Source: CONNECTICUT AGRICULTURAL EXPERIMENT STATION submitted to NRP
TRACKING WHITE-TAILED DEER POPULATION SIZE, MOVEMENT AND HABITAT DAMAGE
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0186018
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
(N/A)
Project Start Date
Jul 15, 2000
Project End Date
Jul 14, 2004
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
CONNECTICUT AGRICULTURAL EXPERIMENT STATION
PO BOX 1106
NEW HAVEN,CT 06504
Performing Department
HORTICULTURE & FORESTRY
Non Technical Summary
White-tailed deer destroy crops and personal property, and carry ticks that can transmit disease pathogens. This study aims at tracking deer population size, movement and vegetation damage, information that can be used to reduce their negative impact around residential communities. The long-term goal of the project is to explore non-lethal methods of controlling deer populations in suburban habitats.
Animal Health Component
50%
Research Effort Categories
Basic
50%
Applied
50%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1240830107066%
2140830107034%
Goals / Objectives
The unavailability of accurate density estimates of white-tailed deer (Odocoileus virginianus) has been one of the major drawbacks in preparing management plans for the species. In regions where deer are harvested to maintain the population size, estimates of deer density are required to calculate the number of deer to be harvested and the length of the hunting season. The use of non-lethal techniques in controlling deer, such as the use of steroids, immunocontraceptives and contragestation agents, also require an estimate of deer density and demography to determine the proportion of individuals in the population to be treated to effectively control population growth. Thus, one of the objectives of this study is to compare the cost, effort and accuracy of different census techniques that can be applied to estimate white-tailed deer populations. Browsing by white-tailed deer in regions of high deer density has been implicated in the failure of forest regeneration and changes in vegetational species composition. Deer preferentially browse on seedlings, and in regions where harvest cutting occurs, can cause an inadequate stocking of tree species and a delay in stand establishment. The preferential feeding on favored species of plants by deer can also result in a change or decrease in plant species composition. However, unless deer damage is systematically measured, it would be difficult to separate the impact of deer browse on vegetation change from other factors such as rainfall, disease or insect damage, reduced seed supply or imperfectly drained soils. Thus, a second objective of this study is to quantify deer browse damage and its relationship to seasonal changes in food availability, population size and habitat utilization. A final objective of this study is to determine habitat use by free ranging deer in natural areas that are adjacent to residential communities. Apart from the damage caused to crops and personal property, white-tailed deer also carry ticks that can transmit disease pathogens such as agents of Lyme disease and human granulocytic ehrlichiosis. Knowledge of the habitat preferences of deer within their home-range, as well as seasonal changes in habitat use and distribution will provide managers with information that can be used to reduce the negative impacts of deer in and around residential communities. The long-term goal of the project is to explore non-lethal methods of controlling deer populations in suburban habitats. At the end of the first year of the study, one method of estimating deer densities will be selected for future monitoring. By tracking deer movement, information on the size of areas used by individuals as well as seasonal shifts in habitat use will be documented. These data will be used to select areas where population control measures will be most effective, as well as provide the most efficient choice of individuals to receive treatment. In conjunction with information on population size and demography, this research can provide the base-line data needed to begin a population control effort, which will be initiated by the end of the second year of the study.
Project Methods
The study site will be stratified into sampling units based on physical features such as vegetation type and proximity to residential communities. Approximately 6 randomly positioned transects will be set up at the different sampling units. The researcher will walk along the transect line and record the numbers, relative age and sex of deer seen. Other measurements that will be recorded are the sighting angle and sighting distance of the herd from the transect line, using a Laser Rangefinder. Using a GPS unit, the exact position of the herd will also be recorded over time. Each transect will be sampled once every month throughout the year. These data will be analyzed using the program DISTANCE. The habitat stratification and sampling units used in the infrared-triggered camera method of estimating deer density will be the same as those used in the line transect ground count. Six cameras will be set up twice every month within each sampling unit. Bait will be placed in front of each camera to lure deer to these locations. Using branch-antlered bucks to identify individuals, the population size will be estimated by using the Lincoln-Petersen Index for mark-recapture data. An aerial survey of the entire study site will also be conducted during the first winter of the study. Deer within a strip width of 100 m on each side will be counted, and the data recorded will be similar to that collected in the line transect method. To document deer browse damage, 12 10x10 m plots will be marked off. Six of the plots will be protected with fencing that excludes deer, 6 will be unprotected, allowing deer access to the plots. At the beginning of the study, the diameter at breast height and species of all trees will be identified to establish relative tree density and dominance within each plot. All saplings inside the plots will be identified and tagged. Within each plot, the number of twigs on each sapling between 0 and 1.25 m above the ground will be counted and scored as browsed or unbrowsed. Once every 4 months (November, March and July), the height of all tagged saplings within each plot will be measured, as well as total number of twigs and number of twigs that have been browsed on by deer. At the end of each year, the species as well as the number of new seedlings within each plot will be documented to quantify sapling recruitment. The sighting location of herds recorded during the ground transects will be geo-positioned and mapped. The location of identified individuals derived from the infrared-triggered cameras will also be mapped. Apart from the positional data provided by the cameras and ground surveys, approximately 3 trial animals will be fitted with GPS collars. The GPS units will provide automatic continuous location data as well as temperature and activity sensor data. The number of collared individuals will be increased the following year. All three methods of tracking deer movement will be used to document deer activity throughout the year.

Progress 07/15/00 to 07/14/04

Outputs
A total of 37 male deer were captured for sterilization. The sterilization technique was tested on tranquilized bucks, where a sclerosing agent was injected directly into each cauda epididymis, thus blocking the flow of sperm. Semen was collected from the animal before treatment. Previously treated animals were captured opportunistically throughout the study. Ten males were captured and sterilized in 2003 and 1 thus far in 2004, bringing the total number of sterilized males on the study site to 37. Eight previously sterilized males were recaptured throughout the study. Semen analyses of these individuals have shown that treated males remain sterile; however, sperm were present in low abundance in one animal sterilized 3 years previous. Field observations of treated bucks during the breeding season indicate they continue to engage in mating and mate-guarding behavior. Though treated animals remain sterile, a population decline as a result of treatment was not observed during the study. Possible reasons for a lack of response include: a large study area, increased immigration and emigration rates of males, and limited capture of breeding age males. This technique may have the most potential when used in concert with female reproductive control efforts or on a site insular in nature to reduce ingress and egress of male deer. Numerous repellent trials have been ongoing. A wireless deer fence that attracts deer with an odor and then delivers an electrical stimulation was effective at preventing damage in an orchard from 2000-2001, but lost its effectiveness afterward. A taste based repellent, DeerStopper, was tested by applying to a rope surrounding the plot, and reapplying every 2 weeks. Two treatment plots and 2 control plots were established in the orchard. Trees enclosed in the rope treatment went from 46% browsed stems to 7% in one month, while the control plots showed an increase from 47% to 67%. Because of the success of the trial, other researchers used the technique. It then became ineffective as deer became habituated. Surveys and informal interviews sent to members of the Connecticut Farm Bureau, Connecticut Nursery and Landscape Association, and fruit growers determined that fencing was near 100% effective. If fencing is not an option, it was found that if multiple types of repellents are used in a biweekly rotation, they remain potent and deer are less likely to become habituated to them. Approximately 125 animals have been captured and marked to date. Utilizing visual observations, radio telemetry, and GPS technology, movements of deer through suburban neighborhoods and adjacent woodlands were monitored. Deer generally utilized residents' backyards during evening and night hours and retreated to the cover of adjacent woodlands during daylight. Damage to shrubs, gardens, and landscape plantings most often occurred during night hours. Deer on the periphery of the study area tended to establish winter home ranges an average of 330 meters closer to residences than summer ranges as landscape and ornamental plantings provide a year-round food source.

Impacts
The need for non-lethal population control has grown over the past two decades as a decline in hunting and an increase in urbanization have combined to create a large white-tailed deer population. The long-term goal of the deer sterilization study is to provide a non-lethal technique to control population growth. If successful, this technique has applications to deer population control efforts in areas of high human and deer densities. Deer damage to cultivated crops and landscape plantings are substantial, and the studies that examine the effectiveness of different repellents will provide growers and homeowners more options to reduce deer damage. The long-term benefit of this research will be less deer damage to cultivated crops and landscape plantings.

Publications

  • Ramakrishnan, U. and S. C. Williams. 2003. Buck sterilization as a potential white-tailed deer population control technique. The 59th Annual Northeast Fish and Wildlife Conference. April 13-16. Newport, Rhode Island, USA.


Progress 01/01/03 to 12/31/03

Outputs
This progress report includes the following topics:(1)Fertility Control of White-tailed Deer;(2) Measuring changes in population size and birth rate; and (3) Evaluation of deer repellents. In 2001 sixteen male deer were captured for sterilization. The sterilization technique was tested on tranquilized bucks, where a sclerosing agent was injected directly into each cauda epididymis, thus blocking the flow of sperm. Semen was collected from the animal before treatment and a few days following treatment. Ten males have been captured and sterilized in 2002, bringing the total number of sterilized males on the study site to 26 males. Four males treated in 2001 were recaptured in 2002, and semen analyses of these treated individuals have shown that the treated males are still sterile. Field observations of treated bucks during the 2003-2004 breeding season indicate that the treated animals continue to engage in mating and mate-guarding behavior. Treated bucks will be captured every year to test for the presence of sperm. Males will continue to be captured until the end of the breeding season in late February. Untreated males will be captured to be treated, treated males will be recaptured to check for the longevity of the sterilization technique. To measure the success of the sterilization technique in reducing the population growth rate, the number of fawns born in 2002 was recorded using both direct sightings and infrared cameras placed at feeders. In 2000-2001, a wireless fence was evaluated for the protection of an apple orchard at Lockwood farm that had previously been heavily browsed by deer. The commercially available device, called the wireless deer fence, contained an odor-based deer attractant that administers a shock on contact. Twenty-one units were placed at 20 ft intervals along the periphery of the orchard. The repellent appeared effective for the first year, with a noticeable decrease in browse damage. However, it lost its effectiveness by the end of the first year, and deer damage became apparent. The wireless deer fence was removed in May 2002, and the effectiveness of another repellent, the DeerStopper, is currently being evaluating at the same apple orchard. The active ingredients in the repellent are mint oil, rosemary oil and salt. The orchard was divided into 2 control plots and 2 treatment plots, with 70 trees in the treatment plot and 80 trees in the control plot. In the treatment plots, the repellent mixture was sprayed onto a half inch thick nylon rope, and the rope was fixed to stakes that enclosed the plot. The height and number of browsed branches are recorded each month. Before treatment, 45.61 percent of the branches in the treatment plot and 46.67 percent of the branches in the control plot had been browsed. After 1 month of treatment, 7.29 percent of the branches in the treatment plot and 67.14 percent of the branches in the control plot had been browsed. Trees in the treated plots also recorded a 19.79 percent increase in overall height in 1 month compared to trees in the control plots that increased by 8.96 percent.

Impacts
The need for non-lethal population control has grown over the past two decades as a decline in hunting and an increase in urbanization have combined to create a large white-tailed deer population. The long-term goal of the deer sterilization study is to provide a non-lethal technique to control population growth. If successful, this technique has applications to deer population control efforts in areas of high human and deer densities. Deer damage to cultivated crops and landscape plantings are substantial, and the studies that examine the effectiveness of different repellents will provide growers and homeowners more options to reduce deer damage. The long-term benefit of this research will be less deer damage to cultivated crops and landscape plantings.

Publications

  • No publications reported this period


Progress 01/01/02 to 12/31/02

Outputs
This progress report includes the following topics:(1)Fertility Control of White-tailed Deer;(2)Measuring changes in population size and birth rate; and(3)Evaluation of deer repellents. In 2001 sixteen male deer were captured for sterilization. The sterilization technique was tested on tranquilized bucks, where a sclerosing agent was injected directly into each cauda epididymis, thus blocking the flow of sperm. Semen was collected from the animal before treatment and a few days following treatment. Ten males have been captured and sterilized in 2002, bringing the total number of sterilized males on the study site to 26 males. Four males treated in 2001 were recaptured in 2002, and semen analyses of these treated individuals have shown that the treated males are still sterile. Field observations of treated bucks during this year's breeding season indicate that the treated animals continue to engage in mating and mate-guarding behavior. Males will continue to be captured until the end of the breeding season in late February - untreated males will be captured to be treated, treated males will be recaptured to check for the longevity of the sterilization technique. To measure the success of the sterilization technique in reducing the population growth rate, the number of fawns born in 2002 was recorded using both direct sightings and infrared cameras placed at feeders. In 2000-2001, a wireless fence was evaluated for the protection of an apple orchard at Lockwood farm that had previously been heavily browsed by deer. The commercially available device, called the wireless deer fence, contained an odor-based deer attractant and administers a shock on contact. Twenty-one units were placed at 20 ft intervals along the periphery of the orchard. The repellent appeared effective for the first year, with a noticeable decrease in browse damage. However, it lost its effectiveness by the end of the first year, and deer damage became apparent. The wireless deer fence was removed in May 2002, and the effectiveness of another repellent, the Deer-Stopper, is currently being evaluating at the same apple orchard. The active ingredients in the repellent are mint oil, rosemary oil and salt. The orchard was divided into 2 control plots and 2 treatment plots, with 70 trees in the treatment plot and 80 trees in the control plot. In the treatment plots, the repellent mixture was sprayed onto a half inch thick nylon rope, and the rope was fixed to stakes that enclosed the plot. The height and number of browsed branches are recorded each month. Before treatment, 45.61 percent of the branches in the treatment plot and 46.67 percent of the branches in the control plot had been browsed. After 1 month of treatment, 7.29 percent of the branches in the treatment plot and 67.14 percent of the branches in the control plot had been browsed. Trees in the treated plots also recorded a 19.79 percent increase in overall height in 1 month compared to trees in the control plots that increased by 8.96 percent.

Impacts
The need for non-lethal population control has grown over the past two decades as a decline in hunting and an increase in urbanization have combined to create a large white-tailed deer population. The long-term goal of the deer sterilization study is to provide a non-lethal technique to control population growth. If successful, this technique has applications to deer population control efforts in areas of high human and deer densities. Deer damage to cultivated crops and landscape plantings are substantial, and the studies that examine the effectiveness of different repellents will provide growers and homeowners more options to reduce deer damage.

Publications

  • No publications reported this period


Progress 01/01/01 to 12/31/01

Outputs
This project includes the following topics: (1) Fertility Control of White-tailed Deer (2) Measurement of Deer Browse Damage; and (3) Effort, economics and accuracy of different methods of estimating deer population size in suburbia. Between September 2000 and December 2001, 70 male and female deer were captured and fitted with cattle tags for individual identification. Some of the animals were also fitted with radio or GPS collars to monitor age-structure and movement patterns of deer at the study site. The proportion of fawns born in 2000-2001 in relation to the proportion of adult females in the site was recorded at 1 fawn to 3.5 females. The proportion of fawns born in 2001-2002 is currently being monitored. Sterilization of males began in October 2001, using a technique to block the epididymus, thus preventing the flow of sperm and causing sterility. This technique has been used on domestic animals but has not been applied to deer. So far, 15 bucks (60% of planned total) have been sterilized. The number of fawns born in 2002 and 2003 will be compared with the proportion of fawns born the previous two years, to measure success of the sterilization technique. To measure browse damage, eighteen 10x10 m plots were set up throughout Lake Gaillard in April 2001. Nine of the plots are protected with fencing that excludes deer, 9 others are unprotected, allowing deer access to the plots. The diameter at breast height (dbh) and species of all trees (stems > 9 cm dbh) were identified to establish relative tree density and dominance within each plot. All saplings (stems > 1 cm and < 9 cm dbh) inside the plots were also identified and tagged. Within each plot, the number of twigs on each sapling between 0 and 1.25 m above the ground were counted. Four techniques for estimating deer population size are being compared at Lake Gaillard. The techniques being tested are - road count; mark-recapture technique; line-transect technique and aerial count. Data collection began on July 15th 2000. This included 12 walking transects, 6 vehicle transects and 10 baiting sites fitted with infrared-triggered motion-sensitive cameras for the mark-recapture technique. Data analysis comparing 3 techniques - the road counts, mark-recapture counts and line-transect counts, has revealed that the mark-recapture technique required substantial effort and expense to conduct. Vehicle counts had the advantage of requiring the least effort and cost, but were not accurate when conducted on moderate to heavily used roads. Of the three techniques, the walking transects appeared to be the most appropriate technique to estimate deer population size in a suburban community, because it provided the most accurate results at the lowest cost and least effort. The population estimates and age structure derived from the different techniques are also being used to design the fertility control program. The aerial count will be conducted in January 2002.

Impacts
Increased urbanization has amplified the need for non-lethal methods of controlling deer population growth. The sterilization technique being tested in this study is permanent, easy to perform, requires no surgical equipment, and has been used successfully on other species. By targeting large males with established territories, fewer numbers of individuals need to be treated, thus reducing the costs of a sterilization program.

Publications

  • No publications reported this period


Progress 01/01/00 to 12/31/00

Outputs
The project has three major objectives: (1) to compare the cost, effort and accuracy of three deer density estimation methods (2) to quantify seasonal browse damage by white-tailed deer in different habitat types; and (3) to record seasonal changes in habitat use and movement patterns of white-tailed deer. Data collection to estimate white-tailed deer densities at Lake Gaillard began on July 15th 2000. This includes 12 walking transects, 2 vehicle transects and 10 baiting sites fitted with infrared-triggered motion-sensitive cameras. The Connecticut Department of Environmental Protection issued a permit authorizing the baiting, darting, collaring and tagging of white-tailed deer at the study site, and since then, 36 deer have been captured and fitted with ear-tags for identification. In addition, 6 deer have been fitted with GPS-collars and 12 deer have been fitted with radio-collars. The movement of collared deer are being monitored.

Impacts
The study comparing deer density estimation methods will provide managers with effective alternatives to calculate suburban deer population size. Knowledge of the habitat preferences of deer within their home-range, as well as seasonal changes in habitat use and distribution will provide managers with information that can be used to reduce the negative impacts of deer in and around residential communities.

Publications

  • No publications reported this period