8:33AM
Good morning. Today starts out with a discussion of young growth - generally
trees less than 150 years old - headed by Mike McClellan. Apparently the
bird discussion yesterday was quite good, and I hope to have those notes
available today, as well as Brown Bear. My apologies for not having those
available yet. Last night we had a spectacular presentation on deer modeling
for subsistence and sport hunting; it was created by Larry Edwards and
clearly delineated the differences between good science and data application
and what happens currently on the Tongass. This afternoon there will be
a Forest Service presentation on the same subject: the deer.
The Tongass has 430,000 acres of young growth, 30% of
which are in old growth reserves. About 25,000 acres need some sort of
treatment.
6 classes of young growth, roughly: growth on wetlands
after clear cutting, growth response to pre commercial thinning, wood
quality effects of thinning and pruning, performance of FVS-SEAPROG growth
model (they say it performs well generally), silvicultural treatments
and under story restoration, effects of variable retention harvesting
of old growth. Those last two will be focused on from a conservation perspective.
Graphics displayed currently compare deer days per hectare,
with old growth over 400, young growth less than 100, and commercial thinning
around 300. I am not certain how these numbers are derived.
Lots of talk about how managed stands provide good foraging
for deer.
Adaptive management: assess, design, implement, monitor,
evaluate, adjust, assess, design...
8:56AM
Various experiments are being conducted under the acronym TWYGS - Tongass-wide
young growth stands: planting red alder in recently cut stands, pre commercial
thinning of 15 to 20 year old stands, pre commercial thinning and pruning
of 25 to 35 year old stands, thinning of older non timber stands by girdling,
treating riparian stands (this is just developing). There is also an extensive
commercial thinning study taking place on Heceta Island via strip thinning
and two intensities of individual tree selection, 25 and 50 percent basal
area removal. They are applying this in single aged and two aged stands.
Alternatives to clear cutting is being briefly discussed
now: study started in 1994, cutting intensity from 0 - 100%, spatial arrangement
is in clumps, gaps, or uniform, and patch size is .2 .8 and 1.75 acres.
The slide shows a graphic of various arrangements with 25% retention.
A disturbing result is the mortality of residual trees.
After the harvesting and 5 years have passed, the survival percentages
are incredibly low. These slides are worth studying further.
Mike McClellan firmly believes in active management of
young stands. as it has a significant potential for restoring diverse
and abundant under story plant communities and perhaps other old growth
structure. Residual old growth trees and snags left for structural purposes
are at considerable risk for losses due to wind throw. It may take a long
time to get new knowledge through these studies. Increased emphasis on
process level mechanistic studies, coupled with modeling, may provide
answers to management concerns in a more timely manner.
Considerations: continue with TWYGS and ATC studies,
add riparian and perhaps variable spacing studies. complement existing
empirical trials with a new program investigating processes, etc. Develop
markets for small diameter wood will be essential for active management
of young stands for habitat improvement purposes (this would subsidize
the more widespread management of young growth).
No data currently to quantify clumping sizes that won't
be adverse. From a logger standpoint, strips of 200 to 300 feet are necessary.
From an ecological standpoint, we do not have data for stripping. It is
ecosystem dependent, perhaps on species.
9:33AM
From an operational viewpoint, all the ATC studies were performed via
helicopter logging. Linda Christian did some sort of analysis on this
(she is not present), and covered costs and production rates at Portage
and perhaps the second ATC site. The estimates for setup costs are up
only 5% - not a huge additional burden, according to Mike McClellan. Colleen
Grundy does not think that within the conservation strategy there was
any contribution from young growth. She believes there should be consideration
of older young growth in the matrix. She does not believe there should
be a standard and guideline for implementation at this point.
A problem for ATC study is finding
meaningful info for wildlife. Under story vegetation for deer is the only
real measure, currently. Difficult to get measurements for birds and for
small mammals. It is cost prohibitive.
It appears there is a push to include
young growth, through study, in a market demand process. Can some commercial
value be defined?
Because beach fringe is out of
the commercial base, they have been the least treated. There is a presenter
stating now that there should be some treatment of beach fringe for the
sake of wildlife.
It may be good for the Forest Service
to do a comprehensive study of where these areas are and what value that
they have, according to some of the working group members.
There is some question about how
different restoration would be if it was pursued in the name of wildlife
rather than for timber. No clear answer it seems, although there is some
value to returning to stands several years after thinning to revamp for
wildlife.
9:40AM
BEAR REPORT rough draft that I will clean up later, but here is the gist
of the presentation....
Rob Flynn:
Hi public interest and demand – viewing, hunting etc
Need to id and mana imp habitat and impact of mana activities
TLMP S&G
Imp eating/foraging sites need addit protect (in addition to rip buff,
beach etc)
Approx 500 ft addit prot for feeding/pot hum interact spots
Import bear eatin site
What does “important” mean in this context
Hi use? Veg food sources? Salmon areas?
Prev info
Admiralty and Chich study sites
New info
Chich- LaVern Beier, Steve Lewis, Grey Pendleton, Rod Flynn
Compare resource use and #s in areas w/ diff mana prescrips
FS & native corp study areas (Freshwater Crk & Spasski Crk)
Very hi-tech study w/ GIS info, DNA analysis
Male/female behavior on streams is very diff
Spasski: Male goes up & down regularly
Spasski: Female spends little time on stream, but goes up into forest
regularaly (even w/o a cub up in a den)
Freshwater: fm goes up into mtns almost daily using diff routes, lots
of time at mouth of stream
Males focus on streams, but a little less than Spasski
Seal Crk: fm goes up quite a bit, but again does visit stream
Freshwater: fm generally stay closer to the stream, but bulk of concentration
is near the crk
Spasski: still bulk is very near stream, but they go much further on avg
More bear use on Freshwater, particularly for fm
Bears eat considerable amount of veg, even when on streams
More salmon consumed on Freshwater, some on Spasski ate hardly any
Considerations
All salmon spawning streams are imp for bear foraging
Sm. streams imp for females and young
Forested buffers are imp
Streams w/ substantial buffers have more fms, they spend more time there,
they eat more salmon
More salmon leads to healthier, more productive salmon
At least 500 ft along all salmon spawning streams
But if you want to maintain abundant pops, need 1,000 ft (b/c bulk of
bear use is within 937 ft of stream)
Use GIS to map buffers, or have field folks have to prove that bears are
not using the area
(DAVE STEPS OUT HERE)
A floodplain model was developed as a function of slope and distance from
the stream. The model creates a variable-width buffer along salmon spawning
streams.
Brown bear model as applied to salmon streams show watersheds that have
the highest value.
Consideration: maintain habitat diversity, minimized habitat fragmentation,
eliminate road access, minimize human access, maintain watershed integrity.
S&G apply to road access. From a management stand point, brown bear
guidelines are of high priority, especially in the guiding arena. FS,
FG use these as guidelines for harvest in Unit 4. Work is now underway
from FS and FG for Unit 1, on the Unich, Bradford. FG are receiving funding
for looking at brown bear density to get real representation across the
land.
Kim Titus- published an article on brown bear. Class 1 streams include
salmon that are little and of no use to them..there needs to be a management
prescription that includes this. We need to include the fisheries to apply
a look at this aspect. Class 1 vs. Class 5
Panel- We feel the same.
DeGayner- can you measure absolute density, see a population response
as a behavior response?
Panel- there might be bears on the stream, but doesn’t equate to
a salmon diet.
DeGayner- tie in the consequences of the fitness of the population
Panel- agree
Kim T- it is more than likely that females change their use patterns,
they don’t change watersheds, social pressure of not having cover,
long term pattern and changes ie salmon
In looking at the model-road or no road. Northern Kuiu- hunters say the
bears are in the north. But models show with the road there are little
to none.
Panel- We picked up several bears in the early 90s
Kim T- female bears on Chichagof have the smalles home ranges of any bears
that have been studied in the world.
Forest- do you know the pop trend on this piece of real estate
Panel- maybe climate increase is good for bears..do you want more for
the future or less..
F. Cole- in terms of comm. use what does the trend analysis show?
Panel- those typically follow where you have more people..like on the
Chich-it’s not really a big impact to show concern. Guided hunting
does take the majority of the bears that are harvested in Unit 1 and 4.
We don’t know how the harvest of parts will increase local interest?
F. Cole- Are you seeing in the trend in the size of animals being harvested
getting smaller..due to climate change, or hunted over time.
Panel- No. For both bear species, we get skull measurements, that is the
reliable measure, and the sex and age..using teeth..over time there has
been no change. Desired harves 60 % male, 40% female. Unit 2, we don’t
see significant changes in size..subtleties can grow. As for this moment
this is not a concern.
Titus:
Guides don’t always kill biggest bears, and don’t always report
the truth
Kuiu did see a sig. change in skull size, sex ratios, and we imposed restrictions
b/c of it
Being able to see the change means it is likely more sig. than we think
DNA technique is good b/c bear is not visually marked
Cole:
Should we modify state bear hunt regs region wide?
????
1000 ft buffer for private lands as well as NF
Flynn
Doesn’t think there is much forest beyond the 500 ft buffer on state
land
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Day
One ~ Day
Two ~ Day
Three ~ Day Four (th)
Conservation Strategies Updates,
continued...
??? L
unit 4 results are not the same as the #s on the mainland
there are less bears on the mainland, and this could be considered
Hastings
Salmon are imp for bears, but what about bears as being imp for spreading
marine goodness throughout the land itself
Lewis
beyond 500 ft is often where they are bedding, so they obviously are
spreading nutrients far inland
Hastings
There is good science on this, and we should use it
Titus
To some extent, once a forest grows beyond a certain lvl, and there
is a certain lvl of canopy, the size of the tree doesn’t really
matter
As long as there is a stream, the bears will use it
Flynn
Buffer does not depend on tree type/size
Partial logging may be ok w/in buffers
Bears in 2nd growth are mean
???? L
importance of salmon is not unique to bear
Bill Hanson
Bears that don’t eat salmon, Spasski fm bears concentrated away
from stream, but what is in these other areas that attracted the bears?
Do these features need to be protected in some way?
???? L
females were up & down the river in similar patterns at diff streams
(therefore general attractiveness, not particular)
berries
Bill Hanson
why are there not similar guidelines for black bears as there are for
brown
DeGayner
Brown bears were greater public concern
Flynn
Parsons
Re sex, age, skull size
Black bear hunted data
Yet to see data look at age structure that was sensitive enough to notice
change
Same with skull size
Cole
Guides want the biggest bears
Are we seeing trends towards a sm. size (answered above)
Jon H
I understand you looked at 2 streams w/ differing buffer widths
3rd stream was not examined b/c 2nd growth was too big a barrier to
bears
what is the functional buffer areas that you are trying to provide for?
What are the specific conditions bears are taking advantage of
Flynn
Study was designed to look at 2 streams w/ similarities
We are looking forward to doing more analysis
We don’t anticipate doing any on the ground site analysis, though
it could be done
????
bears were using small streams as well as the big ones
has logging impacts to these streams been examined in relation to bear
use
Flynn
Bears will travel through clearcuts
Berries etc in disturbed areas
Found little use (& there has been little use analysis) of clear
cuts that abutted steep/high ground
All the bedding etc seems to be in the forest itself, though they will
traverse these bare areas
Tom
Are floodplain's off limits, or just the 500 ft corridor around streams
Cole
TTRA requires protection of class II & I streams
Lunde
Floodplain's themselves are covered by beach fringe and stream protections,
but don’t have any themselves
Tom
These are some of the most species rich areas for bears and others
Titus
Was involved w/ Brown bear S&Gs formation
Appeared policy direction through TPIG was to add clarification for
FS staff
Remove buffers and fringes
What is then left over?
Sm. pink streams are very imp for bear
If these are already protected by other protections, there is no need
to erect additional protections
Lewis
There is not much FS implementation of S&Gs b/c FS still not sure
what they are looking for
Sm. streams are import.
Do you have to protect these streams vs. pollution
Reach of salmon runs varies over years, and this needs to be considered
S&Gs are not being implemented b/c uncertain of their effectiveness
10:45AM
Dave Person is now presenting on wolves in Southeast Alaska. Wolves
in SE are related to wolves in coastal BC. Coastal wolves are a unique
population with low diversity. Wolves on POW are isolated from all other
wolves in Southeast Alaska. The opening premise is that they are difficult
to monitor.
Guidelines:
Deer Density guideline is rather important, based on Monte Carlo simulations,
and produces a model of 17-18 deer per square mile. Does the deer density
guideline work? Deer mortality studies show percentages related to harvest,
wolf, bear, and other. Most bear predation on POW is on neonatal fawn.
Dave Person concludes that the original parameterization
of the model is good after analysis with empirical data (about 100 deer
per wolf).
Road Density guideline is .7 miles per square mile.
The guideline is based on regression of average wolf harvest between
1900-95 within the wildlife analysis areas against total density of
roads on all lands below 370m elevation. It was not based on density
of open roads or all land area. IT has not been applied correctly based
on Person et al. 1996. There have also been questions about the scale
at which it should be applied.
What do we really mean by open and closed roads? Dave Person does not
know.
Dave Person performed analyses of overkill harvests
and max kill harvests. Probability of overkill at .7 mile per square
mile connected to the main road system is 40%. Prohibit overkill at
.7 mile per square mile and not connected to the road system is 13%.
Destructive harvest probability for road system at this number is over
60%.
Roads exert strong influence on wolf mortality. The
.7 number needs to be adjusted for a true open road system. The scale
should be 300 square kilometers.
Denning and timing restrictions: something was mentioned
about 1200 feet, but I missed its premise. Guideline is too small and
should be reviewed. Roads effect den site selection, logging disturbances
less so. Inactivity for 2 years does not imply den is abandoned. Current
guidelines unsupported by evidence and should be revised.
Wolves and old growth reserves: OGRs as structured
in TLMP are more appropriate for wolves, although not specifically designed
for them. Home ranges are considerably larger than the largest OGRs.
Future considerations for wolf must include cautionary
approach to the matrix beyond OGRs.
Ball in the Box Theory is important with predator-prey
systems.
11:50PM
OGR strategy must consider wolves and wolf mortality, says Dave Person.
1200 feet refers to the standard
and guideline for a buffer around active dens between April 15 and July
1. There is to be no road construction within 600 feet during this time.
If the den is not used for 2 years, it is inactive. These are the current
denning and timing restrictions, and faulty, according to Dave Person.
Verrrrrrry few questions for
Dave Person after this presentation. Interesting. Two questions from
Kim Titus and a comment, while the rest of the workgroup is essentially
silent currently.
What will happen as deer decline?
There may be greater pressure to control predators rather than subsistence
or sport hunting.
Illegal hunting of deer and wolf
is a significant problem.
Fish and Game and the Forest
Service need to give more importance to unique species in the Forest,
according to Dave Person.
Gene DeGayner now asks what would
happen if clearcutting was ended. Dave Person says that has been modeled
and while there would be benefits, much of the limitations are due to
practices over the last 50 years.
With dispersal, if wolves do
not settle within 23 weeks, they are dead, according to Dave Person.
1:48PM
Deer are on tap this afternoon, and this presentation is led by Tom
Hanley.
Forage Resource Evaluation System for Habitat (FRESH
- Deer):
a snapshot analysis at one point in time; a food based system; provides
an estimate of deer days per unit area calculated from known nutritional
relations; identifies limiting factors and most important forages; transforms
summer data sets to snow free winter estimates and includes a snow sub
model to account for burial by snow; operates at two major scales: Stand
(web based) (on the UA system)and Landscape (GIS based).
Advantages: objectively based on nutritional science;
can evaluate any habitat without need for use by deer; can evaluate
habitat for any user specified metabolic requirement; identifies limiting
factors and forages;
Disadvantages: data analysis system, not a stand alone
model; deer days is an index, not an estimate of carrying capacity;
data requirements are great and labor intensive (biomass and chemistry);
Tongass databases need much work; snow sub model needs field verification;
does not account at all for animal behavior or other non-food factors.
Added to Dave Person's model for deer, this is applicable
at the landscape level of analysis (watershed) and may provide a behavior
based model.
Advantages: account for animal behavior; incorporate
the full landscape; data based
Disadvantages: Statistical, descriptive, not predictive,
etc.
Deer Pellet DNA Census Technique could produce interesting
comparisons to routine and less expensive techniques.
Tom Hanley is suggesting the Forest Service utilize
FRESH-Deer. Now it appears the suggestion actually is to stay with the
same model, for now, until there is proper data. This comes from a prompting
question from Gene DeGayner.
Also, I found this article interesting: Delusions
in Habitat Management
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