A. PROPOSAL: U.S. Crotalids to be in
CITES II
Inclusion of the species Crotalus adamanteus in
CITES Appendix II.
B. PROPONENT
The United States of America
C. SUPPORTING STATEMENT
1.TAXONOMY
Class: Reptilia
Order: Lepidosauria
Suborder: Squamata
Family: Viperidae
Genus and species: Crotalus adamanteus
Scientific synonyms: none
Common name: Eastern diamondback rattlesnake
2. BIOLOGICAL PARAMETERS
2.1 Distribution and Habitat:
Crotalus adamanteus is the most
venomous snake in North America (Behler and King 1985)
and the largest rattlesnake in the world (Gopher
Tortoise Council 1995). The species ranges along the
coastal lowlands of southeast North Carolina to extreme
eastern Louisiana, including all of Florida and its keys
(Behler and King 1985) (Means 1986). C. adamanteus is
extremely rare in Louisiana and most likely functionally
extinct; specimens show up irregularly but in different
localities (LaClaire and Vendeventer 1995).
Martin and Means (1995) report that presettlement
habitat distribution of Crotalus adamanteus was
primarily open-canopied, pyro-climax, pine dominated
communities, including longleaf pine/wiregrass sandhills
and clayhills, flatwoods, and sand pine scrub. The
species was also common in coastal strand and palmetto
prairie and utilized temperate hardwood forest and
tropical hardwood hammocks, especially where these were
adjacent to pine-dominated habitats. Today C. adamanteus
occurs in the few remnants of the original habitats that
remain plus various ruderal situations such as berms
along canals, citrus groves, and old-field successional
habitats.
C. adamanteus typically spends the coldest months of the
year (November through March) in subterranean shelters,
frequently emerging during warm spells (Means 1986)
(Bennett 1995). Shelters from cold are used everywhere
except extreme southern Florida and the Florida Keys
(Martin and Means 1995).
In the southern portion of its range, the species is
sympatric with the gopher tortoise (Gopherus
polyphemus). The extensive burrows are used by C.
adamanteus for winter refuge sites (Conant 1975). In the
northern portion of their range, stump holes are the
preferred refuge site.
Crotalus adamanteus have large home ranges that may
encompass as much as 500 acres. Males maintain larger
home ranges that females. Home ranges of males and
females in both study groups overlapped indicating that
this species does not defend a specific territory
(Timmerman, 1995).
This species is generally believed to exhibit diurnal or
crepuscular activity patterns (Timmerman 1989). However
nocturnal activity has been noted in the species.
Timmerman (1989) characterizes C. adamanteus as
holotemporal, a term introduced by Bruce Means. This
term indicates that the eastern diamondback, as shown by
Timmerman, is in readiness to capture prey at all times
(Bennett 1995).
In the field, C. adamanteus is estimated to live an
average of ten years or more (Means, 1985). There is one
record of an individuals surviving for over twenty-two
years in captivity (Bennett 1995). The species has few
enemies as an adult. Only deer, pigs and humans are
known to kill an adult (Ernst 1992).
2.2 Habitat Availability:
C. adamanteus is a flagship species in the
endangered longleaf pine ecosystem. The loss of longleaf
pine habitat has been documented throughout the
Southeast (Noss 1989). Conversion of longleaf habitat to
intensively managed loblolly plantations, development,
both residential and commercial, and agriculture have
resulted in lost habitat for the species. In addition
alteration of existing longleaf habitat, in particular
removal of stumps, has likely contributed to the
species' decline (Bennett, 1995).
Several species of amphibian, reptile and bird
intimately associated with longleaf habitats are
currently listed or being considered for listing as
threatened or endangered: flatwoods salamander
(Ambystoma cingulatum), gopher frog (Rana captio), pine
snake, southern hognose snake (Heterodon simus) , gopher
tortoise, Bachman's sparrow (Aimophila aestivalis) and
the red-cockaded woodpecker (Picoides borealis). The
decline of most if not all of theses species is directly
related to the loss and alteration of longleaf pine
habitat in the Southeast. C. adamanteus, while likely to
be suffering declines equal to many of the
above-mentioned species, has until recently been
overlooked in conservation efforts. This is doubtless
due to the sociological problems inherent in any
conservation effort directed at a venomous species that
threatens human life. (Bennett)
Concurrent with the decline of C. adamanteus has been
the decline of the gopher tortoise (Gopherus
polyphemus), for which the species is sympatric with in
the southern portion of its range. Because of the
decline in numbers, the gopher tortoise is listed as
federally threatened in Louisiana, Mississippi, and
Alabama west of the Mobile and Tombigbee rivers. Its
decline has resulted from the same habitat degradation
that has contributed to declines in C. adamanteus
(LaClaire 1995).
The availability of subterranean shelters from fire and
cold such as burrows of the gopher tortoise and
armadillo, rotting and burned out bases of trees, tip up
mounds and rotting logs may be very important in local
abundance (Martin and Means 1995). The removal of
stumps, which are used as refugia has seriously affected
populations in many areas (Martin and Means 1995).
In addition, fire exclusion during the last century has
degraded much habitat by allowing the development of
closed -canopied forest with a dense shrub layer that
shades the ground in many areas. Pine plantations can
provide suitable habitat but if the trees are planted
closed together as is the usual case, then the ground is
eventually shaded and the habitat is not suitable
(Martin and Means 1995).
2.3 Reproductive Biology:
Bennett (1995) references a 7-year study in
Northern Florida which indicates that most courtship and
mating takes place in August and September, and that
females give birth at this same time to 8-29 young
(average 14) every two and sometimes three years.
Sexual maturity takes at least two years (Bennett 1995),
sometimes three (Martin, 1995), to attain. Series from
more northerly parts of the range (Georgia, South
Carolina and Mississippi) suggest that maturity is
usually delayed about one year (Martin 1995).
Females generally give birth to live young during the
fall every 2-3 years; brood size ranges from six to
twenty-one (Bennett 1995). Juveniles are preyed upon by
pigs, carnivorous mammals, raptors, wood storks, and
other snakes, primarily kingsnakes (Ernst 1992).
Following the breeding season, feeding activity
resumes and individuals return to previously used
overwintering sites (Timmerman, 1989).
2.4 Population Status and Trends:
Crotalus adamanteus is believed to be
substantially declining rangewide (Means 1989) (Bennett
1995) over the past four decades (Martin 1995); this
decline continues unabated (Mount 1995). Anecdotal
evidence exists to support this conclusion in the form
of observations by numerous professional and amateur
herpetologists. The species is listed as a Species of
Concern in South Carolina (Bennett 1995) and is
identified as a Species of Special Concern in Alabama
(Means 1986).
In Florida, C. adamanteus is identified as a Candidate
Species of Special Concern (Enge 1993). Florida's
Nongame Wildlife Program developed a system to rank wild
vertebrate taxa according to biological vulnerability,
extent of current knowledge of population status, and
management needs. A biological score was generated for
each taxon to reflect different facets of distribution,
abundance and life history. C. adamanteus was given a
high biological score and matched the median score for
those species already listed by the state as a Species
of Special Concern. Enge (1993) states that a comparison
of biological scores with trade data suggests that C.
adamanteus, "...is the most likely candidate for some
sort of protection from human harvest. It is somewhat
vulnerable to extirpation and is heavily harvested..."
2.5 Geographic Trends: (unknown)
2.6 Role of the Species in its Ecosystem:
Crotalus adamanteus is a carnivore that preys
primarily on rabbits and cotton rats. Other prey items
include other rat and mouse species, squirrels, and
several species of birds (Ernst 1992). Anecdotal
evidence suggests that this species, along with other
large stumphole dwelling snakes found in longleaf pine
habitat, comprise an effective and important rodent
population control system. Changes in the local
population levels of C. adamanteus may result in changes
in local rodent populations. Higher than normal rodent
populations can have deleterious effects on such species
as quail and other ground nesting birds through nest
predation by rodents and direct competition for food
(Bennett 1995).
2.7 Threats:
Habitat loss and alteration, collection for
commercial use and indiscriminate killing are the three
major factors believed to be responsible for a dramatic
decline in Crotalus adamanteus (Bennett 1995). Habitat
destruction affects the species throughout its range.
The commercial trade involves excessively high numbers
of C. adamanteus; from 1990 to 1994, Florida hide
dealers reported purchasing a total of 42,788
individuals (Enge 1995).
The fall breeding season of C. adamanteus, when they
exhibit maximal surface activity, coincides with some
game hunting seasons, increasing the likelihood of
encounters between humans and rattlesnakes. This is
supported by trade data; most purchases of the species
by Florida dealers takes place from August through
October (Enge 1995).
Methods of collection further threaten the species.
Though illegal in Georgia and Florida and vehemently
denied by snake hunters, the collection method of choice
used extensively to this day is via spraying or pouring
gasoline into borrows (Jones 1995) (Enge 1993). This is
of detriment, not only to C. adamanteus but to a large
community of other species of animals that utilize
burrows (Speake and Mount 1994) (Means 1986). Snake
hunters have stated that burrows that have been gassed
can remiain unoccupied by any animals for up to two
years (Jones, L. 1995).
Enge (1993) also reports an apparent decline in the
average size of C. adamanteus collected by reptile
dealers in Florida. Such a decline should produce a
concomitant reduction in the mean number of young per
adult female. Heavily-harvested populations of C.
adamanteus probably have their age rations skewed to
younger, and therefore smaller and less productive
animals (Enge 1993).
Indiscriminate killing also takes a toll on wild
populations. Rattlesnakes are maliciously killed by most
people whenever they are confronted. Of animals rated in
a nationwide survey, only the cockroach, mosquito, wasp
and rat were disliked more than the rattlesnake (Enge
1993). Illustrating the political nature of conserving
venomous snakes, a publication listing C. adamanteus as
a Species of Special Concern (Means 1986) in Alabama
closes with, "...it is unrealistic to assume that
rattlesnakes can enjoy a generally favorable reputation,
much less legal protection, in Alabama for many years to
come...." Likewise, attempts to list C. adamanteus as a
protected species by the Georgia Department of Natural
Resources were unsuccessful (Enge 1993) primarily
because of the species lack of popularity. Obviously,
public education will play a critical role in the future
conservation of this species.
3. UTILIZATION AND TRADE
3.1 National Utilization:
Crotalus adamanteus are captured for utilization
in "rattlesnake roundups", the live pet trade, skin
trade, meat trade and for sale as "novelties" (stuffed
and mounted snakes, jewelry, key chains, etc...)
Georgia and Alabama still have rattlesnake roundups
which utilize large numbers of the species. Four major
roundups are annually held in the Southeast, along with
a number of smaller events. Each of these four major
roundups utilize an average of approximately 300
wild-caught Crotalus adamanteus. At one event in Georgia
in 1994 an estimated 700 C. adamanteus were used (Jones,
L. 1995).
Florida, alone, collects information pertaining to the
sale and trade of reptiles in the states. This allows us
to view a sample of harvests of this species. Enge
(1993) reports that from 1990 through 1992, a total of
428 live C. adamanteus were taken from the wild and sold
in Florida for the pet trade. These numbers are
underestimates of actual numbers of herptiles taken from
the wild because the data does not include reptiles
collected for personal use, those that die or are sold
outside the state. From 1990 to 1994, Florida hide
dealers reported purchasing a total of 42,788 C.
adamanteus from Georgia (78%), Alabama (16%) and Florida
(6%) (Enge 1995).
3.2 Legal International Trade:
The following U.S. export data was taken from
the U.S. Fish and Wildlife Service, Division of Law
Enforcement, Law Enforcement Management Information
System (LEMIS) and Declaration for Importation or
Exportation of Fish or Wildlife Forms (SF-171):
live individual boots
meat(lbs)
1992 32 45
26.7
1993 57 06
119.8
1994 38 187
2419.7
novelties* leather pieces
1992 4,449 1510
1993 330 1475
1994 964 0
*novelties include stuffed and mounted snakes,
jewelry, key chains, hat bands, etc...
3.3 Illegal Trade: (unknown)
3.4 Actual or Potential Trade Impacts: (see
Threats)
3.5 Captive Breeding or Artificial Propagation
for Commercial Purposes Outside Country of Origin:
unknown
4. CONSERVATION AND MANAGEMENT
Collection, sale and purchase of Crotalus
adamanteus is unrestricted in South Carolina (Bennett
1995), Alabama (Levell 1995), Louisiana (Boundy 1996),
Georgia (Beacham 1996) and Florida (Enge 1993). The
species is listed as a Species of Concern in South
Carolina (Bennett 1995) and is identified as a Species
of Special Concern in Alabama (Means 1986). Such status
affords no legal protection in either state. Florida
merely requires a permit for selling reptiles and
record-keeping detailing purchases and sales (Enge
1993). North Carolina effectively prohibits commercial
harvests and sales of C. adamanteus (Wilson 1996).
Similarly, in Mississippi, state regulations require a
permit to collect reptiles and limits to four the number
of individual animals that may be taken per year;
reptiles taken from the wild, or their parts, cannot be
bought, sold, offered for sale, bartered, or exported
for sale (Jones, R. 1996).
4.2 Species Management:
4.2.1. Population Monitoring:
The Wildlife Diversity Section of the South
Carolina Department of Natural Resources has initiated a
study of C. adamanteus demography and ecology in the
state (Bennett 1995). No other states have initiated
population monitoring projects.
4.2.2. Habitat Conservation: (unknown)
4.2.3 Management Measures: No states which
permit commercial harvest, purchase and sale of the
species is known to implement any measures to limit or
manage exploitation.
4.3 Control Measures:
4.3.1 International Trade: (none)
4.3.2 Domestic Measures: (see 4.1.1 National Legal
Status)
5. INFORMATION ON SIMILAR SPECIES
It can be very difficult or impossible to
distinguish skin, parts (e.g.: rattles, skulls, heads),
or products of Crotalus adamenteus from that of Crotalus
atrox (Western diamondback rattlesnake), a species which
is subject to high levels of both national and
international trade. Identification is dependant on the
amount of skin present, the location on the animal that
the skin or part is from, and whether or not the product
has been artificially colored.
REFERENCES
Beacham, M. 1996. Georgia Department
of Natural Resources, letter to Ann Michels,
Environmental Investigation Agency of April 2, 1996.
Behler, J. L. and King, F. W. 1985. The Audubon Society
Field Guide to North American Reptiles and Amphibians.
Alfred A. Knopf, Inc. New York, New York.
Bennett, S. H. 1995. Ecology and Status of the Eastern
Diamondback Rattlesnake (Crotalus adamanteus) in South
Carolina. South Carolina Department of Natural
Resources. Columbia, South Carolina.
Boundy, J. 1996. Louisiana Department of Wildlife and
Fisheries, letter to Ann Michels, Environmental
Investigation Agency of March 26, 1996.
Conant, R. 1975. A Field Guide to Reptiles and
Amphibians of eastern and Central North America.
Houghton Miflin Company, Boston, Massachusetts.
Enge, K. 1993. Herptile Use and Trade in Florida.
Florida Game and Fresh Water Fish Commission. Quincy,
Florida.
Enge, K. 1995. Commercial Trade in Southeastern
Rattlesnakes (abstract). 38th Annual Meeting, Society
for the Study of Amphibians and Reptiles. Appalachian
State University. Boone, North Carolina. August 8-13,
1995.
Ernst, C. H. 1992. Venomous Reptiles of North America.
Smithsonian Institution Press. Washington and London.
Gopher Tortoise Council. 1995. Eastern Diamondback
Rattlesnake: A Species in Decline (brochure).
Gainesville, Florida.
Jones. L. 1995. The Embattled Eastern Diamondback
Rattlesnake. Reptiles Magazine; August 1995.
Jones, R. L. 1996. Mississippi Department of Wildlife,
Fisheries and Parks, letter to Ann Michels,
Environmental Investigation Agency of March 13, 1996.
LaClaire, L. V. and Vandeventer, T. L. 1995. Status and
Conservation of the Eastern Diamondback Rattlesnake
(Crotalus adamanteus) in Louisiana and Mississippi.
Levell. 1995. Field Guide to Reptiles and the Law.
Martin, W. H. 1995. Growth, Longevity and Maximum Size
of the Eastern Diamondback Rattlesnake (Crotalus
adamanteus).
Martin, W. H. and Means, D. B. 1995. Distribution of the
Eastern Diamondback Rattlesnake (Crotalus adamanteus).
Means, D.B. 1985. Radio-tracking the Eastern Diamondback
Rattlesnake. Natl. Geogr. Soc. Res. Rep. 18:529-536.
Means, D.B. 1986. Special Concern: Eastern Diamondback
Rattlesnake in Vertebrate Animals of Alabama in Need of
Special Attention. Alabama Agricultural Experiment
Station. Auburn University, Alabama.
Mount, R.H. 1995. Eastern Diamondback Rattlesnake,
Status and Conservation Strategies -Alabama, Florida and
Georgia (abstract). 38th Annual Meeting, Society for the
Study of Amphibians and Reptiles. Appalachian State
University. Boone, North Carolina. August 8-13, 1995.
Timmerman, W. W. 1989. Home range, Habitat Use and
Behavior of the Eastern Diamondback Rattlesnake.
University of Florida. Gainesville, Florida.
Wilson, R.C. 1996. Norht Carolina Wildlife Resources
Commission, letter to Ann Michels, Environmental
Investigation Agency of March 28, 1996. |