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Crater Lake National
Park Nature Notes
Volume XII, October, 1946
United States
Department of the Interior
National Park Service
E. P. Leavitt, Superintendent
Dr. G. C. Ruhle, Editor, Park
Naturalist |
|
Cover sketch and
illustrations - Nancy P. Wallis.
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|
-
Introduction
- G. C. Ruhle
-
A Greeting
- Dr. G. C. Ruhle
-
Floral Life Zone On The Phantom Ship
- William E. Bush
-
An Ecological Appreciation Of The Lake
Trail - W. J. Nee
-
Mammal Populations, 1946
- Dr. R. R. Huestis
-
Pocket Mice In Crater Lake National
Park - Dr. R. R. Huestis
-
Temerity
- Irving E. Blume
-
East Entrance Desert Animals
- Dr. R. R. Huestis
-
Deer Mice In Lava Beds National
Monument - Dr. R. R.
Huestis
-
"Yellow" Scarlet Gilia
- O. L. Wallis
-
Brown Mountain Beavers
- O. L. Wallis
-
Activity Of Park Beaver
- O. L. Wallis
-
Recovery Of A Banded Gray Jay
- Dr. D. S. Farner
-
Some Miscellaneous Ornithological
Notes - Dr. D. S. Farner
-
Food Habits Of Crater Lake Salamanders
- Dr. D. S. Farner
-
Memorandum On Fishing
- Dr. D. S. Farner
-
New Formations At Oregon Caves
- Robert C. Zink
-
The Back Country Of Crater Lake
- Dr. C. G. Ruhle
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Editorial: An Appraisment
- Dr. C. G. Ruhle
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- o -
This world, after all our science
and sciences, is still a miracle;
wonderful, inscrutable, magical, and more, to whosoever will think
of it.
-- Thomas Carlyle
- o -
A Greeting
By Dr. G. C. Ruhle, Editor
After a lapse of years punctuated by
the war, NATURE NOTES FROM CRATER LAKE NATIONAL PARK, is again
published, a single number being scheduled for the current year. This
issue of NATURE NOTES has been sponsored by the Crater Lake Natural
History Association and prepared by the members of the naturalist staff,
whose mouth piece it purports to be. It is a chronicler of interesting
and important bits of natural history of the park. Its contents are
original articles, notes, digests, poems, sketches, bits of park life,
comments and opinions of interested parties. Members of the park staff
and voluntary contributors comprise its aggregation of writers.
Editorials are included whenever possible, feasible, urgent. These, true
to their name, are solely expressions of conviction or opinion of the
park naturalist as editor, not necessarily the general consensus of
feeling of the National Park Service or of Crater Lake National Park.
Items may be included despite lack of literary merit, for NATURE NOTES
endeavors to preserve and transmit a cross section of the individuality
and atmosphere of the park's dramatis personae.
NATURE NOTES stands primarily for
conservation, for the protection and perpetuation of our natural
features, for the application and operation of the fundamental policies
of the National Park System and of the Naturalist Division. It seeks to
further its aims by the development of a love of nature through
observation and intelligent understanding.
As long as the limited supply lasts,
these pamphlets are mailed free anywhere in the United States to every
one wishing to receive them. But postal regulations require that a
written request be given to the park before they may be franked. One
rare occasions, copyrighted articles may appear in NATURE NOTES by
special permission. These are fittingly marked. All other articles in
the pamphlet are intended for the free use by any publication. It is
merely requested that credit be given to the author and to NATURE NOTES,
CRATER LAKE NATIONAL PARK. The Naturalist Division always greatly
appreciates receiving notice or copies thus used by various
organizations.
NATURE NOTES is prepared for your
instruction and pleasure. The editor is pleased to receive for
consideration contributions of general interest to the readers.
Suggestions and inquiries are encouraged, and your constructive
criticism is invited at all time.
LAVA BEDS NATIONAL MONUMENT in northern
California has been separated from the administrative control of Crater
Lake National Park; Ranger Don C. Fisher, long serving it, remains as
its custodian. OREGON CAVES NATIONAL MONUMENT in southwestern Oregon
retains its connection with the park administration.
Floral Life Zone On The Phantom Ship
By William E. Bush, Ranger-Naturalist
Among the scenic attractions at Crater
Lake, few excel in popular appeal or give rise to greater exercise of
creative imagination than the small island known as the Phantom Ship.
This rugged little island with its spires of andesite, is generally
considered to be no more than a picturesque old rock, furnishing
appealing subject for those who would use it as vehicle for their
contemplations in fantasy by way of mind, palette, or film. Actually,
time is fashioning a biological unit on the island; the usual sequences
and consequences of nature are molding discernible, competitive
boundaries and patterns of adaptation upon its rugged surface.
Physically, the Phantom Ship is a
remaining section of the filled conduit of a fissure from which probably
poured many of the lower layers of lava constituting Dutton Cliff. Its
rocks of pyroxene andesite have in many places been altered by
hydrothermal activity. Quartz filled seems give the rock a character
uncommon to most of the rocks generally found on the crater walls. The
island is about 500 feet long and reaches a maximum width of 200 feet
near the east end. Its east-west ridge of spires, towering 170 feet
above the water, sharply divides most of the island into two slopes, one
very steeply sloping to the south and the other less steeply to the
north. The island is separated from the mainland by a shallow channel
about 200 feet wide. Above this channel, Dutton Cliff rises abruptly,
constituting one of the highest sections of the south-west wall of the
caldera.
Observations noted herein were made
during two visits to the island on August 8 and August 19, 1946. Some
hours were spent in perusal of the situation as it existed, but the
plant tally was made on the second visit only. The listings are not to
be considered as complete and certainly it will be worthwhile to make
additions and corrections as subsequent observations suggest.
The accompanying sketch illustrates
roughly the bio-geographic layout of the island. The west end of the
island is made up of tall spires which rise vertically; a limited talus
at the water's edge is all that lies between the spires and the water.
In this region, few plants have gained a foothold and the area must be
essentially classified as barren.

The remainder of the island is divided
into two slopes which show a definite segregation of species. White bark
pine grows on both slopes in nearly equal areal density, though it
appears to be much more in its element on the north side.
The South Slope - The south and
southeast slopes of the island, while undoubtedly subjected to great
extremes of temperature, are predominantly a warm section. Three
ponderosa pine live a stinted existence in this region. The largest one
is 35 or 40 feet high and 56 inches in circumference, three feet above
the root spread. On this slope are four western white pines, the largest
of which is 34 inches in diameter; it is broken off 20 feet above the
ground and a crown of new growth doubles that height. High on the east
end is a taller one 60 feet high and 25 inches in diameter; it bears an
old lightning scar, now nearly healed. These trees are bearing a good
crop of cones this year. The ponderosa pine cones are smaller than
normal.
A considerable coverage of green
manzanita (A. patula) grows just below the spiring ridge that
separates the island into two parts; it continues to the water's edge.
All of this presents a clear cut transition situation. However, in
addition to this there is considerable mat manzanita (A. nevadensis),
and an intermixture of small white-bark pines. In a few cases there may
be confusion between P. albicaulis and P. monticola, but
most of the trees were bearing cones and no mistake was possible.
The complete absence of lodgepole pine
or alpine fir seems surprising, but may probably be explained by the
dearth of water-stabilized soil or duff. It was also noted that not one
specimen of either red fir or hemlock was found on this slope.
The North Slope - The north
slope is less steep than the south; it presents some areas with a soil
of erosional debris and duff. On this slope are growing trees typical of
the lower Hudsonian Zone. Shasta red fir exist in considerable areal
density, but are small for the specie, while mountain hemlock grow in
about the same stand density, but the mature trees, though small, are
apparently in good condition. The white bark pine on this slope are
normal and of good size. The total number of trees (a foot or more high)
is 66 while the south slope supports only 28.
High, near the east end of the north
slope, is one specimen of white fir about 30 inches high. It appears to
be in good condition and should subsequently be checked for its
existence and growth. It apparently is the only one on the island.
At the foot of this slope there is a
flat talus which is supporting a number of herbaceous plants typical of
shady, moist localities; including shield fern, meadow rue, Jacob's
ladder, and bleeding heart. The distribution of herbaceous plants and
shrubs is apparently controlled by localized circumstances and zonal
distribution is far from obvious. The appended list of the plants
observed gives their general location.
Among the unlisted, but not unnoticed
flora are the brilliantly colored yellow, red, and orange lichens which
cover the vertical walls of the towering spires. Occasional single
plants of grass are to be seen near the water's edge. No attempt at
identification of these was made.
Animal life observed consisted of
birds, obviously transient. There were two Clark's crows and three
Sparrow Hawks but no other birds were observed. On the first visit, one
golden mantled ground squirrel was seen on the talus at the east end.
None was seen on the second visit. No traces of other animals were
noted, but the writer does not profess to be a skilled observer of such
evidences.
Some evidence of human trespass were
evident. Recent foot marks on the upper level soils, a film carton,
three paper plates, a paper drinking cup, a rusty beer can, and several
pieces of orange peel gave evidence that human influence cannot be
overlooked.
From 1910 to 1940, the level of the
lake has been dropping; this year the lake level is three feet higher
than at comparable season in 1940. Evidence of this rise of level is to
be noted in the fact that several shrubs, probably willows, have been
destroyed by the rising water and their roots and stems are now a foot
or more beneath the surface. A half dozen such plant remains were
observed.
Thus the island gives rise to two
rather clearly defined life zones, namely a hybrid sort of transition on
the one side and a definite Hudsonian on the other. A total of about 94
forest trees, including six species, and 32 species of ground plants
were observed to be growing on the Phantom Ship.
The following forest trees large enough
to be considered as firmly established (a foot or more high) have been
noted:
| Tree |
Typical Zone |
South Side |
North Side |
Total No. |
| Pinus
ponderosa Dougl. |
Transition |
3 |
0 |
3 |
| Pinus
monticola Dougl. |
Upper Transition
to Canadian |
4 |
2 |
6 |
| Pinus
albicaulis Englem. |
Hudsonian |
21 |
29 |
50 |
| Abies concolor
Lindl. |
Transition |
0 |
1 |
1 |
| Abies
magnifica shastensis Lemmon. |
Canadian to
Hudsonian |
0 |
17 |
17 |
| Tsuga
mertensiana (Bong.) Sargent. |
Hudsonian |
0
|
17
|
17
|
| Totals |
|
28 |
66 |
94 |
| Ground Plants |
Common Name |
Occurrence |
| Filix fragilis
(L) Gilib. |
Brittle Fern |
Few (2 or 3)
seen. |
| Polystichum
scopulim (D.C. Eaton) Maxon. |
Shield Fern |
Two on North side
near water level. |
| Smilacina
amplexicaulis glaber Macbride. |
False Solomon |
Common. |
| Salix
lasiandra abramsii Ball. |
Abrams Willow |
One small plant
on south side (8 feet). |
| Salix orestera
Schneider |
Sierra Willow |
One plant on
south side. |
| Thalictrum
sparsiforum Turcz. |
Meadow Rue |
Common on north
side near water level. |
| Actaea spicata
arguta (Nutt.) Torr. |
Baneberry |
One plant on
north side. |
| Dicentra
formosa (Andr.) DC |
Bleeding Heart |
Common at lower
levels. |
| Arabis
(specie) |
---- |
East end near
water. |
| Ribes cereum
Dougl. |
Waxy Current |
Common. |
| Ribes lacustre
(Pors.) Poir. |
Prickly Currant |
Common. |
| Mitella
breweri Gray. |
---- |
Common on north
side. |
| Holodiscus
glabrascens (Greenman) Heller. |
---- |
Common. |
| Sorbus
cascadensis G. N. Jones |
Mountain Ash |
One plant on NE
end. |
| Amalanchier
florida Lindl. |
Service Berry |
Most common
shrub. |
| Lupinus
andersonii Watson. |
Lupine |
Occasional on SE
end. |
| Epilobium
glaberrimum Barbey. |
Willow Herb |
Common on north
side. |
| Pyrola picta
Smith. |
White Veined
Pyrola |
One plant, north
side. |
| Pyrola secunda
L. |
One-sided Pyrola |
One plant, with
P. picta |
| Arctostaphylos
patula Greene. |
Green Manzanita |
Considerable on
south side. |
| Arctostaphylos
nevadensis Gray. |
Mat Manzanita |
Common on south
side. |
| Polemonium
shastense Eastwood. |
Jacob's Ladder |
Several plants in
rock crevices on north side. |
| Phacelia
heterophyla Pursh. |
---- |
Common. |
| Penstemon
menziesii davidsoni (Greene) Piper. |
Pride of the
Mountain |
Common. |
| Penstemon
rupicola Howell. |
---- |
Common. |
| Castilleja
miniata Dougl. |
Paint Brush |
Common. |
| Anaphalis
margaritacea (L.) Benth and Hook. |
Everlasting |
Common on east
side. |
| Taraxacum
palustre vulgare (Lam.) Fernald. |
Dandelion |
Several near
water's edge on east end. |
| Chrysothamnus
nauseosus speciosus
(Nutt.) Hall. |
---- |
Common on east
end. |
| Antennaria
geyeri Gray. |
---- |
Several on east
and near water level. |
| Eupatorium
occidentale Hook. |
Western Boneset |
Common. |
| Hieracium
albiflorum Hook. |
Hawkweed |
A few on east
end. |
- o -
Perception of Nature leads to
Knowledge;
Knowledge, to Understanding, Interest, Love.
- o -
An
Ecological Appreciation Of The Lake Trail
By W. J. Nee, Ranger-Naturalist
From the standpoint of botanical
appreciation, one of the outstanding Self Guiding Nature Trails of
Crater Lake National Park is the Crater Wall Trail commonly referred to
as the Lake Trail. This trail has: first, a large number of floral
species; second, a broad range of plant associations due to moisture,
temperature and altitude; and third, the most extreme spread of
flowering time.
Approximately 75 species can be readily
identified on the Lake Trail. The following is a partial list of the
more prominent plants: mountain hemlock, white bark pine, sedge,
Engleman's aster, Newberry's knotweed, false helebore, tall ragwort,
feather-leaf leutkea, heart-leaf arnica, Crater Lake currant, smooth
wood rush, one-sided pyrola, Brewer's mitrewort, Tomie's Saxifrage,
creeping raspberry, crustaceous lichen, staghorn lichen, fireweed,
mountain sorrell, red elderberry, mat huckleberry, rock penstemon,
long-leaf arnica, bleeding heart, columbine, fivefinger, western
boneset, Jacob's ladder, thorny currant, parsely fern, alpine
everlasting, Hall's currant, western white pine, Shasta red fir,
mitella, willow herb, white veined pyrola, Merten's corallroot, mat
manzanita, Bongard's buttercup, Lewis's monkeyflower, Gorman's
stonecrop, pearly everlasting, pine paintbrush, sulphur flower,
phacelia, hawkweed, kellogia, mountain maple, fat solomon seal, slim
solomon seal, snowberry, prince's pine, baneberry, fleabane, western
wind flower, holly fern, mountain ash, squaw carpet, broom huckleberry,
Douglas phlox, veronica, yellow monkey flower, arabis platysperma, and
Sitka valerian. Many of the earlier blossoming plants, the grasses, and
varieties of sedges are not listed here.
A typical plant association of the
upper area is the mountain hemlock, smooth wood rush, and Crater Lake
currant association. An excellent example of this association can be
seen toward the end of the second switchback. At the end of the seventh
switchback is an association of plants that frequent rocky ledges
including parsley fern, and crustaceous lichens. At the end of the ninth
switchback, the altitude is sufficiently low for the Shasta red fir and
western white pine to mingle with mountain hemlock. As on faces the
lake, one looks right into the tops of each of the above named trees.
Limb pattern, foliage, and cones are very convenient for close
comparison. There is a splendid view of a towering cliff immediately
behind this tree association. Along the tenth switchback is a very
beautiful growth of bleeding heart. A decaying log has provided
protection and humus to enhance the beauty of this cluster of flowers.
The thirteenth switchback is a long one
but has an association that is altogether different from any of the
preceding. A ledge of fragmental material has produced a drier situation
upon which characteristic plants have grown. In this association are mat
manzanita, veried-leaf phacelia, pearly everlasting, pine paintbrush,
sulphur flower, Engleman's aster, Gorman's stonecrop, and others.
Another similar association but on a more rocky situation is to be found
on the sixteenth switchback. Here the predominating plant is Gorman's
stonecrop.
One other association of particular
interest is at the bottom of the trail where the Sitka alder and thorny
currant form a dense thicket in the talus. Observation of the alder will
explain the many dense green thickets around the lower reaches of the
crater wall. This grows principally because the drainage from the wall
is constant throughout the growing season.
Because of the exposure, protection
from desiccating winds, and the supply of moisture, the Lake Trail
produces the widest extreme in season of any area so easily available to
the public. From the earliest to the latest part of the season, flowers
can be seen in all stages of development. In early September, this year,
there were Lewis monkeyflowers just coming into bud and blossom while
within a few feet, the same species had completely gone to seed. Within
a radius of twenty feet, one can see the first blossoms of red
elderberry, the green berries and the ripened red berry. Long after the
columbine has disappeared around the Park Headquarters, they are just
coming into blossom at the foot of the Lake Trail. And so it is with
many of the other plants. On this splendid trail, springtime is
determined by environmental factors, which make a brilliant floral
display the whole season through.
Mammal
Populations, 1946
By Dr. R. R. Huestis, Ranger-Naturalist
This note is based upon observations,
made in Crater Lake National Park, upon the most easily observable
mammal species. The present season is distinct in two particulars: The
park is open to the heavy public travel for the first time since 1942.
The heavy snowfall of the 1945-46 season has provided an exceptional
amount of vegetation throughout the area.
Olympic black bear are not numerous as
compared with pre-war years. The policy of garbage disposal at a
considerable distance from any habited area has been successful in
preventing unhealthy concentration of these animals. A few complaints
have been made by campers of bears stealing foodstuffs left exposed in a
vacated camp but these indignant people are outnumbered twenty to one by
visitors equally indignant because they haven't seen a bear since they
entered the park.
Columbia black-tailed deer appear to be
exceptionally numerous. They are commonly seen by visitors and trails
are found to be dotted with fresh footprints whenever they are visited.
Deer are commoner than at any season in the last then years.
Golden mantled ground squirrels are
rather scarce. In 1938 about 150 squirrels, by actual count, inhabited
the rim area between the Lodge and the Crater Wall Trail. This year's
population appears to be about one-fifth of this. Squirrels are very
numerous along Highway 230 east, outside the park.
Townsend chipmunks, never very
numerous, appear in expected numbers. Klamath chipmunks have been rarely
observed in the rim area this year. White-footed mice, which in the rim
area sometimes enter the cafeteria or lodge in considerable numbers,
have caused no comment this year and appear to be below average in
number. A few have been taken in snap traps along Munson Creek.
Yellow-bellied marmots may be seen to
some extent along the highways. None has been observed along the Rim
Walk, where one or two could usually be seen. Conies can be seen in the
talus slopes along Garfield Peak Trails but do not call from the rim
slopes to any extent this year. They appear to be present in less than
average number.
Signs of the Mazama gopher showed in a
few places along the rim where the snow melted. The most extensive
workings in the rim area were in a small flat between the highway and
the cafeteria. When it is considered that spring melts commonly expose
extensive gopher workings in cleared spaced everywhere in the park area,
the numbers of gophers this year can be considered below average.
Among the medium sized and small
carnivores, pine martens have been reported to be about as numerous as
usual. A weasel carrying a
Microtus and, later, the same individual carrying a small
Citellus, was seen at the Information Building. Coyotes have not
been reported at all and foxes rarely.
Pocket Mice In Crater Lake National Park
By Dr. R. R. Huestis, Ranger-Naturalist
On July 31, 1941, to his considerable
surprise, the writer took two pocket mice, (Perognathus parvus
(s. sp.)) within the eastern boundary of Crater Lake National Park. A
battery of ten traps had been set along the turnout for the Wheeler
Creek pinnacles and ten other traps were set south of this along the
east entrance highway. Each battery took a pocket mouse along with a
number of Peromyscus.
This edge of Wheeler Creek canyon is on the 5500 foot level.
The pocket mouse is a type particularly
associated with the Sonoran Zones of the southwestern American desert.
They are included in the family Heteromyidae along with the much better
known kangaroo rats, also typical desert dwellers. The writer once
trapped in a region of the Painted Desert in Arizona so arid that it was
a considerable walk from one small creosote bush to the next, yet here a
small pocket mouse was taken in many of the traps; the only mammal that
touched them and apparently the only one there.
The rim of Wheeler Creek Canyon at 5500
feet is covered by a forest of lodgepole pines (Pinus contorta
latifolia), the cleared spaces being occupied by waxy currant
(Ribes cereum)) and Bloomer's rabbit-brush (Chrysothamnus
bloomeri). The altitude and vegetation would identify the region as
lower Canadian Zone, a rather atypical habitat for pocket mice. However,
the soil along Wheeler Creek rim, a powdery pumice, might be expected to
be congenial.
Pocket mice are burrowing rodents with
small pinnae, and compared with Peromyscus, relatively small
eyes. As in the kangaroo rats the temporal bones are enlarged into thin
walled bullae. These are believed to increase auditory acuity. The
cheeks are supplied with fur lined pouches for storing seeds. The tail
is long and furred toward the end with some relatively long stiff
bristles. The hind legs are long and powerful, but pocket mice run
rather than jump like the kangaroo rats. Like many burrowing mammals
they are solitary and quarrelsome if kept together in captivity, one
usually killing the other.

The specimens taken in Crater Lake
National Park measured as follows:
| Total length |
Tail length |
Foot |
Ear pinna |
| 149.6 mm |
82.2 |
22.5 |
8.1 |
| 155.0 mm |
85.0 |
22.5 |
8.2 |
These measurements are small for even
the smaller of the two subspecies which might be expected to work into
the park area: Coues' pocket mouse, (P. p. mollipilosus), from
the Upper Klamath Lake region. Both specimens were females, both had
been lactating, and both were pregnant. One contained six and the other
four embryos. These evidences of fertility suggest that pocket mice are
in Crater Lake National Park to stay.
Temerity
By Irving E. Blume, Ranger-Naturalist
The golden-mantled ground squirrel is
one of Crater Lake National Park's most interesting smaller mammals,
being a constant source of pleasure to all visitors. One of these
creatures had the ingenuity to establish his homestead in an obscure
hole in the middle of the highway leading to the Rim area from the Park
Headquarters. Just as if he were amusing himself at the consternation of
the passing motorist, he would sit on his haunches inches from his hole
until the automobile was immediately upon him. As the concerned motorist
saw the little fellow and attempted to avoid running over him, the
little squirrel would dart into the hole with the car only inches away.
Many persons got out of their cars and looked in vain for the smallest
traffic cop of the Crater Lake highways.
East Entrance Desert Mammals
By Dr. R. R. Huestis, Ranger-Naturalist
During the latter part of the 1941
season, an investigation was made of the mammalian fauna along the East
Entrance highway from the park boundary to the south-east margin of
Dutton Ridge. Both sides of the highway were set with live traps for a
distance of a little over three miles. Only small mammals can enter
these traps of these four species were represented: Klamath chipmunk
(Eutamias amoenus amoenus),
Sierra least weasel (Mustela cicoquanii muricus), Gambel's deer
mouse (Peromyscus maniculatus gambelii) and Coues' pocket mouse
(Perognathus parvus mollipilosus). This last species had not
previously been reported from Crater Lake National Park or any part of
Oregon north of Fort Klamath. It is associated with relatively arid
territory of north-east California and its presence in a forest-covered
region within the park boundary is of interest. The deer mice taken
along the rims of Wheeler and Sand Creek canyons are in type more like
the Sonoran deer mouse than deer mice taken elsewhere in the park.
Coues' Pocket Mouse: Three
female Perognathus were taken along the rim of Wheeler Creek
canyon. One, the largest was lactating and also pregnant. It contained
six embryos four in one uterine horn and two in the other. One female
was pregnant only and contained for embryos two in each horn. The
smallest female was neither lactating nor pregnant and may not be within
the limits of adult size. The measurements in millimeters are as
follows:
| Body |
Tail |
Tail % |
Foot |
Ear |
| 70.0 |
85.0 |
121.4 |
22.5 |
8.2 |
| 67.4 |
82.2 |
122.0 |
22.5 |
8.1 |
| 60.2 |
82.6 |
137.2 |
22.6 |
8.0 |
From the measurements it may be seen
that these mice are small bodied and long tailed with relatively large
feet and small ears. All these mice are smaller than the species'
average recorded by Vernon Bailey for the state but the beginning of at
least a second brood in one female would make it seem probable that she
was fully adult.
Gambel's Deer Mice: Twelve deer
mice were taken along the highway between the East Entrance and the Lost
Creek Ranger Station. Seven, of which six were females, proved to have a
body length of 85.0 mm or more and may be considered adult enough for
statistical purposes. Most of them were young adults so the average body
length is small. Fourteen mice were taken on Dutton Ridge along the East
Entrance highway. Ten of these proved to have a body length of 85.0 mm
or more. This group was also composed of young adults. The data follows:
|
Body Length |
| Class (in
mm) |
East
Entrance |
Dutton Ridge |
Both |
| 85 |
2 |
3 |
5 |
| 88 |
2 |
5 |
7 |
| 91 |
1 |
2 |
3 |
| 94 |
2 |
- |
2 |
|
7 |
10 |
17 |
| Means: |
82.29 +/- 1.33 |
87.70 +/- .85 |
88.35 +/- .70 |
| Std. Dev.: |
3.52 +/0 .94 |
2.10 +/- .46 |
2.88 +/- .49 |
All means are below 90.0 mm the usual
figure for large samples of
Peromyscus including older mice.
|
Tail Percentage |
| Class (in
mm) |
East
Entrance |
Dutton Ridge |
Both
|
| 76 |
2 |
3 |
5 |
| 79 |
1 |
- |
1 |
| 82 |
2 |
3 |
5 |
| 85 |
1 |
1 |
2 |
| 88 |
- |
2 |
2 |
|
91 |
1 |
1 |
2 |
|
7 |
10 |
17 |
| Means: |
80.71 +/- 2.00 |
82.60 +/- 1.61 |
82.18 +/- 1.24 |
| Std. Dev.: |
5.29 +/- 1.40 |
5.16 +/- 1.13 |
5.10 +/- .87 |
|
Comparisons of Means |
| Crater Lake Rim |
89.6 |
.59 |
| Crater Lake South Entrance |
86.1 |
.85 |
| Dutton Ridge |
82.6 |
1.61 |
| Dutton and East Entrance |
82.2 |
1.24 |
| East Entrance |
80.7 |
2.00 |
It may bee seen that mice from the
southeastern side of the park have considerably shorter tails than mice
taken elsewhere. The fact that they are rather small mice minimizes the
differences for smaller
Peromyscus have relatively longer tails than larger ones.
The differences between the rim and
east entrance samples is 8.9 +/- 2.08 per cent and therefore more than
four times its standard error. The difference in tail percentage between
the Rim sample and the combined Dutton Ridge and east entrance sample of
17 mice is 7.4 +/- 1.37 percent. This difference is more than five times
its standard error. Smaller differences are present between mice from
the east and south portions of the park in tail percentages but they are
still more than twice their standard errors and so of statistical
significance.
A tail percentage of just over 80 is
more typical of the interior valleys of California than of any forested
part of Oregon and this situation emphasizes the effect upon small
mammals which the pumiceous character of the soil and sparse vegetation
seem to be producing.
|
Ear Length |
| Class (in
mm) |
East
Entrance |
Dutton Ridge |
Both |
| 15.5 |
1 |
- |
1 |
| 16.0 |
- |
- |
- |
| 16.5 |
2 |
1 |
3 |
| 17.0 |
1 |
5 |
6 |
| 17.5 |
1 |
1 |
2 |
| 18.0 |
1 |
2 |
3 |
|
18.5 |
1 |
1 |
2 |
|
7 |
10 |
17 |
| Means: |
17.07 +/- .36 |
17.35 +/- .19 |
17.24 +/- .18 |
| Std. Dev.: |
.95 +/- .25 |
.60 +/ .13 |
.77 +/- .14 |
The mean ear size of these mice is
slightly below that of the Rim area, 17.5 +/- .09. Since the ear length
is greater in larger mice the difference in body size between the Rim
90.09 +/- .38 and the eastern series may very well be the factor
involved. The differences are not statistically significant.
Foot length: Since foot length
must be computed separately in each sex that of the females in the
combined East Entrance-Dutton Ridge series is the only one presented:
| Class (in
mm) |
Dutton
Ridge-East Entrance |
| 19.0 |
2 |
| 19.5 |
2 |
| 20.0 |
3 |
| 20.5 |
3 |
|
21.0 |
1 |
|
11 |
| Mean: |
20.0 +/- .19 |
| Std. Dev.: |
.62 +/- .14 |
This mean is smaller than that of the
Rim or South Entrance series both differences being statistically
significant. For females the Rim foot length is 20.7 +/- .08 and South
Entrance 20.6 +/- .15. Whether the difference in body size is the only
factor is more doubtful in this case.
Summary
- Coues' pocket mice were present
and breeding along the East Entrance highway of Crater Lake National
Park in 1941. These mice are at home in arid regions.
- Gambel's deer mice taken from this
region have a relative tail length typical of mice from the interior
valleys of California.
- It is suggested that the sparsity
of vegetation in this region is an important factor in these
distributional arrangements.
Deer Mice In Lava Beds National Monument
By Dr. R. R. Huestis, Ranger-Naturalist
On September 12, 1941, the writer
accompanied Park Naturalist George C. Ruhle to the Lava Beds National
Monument which was at the time associated for administrative purposes
with Crater Lake National Park. Fifty live-traps were set out in the
vicinity of Tule Lake and 32 adult
Peromyscus maniculatus were taken. These were measured and
skilled and the pelages added to the study skin collection at Crater
Lake National Park. A statistical study of the measurements is being
recorded here for the reference of students of the distribution and
systematics of small mammals.
Methods: All measurements were
taken of recently anaesthetized specimens removed from the live traps.
The mouse is stretched to a uniform tension on a measuring board and the
dimensions of the total length, tail length and foot length to the end
of the longest claw are recorded with pins. The dimensions are then
taken with a vernier caliper. The ear is measured, with the same
instrument, from notch to tip. Body length is obtained by subtracting
the tail length from the total length. The tail percentage is then
obtained by dividing the tail length x 100 by the body length. It allows
a better comparison of mice of different size than actual tail length.
Tests have shown that this method of measuring recently anaesthetized
mice can be done with an average error not greater than one-tenth of a
millimeter.
Body Length: This standard
measurement varies with age. All specimens included were 85 mm or more
in length which is taken as the lower limit of adult body length. This
allows comparison with series from other places with a similar lower
limit but does not, of course, entirely eliminate differences in average
size due to age differences in populations. The arrays are tabulated
below:
|
Body Length |
| Class (in
mm) |
Females |
Males |
All |
| 85 |
1 |
3 |
4 |
| 88 |
5 |
7 |
12 |
| 91 |
6 |
3 |
9 |
| 94 |
2 |
1 |
3 |
| 97 |
3 |
- |
3 |
|
100 |
1 |
- |
1 |
| Total |
18 |
14 |
32 |
| Means: |
91.67 +/- .95 |
88.43 +/- .66 |
90.25 +/- .66 |
| Std. Dev.: |
4.04 +/- .67 |
2.49 +/- .45 |
3.75 +/- .47 |
In Peromyscus, as in man, female
mice have a better life expectation than males. Female adults in the
Lava Beds are older and therefore bigger than males. In this series they
are also more numerous.
|
Comparisons of Means of Body Length |
|
Lava Beds |
Silver Lake |
Crater Lake
South Entrance |
Crater Lake
Rim |
| 90.3 +/- .66 |
89.0 +/- .26 |
90.7+/- .45 |
90.0 +/- .38 |
These comparisons are made with a
sample of 72 mice from a sage brush association in Silver Lake, Oregon,
a sample of 45 mice from Crater Lake South Rim and a sample of 27 mice
from a yellow pine and deer brush association at the South Entrance to
Crater Lake National Park. Lava Beds mice do not differ statistically in
body length from any of these other samples.
|
Tail Percentage |
| Class % |
Females |
Males |
All |
| 76 |
3 |
1 |
4 |
| 79 |
1 |
- |
1 |
| 82 |
4 |
4 |
8 |
| 85 |
4 |
3 |
7 |
| 88 |
4 |
4 |
8 |
| 91 |
2 |
2 |
4 |
|
18 |
14 |
32 |
| Means: |
83.8 +/- 1.1 |
85.2 +/- 1.1 |
84.4 +/- .74 |
| Std. Dev.: |
4.65 +/- .67 |
4.0 +/- .74 |
4.2 +/- .52 |
The tail percentage is usually bound to
be smaller in larger mice. These females averaging larger than the males
have relatively shorter tails.
|
Comparisons of Means of Tail Percentage |
|
Lava Beds |
Silver Lake |
Crater Lake
South Entrance |
Crater Lake
Rim |
| 84.4 +/- .74 |
84.6 +/- .43 |
86.1 +/- .85 |
89.6 +/- .59 |
It has been found repeatedly that the
relative tail length in
Peromyscus varies directly with the amount of precipitation and
therefore of vegetation covering the ground. Tails are longer where
ground cover is more abundant. The Lava Beds are the most arid of the
habitats in which series have been taken. They differ in relative tail
length slightly from the South Entrance series and considerably from the
Crater Lake Rim series the differences being 5.9 +/- .95 per cent. This
difference is six times its standard error and therefore statistically
significant.
|
Ear Length |
| Class (in
mm) |
Females |
Males |
All |
| 16.0 |
1 |
1 |
2 |
| 16.5 |
1 |
2 |
3 |
| 17.0 |
3 |
7 |
10 |
| 17.5 |
6 |
1 |
7 |
| 18.0 |
2 |
2 |
4 |
| 18.5 |
2 |
- |
2 |
| 19.0 |
2 |
1 |
3 |
|
19.5 |
1 |
- |
1 |
|
18 |
14 |
32 |
| Means: |
17.7 +/- .20 |
17.2 +/- .19 |
17.5 +/- .15 |
| Std. Dev.: |
.88 +/- .15 |
.70 +/- .13 |
.85 +/- .11 |
Females have slightly longer ears
presumably because they are larger mice.
|
Comparisons of Means of Ear Length |
|
Lava Beds |
Silver Lake |
Crater Lake
South Entrance |
Crater Lake
Rim |
| 17.5 +/- .15 |
17.5 +/- .04 |
17.3 +/- .10 |
17.5 +/- .09 |
Lava Beds mice do not differ from the
other samples in this character.
Foot Length: Besides age
differences there is a constant sex difference in foot length in
Peromyscus the females having the smaller feet. The sexes are
presented separately but not combined figure is given because of the sex
difference.
|
Foot Length |
| Class (in
mm) |
Females |
Males |
| 19.0 |
1 |
- |
| 19.5 |
- |
1 |
| 20.0 |
3 |
- |
| 20.5 |
2 |
2 |
| 21.0 |
8 |
6 |
| 21.5 |
3 |
3 |
| 22.0 |
1 |
1 |
|
22.5 |
- |
1 |
|
18 |
14 |
| Means: |
20.8 +/- .16 |
21.1 +/- .18 |
| Std. Dev.: |
.68 +/- .13 |
.69 +/- .13 |
It may be seen that the usual sex
differences holds for the females with greater body length have the
smaller average foot length.
|
Comparisons of Means of Foot Length |
|
Lava Beds |
Silver Lake |
Crater Lake
South Entrance |
Crater Lake
Rim |
| Females |
20.8 +/- .16 |
20.2 +/- .06 |
20.6 +/- .15 |
20.7 +/- .08 |
| Males |
21.1 +/- .18 |
20.5 +/- .07 |
21.0 +/- .08 |
21.4 +/- .14 |
The Lava Beds series does not differ in
foot length in either sex from either of the Crater Lake series. There
are small but statistically significant differences in the foot length
of both sexes between the Lava Beds and Silver Lake series. It is
possible this is due to the differences in the sandy soil cover at
Silver Lake and the pumiceous or relatively unweathered rock fragment
cover in the other regions.
Summary
- Deer mice were abundant in
September 1941 in the Lava Beds National Monument.
- The 32 adults taken there resemble
series of Peromyscus maniculatus gambelii taken at other
areas in California and Oregon.
- Comparisons of the Lava Beds
series with mice taken at Silver Lake, Oregon, and at the Rim and
the South Entrance of Crater Lake National Park showed no
statistical difference in body length or ear length.
- The Lava Beds series differed
statistically in relative tail length from the Crater Lake Rim
series but not from the Silver Lake or South Entrance series.
- The gradient in relative tail
length varies with the vegetative cover of the regions from which
the series were taken: Rim, South Entrance, Silver Lake, Lava Beds.
- The Lava Bed series exhibited a
small but statistically significant difference in foot length in
both sexes from the Silver Lake series but not from either Crater
Lake series.
- The softer soil cover at Silver
Lake may be a factor in the production of this difference in foot
length between the Lava Beds and Silver Lake mice.
"Yellow"
Scarlet Gilia
By O. L. Wallis, Ranger-Naturalist
In the area west of Vidae Ridge, on
August 2, I discovered two plants of scarlet gilia (Gilia aggregata
(Pursh) Spreng.) with lemon yellow flowers. One plant was 45 cm tall and
had 56 flowers. The second had three stems, the longest of which was 33
cm; 25 flowers grew on the three stems. Although mutants of this type
are comparatively rare, Ranger-Naturalist Elmer I. Applegate collected
one such plant on August 1, 1939, on the road below the old campgrounds.
This plant had five stems, the longest of which was 32 cm, and bore a
total of 55 flowers.
Brown Mountain Beavers
By O. L. Wallis, Ranger-Naturalist
The brown mountain beaver
(Aplodontia rufa rufa Rafineque), furnishes one of the most
individual forms of animal life in Crater Lake National Park,
interesting not only because it is one of the most primitive mammals in
existence but also because of its limited range, its lack of close
relatives, and its intensive food storing activity.
Confined to the Pacific Northwest,
mountain beavers are grouped into the single rodent family
Aplodontiidae, into one genus
Aplodontia and into one species rufa, divided into nine
subspecies. The mammal has several other names: sewellel (Indian name),
boomer, and mountain burrower. Of these, the last is the most
appropriate; for Aplodontia is only distantly related to the
American Beaver (Castor canadensis), the builder of dams and
lodges. Differing in habitat, the mountain beaver lies in a series of
underground tunnels, six to seven inches in diameter, with many external
openings that are connected, above ground, by a network of runways.
There are two types of openings: The one for general use is kept fairly
clean and is used as an entrance and exit. The other type of burrow is
employed as a refuse opening, through which the rocks and dirt of
excavation are pushed forth.
Burrows are usually located in a moist
area, on a hilly slope where the soil is relatively loose, where springs
exist, and the vegetation is dense. During my summer's observations, I
have noted the (inner) workings near Vidae Falls, in Castlecrest
Gardens, in the springy area below the Gardens, and on the south slope
of Munson Ridge near the Park Headquarters. In all of these workings,
water was found to be trickling through at least a section of the tunnel
system throughout the entire summer. For such a timid animal, water
supply of this type proves to be protective as well as convenient. The
creature is able to drink in perfect safety within the confines of its
dwelling; also, the running water offers a means of disposal of waste
vegetation material which readily floats out of the lower end of the
burrow.
Aplodontia is a mammal which is
rarely seen, because it is naturally shy and is mainly nocturnal in
habit. On the early morning of August 26, I saw one of the animals
loping along its runway and sliding into its burrow in the Castlecrest
Gardens.
Ranger-Naturalist R. R. Huestis
reports: "During August 1941, a brown mountain beaver took temporary
refuge just above the ramp leading to the Sinnott Memorial, using the
lower part of a burrow system which has been occupied by a golden
mantled ground squirrel for the last three seasons. During two days the
mountain beaver made a number of emergences to gather forage or to run
the few feet between two entrances to the burrow system, both of which
had been somewhat enlarged to better fit the new occupant. The Sinnott
Memorial ramp is one of the most traveled walks in the park, so many
visitors had the chance of observing and photographing a mountain
beaver's feeding technique, an activity that many experienced
naturalists have never observed. The animal itself largely ignored the
presence of the gallery except when someone moved close to it. Most of
the visitors had never heard that there was such an animal, and, being
duly advised of its rarity in public places, were enchanted at their
opportunity and stood hopefully for considerable periods of time with
their cameras at the ready."
On August 27, at the Munson Ridge
location, I caught a male in a Verbail wire loop live trap. This capture
was made to find out what foods the mammal would eat and to study its
habits. Measurements of the individual were: total length: 326 mm; tail:
23 mm; hind foot: 59 mm; ear: 23.5 mm.
Characterized by short legs, tail and
ears; exceeding small eyes; large feet with naked soles and strong
claws; long and stiff whiskers; the animal is very primitive in
appearance and resembles a Mazama pocket gopher, (Thomomys monticola
mazama Merriam), which has been enlarged fifteen times. Coarse,
shiny dark guard hairs extend above the softer rich brownish or chestnut
fur. Below each ear is a white spot. Its stout body and broad, blunt
head makes it especially adapted to the burrowing life.
Mountain beavers are strictly
vegetarian in food habits, eating most types of herbage which grow near
their burrow. I found the vegetation cut for drying in neat piles around
the entrance holes or upon nearby rocks or logs. All the stems of the
material in any one pile pointed in one direction. Around the hole would
be several piles; each contained the same species of plant and may have
indicated the size of the load carried by the individual. As a rule, the
material constituted plants which grew in the immediate vicinity; on one
occasion, however, red elderberry cuttings were observed 45 yards from
the nearest shrub.
Foliage collected and eaten by mountain
beavers covers a wide variety of plants. Availability seems to be the
important factor in the type of food selected. In each of the locations
the materials collected varied in direct proportion to the species
growing nearby. Although the area adjacent to the burrows at Vidae Falls
and Castlecrest Gardens supported great numbers of Lewis' monkeyflower,
in no case, was I able to find cuttings of this species. But my captive
animal ate this plant quite readily. At the location on the south slope
of Munson Ridge, three of the burrow entrances were located under a
green-leaved alder; but no traces of this shrub were identified in the
bunches of cuttings.
Although F. Lyle Wynd reports that
false green hellebore is fatal to live stock (Nature Notes Volume
2, No. 2 August 1929) and that most species of Aconitum are
poisonous to animals and human beings (Nature Notes Volume 2, No.
3 September 1929), both monkshood (Aconitum columbianum), and
false green hellebore, (Veratrum viride Ait.), were eaten by the
captured beaver without apparent maleffect. Monkshood was identified,
also, in the bunches of drying vegetation at Castlecrest.
Twice daily at 7:00 A.M. and 10:00
P.M., from August 20 to August 26, examinations were made of the food
piles at the Munson Ridge location to determine if the mountain beaver
was active during the daytime. These observations showed that most of
the activity of cutting and stacking occurred during the night; only
once, on August 24, were new cuttings found at the night examination.
Each morning from August 11 through
August 27, the materials appearing at the eleven holes at the Munson
Ridge location were counted and marked. The marking was done by writing
the date on a prominent leaf with pen and ink. By means of this counting
and marking, it was possible to note the number of pieces of vegetation
cut and stacked and the length of time required for the material to dry
before it was taken into the burrow. During this period, the mountain
beaver collected over 3246 pieces of vegetation. Dicentra stems
amounted to nearly 25% of the material gathered and Valeriana
followed with nearly 24%. On August 22, alone, 488 pieces were piled.
Note
Table I.
| |
Plant
Species |
Number of
Stems |
Percentage
of Total |
| |
| Dicentra |
799 |
24.619 |
| Valeriana |
761 |
23.451 |
| Smilacina |
334 |
18.767 |
| Aquilegia |
78 |
2.404 |
| Sambucus |
35 |
1.079 |
| Aster |
44 |
1.048 |
| Senecio |
30 |
.924 |
| Grass |
22 |
.678 |
| Epilobium |
15 |
.462 |
| Misc. |
852 |
26.256 |
|
3246 |
Total |
Table I - Material gathered
at the Munson Ridge location by one mountain beaver during the
period of August 11 through August 27. These figures list the number
of stems of each of the species and not the bulk of the plant cut by
the mammal.
The length of time the cuttings were
left to dry depended upon the species, the weather, and the location of
the pile. Specimens of
Sambucus were not dry after five days. On August 25, four out of
twenty-seven cuttings of Smilacina marked on August 21, and five
out of twenty-one stems marked on August 22 were still present revealing
the length of time some cuttings were left to dry. Dicentra and
Valeriana stems were usually removed the next day after they were
counted and marked; these have thinner leaves. In locations situated in
the dense shrubbery, the drying of the material took twice as long as in
open situations. On cloudy or rainy days, the vegetation scarcely
wilted, and therefore, remained piled for a longer period.
At the Munson Ridge location the
mountain beaver harvested its material as soon as it became completely
dried, while the individual at the Vidae Falls site allowed the material
to stay out until it became so dry that it was brittle.
In captivity the mountain beaver
consumed 497 plants from August 30 to September 5. This count was taken
in the number of plants eaten, therefore, indicates a greater amount of
food than the number applies when compared with the number of stems
counted in the field survey. Twenty-one species of vegetation are
represented. See
Table III.
This range could be greatly increased by more intensive experimenting.
Although the mountain beaver is
considered to be quite stupid and primitive, from these food studies, it
can be assumed that he is quite a diligent and systematic worker.
|
Plants Collected and Eaten by Mountain Beaver
|
| Aconitum columbianum
Nutt. |
Monkshood |
| Anaphalis margaritacea
(L.) Benth. and Hook. |
Pearly Everlasting |
| Aquilegia formosa
Fisch. |
Columbine |
| Aster englemanni var.
ledophyllus Gray. |
Engelman Aster |
| Dicentra formosa
(Andr.) DC |
Bleeding Heart |
| Epilobium angustifolium
L. |
Fireweed |
| Lupinus latiffolius
ligulatus (Greene) C. P. Smith |
Klamath Lupine |
| Salix eastwoodae
Cockerell |
Eastwood's Willow |
| Sambucus racemosa calicarpa
(Greene) Jepson |
Red Elderberry |
| Senecio triangularis
Hook. |
Tall Ragwort |
| Smilacina amplexicaulis
glabra MacBride |
Fat Solomon |
| Valeriana sitchensis
Beng. |
Varlerian |
| Veratrum viride Ait. |
Corn Lily; False Green
Helebore |
Table II - Vegetation
identified in piles stacked by mountain beavers in all of the
locations noted in Crater Lake National Park.
| Rubus lasiococcus Gray. |
Creeping Raspberry |
| Vaccinium membranaceum
Dougl. |
Big Huckleberry |
| Erigeron salsuginosus
Gray. |
Fleabane |
| Ribes erythrocarpum
Coville & Leiberg |
Crater Lake Currant |
| Castilleja miniata
Dougl. |
Paint Brush |
| Mimulus Lewisii Pursh. |
Lewis's Monkey Flower |
| Phacelia heterophylla
Pursh. |
Phacelia |
| Sorbus cascadensis G. N. Jones |
Mountain Ash |
Table III - Plants, in
addition to those found in
Table II,
which were eaten by the mountain beaver in captivity.
Activity Of
Park Beaver
By O. L. Wallis, Ranger-Naturalist
Beaver activity in Crater Lake National
Park at present is at a low ebb. A survey of the old workings of the
American beaver (Castor canadensis pacificus), in the Copeland
Creek region reveals that there has not been any renewal for many years.
Several of the dams observed in 1931 by the park naturalist, (Nature
Notes Volume 4 No. 1, July 1931) still exist and are strong enough
to retain a great quantity of water.
Observations in the Annie Creek basin
near the South Entrance show that beaver have been active here to a
limited extent. Cuttings estimated from the weathering to be no older
than four months occur in the quaking aspens and the poplars along the
stream bed. Older cuttings were seen on white fir, aspen, and poplar
trees. One tree, 15 inches in diameter, remains standing although almost
completely cut through.
Wildlife expert Robert S. Evans in his
1934 "Survey of Animal Life of Crater Lake National Park" states: "Since
last year when an estimated number of 12 was reported for beaver living
along the streams of the west slope, fresh beaver work has been found
along Annie Creek in the southeast corner of the park;" the 1934
estimate was 18, but that exceeds the numbers which exist in the park
today.
The beaver migration from the areas on
Copeland Creek and Annie Creek probably resulted from one or both of two
main causes: lack of sufficient food to support a colony and freezing of
the water too deeply to permit winter activity.
Recovery Of A Banded Gray Jay
By Dr. D. S. Farner, Ranger-Naturalist
On August 6, 1946, in the course of
ornithological investigations along the summit of the Cascade Divide
between Annie Springs and Union Peak, two gray jays (Perisoreus
canadensis griseus Ridgway) were collected from a family group of at
least three. The birds were traveling from tree to tree through a rather
dense stand of mountain hemlock (Tsuga mertensiana (Bong.)
Sargent). The collecting locality was one and one eighth miles southwest
of Annie Springs, about 50 yards west of the Union Peak motorway. The
altitude of this locality is approximately 6250 feet. One of the
collected specimens had on its leg Biological Survey Band No. A283458.
Mr. F. C. Lincoln kindly supplied the information that this band had
been originally issued to Mr. W. T. Frost, formerly a ranger at Crater
Lake. According to the data by Mr. Frost this gray jay was banded as an
adult at Annie Springs on December 27, 1937. The bird was retrapped nine
times on the day that it was banded, and four times on the following
day. Mr. Frost placed and additional band of yellow color on the bird's
other leg for purposes of sight identification. This band had been lost
by the time of the above described recovery. This recovery is of
interest not only because of the age of nearly nine years attained by
the bird but also as an indicator of the extremely restricted range of
individuals of this species.
Some
Miscellaneous Ornithological Notes
By Dr. D. S. Farner, Ranger-Naturalist
These notes have been selected from my
field notes for the summers of 1940 and 1946. Only those which made a
pertinent or interesting contribution to our knowledge of the birds of
Crater Lake National Park have been included.
Erismatura jamaicensis rubida
(Wilson) : Ruddy Duck
A pair observed about one half mile from Cloud Cap on the surface of
Crater Lake, July 4, 1940. This is apparently a new record for the park.
Accipiter velox velox (Wilson):
Sharp-shinned Hawk
Two seen in flight near Red Blanket Creek near the south boundary of
Crater Lake National Park, August 28, 1946.
Accipiter cooperi (Bonaparte):
Cooper's Hawk
One observed near the upper end of White Horse Creek Canyon, August 9,
1946.
Buteo regalis (Gray):
Ferruginous Rough-leg
One seen in flight near Discovery Point, August 2, 1946.
Aquila chrysaetos canadensis
(L.): Golden Eagle
Single birds observed between Wizard Island and the south rim on July
29, 1946 and August 3, 1946.
Circus cyaneus hudsonius (L.):
Marsh Hawk
One seen in flight along south rim, July 19, 1946. This bird was in
brown plumage.
Falco peregrinus anatum
(Bonaparte): Duck Hawk
One seen in flight near Red Cone, July 30, 1946. One seen in flight near
Discovery Point, August 9, 1946.
Charadrius vociferus vociferus
(L.): Killdeer
One observed at the boat landing on the south shore of the lake, July
13, 1940.
Larus californicus Lawrence:
California Gull
Seen almost daily in numbers from one to ten on the surface, or flying
above the surface of Crater Lake, July 18, 1946 to September 1, 1946.
Phalacrocorax auritus albociliatus
Ridgway: Farallon Cormorant
Conspicuous by their complete absence from the Phantom Ship during the
1946 summer.
Megaceryle alcyon caurina
(Grinnel): Western Belted Kingfisher
One observed on Wizard Island, August 4, 1940. One observed on the
Phantom Ship, August 17, 1940.
Asyndesmus lewis Gray: Lewis's
Woodpecker
About three hundred seen between the Watchman and Cleetwood Cove, August
31, 1940. These birds were feeding and not in actual migration. I
observed none in 1946.
Dryobates pubescens ssp.: Downy
Woodpecker
Two observed near Bear Bluff, August 13, 1946. Not previously recorded
from the park. Specimens are needed for further study.
Picoides tridactylus fasciatus
Baird: Alaska Three-toed Woodpecker
One observed and collected near Red Cone Spring, August 14, 1946.
Nuttallornis mesoleucus
(Lichtenstein): Olive-sided Flycatcher
Common throughout the park during the summer of 1946. A pair feeding at
least three young out of the nest observed near Bear Bluff, August 13,
1946.
Tachycineta thalassina lepida
Mearns: Violet-green Swallow
About 15 seen in the open area around the headwaters of the east fork of
Munson Creek, July 23, 1946.
Parus gambeli abbreviatus
(Grinnell): Short-tailed Chickadee
A pair with six young out of the nest seen near Park Headquarters, July
13, 1940.
Sitta carolinensia aculeata
Cassin: Slender-billed Nuthatch
Single birds observed along the south rim, August 9, 19, 26, 1946.
Cinclus mexicanus unicolor
Bonaparte: Dipper
One observed at base of Chaski Slide, July 11, 1940. One observed near
boat landing on south shore of Crater Lake, August 18, 1946. It should
be remembered that the littoral fauna of Crater Lake is essentially that
of a mountain stream and that it is therefore not surprising to find
dippers in this situation.
Salpinctes obsoletus obsoletus
(Say): Rock Wren
An adult and three young seen near the boat landing on the south shore
of Crater Lake, August 2, 1940.
Sialia mexican occidentalis
Townsend: Western Bluebird
Three observed near Red Blanket Spring, August 14, 1946. This new record
for the park needs to be confirmed by collected specimens.
Spinus pinus pinus (Wilson):
Northern Pine Siskin
A juvenile bird following an adult and seeking food from it seen along
south rim, August 26, 1946.
Passerella iliaca ssp.: Fox
Sparrow
Three seen on Red Blanket Creek motorway about 2.5 miles from the south
boundary. One was carrying food in its bill indicating that it was
possibly a breeding bird feeding young. One collected, July 8, 1946.
Melospiza melodia ssp.: Song
Sparrow
One seen in Munson Meadows in areas where lincolni was abundant,
July 20, 1946. This needs to be verified by collected specimens to
establish it as a new park record.
- o -
"Nature is the Art of God"
- o -
Food Habits Of Crater Lake Salamanders
By Dr. D. S. Farner, Ranger-Naturalist
Two species of salamanders, belonging
to the genera Triturus
and Ambystoma respectively, occur under the rocks at the
waterline of Crater Lake. On August 17 and 24, 1946, 56 salamanders were
collected for the purpose of examining their stomach contents.

Of the 27 Ambystoma examined, 19
of the stomachs contained material. Fourteen (74 percent) of these
contained terrestrial arthropods, or fragments thereof. These were
mostly insects such as ants, wasps, flies, beetles, etc. Usually there
were parts of one or two animals only per stomach. Seven stomachs (37
percent) contained aquatic insect larvae. Two stomachs contained
unidentifiable material only. One contained only a piece of andesite
about one centimeter in length.
Of the 29 Triturus examined,
there were 27 with food items in their stomachs. Sixteen (56 percent)
contained the fresh-water shrimp,
(Hyallela), (one to sixteen per stomach). Nine of these sixteen
had no items other than Hyallela. Eight stomachs (30 percent)
contained snails (one to 15 per stomach). In four of these, snails were
the only item; in the other four, Hyallela was also present. Five
(18 percent) contained aquatic insect larvae (Coleoptera,
Trichoptera,
and Diptera), one to three per stomach. Two contained caddis-fly
larvae. In three of the five instances, the aquatic insect larvae were
the only food items. Four (15 percent) contained terrestrial insects or
fragments thereof (never more than one per stomach). In three of these,
the insect, or fragment thereof, was the sole item; in the fourth, there
were also two Hyallela. One stomach contained unidentifiable
material.
The terrestrial arthropods, mostly
insects, found in the stomachs of the salamanders are doubtless
individuals which were either dead at the time of eating or were in a
helpless and easily captured living condition on or in the water. In
view of the fact that 74 percent of the
Ambystoma stomachs with food contained such items and only 37
percent contained items would could have been taken alive it
seems safe to conclude that the Ambystoma of Crater Lake is
largely a scavenger taking mostly dead animals. Live food taken is that
which moves slowly. Apparently fresh-water shrimp and snails, both
abundant in its habitat, are not utilized. On the other hand, it appears
that Triturus acts as a scavenger only rarely since only 15
percent of the stomachs contained terrestrial arthropods. Obviously the
principal source of food for Triturus, at least at the time of
year in which this study was conducted, consists of fresh-water shrimp
and snails. Seventy-one percent of the stomachs examined contained
either or both of these items. Aquatic insect larvae constitute the next
most important item.
It is of interest to note that, in the
stomachs of either species, neither aquatic Coleoptera nor
Turbellaria were found; although both are abundant in the habitats
of these species.
Memorandum On Fishing
By Dr. D. S. Farner, Ranger-Naturalist
The 1946 fishing season at Crater Lake
began on August 3, when the Crater Wall Trail was opened to public
traffic. Fourteen fishing boats were available throughout the season
which ended on September 2. Fishing activities and methods were in
general the same as those of previous years. Many who had fished
regularly in 1941 and 1942 returned during the summer of 1946. In
general the fishing day ended one hour earlier in the afternoon because
of the operator's policy in calling the boats at 4:00 P.M. or shortly
thereafter. As in previous years most of the fishing was done in the
vicinity of Wizard Island and along the southwest shore of Crater Lake.
No attempt is made here to estimate the amount of fishing or the extent
of the catch at the Wineglass. The data on which this report is based
are those boat fishing and a limited amount of shore fishing on Wizard
Island and near the boat landing on the south shore of the lake.
1. The Catch in 1946. The
total catch for 1946 was 97 fish of which 60 were silverside salmon and
37 were rainbow trout. This is the smallest recorded catch since records
were begun in 1937. The estimated rate for 1946 is 0.11 fish per boat
per hour, the lowest yet recorded. This rate is based on an estimate of
boat hours for the season. The lowest rate prior to 1946 was 0.46 in
1938. Most of the silverside salmon were 8 to 12 inches in length and
about 1/4 to 1/2 pounds in weight. A few larger rainbow trout were
taken.
2. Physical and Chemical Studies.
A limited number of observations and measurements were made because of
the brevity of the season. Accurate temperature observations were
impossible because of the lack of a limnological thermometer. However
the use of an improvised method indicated that, at least, no appreciable
changes have occurred. Secci disc readings indicate that the clarity of
the water has changed little. Perhaps it has decreased slightly.
Determinations of dissolved oxygen indicate that the water, varying with
depth, is 70 to 80 percent saturated seven to ten parts per million with
oxygen thus showing no appreciable change from previous years. Total
carbon dioxide is about 33 parts per million of which about 30 parts are
in the form of bicarbonate. This is essentially the same as previous
analyses.
3. Fish Food. Because of
the small number of fish caught, stomach contents from no more than 30
specimens were obtained. Although the data require further study it
appears that there have been no appreciable changes in feeding habits.
The principal items of food continue to be aquatic insect larvae,
fresh-water shrimp (Hyallela),
snails, and, less important, terrestrial insects which drop into the
water. There appears to be no change in the abundance of these food
items. If anything, the snails and fresh-water shrimp are more abundant
than in 1941.
4. Age and Growth Studies.
Because of the small catch and limited amount of data and materials were
obtained. These will be studied this winter and a report prepared at the
conclusion of the studies.
5. Natural Reproduction.
During the summers of 1940 and 1941 more than 11,000 silverside salmon
were taken by fishermen. With negligible exceptions these were the
result of natural reproduction in the lake. The silverside salmon taken
during the summer of 1946 were also the result of natural reproduction.
Also, during the summer of 1946 considerable numbers of fingerlings of
silverside salmon were observed near the boat landing. There can be no
question that this fish can reproduce abundantly in Crater Lake.
However, this year's sparsity of fish in the lake would seem to indicate
that the reproductive success must fluctuate tremendously. Evidence for
the natural reproduction of rainbow trout is not as clear, although
there seems to be little doubt that this species also reproduces
naturally to (a) considerable extent.
6. Why are fish scarce in Crater
Lake in 1946? Because of the similarity of fishing methods used
in 1946 to those of previous years there can be little doubt that there
has been a sharp decline in the fish population in Crater Lake. No
defensible theory for the sharply reduced number of fish in Crater Lake
in 1946 can be given at this time. Although all conditions appear now to
be normal there is no way of knowing or ascertaining the conditions
which existed and transpired between 1942 and 1946. Had observations and
studies been made during this period it is highly probable that the
present decline in population could have been predicted or at least its
cause ascertained. Presumably there has been in the past five years and
probably in the last three, a period unfavorable either to spawning or
to the survival of small fish.
The present decline in population serves only to emphasize the fact
that Crater Lake is biologically a young and unstable lake and that a
wise and successful fish management program can be developed and
maintained only if a consistent and active research program be
maintained.
7. Should stocking be resumed in
Crater Lake? There will doubtless be considerable pressure from
local groups for the stocking of more fish in Crater Lake. Such pressure
is based on sincere but misconceived ideas that lakes can be easily and
simply managed by stocking. Realizing well the difficulty in resisting
such pressure this investigator, nevertheless, recommends that no fish
be introduced into Crater Lake for at least two seasons to come. The
reasons for this recommendation are as follows: (1) Restraining from the
introduction of more fish for the next two seasons should give ample
evidence as to whether or not natural reproduction is adequate to
restore the larger population characteristic of the lake a few years
ago. (2) Examination of the planting data, age-group data, and creel
censuses gives absolutely no evidence to indicate that stocking, other
than originally to establish the populations, has any real effect on the
population and the catch by fishermen. Some of the largest plants
correspond to the lowest catches. (3) Consideration should be given to
the extreme difficulty and expense of properly stocking fish in the
lake. It would seem that the economical and the most sensible
approach from a conservation standpoint would be to rely on research and
management rather than on repeated stocking. After several seasons
it is possible that consideration of further planting may be justified
for one of the following reasons: (1) Possibly, whereas natural
reproduction may at times be extensive, periods may occur in which
spawning and survival of small fish may be so sharply reduced that the
existence of the population may become precarious. Further research is
needed on this point. If such should prove to be true, a matter of
policy is evident as to whether or not Crater Lake should be maintained
as a fishing lake. (2) There is some evidence now that the strain of
silverside salmon now in the lake is one that reaches maturity in or
before its third year and that few if any of the fish reach the
desirable fourth-year size. Should further observations and research
bear out this surmisal it is possible that an additional stocking of
silverside salmon could be justified.
8. Recommendations for further
research. As indicated above Crater Lake is a young and unstable
lake. Proper understanding and management of the fish population will
require continuous research. Investigations have been handicapped by
lack of certain equipment. For example, it requires more than an hour to
take a single sample of water or a single bottom sample in the deeper
part of the lake. Actually to obtain adequate data nearly a hundred such
samples should be taken during the summer.
A table of the catch 1946 as compared
with that of previous years during which records have been kept is found
(below).
| Period |
Number of Boat
Reports |
Number of Anglers |
Total Boat
Fishing Hours |
Total Number
of Fish |