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FOURTH QUARTERLY DATA REPORT” ““*°"

JUNE, JULY & AUG. SUMMER 1975
BOOK 4 OF 9

TERRESTRIAL BASELINE DATA

Sulf Oi) Cargoration

and

Standard Oi) Company (Indiana)

9725 East Hampden Avenue, Denver, Colorado 80231

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Filé NO?.79. C5 742-5 -f 7
_ - SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET

Grid Name i Grid. =. Samplé Period 2.4 “5 Trap Night

\

Date, time traps set__ z4 : -Date, time traps checked 260)

Last toe clip # used on previous day el Plea Analyst (Ss) 5 2...0ce.saacibe

Project | QA Check_ fn ZY;
Animal Fe

Capt. Age Weight Reprod. Additional
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SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET
Grid Name osnill sur. Grid 2 Sample Period . se Trap Night

Date, time traps set 2s 4 _Date, time traps checked . =:

Last toe clip # used on previous day ~°>-— = Field Analyst(s)

= Lee

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File No: 8.C.5/42.353-/9 -

SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET

Grid Name Dosraiil Saat Grid. .¢. Sample Period |. \ Trap Night

Date, time traps set_(ct5?) 274) Seta 7s ‘Date, time traps checked

Last toe clip # used on previous day _ 522 \ Field Analyst(s)
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File No: /6.C 5.423720

SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET

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Last toe clip # used on previous day PETERS Field Analyst(s) LA © Se ee
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SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET Aid}
Grid Name Horse P,), Grid [, Sample Period _o.y ~< Trap Night__|
Date, time traps set osco 25 \ury 75 ‘Date, time traps. checked ©O8°> ZG Suty 75
Last toe clip # used on previous day 0209 Field Analyst(s) Si: Savids

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Project {2 Bas ted - 43 4 QA Check Rin 1

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File No: J3CS 42 ee SS IZ

SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET Ay t
Grid Name_lin-ce 0.” chi Grid. .!s Sample Period 15:4 75 Trap Night 2
Date, time traps set (p2)24 || : Date, time traps checked (/3e) 27 (5. :
Last toe clip # used on previous day =)” Field Analyst(s) S,wn), “Sn ar,
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Reprod. Additional
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BAT MIST NET SAMPLING SHEET
Collector(s) Fi. Guire {Mace eger Date 6/ ZE / 76 Project RéasPp— 93
Location: T 2S R 73WS 7 1/4 1/4 S?2“”5E Time Net Set Zc 30
Description ky “a gases s Pecka gond drove. R44 Poi QA Check bean b-29-F,
rt ee a a OT | a

Time Net “ Comments
Species Sex ,(condition, collection, release, etc.)

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ae eS Smal? Mammals
a Introduction

No change’ has occurred since Progress Report 2. See section 3.5.1 in
Progress Report-2 for the introduction to the small mammal section.

2.3.3.2 ' Methods
2.3.5.2.) Live Trapping

No change has occurred since Progress Report 3. See section 2.3.3.2.1
in Progress Report-3 for the specific methods used in live trapping
smal] mammals.

2.3.3.2.2 Collection of Animals for Laboratory Analysis

A removal trapping program designed to collect small mammals for jabo-
ratory analysis of reproductive effort or stomach contents will occur
during each of the small mammal live trapping periods. Animals are
being collected for analysis of stomach contents during October and
December, 1974; during May, July, September and December, 1975; and
during May and July, 1976. Animals are being collected for analysis

of reproductive effort during May and July, months of peak smal]

mammal breeding activity, 1975 and 1976. The removal program is con-
ducted sufficientiy far from the live trapping grids to prevent inter-
Terence with the live trapping operations. Ideally, for each of the
three most common small mammal species, up to five specimens (including
at least two females) are collected by a line of 40 snap traps in the
major vegetation types where that species occurs. Daily trapping
effort is increased in those vegetation types where capture success

is low. Trapping is terminated after four nights, however, even if

the desired numbers of animais have not been collected. Prior to the labo-
ratory analysis of reproduction effort or stomach contents any

internal parasites and general internal condition, if other than
normal, will be noted. The species which are being collected and the
vegetation types being sampled are listed in Table 2.3-3].

2.3.3.2.3 Laboratory Analysis of Reproductive Effort

The number of placental scars, pigmented areas of the uterus occurring
at sites of previous placental attachments, has been used to determine
litter size in small mammals (Davis and Emlen, 1948; Corthum, 1967).
Since placental scars become increasingly lighter with increased age
(Corthum, 1967) the degree of scar pigmentation can be used to indi-
cate the approximate time of parturition (birth). Thus by examining
the reproductive tract of adult females of selected species at regu-

_ lar intervals during the breeding season, information on litter size,

_ number of litters per season, and time of parturition can be provided.

2.3-133

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The laboratory procedures for examining placental scars involve
removal of the female reproductive tract, which is placed in a watch
glass filled with water. The uterus is stretched to insure that all
scars become visible, and a count is made and recorded on a standard
data sheet (Figure 2.3-9 ). If the female is pregnant the number of
fetuses is counted.

2.3.3.2.4 Laboratory Analysis of Stomach Contents

Basic dietary preferences or food niches of small mammal species are
becoming well-studied by mammalogists, and a solid literature base is
developing which can be employed to support interpretation of trophic
relationships of mammals within various plant communities. The
International Biological Program's Grassland Biome work has provided
recent data on small mammal diets through its Diet Laboratory in

Fort Collins (e.g., Grant, 1972; Hansen and Moir, 1971; Flinders and
Hansen, 1972). These data will be utilized whenever feasible to
Support interpretation of dietary habits and trophic level position
of the small mammal species found on or near Tract C-a.

Stomach contents of animals are emptied into a Petri dish containing
water and examined under 30 x magnification through:a dissecting
stereoscope. The particle on or closest to a mark in the center of
the dish is characterized as to whether it is of arthropod, verte-
brate or vegetal origin and the data are recorded on data forms
(Figure 2.3-10). Vegetation is being differentiated between seeds
and succulent parts. A total of 50 particles are examined for each
stomach with sufficient agitation of the dish contents between
examinations to ensure randomization.

2-3.3.2.5 Collection of Voucher Specimens

No change has occurred since Progress Report 2. See section 3.5.2.5
in Progress Report-2 for the specific methods used in collection of
voucher specimens.

2.3:3.2.6 Pitfall: Trapping

No change has occurred since Progress Report 3. See section 2.3.3.2.6
in Progress Report-3 for the specific methods used in pitfall trapping.

-2.3.3.2.7 Night Spotlight Census

A night spotlight census route has been established to record activity,
distribution, and abundance of nocturnally active mammals, particularly
rabbits, hares and predators. This census is being conducted on two
clear nights during February, June, and October of each year along a
48.4 km (30 mi) route which traverses all major vegetation associations
Within and adjacent to Tract C-a (Figure 2.3-11). The route is driven
at approximately 16.1 km (10 mi) per hour with an observer situated

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REPRODUCTIVE STATUS DATA SHEET

Project Date Investigator
Location Habitat

Capture Technique

Comments

Embryos. Placental Scars

grams Inactive

Comments

Figure 2.3-9. Reproductive status data sheet for Soe ort eee
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2.3-138

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on the passenger side of the vehicle operating a spotlight. All
mammals sighted within a strip up to 25 m (82 ft) wide on the right
side of the vehicle are being recorded to species. Odometer readings
to the nearest 0.16 km (0.1 mi) are recorded at the start of the
census and each time a mammal is observed. Habitat is also noted.

All data are recorded on a standard field data sheet (Figure 2.3-12 ).

Because of variations in topography and vegetation density it is not
possible to census accurately all active mammals within a 25 m strip.
To account for these variations the "observable distance", up to 25 m
jn each 1.0 mi portion of the survey route is estimated to the nearest
1.0 m. Multiplying mean width (observable distance) times length
provides an estimate of the total area sampled by the night spotlight
census route. The number of animals sighted divided by the area
sampled gives an estimate of density per unit area.

2.330828 Bat Investigations

During the summer months of June and August, 1975 and 1976, ECI employs
two techniques to determine the distribution and relative abundance
of bat species within and adjacent to Tract C-a.

During daylight hours old buildings, rock overhangs, crevices and
other likely places are searched for roosting bats. Ponds in
the vicinity of Tract C-a are sampled by mist netting. At dusk on
four consecutive nights during the sampling periods, these nets are
placed in a vertical position with the bottom shelf less than 0.3 m
(1 ft) above ponds or water tanks which bats are visiting. Bats
striking the net while sweeping low over the water to drink are
captured in the pocket of the net. The mist net is examined as often
as necessary to prevent escape or death of captured bats. Sampling
‘ is discontinued when no bats are observed for 1/2 hour. The first
individual of each species captured is sacrificed and prepared as a
voucher specimen. For subsequent captures, the species and sex of
the animal, the date and location of sampling and the collector's
name are recorded on a standard field data sheet (Figure 2.3- 13).
The bat is then released.

2.3.3.3. Results
2.3.3.3.1. Live Trapping

Results of small mammal live trapping studies conducted during four
sample periods at grids located in 14 different vegetation

types are presented below. Grid designations and habitat descriptions
for each sampling location are listed in Table 2.3-32. While
interpretations will emphasize results obtained for each grid during
the July 25-30, 1975, sampling period, seasonable trends in smal]
mammal population parameters will be identified in the summary and
conclusion section. Detailed interpretations of all data will be

2.35-1 39

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MAMMAL NIGHT ROAD CENSUS DATA SHEET
Project Transect @ Date Sunset Time
Time Begun Temp. Time Completed Temp. Cloud Cover

Starting Point Finish Point Length of Transect

Mile 1 a: 3 meaty ae ; 6 me | s 8 fe a -
11 Cie ae & | + 34 15 . 6 * 7 ; 18 ma 2 20 :
21 30274 23 th 3 PAS: + 26 AA Zo Aree, es 9,
Odometer Species Odometer Species :
Reading Observed Habitat Readiag Observed Habitat
Nee ee re ee ernie | ot amen | prmae Somareareemene|
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a
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ae Ses
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A SS ee
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2 os Gees a Se a
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ocology consultants, lic.

Figure 2.3-l2. “Mamma night road census data sheet for RBOSP.

2.3-140

Tn sd ;
ta _
ih pertine vo YQolase
——* :
92088 xo? Josie bisb edenen bsoy thorn femme .ST-E.S5 spr
: s
%
- al ,

Filic NO.

BAT MIST NET SAMPLING SHEET

" Collector(s) Date Project

Location: T R S 1/4 1/4 S Time Net Set

Description QA Check

Time Net . Comments

hecked Species Sex ,(condition, collection, release, etc.);

4 .
5 .
—) Se — SS es es ee Oe SS ——

6/75

ecology consulfants, in

Figure 2.3-13. Bat mist net sampling sheet ‘for RBOSP.

2.3=141

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2.3-142

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provided in the Second Annual Report.

A total of 580 individuals, comprising twelve small mammal species,
was captured during July live trapping. The species encountered are
listed in Table 2.3-33. The ecological distribution and abundance
of each species, expressed in numbers of rodents captured per 100
trap nights for each sampled habitat type are’ summarized in Table
2.3-34 to 2.3-87. Table 2.3-88 provides a capture summary over all
species for each grid during all sampling periods. Trapping results
for Grid G, aspen, during October and December, 1974, are excluded
from the above tables as this grid had to be moved to a different
aspen site in May, 1975, due to the presence of. a neavy snow cover.

Jolly-Seber estimates of population size and other population para-
meters including immigration and survivability (Cromack, 1968; Seber,
1973) for selected small mammal species encountered on the large

(7.29 ha) grids are presented in Tables 2.3-89 through 2.3-106. In-
sufficient recapture data for individual animals preclude reliable
population estimates for all species captured on all grids. Definition
of population parameters estimated and their corresponding notations

as used in the above tables are provided in Table 2.3-107.

Shannon-Weiner diversity indices, calculated by the methods outlined

~ in Poole (1974) are shown for all grids investigated during each
sampling period in Tables 2.3-108 through 2.3-111. While the diversity
indices express numerically the number of species and distribution
of individuals among species (equitability), direct comparison of
results obtained within different habitats requires a consistency
of sampling effort. Therefore species diversity indices obtained
from small (0.81 ha) and larger (1.35 ha and 7.29 ha grids) cannot be
directly compared. ;

Average weights, variance and standard error of the mean are presented
in Tables 2.3-112 through 2.3-139, for all species encountered on grids
during May and July, 1975, sampling periods. Weights were not

recorded during October and December, 1974, live trapping efforts.
Since repetitive trapping of individual small mammals effects an
artificial decrease in body weight, only the initial capture weights

of animals are used in the analysis.

2.3.3.3.1.1 Bottomland Meadow (Grid 1)

The unexpected initiation of haying operations by a local rancher at
this grid site forced termination of trapping after three nights
during the July sampling period. Therefore direct comparison of
results with other grids is not possible.

However, this grid was only one of two on which the montane vole
(Microtus montanus) was captured during July. This vole prefers
grassy meadows (Armstrong, 1972) and both Williams (1955) and Brown
(1967) reported the montane vole to be common in orassy meadow situa-
tions in central Colorado and southeastern Wyoming, respectively.

2.3-143

. ah ‘
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poe uitoatth -4
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»efsvidsegzet .gnimoys ristesartuez bit obsolod Tmgnso ni edo

Table 2.3-33. Species of wild nareg} encountered to date in the vicinity of

Tract C-a for RBOSP

FAMILY
Species

SORICIDAE (Shrews)

Sorex cinereus

Sorex merriami (not previously recorded

in the area)
VESPERTILIONIDAE

Myotis californicus
Myotis sp.

Myotis evotus
Myotis subulatus
Lasiurus cinereus

LEPORIDAE (Hares and rabbits)

Sylvilagus sp.
Lepus californicus

Lepus townsendii

SCIURIDAE (Squirrels, ground squirrels,
chipmunks )

4/

Eutamias minimus —

Eutamias quadrivittatus,7!
Spermophilus jateralis — /

4
Spermophi lus tridecemlineatus —
Tamiasciurus nudsonicus

GEOMYIDAE (Pocket gophers)

Thomomys talpoides

HETEROMYIDAE (Pocket mice, kangaroo mice
and kangaroo rats)

Perognathus apache 4/

CRICETIDAE (New World mice and rats)
Peromyscus maniculatus Af

Peromyscus truei 4/
Neotoma cinerea erea 4/

Clethrionomys g gapperi 4/

Common Name

Masked: shrew
Merriam's shrew

California myotis

Long-eared myotis
Smal1-footed myotis
Hoary bat

Cottontail
Black-tailed jackrabbit
White-tailed jackrabbit

Least chipmunk

Colorado chipnunk
Golden-mantled ground squirrel
Thirteen-lined ground squirrel
Red squirrel

Northern pocket gopher

Apache pocket mouse

Deer mouse

- Pinon mouse

Bushy-tailed woodrat
Gapper's red-backed vole

2.3-144

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2 ty ty |
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thortue briverty jel tue2) anaesur9e
(Casunng tito

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(exsriqop: tsa909) 3A01YM030
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™ eenden i zywonbis/

Table 2.3-33. (Continued)

FAMILY
Species Common Name

CRICETIDAE (Continued)

Microtus longicaudus 4/ Long-tailed vole
Microtus montanus 4] Montane vole
Lagurus curtatus 4/ . . Sagebrush vole

_ ERETHIZONTIDAE (Porcupines)

Erethizon dorsatum Porcupine
CANIDAE (Coyote, wolves and foxes)

Canis latrans Coyote

MUSTELIDAE (Mustelids, weasels, skunks)

Mustela erminea Ermine
Mustela frenata Longtailed weasel
Taxidea taxus Badger

FELIDAE (Cats)

Lynx rufus Bobcat
EQUIDAE (Horses) = - .

Equus caballus Feral horse ~
CERVIDAE (Deer and elk) 2/

Cervus canadensis Elk
Odocoileus hemionus q Mule deer

Vthe following authority is used for smal] mammal nomenclature:

Hall, E.R. and K.R. Kelson. 1959. The mammals of North America. Ronald Press
Company, New York. 1162 pages.

2/The following authority is used for feral horse nomenclature:

Blair, W.F., A.P. Blair, P. Brodkorb, F.R. Cagle and G.A. Moore. 1968.
Vertebrates of the United States, second edition. McGraw-Hill Book
Company. New York. 616 pages.

3/the following authority is used for large mammal (except feral horse)
nomenclature:

Lechleitner, R.R. 1969. Wild mammals of Colorado. Pruett Publishing Company,
Boulder. 254 pages. | 2

ot
se

4/Encountered during small mammal sample period 4, July 25-30, 1975.
2.3-145

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OOOs00 6 «9°50 2c*0 9° CL An (*abSs *pas peuT[—-waeq,atyy) »

snqyeout weceptay, sn TTydouseds

ul I ll W eouepunqy s4yusTtN Gedy OOL ted
eTrusAnr tTUpy aATZETAY pernydep sTenpTatpur #
peanqzaep woT4zsododg xx x

aSOGU ToT ‘SL6L ‘9z-g1 LEW _‘¢ potaed eTdues pue
‘usnaqeses ‘2 ptad soy ATewums Sutdder. Temwew TTeus ‘Op-E’Z PTAeL

2.3-152

ool x (setoeds [Te Fo sTenpTATput FO i / setoeds yoea JO STenpTATpuT fo i!) «x
sanoy pe toy Jes pue pe Ted dex. suo = qustu dez} t. «

Lt Se rr

19°0g = Te4OL

60°O 00°O O0°O HOcL . 6°2 L9°O | (asnow yexood ayoede
dyocue Snyyeusotsg

00°0 62°0 ¢€¥r°0 62°0 9°02 . eee (asnow z80p
Y Snjetnotueu snosAuosod

00°O OL*O O”’O 0S°0 9°9G 2\ fe (smudtyo_4seaT)
. Snututu SetTue yng

ogee DLO VLL SO EL%0 9° Lb vo e (*abs * pad pauTT—woe a tyy

Snjyeout [wecepta}y Sn TTYydowstedgs

ne

ul W ul I Qgouepunqgy SUUSTN APL COOL 49d
aTTUSANL SATLETOY peanydeg sTenpTATpul #
Poanjdeg woTysodoTg xx eI

reece ih i a

ISOTY or *GLEL ‘0S—-Sz ATne ‘fy potaed eTdues pue
‘ysnaqeses ‘¢ pTas soy ATewums Sutdder, Teuureu TTeuls “Lp-e°Z STASL

2.3-1 52

OOL xX (setToeds [Te FO sTenpTATput fo # / sotoods yoes JO STeNpTATputT JO #) xy
sanoy pg TOF 3es8 pue peyteq deay auo = 4ustu dezy 4, x

y9°¢2 Te4.04

GO°0 00"°0 00°00 00"1 9°2 : L9°O (8TOA paTte4—-su0t
SsnpneotwuotT sn4oaorty:
00°0 00°O0 8€°0 29°0 C°ee ee°L (asnou 2099p)
; sn{eTNOTueu SNosAWwoOtag
00°0 00°0 9L°0 ¥2°0 L°v9 GL°SL (qunumdTYyo 4SeaT)

SNUTUTM SeTueyngT

a W ad W goue puNnqy S4ZUsTN Gea OOL ted
aTtTusane 4Tney OATLETSY peanydeo sTenptatpur #
Ppoanjded wotTzao0dorg xyz ¥

dSOdu tos ‘p16, fy2-6) 229qQ0300 *| potazed etdues pue
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OOL X (setoeds [Te Jo sTenpTaTput fo # / setoods yoea FO sTenpTATpuT JO #) xx
sanoy pg Joy yes pue poyteq dexzq suc = 4yustu dea, 1

GE°GL © T2404
00°0 00°0 0S°0 0S°0 O°9L aye

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snpnectsuol sujyoOdotH
60.0 00°20 -25°0 8r’o O° v8 CL or (asnow aap
snjyetnotuew snoskuoreg

ue W ul IN goue puny SUYUoTN Gdeay OOL ted
eATZETOY peanydep sTenptatpur #
HH *

peangdeo uotqazodoag

dSOdu 1OF *PL6L fZL-L aequeoeq ‘zg potaed etdwes pue
‘ysnaqztqqer *¢ pTaz# azoxy Azeuums Sutdder, Teuwew [Tews ‘¢p-e-z PTaey

223-155

OOL xX (seToeds [Te FO sTenpTaTput fo # / sotoeds yoes so sTenptatput jo +

Svea:
sanoy pg foxy 108 pue poayteq der, ouo = 4yustTu deazy |

*

9b°Se = =Te7 OL

G0" 07 CO" 0" cS" 0" ey" 0 8°SL — 9°91 (osnou I5ap)
snjieTaotuew snosAwozeg
(yunudTYyo 9SeeT)

ENUTULW SeTWeINT

(*abs * pas OT} UetI-Ud PTOW)

(6/0 (pe © 10 ul @ hed) Oa Saat cL = L6°9L
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StTledeyert Sn~TTyuoureas

eee ii a Wd oowepunqy SqustN deal oo, ted
aTTusane q1npy_ eATAZETSY peangdep sTenptaTpul #
pednjaeg uoTzaAOdoIg xx ¥

asoqy toxz ‘¢/6L ‘92-91 Sen ‘¢ potaed oTdures pue

‘usnaqytqqer ‘¢ ptad roy ATeuums SutTdderz, Teuwew T[Teug “pe-E°2 «8TAeL

23-156

i690 efaubivibal 4

{ Sajees " ¢ = - 7 ¢ > 7a" ‘ OT Taq

_— ‘ory (Sages
: euse Luci nem Bibs
“(senor i

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| ee ee ee ee ee ieee oteieg

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OOL X (SeTosds [Te FO STeENPTATpUT FO # / sotoeds yoea FO sTenpTAtTput jo Ht) ex
gsanoy pz rox 4es pue peqyteq dex, euo = 4ustu der, 4, x

| eer. Texon
S0* 0, 9020 Ly’ by oO 0°18 O¢° OL (asnow zeep)

snzeTnotueu snosAuo leg
O0°O 00°O 00°! 00" Oo G°6: ia (~unudtTyo 4Se9T)

SNUTUTU SetTueqyny

0O°6..00°O. 06°C GS” G°6 bert (°aibs ‘pas oT }Wweu-useptos

STTeIszeT snp[tyaourodasg

ul W cl Wo souepunqy Ss4yoTtN G@ety OOlL 4d
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pemnzaey uwoTzZsoadolg xx %

aSOGU TOF ‘GLEL foe~-S2e ATue ‘py potaed aTdures pue
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a. 2: tol Yesemve gaiquert Leamem fiers .a0-€.8 afie?
sone rei a sinsilaaie siomse Hrs ¢

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OOl X (seToeds T[Te fo sTenptTatput fo # / Satoods yoea FO sTenpTatput jo it)

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sanoy pe tof 49S pue peqteq dex, auo = quStu dex |

*

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(sTunud tyo 4.Se3T)

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00°0 0070 1¢°0 69°0 0° Or | OL°6

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225-1 58

OOL X (setToeds TTe FO STeENPTATPUT go # / satoeds yoea jo STENPTAT Put jo #) xx
ginoy ~2 TOF 7OS pue pe ,Teq der. eud-= gustu det4 [--«

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ALLL LLL LOLA LA rr ana Tn Ora

| ISomy rox ‘pL6lL ‘2L-L toqmeoeq ‘z potazed eTdues pue
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2.3-1 59

OOL X (seToads [Te JO sTenpTatTput fo # / satoeds yoee Fo sTenpTaTput FO #) xx
SAN0Y pe BOT YVSE pus peqteq ded suo = 4usTU der [|

ev'cg@ Te z,OL

Oo"O 0CO"O 7S°0 9r*0 L°S¢ ee°L (8snow Tap)
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: SnVEU4TATApend SeTwe ny

00°0 00°0 OF°O 09°0 L° 7G eLsct (xunudtTyo 4svoT)
SNUTUTW SeTue yng

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STTeV194eT sn[TTyuourseds

ce lw qi W eouepunqy squstn deay Col ted
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OOl X (Satoeds [Te Fo STENPTAT DUT Jo # / satoeds yoea fo STENPTAT PUT gO 7): xy
smmoy pg tO 10s pue peyteq der suo = 4yusTu dey 1, x

co* el Teor
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Stletoyert snittydoudeds

ein i qd WW oowepunqy SsqustN deay oor ted
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peanideg uoTzaodeig x» Ps |

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2.3-161

COOL X (sotoads bie, BO SUSPLADEL T0, ¥./ soToods yoea JO STeNpTATpuT JO f') xx
Bano. #2, LOF 18s pue pertea dexzy suo = 4usTuU dem. | “y

LosGe Tenor
06°0, 06,.0, €2.%0, 290 ri oe else

( a9snow 2s9p

snjeTnotuem snosfmoiog

(sunumd Tyo 4seoT)
SNUTUTU seTueIngT

OO"0: CO"O, SPO 2G:°0 8°19 CL* el

ul W ul I] souepunqy Ss yusTN Gedy OOL 49d
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podnqzaey uoTzAoOaortG xx %

aSodu 20s ‘pL6r ‘pe-6) 2eq0400 £} potaed oa [cures pue

Susniq pextu *G ptas azoxy ATewums SutTdderz4 Teummewm {[Teus "OSs-e°2 FTASL

2.35-162

OOL xX (setoeds [Te FO sTenpTatput jo # / saetoods yoes JO sTenptatpuTt jo #) xx
sanoy pg fOJ 4osS pue poyteq dezq suo = qustu dem 4 x

Lert TEL OL

O07 0x00" 0 e000? G00? | OMDG L9°O (8TOA ysnagazes)
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00°0 00°0 00°! 00°0 0° 0S L9°O (asnow Ieap
| snyeTnotuew snoskwoiog
a ini ci Wl eowepunqy squvty deal oo, aed
eTrIuoane 4 IRPY OATLETOY pornzdeo sTenptatpur #
poungde) uotaaodoig xy x

dSOGU TOF PLE, *Zt-L aoqmeoeq ‘2 potazed otdures pue
‘ysnaq pextu *G pTas azoxy Laewuums Sutddex4 Teumrew TTeus “LS-E°2 eTqey

2.3-163

Cot x (setoads TTe FO sTenptatput jo # / satoeds yora To STENPTATpUT FO #) yxy
sanoy pg TOF 49S pue ported dery suo = 4UsTU deqId | x

€o°¢2 8 =Te40L

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SnuUTUTW SeTWeINT
ul W ue WI goue puny SZUSTN Gedy COOL ted

Peainsden Uliidoeol, 2% ¥%

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2.3-164

OOL X (setoeds [Te JO sTenptatput jo # / setoads yoea JO SsTenpTATpuT fo #) 4%
Sanoy 2 tof 20s pue peqtTeq der. ouo = guatu der 4°

8r7°s Te VOL

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OR On Or 0g" Ob: 6 Gey y9°¢ (Unc Tyo _4seoT)

SNUTUTU SeTWeInT

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poangdeg UOTZaOdoOTgG xx ¥

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2.3-165

OOL X (SeToeds TTe FO sTenpTATpuT jo # j setoads yoes FO STenpTATpuTt fo #)

xX
saoy pg tOf 4eS pue peateq dezy suo = yustu dex |

*

SlL*St Tey On

OG:'0 00"0 6L°O ¢2e*0 0°09 L6°OL (osnow 2a9D)
| snzeTnotuew snosAuoteg
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(xunud Tyo 4S22T)

SNUTUTW SeTueINT

aq WW iN ——eouepungy.._siqsin deap_ooltea
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CO poy (Soeate Tle FO sTenpTaTput jo # / satoeds yoes JO sTenpTATput To #). 4%
Sunoy vg TOF 4eSs pue peqyteq dex suo = 4UusTu dem 4, x

90°9 Te.01
06°C GOO obo 0¢°6 0°00! 90°9 (esnow raep
snyeTnotuem snoskmorag
a. aq W oowepunqy szusty dezy oo; ted
aTTuaane 1 TOpy eATZETOY peanzdep sTenptTatpul #

peinideg uoTzaodoig x,y %

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OOl X (Setoeds [Te JO sTenpTatTpur fo # / sotoeds yoeea JO STeNpTATpuT JO #) xy
samoy yg LOS 4eS pue poyteq dez4y suo = 4ustu der Pe

Le*l¢e 8 8TeyOL

00"0 GO"0 00" 0 001 | Pag S ie A (asnou gaxood ayorde)
; ayoede Snuj,eusoded
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Snzelnotuell SNOSAWUOLed

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SQUTUTW SeTWeIng

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é‘ysnaqeses /redtume-uofkutd ‘9 ptaz azoxy ATewums supddery Teuuweu TTeus "9G-f°2 ETQeL

2.3-168

COOL X (setoeds [Te zo STeENDTATPUT pole ae | sotoods yoees JO STENPTATpUT IO #') xx
. Smoy pd tOJ 18S puwe poqteq dexq ouo = qustu dexy. , x

Gi) to) = rex0y

00°C 00°0 00°} 00°0 (ahaa me eae) (esnou royood ayoede
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. snzeTnotuceu snossuorag

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: SNUTULTW SeTuUeI INT

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cr OW a WW eowepunqy squvty der, ool ted
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2.3-169

CO: & (setoods Tre gO STenPTATPUT FO # / setoods yoea FO sTenpTATpuT fo };)

KX
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SuUTUTW SeTuUe Ing

d in ad Wl eouepunqy syst deal COL ted
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2.3-170

COOL X (ssToeds [Te JO sTenpTAtput fo # / satoads yoea Fo sTenpTaTpuT jo tt) x%
sinoy po TOF Yes pue peyteq dezy euo = 4yustu der 4 x

Cand VO STVIIIV TIVIS ON

ul i eouepunqy S4yuvTN aeay OOL fed
OATZETSY pamadep sTenptatpul #
xX *

dSOGU TOF *pL6L SZ ,-L roqmeoseq 2 potazed otdwes pue

‘mopeom puetdn ‘*) ptaz aoy Aremms Sutdder, Temmeu TTeug “6S-E'2 PTQeL

225-171

4 €

aittqaext Saeentn. ffeeR -22-£.8 eidst
va E peacoat = boiteg ignse brs P

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a 32 sipttptosd a
a _syttetol Serax ga

ae. es gore basic

pieuntve es .

H ger? 00: at " : ai - 5

mr.

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pt X (eoteone Lis te eee ='s W \ @bf0ege tidsg To elauSivibat to y aad

COOL X (SetToeds [Te FO sTenpTATpuT fo 7 / setoeds yoea JO STeNpTATpUT Jo it) x%
saoy pe toy 408 pue poyteq deay suo = yystu der, 4p x

—_—_—$—$— ————— $n

69°6 e401

BO°O CO°O UL"°O GZ*O 0°08 | La*é (asnow to0op
snjeltnotuew snosAuoiseg

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SNUTUTW SeTwWe ny

com i WW oouepunqy squstn deal oo, ted
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poangdeg uoTzyaodorg yx *

a

aSOGU TOF *GLEL ‘92-81 AeW_‘¢ potaed eTdures pue
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OOL X (setoeds TTe FO sTenpTATput jo # / setoeds yoea so sTenptTATput fo #) ax

samoy ~zg dor 1eS pue peyteq dezy ouo = 4yustu deay 4, »

b's Te, 07
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pednjydeg uOTZAOdorTT xy x

dSOGY TOF *GLEL ‘oE-S2 ATne ‘fy potaed etdwes pue
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COL X (SseToads [Te FO STenpTATpuT fo # sotoods yoeo FO STeNPTATpUT JO 7) xx
smoy ye doy 19S pue peyteq dezy suo = 4ystu der, x

92° d¢ Te7 On
0070 00° 0 - 02°06 0 EOL, 90°C (OTOA potTte4,—-Lu0T)

snpneotsuot snqzosoT]]

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SUUTUTWU SeTWe Ng

ad W ue mt 9o0ue punqdy SUY4sTH Gea OOL ted
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dSOGU TOF *yL6L ‘72-64 teqo400 ‘, potaed eTdures pue
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2.3-174

7
‘ae A es

a PSS 6 Ck a ee re ee Se he es ap te

OOl X (SeToeds [Te FO sTenpTATputT fo # / setoeds yoea FO STenpTATpuTt Fo #) yxy
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EL ob TePOL

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Table 2.3-107 Definition of population parameters measured by the
Nem Jolly-Seber method and corresponding notations used in
Tables 2.35-89 to 2.3-106 for RBOSP

Notation Definition

i Trap night
; (1-5 ~- Sample period 1, Oct. 19-24, 1974)
(6-10 - Sample period 2, Dec. 7-12, 1974)

(11-15 - Sample period 3, May 18-26, 1975)
(16-20 - Sample period 4, July 25-30, 1975)

a Proportion of marked animals in sample i

p Probability an animal alive at time i is caught at
time i

M Estimate of the size of marked population just

before the ith sample

N Estimate of the total population size iter before
the ith “EEls

var (N(N) ) Error of estimation of N
B Number of new animals joining the population in
the interval from time i to time i + 1 which are
still alive and in the population at time i + 1
var (B) , The variance associated with estimating B
0 Probability an animal alive at time i survives to
TA mec) i
var (0) The variance associated with estimating O

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2. 323.35-15

The deer mouse (Peromyscus maniculatus), represented on all grids
except the one in Douglas fir during July,-was the only other smal]
mammal species captured on grid 1, bottomland meadow, in sample period
4. Based on the number of different individuals captured, this
species comprised 380 percent of the total sample.

Sagebrush (Grid 2)

This grid, located on 84 mesa, exhibited the second highest species
diversity value (1.047) of the small grids and the highest total
abundance figure (20.61 individuals/100 trap nights) for all grids.
Four species were captured on the grid during July, including one,

the thirteen-lined ground squirrel (Spermophilus tridecemlineatus )
unique to this trapping grid in all samples to date. Armstrong (1972)
indicated that this species as well as the Apache pocket mouse
(Perognathus apache), encountered here and on one other grid in July,
prefer sandy loamy soils which appear to be characteristic of 84 mesa.

Typically, the least chipmunk (Eutamias minimus) and the deer mouse
were the predominant species found on this sagebrush grid accounting
for 58.8 and 20.6 percent of the total sample, respectively.

Rabbitbrush (Grid 3)

Three species were encountered on this grid in July. Total abundance
(12.73 individuals/100 trap nights) was moderately high and species
diversity (0.619) was low. The latter was due to the predominance
of the deer mouse which accounted for 81 percent of the total
abundance. .In fact, the deer mouse was more abundant in rabbitbrush
(10.30 individuals/100 trap nights) than in any other type sampled
during July.

Pinyon-Juniper/Mixed Brush (Grid 4)

Both total abundance (13.33 individuals/100 trap nights) and species
diversity (1.038) were moderately high on this grid in July. The
least chipmunk was the most abundant of the three species encountered
(6.67 individuals/100 trap nights) with the golden-mantled ground
squirrel (Spermophilus lateralis) and the deer mouse present in
approximately equal numbers. .

Mixed Brush (Grid 5)

Only 2 species, the least chipmunk and the deer mouse were captured on
the grid in July. As a result species diversity was low (0.683)

and total abundance was only 8.48 individuals/100 trap nights. The
deer mouse was more commonly encountered accounting for 57.1 percent

_of the total abundance.

2 e 3-252

» 2.3.3.3.1.6. Pinyon-duniper/ Sagebrush (Grid 6)

This grid, represented by four species, exhibited the highest species
diversity value of the small grids (1.133). Total abundance was also
quite high (15.15 individuals/ 100 trap nights) and was exceeded only
by the bottomland meadow grid and Grid B, pinyon-juniper south slope,
in July. The deer mouse accounted for 52 percent of the total abun-
dance while the golden-mantled ground squirrel and the least chipmunk,
present in approximately equal numbers, made up 44 percent of the
total. A single Apache pocket mouse was also captured.

2.3.3.3.1.7. Upland Meadow (Grid 7)

Lack of cover is probably the greatest contributing factor to the

very low species diversity (0.520) and low abundance (8.48 individuals/
100 trap nights) exhibited by this grid. Only two species were
encountered, the deer mouse and the least chipmunk, with the former
accounting for 78.6 percent of the total abundance.

2.3.3.3.1.8. Greasewood-Sagebrush (Grid A)

The presence of only four species coupled with the predominance of least
chipmunk and deer mouse species (33.3 and 51.2 percent of the total
abundance, respectively) resulted in the lowest diversity vaiue
{1.040) of any of the large 7.29 ha grids. Total abundance was

) moderately high (12.63 individuals/ 100 trap nights). However, the
grid was responsible for one of only two captures of the long-tailed
vole (Microtus longicaudus) during the July sampling period.

2.3.3.3.1.9. Pinyon-Juniper (south slope) (Grid B)

The additional tree stratum, by providing more food and potential
nesting sites, probably resulted in the presence of three species on
this grid, the Colorado chipmunk (Eutamias quadrivittatus), the

pinon mouse (Peromyscus truei) and the bushy-tailed woodrat (Neotoma
cinerea) not generally found in other habitat types in the area. The
additional three species and the lack of predominance by any of the
seven species encountered resulted in the highest species diversity
value (1.634) of any of the large grids. Total abundance of 16.09
individuals/ 100 trap nights was the second highest of any grid
sampled during July.

While small mammals may utilize pinyon-nuts and juniper berries for
food, particularly during winter (Douglas, 1969) the most significant
contribution of pinyon-juniper trees to small mammal inhabitation is
in the form of potential nesting sites. Both the pinon mouse and the
bushy-tailed woodrat use pinyon and juniper trees extensively for nesting
within this habitat type. Also, most of the other species encountered
during trapping, particularly the Colorado chipmunk, were observed

) retreating to trees and old deadfalls upon their release after capture.

225-2535

) 2.3.3.3.1.10.Pinyon-Juniper (north slope) (Grid C)

2.d.dceel. tt

As expected, this grid also exhibited a high Species diversity value
(1.477) for July. The presence of one less species and the pre-

Pe of the golden-mantled ground squirrel and the least ,
chipmunk (30.9 and 33.0 percent relative abundance, respectively)
resulted in a diversity value slightly lower than that for Grid B
(Pinyon-Juniper/ South Slope). Total smal] mammal abundance (14,59
individuals/ 100 trap nights) was also quite high.

.Sagebrush (Grid D)

As a result of the nearly equal distribution of individuals among
three of the species captured on Grid D, species diversity (1.165)
was moderately high. Total abundance (7.97 individuals/ 100 trap
nights) was very low, however. This is uncharacteristic for sage-.
brush type communities in the area and could relate to a number of
factors on a microhabitat scale, such as quality and quantity of the
food supply and availability of nesting sites. Alternatively, an
increase in natural food supplies in July could have reduced the
attractiveness of the trap bait and therefore trap success.

In addition to the golden-mantled ground squirrel, léast chipmunk,

‘and deer mouse species encountered,a single individual of the sage-

fi oesn ae bole.

rae Hix Oe Be 8 2

brush vole (Lagurus curtatus) was captured. This species was observed
in only one other grid in July (Grid E, Mixed sy uahie Both Armstrong
(1972) and Larrison and Johnson (1973) indicate that the sagebrush
vole is generally limited to stands of sagebrush mixed with other
shrubs up to 9000 ft.

Mixed Brush (Grid E)

“Both species diversity (1.137) and total abundance (11.13 individuals /

100 trap nights) were moderately high on Grid E. Five species were
encountered, including the long-tailed and sagebrush vole. The

least chipmunk was the most abundant species (45.9 percent relative
abundance) while the deer mouse and the golden-mantled ground
squirrel exhibited relative abundance values of 37.8 and 12.2 percent,
respectively.

Douglas Fir (Grid F)

Only two species were encountered on Grid F in July resulting in a
very low species diversity value (0.693). Furthermore, total abun-
dance (3.31 individuals/ 100 trap nights) was the lowest of all grids
sampled. The harsher environment and shorter growing season at the
higher elevation (8200 ft) together with the homogeneity of the
habitat type may partly account for the low species diversity and
abundance ‘afuest )

2. 3-254

2.35320. 1-84

2:53.323.2

The two species captured, the least chipmunk and the red-backed vole
(Clethrionomys gapperi) were present in equal numbers. In contrast to
the ubiquitous nature of the least chipmunk in the Piceance Basin,
the red-backed vole has specialized habitat requirements. Warren
(1942) reported that this vole rarely occurs below 8000 ft. ele-
vation and Armstrong (1972) stated that this boreal forest species

is usually confined to well developed coniferous zones from 8000 to

11000 ft. in Colorado.
Aspen (Grid G)

Although an additional species, the deer mouse was trapped in Aspen,
the predominance of the red-backed vole (80 percent of the total
abundance) resulted in a lower species diversity value (0.613) than
that for Douglas fir. Total abundance (6.56 individuals/100 trap
nights) was relatively low; again probably reflecting the constraint
of the high elevation (8100 ft) on increase in small mammal popu-
lation size.

Laboratory Analysis of Reproductive Effort

Analysis of small mammal reproductive effort was conducted on
seventeen adult females of three predominant species captured

during the July 1975 small mammal trapping period; three long-tailed
voles (Microtus longicaudus), two least chipmunks (Eutamias minimus)
and twelve deer mice (Peromyscus maniculatus) were captured in six
major vegetation types and analyzed for reproductive effort. Corpora
albicantia were counted to verify litter sizes in cases where resorb-
tion of embryos was suspected. Results are given in Table 2.3-140.

The low capture success during this mid-summer sampling period is
probably due to an increased natural food supply evidenced during
field sampling by a lush herbaceous understory with many fruiting
plants in most vegetation types sampled. As the natural food supply
increases it is usually more difficult to attract animals to baited
traps. Additional traps did not noticeably affect trap success.

Fifteen (88 percent) of the seventeen females examined contained
embryos or recent placental scars and were classified as repro-
ductively active. Placental scars were present in six (35 percent)
of the females examined; four of these females were lactating. Only
45 percent of the females examined in-May were reproductively
active, i.e., contained placental scars, were lactating or were
pregnant. Three long-tailed voles examined from the aspen (north
slope/8400 ft) vegetation type were all pregnant, and average number
of embryos found was five. Reproductively active females were

not captured in this vegetation type in May.

Eleven (73 percent) of the fifteen reproductively active females
captured during July were deer mice. Deer mice embryos from both
May and July sample periods averaged five. Five deer mice from

the lower elevations (below 7000 ft) exhibited placental scars; one

2.3-255

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2.3-256

2.da dono

female from greasewood-sagebrush (flat/6200 ft) exhibited both
embryos and placental scars, indicating that this was its second

litter this season. None of the females examined from above 8000

ft elevation exhibited placental scars. This may be an indication
of later reproductive activity for animals above 8000 ft elevation.

Laboratory Analysis of Stomach Contents

During the July 1975 small mammal sampling period twenty-two animals -
were collected and prepared for analysis of stomach content. Results
of this analysis are summarized in Tables 2.3-141 through 2.3-146.
Fifteen deer mice (Peromyscus maniculatus), two least chipmunks
(Eutamias minimus) and five long-tailed voles (Microtus 1 longicaudus)
were Captured during July 1975 sampling and analyzed in the laboratory
for stomach content.

The low capture success during this mid-summer sampling period is
probably due to an increased natural food supply evidenced during
field sampling by a lush herbaceous understory with many fruiting
plants in most vegetation types sampled. As the natural food supply
increases it is usually more difficult to attract animals to baited
traps. Additional traps did not noticeably affect trap success.

Mice of the genus Peromyscus are known to eat a wide variety of foods,
and to be highly opportunistic in selection of these foods. In the
spring, tender sprouting herbaceous vegetation may assume importance
in deer mice diets, but these succulent plants are available for only
a brief period during early spring (Douglas, 1969). As the warm
season progresses these tender young sprouts become less available

at the same time that recently matured seeds are becoming increasingly
available.

Accordingly, small mammals captured at sample sites below 7000 ft
elevation utilized seeds more extensively during July than they had
during the previous (May) sampling period. Deer mice captured in
pinyon-juniper (north slope/6900 ft) utilized seeds exclusively

(100 percent stomach contents) while deer mice captured in pinyon-
juniper (south slope/6700 ft) utilized seeds to a lesser extent
during the same sample period (79 percent of their stomach contents).
The percentage of seeds in the stomachs of deer mice analyzed

from pinyon-juniper south slope rose from 66 percent in May to 79
percent in July. Thestomachs of deer mice collected from greasewood-
sagebrush (flat/6200 ft) contained nearly 98 percent seed in July

as compared to 85 percent seed in May. In mixed brush (south slope/
8200 ft) stomach content percentages for seed rose from 57 percent
in May to 74 percent seed in July for deer mice. Only one deer
mouse was captured in sagebrush (flat/7200 ft); its stomach contents
were 94 percent seed.

2.3-257

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-263

2

2.3. 3ad24.

re PE ge

ra FAS. pas eS

Long-tailed vole stomach contents examined from Aspen (north slope/
8400 ft.) contained 94 percent succulent plant material and 6 percent
seed in July. This contrasts with May data showing long-tailed voles
with 96 percent seed and only 25 percent succulent plant material.

This rather drastic decrease in the use of seeds as a food source
during July as compared to May is probably due to the persistent snow
in early spring which limited other food resources such as succulent
vegetation. By July, as the result of the snow melt, new and abun-
dant herbaceous plants became available at these higher elevations
and probably replaced seeds as a major food source for the long-tailed
vole. Voles of the genus Microtus demonstrate a definite preference
for herbaceous vegetation and take advantage of it when available
(Rieve, 1973). Four of the five long-tailed vole stomachs examined
contained over 97 percent succulent material. Food preferences and
seasonal changes in food habits will become more apparent as more
data are accumulated.

Collection of Voucher Sepcimens

No new species were added to the Voucher specimen collection during
the reporting quarter June ig August, 1975.

Pitfall Trapping

Thirteen pitfall trapping stations were repaired and operated during
late July, 1975, for four consecutive days. The bottomland meadow
pitfal! trap was closed one day early because haying was to begin the
following day. An additional pitfall trap was established in the
aspen habitat, which was not sampled during May, 1975. because of
excessive snow. Ten individual small mammals representing three
species were captured at five different pitfall locations. The
sagebrush (flat/ 6500 ft.) and rabbitbrush (flat/6800 ft.) pitfall
traps were the most successful, capturing three Apache pocket mice
(Perognathus apache) and three deer mice (Peromyscus maniculatus).
Two deer mice were also captured in pitfall traps located in sage-
brush (north slope, 7100 ft.). Two long-tailed voles (Microtus
longicaudus) were taken in pitfall traps located in both aspen
(north slope, 8400 ft.) and mixed brush (south slope, 8400 ft.)
habitats.

Night Spotlight Census

Night spotlight censuses were conducted on June 22 and 25, 1975.
This method of censusing nocturnally active animals, eSpecially
lagomorphs, has proven valuable in short-grass plains situations
but encounters visibility problems in the Piceance Basin due to the
dense vegetation and varied topography. The method used by ECI

“helps to account for this obscured visibility. The results of the
night spotlight Censuses conducted this quarter are presented in

Table 2.3-147).

2.3-264

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LaF 3-265

ie TE BR A

The presence of at least three species of lagomorphs have been
documented to date on or near Tract C-a. The white-tailed jack-
rabbit (Lepus townsendii) and the black-tailed jackrabbit (L.
californicus) were easily identified by field observation but the
cottontail (Sylvilagus sp.) is much more difficult to distinguish
to species. A specimen was collected by ECI personnel and identi-
fied by Dr. Robert B. Finley of the National Fish and Wildlife
Laboratory as a Nuttall's cottontail (Sylvilagus nuttallii). How-
ever, it is possible that more than one species of cottontail
resides in the study area. Two lagomorph species (cottontail and
white-tailed jackrabbit) and the porcupine (Erethizon dorsatum)
were observed during night Spach ign censuses conducted this quarter
(Table 2.3-147).

Lagomorph population estimates and general field observations during
the summer quarter seem to indicate an increase in lagomorph popu-
lation. However, so few individuals were observed that it is
difficult to formulate any firm conclusions relative to population
numbers at this time.

Bat Investigations

Mist netting for bats took place on four consecutive nights in June
and on four consecutive nights in August, 1975. At three locations
nets were placed over stock tanks, two of which were stiuated in
bottomland sagebrush habitats while the other was on Cathedral
Bluffs at a spring near mixed brush and aspen stands. Another net
was placed over a small pond below the Stake Springs and near
abandoned cabins. This pond was surrounded by a dense stand of
rabbitbrush. a

In June, the long-eared myotis (Myotis evotis) and the small-footed
myotis (M. leibii) were captured at the two stock ponds in bottom-
land sagebrush habitats.

In August four species of myotis were captured at one of the same
stock tanks sampled in bottomland sagebrush in June. In addition to
the two previously mentioned bat species, the California myotis
(Myotis californicus) and as yet unidentified myotis (Myotis sp.)
were netted during August sampling. Also during the August sampling,
a hoary bat (Lasiurus cinereus) and a small-footed myotis were
captured at a small pond below the Stake Springs pond.

One night during August sampling a. net was placed over a stock tank
on Cathedral Bluffs where larger bats were seen flying. However,
no bats were captured.

Bats were not recorded during daytime searches of rock crevices, old
buildings and rock overhangings.

2.3-266

2:33. Summary and Conclusions

A total of 580 individuals representing 12 species were captured during
July small mammal live trapping operations. Grid 2, sagebrush, had

the highest capture success during this period accounting for 13.2
percent of the total individuals of all species trapped per 100 trap
nights (Table 2.3-88). The small Grid 6, pinyon-juniper

sagebrush, and large Grids B, pinyon-juniper (south slope) and C,
pinyon-juniper (north slope) also exhibited high capture success.

The most species encountered on any one grid occurred on Grid B where
seven were captured. This and the lack of predominance by any one
species resulted in the highest species diversity value (1.634)
recorded for any of the large grids. The increase in number of poten-
tial nesting site and refuge areas afforded by the additional tree
stratum in pinyon-juniper types probably resulted in the
addition of three small mammal species, Colorado chipmunk (Eutamias
uadrivittatus), pinon mouse (Peromyscus truei) and bushy-tail \ood-
rat (Neotoma cinerea) not generally found in other habitat types in
the area. Consequently, the grids located in the Dinyon-juniper types
had among the highest species diversity indices recorded for the
large and small grids, respectively (Table 2.3-111).

The deer mouse (Peromyscus maniculatus) was the most commonly
encountered small mammal species during July trapping efforts accounting
for 39.6 percent of the total captures. It was represented in grid
samples from all habitat types except Douglas fir. The least chipmunk
(E. minimus) was also captured on all grids except one, (Grid 1,
bottomland meadow) and this species accounted for 34.2 percent of the
total captures. The golden mantle ground squirrel (Spermophi.lus
lateralis), though not as frequently encountered, was observed in a wide
variety of habitat types. The Colorado chipmunk, pinon mouse and
bushy-tail woodrat were generally limited to pinyon-juniper woodlands.
Sagebrush vole (Lagurus curtatus) captures were restricted to sage-
brush and mixed brush communities while both the montane (Microtus
montanus) and long tail voles (M. longicaudus) were captured in two
seemingly different habitat types. The red backed vole (Clethrionomys
gapperi) was observed only on grids established in the aspen and
Douglas fir communities. . The thirteen-linc< ground squirrel (S.
tridecemlineatus) and the Apache pocket mouse (P erognathus apache) were
both found in association with loose soils with the former

species being captured only at one location, Grid 2 on 84 Mesa.

Excluding the winter sample, the July sampling experienced the

lowest capture success of all smal] mammal trapping operations to
date (Table 2.3-88). The low smail mammal population abundance for
‘July may be explained by 1) the population levels are in fact tow
“resulting from a combination of factors which might include high

natural mortality, and a normally late or delayed breeding period;
low population levels and high mortality are indicated by the Jolly-
Seber population size estimates given for selected species in Tables
2.3-89 through 2.3-106 and/or 2) an abundant food supply at this time
of the year may have resulted in fewer animais being attracted to
non-natural baits.

Although abundance was low during sample period 4 relative to other
warm weather sample periods, small mammal species diversity was
generally higher over all grids during the July sampling efforts.

The increase in trapping success of thegolden-mantled ground squirrel
relative to decrease in other small mammal species effecting a more
equitable distribution of individuals among species no doubt resulted
in the higher species diversity values. In fact, of the nine grids
in which the golden-mantled ground squirrel was represented in both
May and July samples the average trapping success was 0.92 and 2.68
individuals per 100 trap nights per grid, respectively. As a result,
eight of these nine grids showed an increase in species diversity

in July. The golden-mantled ground squirrel was only captured twice
during October.

No particular relationships between habitat type and average species
weight are as yet evident from the results presented in Tables 2.3-112
to 2.3-139. However, weights do appear to be somewhat lower in

sample period 4 than in sample period 3 for most species. However,
this may reflect the inclusion of newly-turned-adults into July

weight samples rather than any real difference between adult weights
for the respective sampling periods.

Seventeen adult females of three predominant species (least chipmunk
deer mouse and long-tailed vole) were collected from 6 major vegetation
types during July and analyzed for reproductive effort. Fifteen of
the 17 females (88 percent) contained embryos or placental scars and
were classified as reproductively active. Only. 45 percent of the
females examined in May were reproductively active. The increased
reproductive effort together with the low population levels (Tables
2.3-89 through 2.3-106) and few juveniles in the population (Tables
2.3-34 to 2.3-87) during July suggests that the major recruitment

of young into the active small mammal population occurs in late
summer .

Twenty-two animals of the above three species were also collected
during July for analysis of stomach contents. While the deer mouse
revealed an increased utilization of seeds as a food item from May
samples the long-tailed vole showed a higher percentage of succulent
vegetation parts in its diet. This is probably indicative of the
increased availability of a preferred food for both species during

2.3-268

July. The small number of least chipmunks collected for stomach
analysis precludes definite conclusions concerning their food habits
at this time.

Ten individuals of three species were collected in thirteen pitfall
trapping stations operating for 4 days during July, 1975. All species
captured, deer mouse, Apache pocket mouse, and the long-tailed vole,
had previously been documented by live trapping efforts.

Two lagomorph species (Lepus townsendii and Sylvilagus sp.) and the
procupine (Erethizon dorsatum) were observed during night spotlight
censuses conducted in June. Although lagomorph population levels

seemed to increase slightly during the summer as indicated by the

census results and general field observations, the data are insufficient
to permit formulation of definite conclusions at this time.

Five species of bats were documented by mist netting during June and
August, 1975. The long-eared myotis (Myotis evotis) and the small-
footed myotis. (M. leibii) were captured in June while the California
myotis (M. californicus), the hoary bat (Lasiurus cinereus) and an as
yet unidentified Myotis were added to the collection in August.

2.3.3.5--SMALL MAMMALS RAW DATA

2 e 3-270

2.3.3.5--SMALL MAMMALS RAW DATA

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Grid Name Horse—PL1.. Grid, Sample Period Jury 175 Trap Night_ |

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File Nez 93.¢C.5. 1.2, 16-36
SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET /
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File No? 93,¢.5.1.2.14-37__.
ye

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SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET

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Date;- time traps set (Mio) 27 Jw 96 __ Date, time traps checked Laecol, 26) la ee

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SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET

-B3.C.5.01.2, 14-39

Grid A _ Sample Peried Quiu_jq7.g7 Trap iene « Bie &’ oe

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File No: 7.6.4 4a -29
SMALL MAMMAL LIVE TRAPPING FIELD DATA SHEET of .

Ps Geary ‘ Sas ae a i) (
Grid NameSon wd RT ria Sample sustadiit tole pt Trap thiptie: = fie a

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P; Ny tn Si ONT South opt
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2.3.4
2. FAL

2vdc4e2
2 achelok

Large Mammals
Introduction

Large mammal investigations are designed to determine the distribution
and relative abundance of mule deer, elk, and feral horses in the
vicinity of Tract C-a on a seasonal basis. Investigations are also
being conducted to determine relative use of portions of the study
area during seasonal movements of mule deer.

Methods
Aerial Surveys

Aerial censuses being conducted to determine relative distributional
abundance of mule deer, elk, and feral horses on Tract C-a and
surrounding areas employ a high-wing Cessna aircraft designed to
permit slow flight at low levels above the ground. The plane is
flown along standardized transects (flight paths) within the range
of 120-136 -km (75-85 mi) per hour (indicated air speed) at an
altitude of approximately 45.7 m (150 ft) above the ground. Due to
the varied topography, the above-ground altitude varies slightly
within transects, however, the flight paths, speed, and altitude of
the aircraft are duplicated as much as weather conditions permit.

Weather conditions are of such a variable nature that perfect flight
conditions are not possible for every flight. At times, the weather
may postpone a flight or terminate a census tnat is in progress.

The observer makes a decision if the census is to be conducted or
continued after consultation with the pilot concerning the limitations
on flight caused by the weather. The decision is based on consider-
ations for safety of the observers and the effectiveness of the survey.
The level of effectiveness of the survey is a judgment made by the
observer based on past experience in conducting censuses. If. a
flight is postponed or not completed, it is conducted in its entirety
when weather conditions become more favorable.

Census flights are conducted at cee inane two week intervais from
late October through early April to assess the mule deer population
during the winter period. Flights conducted bimonthly during the
Summer months are intended mainly for elk and feral horse observations.
All species of animals observed during each census flight are recorded.

Complete coverage of the area of investigation is accomplished by 19
north-south transects. The flight paths parallel each other at
approximately 0.81 km (0.5 mi) intervals east of Tract C-a and 1.6
km (1.0 mi) intervals on the tract and to its west (Figure 2.3-14).
More intensive coverage is applied to the east of the tract since
Baker (1970) identifies this region as a major mule deer winter con-
centration area.

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2.3-272

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The aerial censuses conducted to the east of Tract C-a survey an area
of approximately 16.1 km (10.0 mi) by 8.9 km (5.5 mi). The boundaries
of the area are Duck Creek on the north, a line running north and

south approximately 1/2 mile east of Duckett Ranch on the east, Duckett
Ranch on the south, and the eastern boundary of Tract C-a on the west.

The remaining 8 transects survey an area of approximately 16.1 km
(10.0 mi) by 12.1 km (7.5 mi). The boundaries of this area on the
north and south are extensions of the northern and southern boundaries
of the area east of the tract. The eastern most transect is located
along the eastern boundary of the tract while the western-most
transect is along the north-south section lines immediately east of
Cathedral Bluffs. '

To permit constant observation of the transect area along the flight
paths, portable tape recorders are used to record information during
the census. All animals seen by the pilot and two observers (positioned
on opposite sides of the plane) are identified to species, counted,
and their locations noted. The observers communicate with each other
and the pilot when necessary to confirm the location of animals
observed. When possible, information on age, sex, activity patterns
and habitat is also recorded on the cassette tape. Immediately
before the censuses commence, each observer identifies the category
of data to be recorded (i.e., Large Mammal Aerial Census), the date,
area to be surveyed, observer's name and observation position in the
aircraft, the name and position of the other observer, name of pilot
and make and model of aircraft on the tape. Weather conditions such
as temperature, estimated wind speed and direction, and estimated
cloud cover are also recorded. The time is recorded at the beginning
of the first transect and at the end of the last transect for the

_- census area. General impressions on animal distribution, ground cover
’ characteristics, changing weather conditions, light and spotting

conditions, and flight characteristics are recorded at appropriate
times throughout the census flight. Other species of animals (such
as coyotes) observed incidentally during the aerial surveys are also
noted to aid in the evaluation of the distribution of these species.

The information recorded on the tape is transferred by each observer
from a transcript onto a standard data form (Figure 2.3-15). Dis-
tribution maps showing locations of the animals observed are generated
at the same time. Incidental observations are recorded on Field
Observation Sheets (Figure 2.3-16). The procedure described above is
completed as soon as possible upon completion of the census flight.

If circumstances should occur which cause a delay of over 14 days

or if another flight is conducted before the data are recorded on

the data forms and distribution maps, the analyst notes such a delay
on the forms and map.

2 e 3-273

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File No.

LARGE MAMMAL AERIAL CENSUS REPORT AND DATA SUMMARY FORM

Proj/Study Date Flown Species Survey Area
Observers: R L Pilot/Aircraft

Start Finish Ave. Indicated Air Speed Est. Altitude
Counting Conditions: Ground Cover Light Air
Weather: Temp. “Wind Cloud Cover Analyst QA Check _
a Location : Notes and Comments

Pas ie fac eae eee ae tie eer ve boel cmosl

Total Animals Counted:
Animal Distribution:

Figure 2.3- 15. Large mammal aerial census report. and data summary form
for RBOSP.

2.3-274

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FIELD OBSERVATIONS ;

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Species Date Time

Means of Edent (ficeeien

Number Observed ; fos 2

Adult Juv.
Habitat

*
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Observer * Include any distinguishing field marks for
. horses.

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Figure 2.3-1l0. Field observation sheet for RBOSP.

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2.3.4.3 Results
2.3.4.3.1 Aerial Surveys

Large mammal aerial surveys were conducted on June 26 and August 18,
1975. The number of mule deer, elk and feral horses observed during
each survey is presented in Table 2.3-148. Deer or elk were not
observed during the surveys. It is expected that mule deer and elk
were located in the mountain brush, aspen, and Douglas fir vegetation
types during this period and consequently were not readily visible
from the air. Feral horses are more visible, due in part to their
varied coloration, larger size, and habit of frequenting more open
areas. Most of the feral horses were observed in the southwest
quarter of the study area during the aerial counts (Figure 2.3-17).
More horses were observed during the June survey than during the
August count. |

2.3.4.4 Summary and Conclusions
Mule deer and elk were not observed during the two aerial surveys
conducted on June 26 and August 18, 1975. A total of 156 feral

horses was observed during the surveys and most of these occupied
areas southwest of Tract C-a.

2.3-276

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7 aN . Bo S900T Fo Szayiiivee 269%6
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9 Table 2.3- 148. Number of mule deer, elk, and feral horses observed during
aerial censuses on June 26 and August 18, 1975 for RBOSP

Feral Horses

Date Mule Deer Elk Adult Foal Unidentified

June 26 0 0 go. 22 0

August 18 9 genes encase
Totals = 08 ase tk. Grae 0

os

2.3-277

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2.3.4.5--LARGE MAMMALS RAW DATA

2 e 3-279

2.3.4.5--LARGE MAMMALS RAW DATA

ATAG WAS) CIAMMAM SaMAJ--2.%-6.S

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————_—____.

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File No, 2s 72 7,5 f see

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LARGE MAMMAL AERIAL CENSUS REPORT AND DATA SUMMARY FORM Leg /

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Proj/Study K3/o0¢Y_ Date Flown p§ cee npeyx 76 Species 2h. Le a Survey Area £> “%~.. LL
@ervers: Re Cf King Ligeti Kewuptd 4 Pilot/Aircraft Ze lb cep {CC 2672 a
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mM] F Jouvlu poe) | Notes and Comments

Total Animals Counted: iF

Animal Distribution:

pity SANK ALKLAL CENSUS REPORT AND DATA SUMMARY FORM C6. Oro, F, 1-5

roj/Study _ Blo Date Flown EDL L2\— Species Kf/K Survey Area Kin 8 tis Srwt eo
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File No. J75 50 isle as dee

LARGE MAMMAL AERIAL CENSUS REPORT AND DATA SUMMARY FORM / 2h (

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Proj/Study ¥3 Date Flown V4, _ Hes Species ASK __ Survey Area Jiga (Maree Ahk
( @ vers: R paNt FE Le Eo Keine ey pilot/Atreratt Lf Bee | Covere 226
Start COL Finish OF/Q- Ave. Indicated Air Speed FO orb Est. Altitude 4yo7 _
Counting Conditions: Ground ig i a mea Light. eee a 2 ie wee

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Observations
Location N -and I
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LARGE MAMMAL AERIAL CENSUS REPORT AND DATA SUMMARY Fora 727

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2.3.5.1

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2.3.5.2.1.1

Mammalian Predators
Introduction

No change nas occurred since Progress Report-2. See section 3.7.1] in
Progress Report-2 for the introduction to the mammalian predator
section.

Methods
Large Predators

Two census methods, the scent-station visitation technique and the
siren-elicited howling response procedure are being used to gather
information on large predator populations. These methods were
selected after a thorough review of the literature, and promise to
yield reliable indices of large predator abundance and distribution.

Scent-Station Visitation Techniques

The scent-station visitation technique was developed in New York State
by Cook (1949), who suggested that records of fox sign at scent posts
provided a practical index to the relative abundance of foxes between
areas, and from year to year. Richards and Hine (1953) in a survey
conducted to inventory foxes in Wisconsin, used a variation of this
technique as did Wood (1959) in 25 counties of Florida, South Carolina
and Georgia.

The method has been standardized by the Denver Wildlife Research
Center (Linhart and Knowlton, 1973). In cooperation with the Division
of Wildlife Services, this center has used it- to survey the relative

- abundance of predators in 17 western states. Approximately 350

scent-station lines of 50 stations each were distributed across more
than 1.8 million sq mi and checked during the fall of 1972, 1973 and
1974 as part of a federal monitoring program. The results of the
Ongoing program are currently housed in ECI's library. Additional
results will be available from the Fish and Wildlife Service as
analysis of federal data will, in future years, be the responsibility
of this agency. A statistical evaluation of the survey method is
being developed under federal contract with Oregon State University
and a contract completion report is expected in July 1975. An
adaptation of this method is used on and near Tract C-a so that data
collected by ECI personnel might generally be comparable to data
obtained by federal agencies.

The technique as applied on Tract C-a involved the initial establish-
ment of one "survey line" for November, 1974 and February, 1975 and
the addition of a second survey line for June, 1975 and all subse- é
quent samples. Each survey line consists of 50 scent-stations spaced
approximately 0.5 km (0.3 mi) apart along a 24 km (19.7 mi) route

2.35-280

» (Figure 2.3-18). At each station, a small perforated plastic capsule
containing about 1 q of granular fermented egg extract as an attractant
is positioned in the center of a circle of sifted earth 1 m (3.2 ft)
in diameter. During sampling periods when snow is present, stations
are placed in an unmarked patch of snow; only those tracks within.
the 1 m circle are recorded. The capsule is supported above the
ground or snow by a thin wire rod. Stations are placed adjacent to
the road edge and alternated from left to right sides of the road
to reduce the influence of wind direction. Survey routes are checked
daily for five consecutive days every fourth month, beginning in
November 1974 (originally scheduled for October) and continuing
through June 1976. Animal visits based on tracks are recorded for
each station on a standard field data: form (Figure 2.3-19).

Stations that are visited or disturbed are resifted or, in the case
of snow, relocated in an unmarked area nearby. The fermented egg
attractant remains active throughout the five-day sampling period
and is only replaced if rendered uneffective by wind, rain, sleet
or animals (Linhart and Knowlton, 1973). An olfactory check is
made when conditions suggest the possibility of attractant ineffec-
tiveness. ee:

2.3.5.2.1.2 Coyote Siren Census

The siren-elicited howling response coyote census technique is being
® employed concurrently with the scent-station visitation technique.
The former method has been tested by the Denver Wildlife Research
Center (Carley, 1973) and has been used by the Oregon State Game
and Fish Agency (Wolfe, 1974). The following procedures, patterned
after Alcorn (1971la, 1971b) of the Bureau of Sport Fisheries and
Wildlife, are being used for Tract C-a. A 48 km (30 mi) transect
- consisting of permanently marked siren stations spaced approximately
4.8 km (3 mi) apart was established along existing roads as shown
in Figure 2.3-18. To help maintain a 10-station sample during
nights when wind on Cathedral Bluffs or noise interferes with data
collection, an eleventh station has been added to the end of the
transect. A maximum of ten of the eleven stations are recorded on
the data sheet for any one night. At each station, an electronic
siren is sounded for two complete pitch cycles (=20 seconds),
followed by a 1l-minute listening period. A second two-cycle
sounding of the siren is followed by a 2-minute listening period.

Data recorded on a standard form (Figure 2.3-20) inciude time of
soundings, response (defined as the number of groups or identifiable
individuals heard) to the first sounding, response to the second
sounding and total response, addition of the recorded howling response
during the two listening periods. Notes on conditions which might
affect data such as wind, precipitation, proximity to humans, or
interference by noise are also recorded. Alcorn (1971a, 1971b) and
Dd Wolfe (1974) recommend that the survey be discontinued or the affected

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2. 3-282

PREDATOR SCENT-STATION VISITATION FIELD DATA SHEET GC

Figure 2.3- 19. Predator scent-station

- for RBOSP.

Ze 3-283

ooology consultants, Inc

Location Proj. No. Date Day #
_ Investigator Survey Route
Weather
: ~~ —_
2 27
3 28
4 29 ;
5 30
6 31
7 32
8 33
“ 34 |
10 35 : ai
11 36 - ae }
12 37
13 38
14 39
15 -40
16 “41 :
17 42 '
18 43
19 44
20 45
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24 49
25 50

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2 e 3-284

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2:3.5:2.193

259.9252

Cedwtaa

station eliminated if winds are encountered in excess of 10 mph or
if precipitation occurs. Stations where there is much interference
by noise are omitted from the computation of relative abundance
indices. Siren sampling is accomplished after dark on two nights
with suitable weather conditions during the scent-station sampling
period.

Other Large Predator Investigations

Two other kinds of field evidence are being compiled on the distri-
bution and relative abundance of large mammalian predators. During
the 24 aerial censuses of big game animals in the winter months

and the six summer aerial censuses of wild horses, raptors and
domestic livestock, the observing biologists record and map the
location of all large predators seen. Other field data result from
the winter track counts and the recording of sightings of large
predators on field maps (Figure 2.3-16) by personnel working in the
field throughout the year. Locations of deer and livestock carcasses
are also being noted, as is possible evidence of predation or carrion
usage.

In conjunction with a literature review on specific information of
past records of abundance and distribution of large mammalian pre-
dators in this area, State of Colorado Division of Wildlife personnel
are being interviewed for records of damage claims to livestock, and
for hunting kill and trapping records of predaceous mammals in the
region. Government hunters from the Bureau of Sport Fisheries and
Wildlife who have been taking coyotes in western Colorado from
helicopters, are also being contacted for specific information on
large predators in the Piceance Basin.

Small Predators

Havahart live traps using baiting material deemed appropriate by a
review of. the literature are being routinely set during small mammal,
mammalian predator and winter track count sampling conducted in every
major habitat type in the study area. All traps are checked daily;
any animal captured is identified to species and released. Location
of captures, sightings by field personnel, scats, dens, and other
definitive signs are carefully plotted on field maps (Figure 2.3-16).
Compilation of all maps aids in determining the distribution of smal]
mammalian predators within and adjacent to Tract C-a.

Results

The mammalian predator scent-station survey was conducted during the
period June 22 through June 26, 1975. The siren-elicited howling
response method was employed as a coyote census technique concurrently -
with the predator scent-station method on two nights of suitable
weather conditions (June 22 and 25) during the 5-day sampling period.

2 e 3-285

®

2.3503.)

2.3.ted.2

2.3.5.3.3

2.3.5.4

The results of the predator scent-station technique and the corres-
ponding relative abundance indices for the summer sampling period
are summarized in Table 2.3-149, and the results of the siren-
elicited howling response technique are presented in Table 2.3-150.

Scent-Station Visitation Technique

The scent-station visitation technique is not designed as a census
technique, but may be applied as an index of relative abundance if
the sample size is large enough. Although the sample was increased

to two 50-station lines, this still doesn't constitute an adequate
sample size to be statistically compared with larger geographic

areas such as the state-wide index. The technique is presently the
subject of statistical study to determine its sensitivity in limited
areas and possible application as a census technique (Robert Roughton,
U.S. Fish and Wildlife Service, personal communication).

Results of these surveys on Tract C-a to date indicate that the coyote
and weasel (species uncertain) are the most abundant mammalian pre-
dators. They are the only predators that have responded to this
survey technique.

Response during June, 1975 was moderate for the two sampling lines.
A total of 12 coyotes and 12 weasels visited the scent stations during
June (Table 2.3-149).

Coyote Siren Census

June, 1975 was the first sampling period when all ten siren stations
were accessible. Snow-packed roads have prohibited complete sampling
during previous sampling periods. A total of twenty responding
groups a coyotes was recorded during the June, 1975 census (Table
2.3-150).

Small Predators

Havahart live-traps were set in the vicinity of the small mammal
live trapping grids during June and July, 1975. No captures were
recorded.

Summary and Conclusions

Records of tracks, scats and other definitive sign recorded by ECI

personnel on and near Tract C-a to date as well as the results of
the scent-station visitation census indicate that the coyote (Canis

latrans) and the weasel (Mustela sp.) are tne most abundant mammalian

predators in the area. Both the long-tailed weasel (Mustela frenata)
and the ermine (Mustela erminea) have been captured during live
trapping.

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0) Table 2.3- 150. Coyote siren census results and station and group response
indices calculated from data collected during 1975 for RBOSP

Number
of
Stations

20

V/

Number Number
of oT Station
Responding Responding Response, ,
Stations Groups Index —

Sample 3 (June 1975)
10 | far? | 50.00

“’station Response Index = Total number of stations with response

Total number of stations

2/ croup Sesnonee Dida = Total number of groups respondin

»

Total number of stations

2 e 3-288

Group
Response
Index =

100.00

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Other mammalian predators that have been documented by tracks and
direct observation on the site to date are the bobcat (Lynx rufus)
and the badger (Taxidea taxus), respectively. Havahart traps were
unsuccessful in recording the presence of small predators during
June and July sampling. Further terrestrial investigations should
yield additional species.

2 e 3-289

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2.3.6.3

Winter Track Counts

Introduction

No change has occurred since Progress Report 2. See section 3.8.1
in Progress Report 2 for the introduction to the winter track count
section.

Methods

No change has occurred since Progress Report 2. See section 3.8.2
in Progress Report 2 for specific methods used in winter track count
studies.

Results

Winter track count data were not gathered during the reporting quarter
June through August, 1975.

2.3-291

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