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Overview
For the last thirty years, there has been minimal research conducted on the
herpetological
communities in the Las Vegas Wash (Wash). For this reason, the Las Vegas Wash Project
Coordination Team (Wash Team) conducted a
reptile
monitoring program from May of 2001 to September 2003. The goals for the program
were to determine the presence or absence of reptiles near the Wash and to gather
general information on their distribution within the Wetlands Park.
Survey Location
| Survey Methods

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Survey
Location
Reptile array sites were located on the north side of the of
the Wash channel within the Clark County Wetlands Park (Wetlands
Park) boundary. When the study was initiated, a total of six
site locations were chosen according to habitat suitability in
the Wetlands Park, avoiding archeological sites and planned Wash
improvement areas. Sampling locations were further selected based
on road accessibility. Habitat adjacent to each of the reptile
array sites was moderately disturbed due to off-highway vehicle
(OHV) traffic. Four site locations were added in the third year
of the study, including two locations in revegetation sites and
two in tamarisk dominated areas.

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A basic habitat description for the array sites is described below.
Array
Site 1
Dominated primarily by creosote (Larrea tridentata) and white
bursage (Ambrosia dumosa), associated Mojave Desert scrub species
included on this site are ratany (Krameria erecta), desert senna
(Senna armata), ephedra (Ephedra sp.), and big galleta (Pleuraphis
[Hilaria] rigida). The slopes are generally low, vegetation
is sparsely clumped and the substrate is silty sand with pebbles
and gravels. This array is the most distant site from the Wash
and is surrounded by OHV roads.

Array Site 1
Array
Site 2
Dominated by fourwing saltbush (Atriplex canescens) with infringement
from honey mesquite (Prosopis glandulosa), shadscale (Atriplex
confertifolia), and non-native tamarisk (Tamarix spp.), this
site is characterized by steep hills with variable slopes and
is within 300 feet of the Wash. OHV roads are in the vicinity
of the site.
Array
Site 3
Located within a silty sand flat wash that receives periodic
flooding indicated by the mudcracks near the site, this array
is also dominated by fourwing saltbush, with creosote, white
bursage and tamarisk also associated components of this habitat.
Telephone Line Road/Hollywood bisects Array Site 4 on the south
and Array Site 3 on the north.

Array
Site 3
Array
Site 4
This site is dominated by dense thickets of fourwing saltbush
with interspersed catclaw (Acacia greggii) and tamarisk.
Array
Site 5
Dominated by non-native Russian thistle (Salsola tragus) and
fourwing saltbush, the soils are predominately fine grained
sandy silts and there is a large percentage of downed debris
near the site. OHV roads are readily apparent next to this site.
Array
Site 6
Robust tamarisk trees and large quailbush (Atriplex lentiformis)
bushes dominate this site. The south side of this site is in
a riparian buffer adjacent to the Wash that is perched 50 feet
above the Wash channel.
Array Site 7
This site is located within an area that was cleared of non-native tamarisk and revegetated with native riparian and desert wash taxa, including cottonwood (Populus fremontii), Goodding willow (Salix gooddingii), sandbar willow (S. exigua), as well as honey and screwbean mesquite (S. pubescens), desert willow (Chilopsis linearis) and quailbush. The site was planted in February 2002.
Array Site 8
This site is dominated by mature tamarisk with some large quailbush.
Array Site 9
This site is located within a revegetation site that was planted with similar vegetation to Array Site 7. The site was planted in November 2001.
Array Site 10
Mature tamarisk trees dominate this site, creating a thick canopy overhead.
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Survey
Methods
Since the reptile trapping season in the Wash is best from early
spring to early fall, Wash Team biologists commenced surveys in
the early spring. Traps were opened for three nights at a time
every other week of the trapping season. The traps were opened
on a Tuesday evening and checked for reptiles on Wednesday,
Thursday, and Friday mornings.

Drift Fence Array
There
are many types of methodologies that biologists can use to capture
reptiles. A popular technique that is used in southern Nevada,
and the technique that Wash Team biologists are using, is the
drift fence array. This methodology incorporates two different
types of traps (the pitfall trap and the funnel trap) with each
trap targeting different reptiles. The concept behind the drift
fence array is that a reptile moving randomly in its habitat may
move in the direction of a drift fence array and it will be obstructed
by the fine mesh fabric of the fence and will "drift"
towards one of the pitfall or funnel traps. There are three components
of a drift fence array, the drift fence, the pitfall trap, and
the funnel trap.
The Drift Fence
The first component of the drift fence array is the drift fence.
The drift fences are made of a fine mesh fabric 1.5 feet in height
by 50 feet long. A total of three drift fences are installed in
a "Y" like configuration per array. The drift fences
are fastened to wooden stakes for stability and structure and
approximately 0.5 feet (of the 1.5-foot side) of the drift fence
is buried underground.

Drift Fences
The Pitfall Trap
At the center of the drift fence array and at the middle and end
of each drift fence is a pitfall trap (a total of 7 per drift
fence array). The pitfall traps bisect the drift fences at the
middle point so that a reptile may be captured if it comes into
the drift array from any angle.

The Pitfall Trap
The
pitfall trap is a 6-gallon bucket that is buried in the ground
so that the lip of the bucket is flush with the ground surface.
It is important to have a bucket deep enough to detain a reptile
that may otherwise be able to get out. The bucket lid of the pitfall
trap is modified with three wooden feet attached to its top. When
pitfall traps are "opened," the modified lid is inverted
over the bucket and secured with bungee chords from within the
bucket. This configuration creates shade in the pitfall trap.

Secure Pitfall Trap
When
pitfall traps are "closed," the lid is securely fastened
to the bucket to prohibit a reptile capture. This type of trap
is usually more effective for capturing lizards than snakes. Small
lengths of PVC piping are placed in the pitfall traps to create
cover for reptiles that are detained.
The Funnel Trap
There is only one funnel trap for each drift fence arm (a total
of 3 per drift fence array). Each funnel trap is located three-quarters
of the distance from the drift fence center and only on one side
of the drift fence.

Modified Funnel Trap Lid
The
funnel trap consists of a modified lid and a 6-gallon bucket that
is buried in the ground so that the lip of the bucket is flush
with the ground surface. A mesh wire cloth cylinder with funnels
on either side is attached to the lid. Within the cylinder, there
is PVC piping in the shape of a "T." One end of the
"T" shaped PVC piping protrudes through the bucket lid.
When the lid is securely fastened to the bucket, the PVC piping
acts as a funnel into the bucket.
The
funnel trap is completed by angling a piece of plywood over the
funnel trap lid when it is secured to the bucket. This creates
shade in the event that the captured reptiles stay within the
cylinder and do not funnel into the bucket. Small lengths of PVC
piping are also placed in the funnel traps to create cover for
reptiles that are detained. When the funnel traps are "closed,"
an unmodified lid secures the opening of the funnel trap.

Funnel Trap Configuration
Because
reptiles can not produce internal body heat (ectothermy) they
are subject to external heat sources to maintain their body temperature.
Creating shade over the pitfall and funnel traps increases the
survival rates of captured reptiles because it reduces their exposure
to the sun. Wash Team biologists also check traps in the early
morning to reduce the amount of time a reptile may be subject
to the intense heat of the sun.
When
a reptile is found in a pitfall or funnel trap, it is weighed
and measured for length; examined for age, sex, and the presence
of parasites; and marked by toe clipping (lizards only). Wash
Team biologists use the toe clipping methodology, which utilizes
a systematic numbering system to uniquely identify each lizard,
in order to estimate the relative abundance of lizard populations
near the Wash.
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| Toe
Clipping Numbering System |
Toe
Clipping a Desert Horned Lizard |
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