kuntz, North
Cascades National Park
During
the winter months from 2001 through 2004, biologists at Olympic, Mount Rainier, and North Cascades national parks conduct
forest carnivore surveys. We used
standard methods, developed and employed elsewhere by the USFS and others, with
slight modification for use in the backcountry.
In each park the survey effort was conducted for 2 years, with the
sampling effort rotating throughout the parks.
During the study we sampled 85 4mi2 blocks: 26 in Olympic
National Park, 20 in Mount Rainier National Park and 39 in North Cascades
National Park. Researchers obtained over
4600 animal photographs and detected 32 species, 10 of which were forest
carnivores. In no park did we detect
fisher, lynx, or wolverine. The most
common species detected in all three parks combined were marten, spotted skunk
and bobcat. Marten were detected in 66%
of the sample blocks in the Cascade parks, but were undetected in Olympic
National Park. Trends in species
distribution relative to precipitation and elevation gradients, and the
implications of the survey results for carnivore management, will be discussed.
Key 4 The Olympic Marmot: Sentinel of the High Country
11:00 Suzanne Cox Griffin, University of Montana, Missoula; Julia Witczuk,
University of Montana, Missoula; Mark L.
Taper, Montana State University, Bozeman; L. Scott Mills, University of
Montana, Missoula
In the late 1990s, anecdotal reports that the Olympic marmot (a
large ground-dwelling squirrel endemic to high-elevation meadows of Olympic
National Park) was missing from historically occupied areas, combined with the
precipitous decline of the closely related Vancouver
Island marmot, prompted concerns that climate change, tourism, or
some other force may be impacting the species. Beginning in 2002, we have
investigated the extent and causes of this apparent decline. We conducted
extensive surveys for marmots in both historically occupied and randomly chosen
meadows, collected DNA samples (via non-invasive sampling) from marmots
throughout the park, and estimated survival, reproduction and dispersal of
marmots that were individually tagged (n=195) and implanted with
radio-transmitters (n=78). Additionally, we used behavioral observations
and experiments to determine the potential impact of tourists on marmots, and
we are collecting coyote feces for DNA and diet analysis.
The Olympic marmot population appears to be declining in many
areas. Marmots have disappeared from well-documented, historically occupied
sites, they are absent or locally rare in parts of their range, including areas
where unoccupied burrow systems attest to their recent presence, and they are
declining at most of the sites where researchers have been intensively
monitoring animals. Marmots do remain locally abundant in some regions and are
not in immediate danger of extinction. However, both observations of marked
animals and genetic evidence indicate that dispersal is rare – recolonization
of abandoned sites is likely to be slow. In areas that have been intensively
studied, results consistently point to the non-native coyote as the primary
driver of current Olympic marmot declines. There is little evidence that direct
effects of climate change, disturbance by tourists, or disease are causing
declines. We cannot rule out subtle (possibly beneficial) effects of climate
change or that inbreeding depression may be aggravating the decline at some
sites. It is uncertain whether declines in other regions of the park are
related to coyotes – researchers expect the coyote diet analysis to shed
additional light on this question. It is likely that agricultural and managed
timber lands outside the park serve as a source for high-elevation coyotes,
since habitats with deep snow are typically marginal for the species. Low
snow-pack in recent years may be further facilitating coyotes’ success in the
high country.
Key 5 Black Bear Distribution Patterns in the Elwha River
Watershed of Olympic National Park
11:30 Kim Sager, USGS - Forest and Rangeland Ecosystem Science
Center, Olympic Field
Station
For
approximately 90 years two hydroelectric dams have blocked annual returns of
anadromous fish to over 113 kilometers of the Elwha
River in Washington’s Olympic National Park
(NP). The Department of Interior now
proposes to remove both dams to fully restore the Elwha River
ecosystem and native anadromous fisheries.
Dam removal and subsequent salmon restoration may result in altered
nutrient flow dynamics throughout the watershed, with potentially profound effects
on the park black bear population. To
provide baseline information by which to assess the long-term ecological
effects of salmon restoration on distribution patterns of bears in Olympic NP,
we used Global Positioning System (GPS) radio-collar technology to describe
broad-scale patterns in seasonal distribution and movements of black bears
prior to dam removal. Our presentation
will provide an overview of results from this research, including black bear
home range size, habitat use, and patterns in elevation use. These data provide valuable baseline
information for assessing the future effects of salmon restoration, and help
Olympic NP biologists prepare for monitoring programs along the Elwha River.
LUNCH BREAK: 12:00 – 1:00 pm
Key 6 2002-2005 Botanical
Surveys in North Cascades and Mount Rainier National Parks: What We Found and
Why it Is Important
1:00 Dr.
David Giblin and Ben Legler, University
of Washington
Since 2002, the National Park Service has partnered with the University of Washington Herbarium to conduct vascular
plant surveys at North Cascades National Park (NOCA) and Mt. Rainier National
Park (MORA). We have conducted a total
of 8 backcountry trips to date supported by over 30 volunteers. Nearly 1,600 specimens have been collected
during these trips. Approximately 465
species, subspecies, and varieties (taxa) have been collected at NOCA since
2002, and 23% of these are new taxa for the NOCA Herbarium. At MORA, 10% of the 213 taxa collected are
new additions to the herbarium there.
Volunteers on these trips have not only added to the National Park
Service's understanding of the vascular plant richness contained within each
park's boundaries, but they have also highlighted the important contributions
that citizens can make to scientific efforts in the our National Parks.
Key 7 Butterflies on the
Brink: Here Today; Where Tomorrow?
1:30 Ted
Thomas, U.S. Fish and Wildlife Service,
Division of Listing and Recovery
The
Island Marble butterfly (Euchloe
ausonides insulanus) is a rare northwestern butterfly found only in San Juan County, Washington. Fourteen specimens of the subspecies were
collected between 1861 and 1908. All
historic collections had been observed in Canada
until the subspecies was rediscovered in 1998 on San Juan Island. In 2002, the U.S. Fish and Wildlife Service
was petitioned by the Xerces Society and other organizations to list the
butterfly as endangered. A settlement
agreement was worked out in early 2005 and included a plan to conduct extensive
surveys of suitable habitat on private and public lands in north Puget Sound during the summer of 2005. The Washington Department of Fish and
Wildlife, Washington Department of Natural Resources, National Park Service,
Xerces Society and local volunteers partnered with the U.S. Fish and Wildlife
Service to survey for butterflies and assess their habitat in 2005 and
2006. By May, 2006, more than 350
surveys were conducted at more than 140 discrete locations. Up to three populations of Island Marble
butterflies may occur on Lopez and San Juan Islands. Very few butterflies are now known to exist,
possibly as few as 200 to 500 adults.
Numerous threats exist, including loss of habitat to invasive
encroachment, residential development, road maintenance activities, and modification
of habitat from periodic storms.
Although habitat restoration has caused short-term adverse effects, we
also anticipate a long-term positive response from this work. Support from local private and public
landowners to conserve the butterfly has been encouraging. A number of conservation partners are
currently developing a plan to address the long-term conservation needs of this
rare butterfly.
Key 8 The Island
Marble Butterfly: A Good Candidate for
Restoration?
2:00 Amy
Lambert, University
of Washington
I
will be presenting the results of my research on the population ecology and
life history of the Island Marble butterfly (Euchloe ausonides insulanus Guppy and Shepard, 2000; Pyle, 2000). The Island Marble was
presumed extinct until 1998, when a small population was discovered in San Juan
National Historic Park (SAJH) on the southern end of San
Juan Island in Washington State (Fleckenstein, 2002). Due to the Island Marbles’ small population size and
potentially threatened status, several conservation organizations have
petitioned the species to be listed under the Endangered Species Act (Black and Vaughan 2002). The focus of my presentation will be on egg,
larvae and
adult stages of development. In
addition, I will address habitat requirements, distribution and dispersal
behavior of the Island Marble that may contribute to passive adult recruitment
in areas of native plant prairie restoration.
Key 9 Unraveling the Mysteries
of the Marbled Murrelet
2:30 Dr.
Martin Raphael, USDA
Forest Service
The
Marbled Murrelet is a seabird in the family Alcide that nests on limbs of large
coniferous trees along the west coast of North America. Listed as Threatened, murrelet populations
have declined with the loss, mostly from logging, of their nesting habitat. Because the murrelet’s behavior is very
secretive, the Marbled Murrelet remains one of our most poorly known
birds. However, we are slowly gaining
knowledge about its movements, nesting habits, and population trends. Over the past 10 years, my research group has
been conducting at-sea surveys for the bird throughout the San Juan Islands and
Puget Sound.
Population size has been fairly consistent over this time, averaging
about 10,000 birds each year in Washington
waters. Reproductive rates are very low
and we observe only about 6 young for every 100 adults. Reproduction suffers from loss of eggs or
chicks due to predators, and from periodic shortages in prey that inhibit
breeding. Locally, our surveys indicate
that numbers of birds in the San Juans increase dramatically from May to August
but the reasons are not clear. We think
this increase reflects better feeding conditions around the San Juans and may
also result from birds that visit this area before dispersing further
south.
Over
the past three years we have captured nearly 100 murrelets and fitted them with
tiny radio transmitters. We locate the
birds each day by searching for their radio signals from a small aircraft
outfitted with antennas and a receiver.
This work has shown that murrelets cover a very large area and are able
to fly long distances. For example, one
of our birds was captured on June 8
near La Push. We observed that bird
along the outer coast until June 26 when we found it about 100 yards off the
beach near Kalaloch. The next day we
found it just north of Shaw
Island, a straight line
distance of over 100 miles. Two birds
that we captured near Port Angeles nested on Vancouver Island and regularly flew round trips of 120
miles each day to attend the nest.
Murrelets nest on the mossy limbs of large old trees,
most often in large intact patches of forest.
Over the past 10 years, we have developed a much better understanding of
the bird’s habitat requirements and have produced maps showing the amount and
location of suitable nesting habitat throughout the bird’s range in Washington, Oregon, and California. We are using this map to estimate changes in
habitat over time on both federal and nonfederal lands and to relate these
conditions to our population counts from our at-sea surveys. We have found that the amount of potential
nesting habitat is the primary driver of at-sea population size, so that
conservation and restoration of suitable habitat remain our primary means to recover
this fascinating bird.
Key 10 Effects
of Forecasted Climate Change on a Butterfly-Plant Interaction in North Cascades
National Park
3:00 Susie Imholt, Western
Washington University
Climate
change can impact butterfly populations by shifting butterfly and plant
phenologies relative to each other and by shortening the growing season. I studied the effects of day length, soil
moisture, and stream proximity on the phenology of common red paintbrush, Castilleja
miniata, a host plant of the Anicia checkerspot, Euphydryas anicia,
at two subalpine meadow sites in the North
Cascades National
Park. I
considered 14 models that include the following variable combinations to
predict growing season length: 1) day length, 2) soil moisture, 3) proximity to
stream, 4) soil moisture and proximity to stream, 5) day length and proximity to stream, 6) day
length and soil moisture, 7) day length, soil moisture, and proximity to
stream.
I
used multi-model inference to determine the relative importance of day length,
soil moisture, and proximity to streams.
I used Akaike’s Information Criterion to select the best models from the
candidate set. Day length is the most
important variable, followed closely by soil moisture. The model-averaged prediction for growing
season length for plants in moist soils is 9.5 days longer than for plants in
dry soils. Contemporary and forecasted
climate change effects on C. miniata phenology suggest that a
substantial of current habitat will become unsuitable for E. anicia due
to advancement and shortening of the growing season.
Key 11 Looking at Present and Past Forest Stand Structure at San Juan Island
National Historical Park
3:30 Dr.
Bruce Larson, University
of British Columbia
In preparation for the initiation of a larger project to
determine protocols for the management and monitoring of the forest vegetation
at San Juan National Historic
Park, we undertook to
study three forest stands in detail. One
stand with evidence of partial cutting, one with extensive windthrow, and one
with little indication of major disturbance were chosen. We used different
sampling techniques to determine in each case the nature of the disturbance and
the effects on growth and changes in stand structure. For example, we were able to learn how the
diameter structure of the stands changed over time. We will use some of the basic knowledge we
were able to acquire to assist our efforts in the larger project. Immediate findings should be of use for the
park Interpretation programme.
Saturday June 24, 2006
9:30 Welcome
William F.
Paleck, Superintendent, North
Cascades National
Park Service Complex
Key 12 Tailed Frogs in Olympic
National Park: How the Landscape Affects Gene Flow and Population Connectivity
10:00 Stephen Spear, Washington
State University:
Tailed frogs,
Ascaphus truei, are a stream-associated amphibian species that is especially
prevalent in old-growth forests such as found in Olympic National Park. There is growing concern on how logging in
unprotected areas might impact this species, but there is little data on
natural population connectivity from which to base management on. Olympic National Park is an excellent study
area to obtain information on natural population structure because of its large
tracts of intact forest. Dispersal and
gene flow in this species has always been assumed to be low because tailed
frogs have low tolerances to high temperature and desiccation. However, dispersal and gene flow have rarely
been measured.
In this
study, we sampled tailed frogs at ten sites in three different drainages in
Olympic National Park. We used
microsatellite DNA markers to estimate gene flow among sites, and quantified
the effect of landscape variables such as streams, solar radiation, canopy
cover, and slope on gene flow. We found
much higher gene flow than expected, with populations up to 10 kilometers apart
connected through gene flow. There was
little evidence to suggest that gene flow occurs exclusively through stream
corridors, and solar radiation seemed to drive overland gene flow, as sites
separated by high solar radiation had lower levels of gene flow. These results imply that the stable,
old-growth forests of the Olympic Peninsula have allowed this sensitive species
to have long movements away from streams, and suggests that populations may be
isolated in highly fragmented areas.
Key 13 Burn Severity and Whitebark
Pine (Pinus albicaulis) Regeneration
in the North Cascades
10:30 Stephanie
McDowell, Western
Washington University
Whitebark pine (Pinus albicaulis,
Engelm.) is a long-lived and slow-growing high elevation tree and an
ecologically significant part of subalpine communities in the North
Cascades. Cascadian whitebark pine
populations in Washington
are declining due to fire exclusion and an exotic fungus, white pine blister
rust (Cronartium ribicola). Stephanie McDowell, a Western Washington
University graduate
student, conducted her Master's thesis research on the relationship between
post-fire whitebark pine regeneration and burn severity. In the summer of 2005,
she studied the regeneration dynamics in the Boulder Creek Burn near Juanita Lake
in the North Cascades
National Park and in the Tyee Complex
Burn in the Wenatchee NF.
She analyzes whether there are more whitebark pine seedlings on burned
or unburned sites, and what level of burn severity produced the most whitebark
pine seedlings. Additionally, she presents an ecological model of the relationships between
environmental and biological factors that can assist in predicting the
system's response to fire.
Key 14 The Ecological Consequences of Japanese
Knotweed Invasion into Riparian Forests
11:00 Lauren Urgenson, University of Washington
Japanese (Polygonum
cuspidatum), giant (P. sachalinense)
and bohemian (P. bohemicum) knotweed
are closely related congeners invading riparian areas, roadsides, and parklands
throughout the United States
and Europe. The rapid spread of “Japanese”
knotweeds along river corridors has been of particular concern to natural
resource agencies and conservation organizations. Knotweed’s invasion of
riparian forests has the potential to alter critical ecological processes
including stream bank stability, channel morphology, nutrient cycling, forest
and understory regeneration and organic matter inputs into aquatic food webs.
Currently, there is limited field research documenting the level and
significance of these suspected impacts.
As a graduate student at the University of Washington, I have been conducting
research that investigates two suspected impacts of knotweed’s invasion: 1)
displacement of native riparian plant communities and biodiversity, and 2)
alteration of the quantity, quality and decomposition of riparian leaf litter
inputs into streams. The first year’s
field study was conducted in 2004 at Grandy Creek, a tributary of the Skagit River
densely colonized by giant knotweed, Polygonum
sachalinense.
Study results indicate a negative
relationship between knotweed invasion and the species richness and/or
abundance of native understory herbs, shrubs, and juvenile trees. A reduction
in riparian tree establishment could have detrimental and long-lasting effects
on the successional trajectory of riparian forests, bank stability, hydrology,
nutrient loading, micro-habitat conditions and aquatic biota of adjacent lotic
systems.
In addition
to the displacement of native vegetation, data suggest that knotweed invasion
alters stream
nutrient subsidies from riparian litterfall.
Results demonstrate an average 70% reduction of native litter inputs correlated
with knotweed invasion. Additionally, the C:N of senesced knotweed
leaves is 52:1, a value 38% (Salix) to 58% (A. rubra) higher than
dominant native species.
Analysis of nutrient re-absorbance from senescing leaves reveals that
knotweed reabsorbs 75.5% of its foliar nitrogen prior to litterfall. In
contrast, native species reabsorb 2.3% (A.
rubra) to 33% (Salix), thus
contributing a greater proportion of their nitrogen resources to riparian soils
and aquatic environments through leaf litter.
Litterfall from riparian vegetation
comprise a primary source of nutrients and energy in forested streams and
backwater channels. By altering the composition and nutritional value of
allochthonous litter, knotweed invasion could have a detrimental impact on the
productivity of aquatic food webs.
Key 15 Biological
Soil Crusts: An Unexplored Component of the Ecology of the High Cascades
11:30 R. Gus Jespersen, University of Washington
Understanding species distribution patterns is a central problem
in ecology, and one that has gained urgency with apparent shifts in the global
climate regime. Traditional explanations
of alpine plant distributions have focused on environmental variables,
including timing of snowmelt and soil moisture. However, a growing body of
recent work has demonstrated the importance of facilitation in driving alpine
plant distributions. This newfound
recognition of a community-level process in shaping alpine plant communities
highlights the need for a more holistic assessment of species interactions and
their controls in alpine ecosystems. Considering the number of national parks
in the Americas
with high-elevation terrain, such an effort may prove vital to forecasting how
the natural and cultural resources of these areas will change over the next
century.
Alpine meadows in the Pacific Northwest
are mosaics of plants, bare ground, and a thin layer of lichens, mosses, and
cyanobacteria, otherwise known as a biological soil “crust.” Structurally similar crusts are well-studied
components of arid and arctic ecosystems worldwide; this thin layer fixes
valuable inorganic nitrogen, stabilizes highly erodable soils, and serves as a
reservoir for scarce soil moisture.
Recent adventures in China,
Nepal, and Washington State
suggest that these crusts are ubiquitous to alpine ecosystems worldwide. I propose to investigate the ecological
functions of alpine biological soil crusts in Olympic National Park via a
series of
manipulative field experiments and descriptive surveys. I will transplant crusts surrounding adult
and established seedling plants to adjacent plants living on uncrusted
substrates and follow the growth response of the plants over the course of two
years. To elicit mechanistic pathways, I
will measure the effect of these treatments on the subterranean physical and
chemical environment. Finally, to
interpret these experimental results at the landscape scale, I will describe
crust composition and vegetation associations in this alpine basin. This work is a necessary subsidy to our
understanding of alpine ecosystems throughout western North
America, and a missing piece of the alpine plant distribution
puzzle.
LUNCH BREAK: 12:00 – 1:00 pm
Key 16 Ecological Investigations of the Elwha River:
Setting the Stage for Long-Term Monitoring of Fisheries and Ecosystem Recovery
1:00 
In 2009, Olympic National Park will begin a large-scale
fisheries and ecosystem restoration of the Elwha River.
Once a prolific salmon producing river, migration past the lower 4.9 miles of
river is blocked by 2 of the largest dams ever set for removal. These dams have
stood for over 90 years, blocking access to 70 miles of mainstem, floodplain,
and tributary spawning and rearing habitat.
The dams have altered natural cycles of sediment transport and large
wood recruitment in the reaches between and below the dams, which has had a
dramatic effect on habitat for many species, including salmon. Full restoration
of the Elwha River is expected to include runs of all
5 species of Pacific salmon, as well as lamprey, coastal cutthroat, and char.
In order to learn as much as possible about the process of ecosystem recovery
through dam removal, especially in regards to the role of salmon, we have begun
collecting baseline data of the aquatic ecosystem throughout the Elwha basin.
Our goal is to describe existing, habitat-specific patterns of microbial,
algal, macroinvertebrate, and fish communities. We are also collecting water
samples to determine levels of dissolved nutrients and stable isotopes to
develop baseline levels of "marine-derived" nutrients. These data are
necessary to describe existing conditions and will allow comparisons in both
the short- and long-term. Our presentation will include an introduction to the
scientific questions being asked, the methods employed, and preliminary
results.
Key 17 Sources
and Dynamics of Large Wood in the Queets
River
1:30 Josh Latterell, University
of Washington
Large wood supports biocomplexity and creates ecologically
valuable habitats in alluvial rivers but has declined to critically low levels
in many rivers. Some of the most
important pieces come from the erosion of mature forests containing large logs,
which play an irreplaceable role as the foundational structural members of
logjams. Conservation and restoration of large logs and the habitats they
create relies, in part, on understanding their sources and dynamics in
reference systems. We quantified the delivery of large logs (? 1 m diameter) to
the channel through bank erosion and their cycling within the channel and
floodplain over time (1939-2002) and space in the Queets River.
Our results show that 76% of large logs annually recruited to the channel by
bank erosion originate from mature fluvial terraces. The remaining 24% are
recaptured from the floodplain stockpile, consisting of abandoned and/or buried
logs previously deposited by the river and incorporated into developing
forests. Input rates increase with the size of the annual peak flows, and
channel meandering is a particularly important driver, cutting laterally up to
0.5 km through wide swaths of forest.
We estimate 95% of the logs captured by the river from 1939-2002
originated within 265 m of the initial channel margin. Input rates vary widely
among locations; wood 'hotspots' supply 38% of the large logs but compose only
10% of the valley length. These often occur at the downstream cutbanks of
newly-forming meanders fringed by mature forests. Tagging studies and photo
interpretations indicate that approximately 42% of large logs remain stable for
?10 y after they initiate a logjam, but once incorporated by riparian forests, they
become relatively stable. We estimate large conifer logs have a 50% probability
of occupying ? 3 locations and traveling ?1.5 km before disintegrating, but 10%
will travel ?12 km and occupy ?7 locations. The ongoing rearrangement of large
logs supports a shifting mosaic of habitats in aquatic and riparian
environments. Wood recruitment and dynamics in the Queets River
reflect, in part, the proximity of mature forests, patterns of channel change,
and variation in flood magnitude, providing a model system for floodplain river
conservation in the Pacific coastal ecoregion.
Key 18 Monitoring Streamflow in Cascade Mountain
Headwaters: Why is the Hydrograph Useful
and What Can It Tell Us (Or Not)?
2:00 Anne Weekes, Ph.D. Candidate, University of Washington
Streamflow
gauges were installed in comparable headwater catchments in North Cascades
National Park and Mount Rainier National Park
to investigate potential differences in patterns of response. Installed as part
of a park-wide monitoring program, analysis of the gauge data has shown that
aquatic habitats may vary considerably between seemingly analogous streams
based on differences in streamflow regime. Some of these differences suggest
that earlier assumptions about the behavior of mountain streams were too
generalized to be useful.
For
example, it was commonly assumed that little groundwater storage occurs in
mountain basins. Particularly in mountains composed of the crystalline bedrock
found in many parts of the North Cascades, hydrologists were confident that the
groundwater contribution was slight. The combination of steep slopes, thin
soils, impermeable bedrock and rapid response to rain and rain on snow events
led scientists to assume that little water was stored within the basins
themselves. This “Teflon
Basin” theory was
difficult to test in remote mountain drainages for a variety of reasons, not
least of which were the inability to “see” below the surface in remote
wilderness areas.
Streamflow
gauges placed in adjoining headwater drainages demonstrate that some basins
will show rapid response to storm events while others will behave like
traditional groundwater systems with a muted response to precipitation events
and comparatively high flows during dry periods. The story does not stop there; results from
the use of stable isotopes to determine the age of water have displayed marked
differences in the residence times of water in adjoining basins. As
precipitation falls on headwater basins with larger storage capacities, the
“old” stored water is displaced by the new water so that water flowing
downstream is not always dominated by runoff from the current storm.
Streamflow
hydrographs can also reveal other differences and similarities in the response
patterns of these headwater catchments. In conjunction with potential changes
in climate patterns in the coming years, these gauge records will provide
important insight into current conditions, especially when compared to past
years of record.
Key 19 Effects of Thinning and Prescribed Burning in Forest Fuel Reduction
Areas of the Stehekin
Valley
2:30 Karen
Kopper, North Cascades National Park
The
fire management team at the North Cascades National Park
utilizes thinning and prescribed fire to accomplish its goal of hazard fuel
reduction in the Stehekin
Valley. Thirty-four forest plots have been
established within the treatment units in order to monitor the effects of the
treatments on tree density and basal area, native ground-cover and fuel
loading. Preliminary results from the
monitoring suggest that a combination of thinning followed by prescribed
burning may yield a more desirable outcome than using either treatment
exclusively. Selective reduction of the
canopy trees can be successfully achieved through mechanical means, whereas
prescribed fire is needed to consume the additional fuel concentrations in the
thinned areas, and to stimulate new growth in understory vegetation.