Official Comments of
MFMU
Kootenai National Forest Supervisor Bob Castaneda
1101 U.S. Highway 2 West
Libby, MT 59923
RE: Grizzly Bear Recovery Zone Environmental Impact Statement (EIS)
Dear Mr. Castaneda,
In general, Montanans for Multiple Use position in regards to the "draft
environmental impact statement (DEIS) forest plan amendments for motorized
access management within the Selkirk and Cabinet-Yaak grizzly bear recovery
zones" affecting the Kootenai, Lolo and Idaho Panhandle National Forests,
is that it is not necessary or appropriate to amend three forest plans to
accommodate the grizzly bear. The various lawsuits and agency decisions that are
driving the "need" for an EIS do not specify the conditions of road
access - only that management must address the issue "using the best
biological information and considering the social and economic impacts." If
this had been done, a Grizzly Bear Recovery Zone EIS wouldn’t be necessary.
The science used in the DEIS, while "best available", is outdated
and suspect. Two premises are being used to justify road closures and road rip
(destruction). One is that grizzlies avoid roads thus denying themselves the
survival benefits of roaded habitat, and two, that roads contribute to the
untimely deaths of the bears. Part of the "science" used to determine
that grizzlies require roadless areas is suspect. One of the main contributors,
Mr. Wayne Kasworm was president of the Montana Chapter of Wildlife Society,
before, during and after much of the original research was being done. The
philosophical bias of this organization towards limiting all human access to
forest areas is well known. Is Mr. Kasworm’s science biased? Is this
"conflict of interest" too much like the "scientists"
recently caught planting evidence to prove the existence of Canadian Lynx
population in Washington state, which also would have denied human access to
those forests being studied?
Close scrutiny of the "Final Report: Grizzly Bear Ecology in the Swan
Mountains", 1997, R. D. Mace and J. S. Waller, used as the scientific
bedrock to justify closure of forest access to motorized vehicles, reveals
insufficient data collection, unsubstantiated and contradicted telemetric
sessions and resulting analysis anomalies, potential inflation of core area
data, no recommendation for road rip (destruction) at all, and unproved
"hypothesizes" such as increasing road traffic tends to lead to
decreasing bear use. Current science is uncertain about how grizzlies react to
roads in their neighborhood, and an actual number count of grizzlies in the
wild is still "speculative", even after nearly two decades of grizzly
bear study and management. How do we know whether current recovery methods have
been successful, or that further restrictions of human access to valuable forest
resources is appropriate? How do we know that "increased human caused bear
mortality" - cited numerous times in the DEIS as justification for proposed
action - isn't a result of a flourishing bear population spreading into
developed areas? The Interagency
Grizzly Bear Committee recovery specialist (Servheen) has stated that higher
mortalities would be a product of a larger bear population: "If there are
more bears out there, you would expect more mortalities." (Jim Mann,
"The Daily Inter Lake", 12/02/01.)
The consequences of decommissioning roads were improperly evaluated. Very
little weight has been given to habitat manipulation options that will be
foregone in the future or the significant social and economic impacts. As we
understand the DEIS, the Forest Service proposes to reclaim
(rip/decommission/destroy) 520 miles of restricted roads, reclaim some 61 miles
of open roads, restrict some 36 miles of open roads, and restrict some 13 miles
of trails. Where is the map that discloses this information? How can these
destructive measures be justified to limit access to another 2.2-million acres
of forest resource lands, given that past closures dismiss human and economic
impacts with statements like "no significant impact" or "moderate
impact?" Why aren’t the original construction costs and purposes of these
roads included in the DEIS? The loss of millions of dollars worth of roads will
mean that the areas can no longer be accessed for its intended purpose and the
resource use as well as recreational use is lost forever. Isn’t the Forest
Service supposed to reveal the cumulative effects of its actions as well as
opportunities foregone? What are the opportunities lost and associated costs?
The economic sections of the DEIS don’t even mention the timber industry and
what has happened to it since 1982, when the original Grizzly Bear Recovery Plan
was implemented, nor the current Kootenai National Forest Plan approved and
implemented in 1987 - no mention. Doesn’t this seem odd since Lincoln County
is a resource-based industry county? Under the 1987 Kootenai Forest Plan, the
Forest was to produce 227-million board feet of regulated timber, and another
6-million board feet of unregulated, annually. In 2001, the Forest only sold
51.8-million board feet and actually harvested 50.2-million. Why the
discrepancy? And what is the economic impact of present policies, let alone the
closures proposed in the DEIS? How can you possibly manage these lands with a
57-trip restriction across three forests with different management groups?
Decommissioning or road rip (destruction) surely causes more short term and
long term sedimentation of streams than asserted by the DEIS. Pictorial evidence
of South Coal Creek culvert removals on the Flathead Forest showed massive
erosion, well above predictions. Long term forest employees will tell you that
culvert failures are very rare. Coupled with this erroneous hypothesis is the
fact that the costs of reduced fire prevention and suppression haven’t been
identified.
Lastly, our understanding is that it is improper and illegal to fail to
include a no action alternative in a DEIS, even if the action has been forced by
litigation. By definition of your proposed "Alternative A - No
Action", you have not truly provided a "no action" alternative.
Despite all the "legalese" wording of the DEIS, it appears to us that
you are ignoring the law. Are you? We propose that the Forest Service tell the
judge and the litigants who filed the lawsuit, that it is impossible to comply
with the National Environmental Policy Act, the National Forest Management Act,
and sound professional ethics, by submitting the DEIS as written.
Sincerely,
Clarence Taber
President, Montanans for Multiple Use
Official Comments of NorthWest Montana
Gold Prospectors
December 24, 2001
NorthWest Montana Gold Prospectors
Box 3242
Columbia Falls, MT 59912
Kootenai National Forest Supervisor Bob Castaneda
RE: Grizzly Bear Recovery Zone EIS
Dear Sir:
Northwest Montana Gold Prospectors is a non-profit association of
recreational prospectors and small miners banded together to promote our mutual
prospecting interests. We have 185 member families, mostly from Flathead and
Lincoln counties. We have claims on drainages on the east side of the Cabinets.
We also prospect in the Vermillion River, Silver Butte, West Fisher and Yaak
areas of Montana and the Boulder Cr. and Clearwater River areas of Idaho.
The various lawsuits and agency decisions that are driving the need for this
EIS do not specify the conditions of road access only that management must
address the issue "using the best biological information and considering
the social and economic impacts.", Ch 1, pp5 If this had been done we
would not have the Grizzly Bear Recovery Zone EIS
We believe that none of the alternatives are adequate because:
The biological information used in this EIS is not necessarily the best and
much of it is suspect.
The consequences of decommissioning were improperly evaluated
Insufficient consideration was given to the social and economic impacts of
this EIS.
"A majority of the public clearly displayed their disapproval of
additional access restrictions, particularly on the Kootenai National Forest
portion" Ch 1, pp6
It is improper and illegal to fail to include a true no action alternative
in an EIS.
The irreversible and irretrievable loss of the road assets that will be
decommissioned is not sufficiently addressed.
THE SCIENCE IS INADEQUATE TO JUSTIFY WIDE SPREAD CLOSURE OF ROADS ESPECIALLY
THE IRREVOCABLE LOSS OF RESOURCES INVOLVED WITH ROAD DECOMMISSIONING
Two premises are being used to justify road closures and road rip. They are
that grizzlies avoid roads thus denying themselves the survival benefits of
roaded habitat and that roads contribute to the untimely deaths of the bears.
Part of the "science" used to determine that grizzlies require
roadless areas is suspect. One of the main contributors, Mr. Wayne Kasworm was
president of the Montana Chapter of Wildlife Society before, during and after
much of the original research was being done. The philosophical bias of this
organization towards limiting human access to forest areas is well known. Is Mr.
Kasworm’s science biased?
Additionally, the science for this proposal is based on two studies, one of
which is "research from the South Fork of the
Flathead River regarding how road access affects grizzly bears (Mace and Manley
1993, Mace and Waller 1997).Ch 3a pp16.
The title of the research is Final Report: Grizzly Bear Ecology in the Swan
Mountains. We examined this research and found some inadequacies with it
that suggest this study is in an unsuitable basis for a forest plan amendment.
DEFICIENCIES IN THE "Final Report:..." REGARDING ROAD AVOIDANCE BY
BEARS.
Data Insufficiencies
Not enough data
"...it is clear that bi-weekly aerial telemetry flights were
insufficient to accumulate the telemetry sample sizes necessary to analyze the
fine scale patterns of habitat selection." Mace, R.D. and J.S.
Waller. 1997. Final Report: Grizzly Bear Ecology
in the Swan Mountains , pp 27
How then can something as finely scaled as a road habitat selection be
analyzed? This lack of data affected several areas of the study.
Telemetric sessions
The telemetry was limited to 1 session/wk in 1988 and 1989 and 2 session/wk
from 1990-1994. They only gathered data in the morning between 7am and 11am
ibid. pp13. The statement that bears "moved little at night" is
unsubstantiated and contradicted by data from movement collars. According to
charts on page 100, bears are active from 5am to 11pm.
The data is biased because it was collected only in daylight for 4 hours in
the morning while the bears were active for16 hours/day. If these bears are
clever enough to recognize a threat from humans, they also must be clever enough
to figure out that humans are not very active or dangerous in the dark. One
could expect to find different results from data that took the nocturnal
wanderings of the bears into account.
A new study in the Middle Fork of the Flathead that is now in progress uses
GPS collars that sends satellite location data every hour, 24 hours/day.
Although this study is not intended to investigate bear reactions to roads,
perhaps the study could be adapted to shed light on this subject.
Core Areas
Seasonal home ranges were determined with data from only 19 bears. Ibid.
pp13
"We were unable to estimate core home ranges for each individual
annually and therefore combined the summer and autumn season into I period(
late season) to obtain a minimum sample..." ibid. pp19
"...therefore we could not investigate annual shifts in core
areas." Ibid. pp20
Because of this a multi-year core area was used for study. This
potentially caused an inflation of observed core areas - a data bias that
reverberates throughout the science. More sessions and more collared bears
would have increased data reliability
Cutting Units
The study discovered that bears actually favored some cutting units during
Summer. ibid. pp27
High succulent forage which is valued by bears was "due in part to
past timber harvest..." ibid. pp92
"We found that cutting units can provide preferred habitat during
summer,..." ibid. pp120
Since logging has a beneficial effect on bears and roads are necessary for
logging, some roads would be indirectly beneficial.
Difference Between Low Use And High Use Selections
Table 7.1.5 indicates that bears were neutral or only slightly negative in
their reaction to low use roads (<=10 car trips/day) in their home ranges.
ibid. pp72
"Conversely, no strong relationships were observed for closed road
density and bear density." ibid. pp33
"Most grizzly bears exhibited either neutral or positive selection for
buffers surrounding closed roads and roads receiving <10 vehicles/day." Ibid.
pp64
"Neutral use of, or positive selection towards habitats near roads
implies that important habitats occur near roads." ibid. pp73
The reverse must also be true. Negative selection implies that important
habitats are not at that time occurring near roads. Bears make seasonal habitat
selection based on foods of choice for that season - whether near roads or not.
Hungry bears go to where the food is.
Road Rip
There is no recommendation for decommissioning or road rip anywhere in this
document although the authors do recommend road closures. ibid. pp 73
Assuming that Mace et al are correct and bears do avoid OPEN roads to some
extent, road rip is not necessary; neither is closing roads in some cases. Often
seasonal closures will suffice.
Spring And Lower Elevation Habitat
Spring closures
Since authors believe bears avoid roads and since most roads occur at lower
elevations which is also where a lot of early spring forage is found, the
authors think that detrimental road impacts are highest during spring. Ibid.
pp91 This hypothesis could be tested by carefully studying bear use in a low
temperate forage area that is heavily roaded and then restudy after a few years
of spring closures or do the reverse and open a closed road and study.
Year round closures and road rip are not necessary to provide a benefit to
bears if indeed there is a benefit.
"Motorized restrictions should be most pronounced during spring, and
could be relaxed somewhat in non-core areas during other seasons."
Ibid. pp121
Lower elevations
Mace et al postulated that bears avoided lower elevations because of greater
human presence. Ibid. pp16
However they overcame there fear in spring when they were hungry, if indeed
they really were fearful, to feed on new green plants at lower elevations. The
question is did they underuse lower elevations during summer and fall because of
fear of humans or because of preferential food sources higher up later in the
year?
Table 7.1.4 shows that from a sampling of 15 bears there was almost an equal
preference for or against selecting roaded habitat in the spring. Ibid. pp71
"Under certain habitat conditions and seasons, the positive
attraction to specific cover types were stronger than the negative impacts of
roads." ibid. pp120
Both this study and the Grizzly Recovery EIS assume that bears avoid roads to
their detriment. This is definitely not the case with closed or low use roads
and may not be the case with moderate use roads. Are they avoiding roads or
following their nose to habitat not commonly found near the more heavily roaded
areas.?
HABITUATION IS NOT THE ONLY REASON FOR INCREASED MORTALITY
Population
In the Swan,
"There was a 59% probability that the population was stable to
increasing." "...area was at or near capacity under present landscape
conditions." ibid. pp 102
Experience in NCDE indicates that population estimates made by radio collar
techniques are low.
"But in 1998, U.S. Geological Survey researcher Kate Kendall
embarked on an elaborate study to develop a population estimate for the
greater Glacier area. The study involved scent-baited sites surrounded by
barbed wire that snagged bear hair. The hair samples were analyzed for
genetic information that led to a count of individual grizzlies within the
study area.
Through a mark-recapture statistical analysis, Kendall developed a
population estimate of 332 bears in Glacier National Park and 437 bears
within the 2-million-acre greater Glacier study area.
The unprecedented count surprised many because it was higher than expected.
And it raised the possibility of counting bears throughout the
ecosystem.", Jim Mann The Daily Interlake 12/02/01
In this grizzly recovery area:
"Until 1999 the population had been slowly increasing; however,
mortalities during 1999 and 2000 apparently put the population on a slightly
declining trend, though the confidence interval makes this conclusion
statistically uncertain. ", EIS Ch 3a-pp6
Mortality
Repeatedly this DEIS refers to increased human caused bear mortality as a
perceived reason for the Need for the proposed action. If population is at
maximum carrying capacity then the mortality rate, both natural and human
caused, WOULD increase.. Increased mortalities may indicate population growth
pushing bears out into human zones.
"But Servheen sees the higher mortalities as a product of a larger
bear population: ‘If there are more bears out there, you would expect more
mortalities.’" , Jim Mann, The Daily Interlake, 12/02/01
If the increase in mortality is a result of a flourishing bear population
then there is no Need for this action to protect them. We need something more
than population estimates that are several years old and are based on outdated
methods and questionable assumptions.
The authors of the Swan study document 3 cases of "malicious
killings" - unreported outside of hunting season. Ibid. pp 105-106
Malicious killings may be the result of anger directed at bears for loss of road
access. Thus road closures and other FS policies designed to protect bears might
also cause increased mortality. Law of Unintended Consequences.
If the Grizzly Bear Recovery Plan requires 0 mortality, Ch3a-pp14, it is an
unreasonable plan because the nature of this animal would bring it into
increasing conflict with humans as the population recovered. Since the plan is
flawed, it cannot be used as an impelling need for this EIS or as a basis for
the standards for this EIS, particularly for the drastic measure of
decommissioning 598 miles of road..
CONCLUSION to CRITIQUE OF Final Report: Grizzly Bear Recovery in Swan
Mountains
This study only shows that, for some reason and to some degree, bears use
roaded areas less than unroaded areas. It hypothesizes that increasing road
traffic tends to lead to decreasing bear use. The hypothesis is unproven. There
were occasions when at least one class of bear used roaded areas greater than
expected. The more heavily roaded areas tend to be at lower elevations with
different vegetation types which may not be preferred by the bears during some
seasons. More study is needed to determine the cause of underuse of roaded areas
by grizzlies.
The study does not quantify harmful road densities. That is left to forest
managers who are often too eager to close roads to the public.
The study also shows that year round road closures and road rip are not
necessary for grizzly survival even if avoidance behavior is accepted as fact.
The study does not support the need for the extreme road proscriptions
proposed by Alternatives C & E. Nor does it support the proscriptions
proposed in A & B, to the extent proposed.
CURRENT SCIENCE IS UNCERTAIN ABOUT HOW GRIZZLIES REACT TO ROADS IN THEIR
NEIGHBORHOOD. The fact that some bears ignore the presence of roads and
others avoid them can be interpreted in contrasting ways.
"Some bears may become conditioned to the presence of vehicles and
humans on roads and thus become more vulnerable to direct mortality through
the means identified above. Other bears may be displaced from preferred
habitat by the human disturbance associated with road use, with a resultant
reduction in habitat availability and quality and potential effects on
nutrition and reproduction." Ch3a-pp11
All the bases are covered in this unscientific justification for closing
roads. You could just as easily say that some bears will become comfortable with
roads and thus able to cross highway barriers and enrich the gene pool of a
grizzly recovery area other than their own while other bears learn to stay away
from human developments thus protecting the core population from human caused
mortality. The position one takes on this issue often depends on pre-conceived
opinion rather than scientifically discovered fact.
Until an up to date population study and a carefully crafted study to
determine the real affect of roads on grizzlies can be done to verify the Need
for more restrictive habitat controls, the irretrievable loss of 598 miles of
taxpayer funded roads must not take place. Nor should the public
be discomfited by road closures that are based on conjecture and outdated
studies.
THE DECOMMISSIONING/REHABILITATION OF ROADS, WHICH WE REFER TO AS "ROAD
RIP", IS UNNECESSARY, WASTEFUL, DESTRUCTIVE AND NOT SUPPORTED BY SCIENCE. Road
rip is a highly controversial action. It is relatively new and not well
understood.
IT:
adds more sediments to streams than simple closure or even
public use.
On page 67 of Ch 3a the claim is made that many road failures have
occurred. The claim is not documented and the exact number and severity of the
failures is not recorded. Personal testimony from retired long time FS
employees on the Flathead NF reveals that culvert failures are very rare.
Statements on 3a-70 to the effect that culvert removal would "outweigh
the short-term negative effects of the work required to make proposed roads
hydrologically neutral." are contradicted by photographic evidence (www.mtmultipleuse.org)
in the Big Creek drainage of Flathead NF
The erosion from road rip extends long after the initial excavation of
culverts and is many times more extensive than indicated on page 70. A retired
30+ year veteran of the Flathead National Forest states that he does not
recall more than 2 or 3 total culvert failures in his entire career. If we
take a rate 3 times that, which is highly unlikely considering that road
construction standards are much higher today than previously, we could expect
9 culvert failures in 30 years.
Using figures from the Spotted Beetle project on the Flathead Forest the
expected average sediment delivery from a road failure is 11.5 cu. ft. Nine
failures in 30 years would yield (9 X 11.5 = 103.5 cu.ft.).. They expected to
remove 44 culverts to rip 48 miles of road which, by their calculations would
immediately yield a total of 127.6 cu. ft. under a moderate" erosion
scenario. Thus nine failures over 30 years would yield less than the sediment
delivered immediately after culvert removal.
The total sediment delivery of culvert removal which includes the
inevitable and serious erosion that will occur during the first and possibly
second or third succeeding spring runoffs will be at least two and possibly up
to ten times the initial erosion (see the pictures), Consequently, in the
short time of one or two summers the road rip activities, proposed for the
Spotted Beetle project would deliver at least (2 X 127.6 =) 255.2cu. ft. of
sediments for the Best Case, Moderate depth scenario. This is 2.5 times as
much DIRT as would be expected with 9 culvert failures of similar type in 30
years - all delivered in one or two years!!
This EIS does not reveal how many culverts will be removed but figures from
the Spotted Beetle project should be similar
precludes any meaningful management action including efficient fire
suppression in affected areas.
"Extended response times due to reduced surface access increases
the possibility of an escaped fire.. The cost of suppression increases due to
needs for aviation support and firefighter support in remote areas."Ch
3,pp117. The belief expressed in this EIS that there would be fewer human
caused fire ignitions after road rip because of difficulty of human access
would also apply to barriered roads. However, barriered roads could be used
for fire suppression but ripped roads could not. A combination of restricting
admin access to 57 trips for all affected areas per year and up to 580 miles
of road rip for Alternative E will lead to severe impact on forest management
particularly if a situation arises that requires admin attention such as
flooding, disease or fire rehab
Endangered/threatened bull trout, white sturgeon, and burbot in the Kootenai
drainage will be affected by severely increased sedimentation.
Is it wise to destroy valuable roads that will be needed in the future?
What scientific study that uses current information and has been subjected to
a rigorous peer review, differentiates between a barriered road and a
decommissioned/obliterated road?
How do you know that a grizzly bear can tell the difference between a
barriered road and an obliterated one? If he cannot then why go to the expense
of obliteration, causing a large increase in stream sedimentation in the
process?
THIS EIS IS FLAWED BECAUSE THE ONLY REAL NO ACTION ALTERNATIVE, WHICH IS F,
HAS NOT BEEN INCLUDED. An EIS must have a no-action alternative in order to
represent all the choices available. Alternative F was "designed to respond
to comments requesting the Forest Service maintain the existing levels of closed
and open roads on the landscape. It also responds to public comments asking for
no additional road closures." Alternative F should have been included.
THE SOCIAL AND ECONOMIC CONCERNS OF LOCAL RESIDENTS WERE ACKNOWLEDGED BUT
NEVER REALLY CONSIDERED. The authors claim that the effects on the economy
and on recreation would be moderate. How can they know what the cumulative
effect of yet another forest shutdown will be on the lifestyles and livelihoods
that have sustained these communities for generations. This is especially true
in the town of Libby which is reeling from the closure of mining and logging and
now the recreation in the area is being slammed by the nationwide coverage of
the asbestos problem.
The writers tried to convey the idea that the local residents have mixed
feelings about grizzlies and road closures. NOTHING COULD BE FURTHER FROM THE
TRUTH. The residents of Boundary, Sanders, and Lincoln voted 80% against the
roadless initiative and any other extension of roadlessness or road closures.
The EIS acknowledges that "The reduction in
access and associated timber management and recreation would constrain the
outdoor lifestyle of local populations and increase the perception that public
participation does not appear to be effective at influencing management of the
Forests." How could anyone have any other perception after reading how
lightly hard-boiled, cold-eyed FS officials passed over their needs and
concerns.
"...it was determined that the present status did not fully meet any
particular desired biological or social condition. The
"freezing" of the present status would not provide an option that more
fully resolved any of the biological or social concerns identified as
significant issues. With this language the EIS writers dismissed the social
concerns that they had elaborated on for 16 pages.
How could the team have "fully" considered Alternative F if
they concluded that it does not resolve social issues? The EIS mentions in
several places the repeated concerns of the public over road closures. Are the
legitimate concerns of the public not "social concerns" or are they
not "significant"? What would the team consider to be a
"significant" social concern? What significant social concerns did the
team discover other than the concerns about loss of access ?
NEPA requires that the agency fully and carefully address social and economic
concerns. Brushing them away without a backward glance hardly fulfills the NEPA
requirement.
THIS EIS IS DEFECTIVE BECAUSE THERE IS NO RECOGNITION OR ACCOUNTING FOR THE
IRREVERSIBLE AND IRRETRIEVABLE CONSEQUENCES OF ROAD OBLITERATION. The
opportunity cost of loss of access is not accounted for in this EIS. "With
the loss of access and further access restrictions comes a higher economic cost
to access public lands, or in some cases, an inability to manage these lands for
certain uses." Ch3b 8-57 How could FS manage the 57 trip restriction
across 3 forests with different management groups? These roads cost millions of
dollars of public funds to construct and maintain but the cost of the loss of
this capital asset is not accounted for in this EIS.
The supposed benefit for grizzlies in the preferred alternative amounts to a
1-2% overall change in core areas and road densities. Most BMUs are already
below the recommended targets for OMRD, TMRE and Core Area. Those few BMUs that
are not can be addressed on a site specific basis in order to meet the legal
mandates. To approach the stated need as a forest plan amendment is heavy handed
and inefficient and will unnecessarily tie the hands of local forest
supervisors. Therefore, we request that Alternative F be reconsidered because
the marginal if any benefits to grizzlies are more than offset by social and
economic costs.
The FS must find some way to satisfy its legal difficulties without severely
impacting the human environment, which would occur with all the alternatives in
this EIS except F. The Forest Service should re-evaluate the need for this EIS
and either withdraw it or rework it with alternatives that address the
social/economic impacts on even terms with grizzly bear needs. A true no action
alternative must be included. If no peer reviewed, up-to-date, carefully crafted
scientific studies can be found to support road closures are available, then no
road closures should be attempted.
Please put NWMGP on the mailing list for this EIS.
Sincerely,
Harm Toren, President
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