Noninvasive Techniques to Assess Health and Ecology of Wildlife Populations

Chapter 9 Noninvasive Techniques to Assess Health and Ecology of Wildlife Populations



The use and varied applications of molecular technologies has rapidly expanded over the past 20 years, transforming how veterinarians and researchers diagnose, treat, learn about, manage, and conserve wildlife, including elusive and less well-known species. Medically, the word noninvasive has been used to describe diagnostic procedures that do not involve penetrating the skin or organism with an incision or an injection. In this chapter, noninvasive techniques are defined to include the collection of samples without the need for immobilization (e.g., skin samples collected by remotely fired biopsy darts).


There are many advantages to noninvasive assessments using samples such as hair, feathers, feces, urine, saliva, regurgitated material, sloughed skin, or even museum specimens. Analyzing urine or feces to evaluate endocrine function without animal capture, restraint, and/or anesthesia minimizes stress and provides a broader measure of endocrine status over a period of hours to days when compared with point in time measures obtained from blood samples. Data collected from fecal hormone and genetic analyses and then overlaid by sample location data may provide information about home ranges, animal movements, stress levels, and habitat use,24 as well as gender and gender ratios. Hair may be analyzed to yield much information about the following: occurrence, distribution, and relative abundance of populations; aspects of population genetics, niche, or diet; detection of rare species; and identification of individuals for wildlife management and forensic purposes.18 Skin samples may be used to create stress response profiles, which may serve as early indicators of health risks.2


Given the growing number of analytic tests that may be performed with single samples, it may be tempting to include a broad range of parameters in analyses and then derive meaning from the results. However, it is the research question and experimental design, not the analytic tools used, that will produce meaningful results. Why, what type of, and how data should be collected are key questions that need to be addressed when designing a study. Molecular tools may then be applied thoughtfully to answer important questions.


This chapter describes collection methods as well as DNA- and non–DNA-based analytic procedures used to study the reproductive status, nutritional state, genetic characteristics, and general health of free-ranging wildlife. Methods to collect and store samples are covered separately because single samples may often be used in several analytic techniques, and field and laboratory research activities are often conducted by different individuals. This brief overview provides the reader with enough basic information to understand and apply noninvasive analytic tools currently available for wildlife field research.



Sample Collection and Storage Methods


The tradeoffs and benefits of working with different samples and analytic techniques must be weighed against research objectives and priorities. Frequently, a variety of samples and analytic approaches may be combined to answer research questions in greater depth or provide a broader understanding of wildlife population health (Table 9-1). Through the collection of hair or fecal samples, large remote areas may be surveyed, several population metrics may be calculated, and collection costs are minimal. In some cases, collections must be made noninvasively to avoid sampling bias. The types of samples and collection methods used will vary depending on the species, study objectives, and environmental conditions. For example, hair is collected relatively easily and may be stored for long periods of time but contains smaller amounts of DNA compared with fecal samples. On the other hand, chemical inhibitors present in feces may restrict the amplification of DNA.18




Hair


Determining the occurrence and distribution of populations is a common goal of hair collection studies, and hair may be used to answer questions about population genetics and structure when DNA quality is high. However, estimating population size or abundance via hair collection surveys is not as effective because it depends on reliable individual identification based on nuclear DNA analysis, and collection methods may not be efficient enough to provide a sufficient capture-recapture sample size. Population trends may be estimated by repeatedly monitoring occupancy if detection probability may be determined, and these data may guide wildlife management decisions (e.g., documenting wildlife use of highway crossing structures). Evaluating relationships of species with habitat and human variables using grid-based sampling, combined with identification of individuals through genotyping, is possible,1 and hair samples may be analyzed in nutritional studies as well.


The best source of DNA is follicles, which are more frequently present on plucked as compared with shed hair,10 although hair shafts may provide useful DNA contributed by saliva, dander, or other adherent tissue.26 Hair should be collected within 3 to 4 weeks of deposit for the best genotyping results because ultraviolet light and moisture degrade DNA over time. Hair may be collected opportunistically or with sampling devices, which may be passive or baited. Passive devices collect hair during normal behavior and include hair-snagging devices mounted on natural rub objects (e.g., on trees for bears) or along travel routes (e.g., barbed wire strands for badgers). Baited sampling devices include food or scent lures to attract animals to collection sites. Catch structures should be designed to minimize collection of hair from multiple individuals or species, and variables such as animal behavior, movement, concentrations, and collection intervals should contribute to design strategies. Hair should be stored dried in small paper envelopes or vials with silica gel desiccant until it is analyzed.



Feces


A single fecal sample may provide information about reproductive status, genetic makeup, stress, viruses, internal parasites, predation, and diet. Noninvasive capture-recapture survey techniques may be adapted to estimate population size by supplementing detection data with genetic analyses of hair or scat samples, indigestible plastic chips recovered in scat, or cameras to identify individuals.20 Capture-recapture methods through scat collection may be successful if the target population is not of extremely low density, sampling methods have a high rate of detection and low level of sampling bias, population size does not change between collection periods, and accurate identification of individuals is possible.14 Collection of fecal samples may be greatly facilitated by the use of dogs that have been trained specifically to search for wildlife scats.24 Dogs may even be trained to distinguish individual animals by their scat. However, detection rates may vary among dog-handler teams, making proper training and a study design that allows for estimation and correction of detectability highly important. Thorough mixing of a fecal sample prior to collecting a subsample will help ensure reliable results because corticosteroids and their metabolites may be unevenly distributed in feces.15


There are several ways that fecal samples may be stored, depending on the analyses to be performed. For endocrine assessment, sodium azide or other preservatives such as ethanol may be mixed with feces to prevent bacterial growth because bacteria and their enzymes will degrade steroid metabolites in a few hours. Alternatively, fecal samples may be stored frozen at –20° C for preferably no longer than 90 to 120 days prior to extraction and analysis.13 A field-based extraction and storage technique using C18 cartridges (Varian, Walnut Creek, Calif) makes it possible to store samples at ambient temperatures for up to 2 weeks before freezing or analysis.3


Fecal samples collected for genetic studies can be stored using various techniques, such as drying and storing in 70% to 100% ethyl alcohol or in a desiccant, freezing at –20° C, or saturation and storage in a buffer solution. Hydrolysis, oxidation, UV radiation, alkylation, and structural damage from freeze-thaw cycles are the primary activities that may damage DNA; storage techniques are aimed to minimize these effects. Efficacy of storage techniques vary widely from one study to the next, depending on different species and their diets, environmental conditions, and protocols used in the field and laboratory. Conducting pilot studies to test storage and extraction methods, and performing extractions shortly after collection, will help minimize the deterioration of DNA in fecal samples.


For nutritional studies, fecal samples should ideally be collected within 24 hours of defecation, and indicators may include degree of wetness and lack of insect damage. Dietary components may be determined by gross physical examination of fecal samples as well as laboratory analysis to determine diet preferences of various species, assess nutrient content, and monitor forage quality. Molecular tools have forensic applications as well—for example, in areas in which predation on livestock is suspected.8 For carnivore species, scats may be air-dried on sterile paper, prey remains examined grossly for rough identification and subsequent DNA analysis, and bile powder separated to identify predator species. Dried samples should be stored in Ziploc bags in a dark, dry location until DNA extraction. Fecal samples from herbivores should be dried at 80° C for 48 hours, ground into a fine powder, and then stored frozen until time of analysis.


Routine collection and storage of fecal samples for health diagnostics will vary, depending on the tests to be performed. Gastrointestinal parasites and viral or bacterial infections may be detected using various diagnostic tools, including fecal flotation and sedimentation tests, cultures, and genetic techniques.



Urine


Urine samples, like fecal samples, may be used for endocrine evaluations and genetic analyses.12 Urinary DNA is easier to extract and analyze than fecal DNA; however, potential gender-specific differences in urination behavior may affect estimation of population size and gender ratios. Urine samples may be collected from captive wildlife housed in exhibits with concrete flooring and may also be extracted from natural substrates such as snow or sand.16 Simple collection devices may also be devised (e.g., containers mounted on the end of sticks to catch urine from arboreal primates). Although collection of urine samples in the field may occasionally be challenging compared with fecal samples, urine requires no further processing before being assayed in the laboratory and may be preserved by absorption onto filter paper, mixing with 10% ethanol for storage at room temperature for up to 12 weeks, or freezing indefinitely.18





Supplementary Observational Techniques


Behavioral observations, track surveys, images from remote cameras, and movements monitored via radio or satellite telemetry units may augment data acquired from field samples and help validate assays. Surveys of tracks in mud or dust may assess the presence and distribution of animals in remote or relatively inaccessible areas (e.g., aerial track survey), but determination of relative abundance requires identification of individual animals. Natural sign surveys have been documented for numerous animals and may be affected by adjacent habitat characteristics and environmental conditions. Population size may be estimated when the probability of scat detection is known; this depends on an understanding of the rates of scat decomposition and defecation,14 especially when search areas cannot be cleared of scat (as by a snowstorm) prior to surveying.


Various cameras, motion sensors, and triggers may be used to collect information about different species noninvasively, even those that are very shy. Use of camera traps requires knowledge of an animal’s natural history and the technical function of remote cameras. Cameras triggered by pressure pads may exclude smaller bodied, nontarget species and may only operate within precise triggering distances. Active infrared (AIR) sensors detect motion when a narrow pulsing beam of light energy is broken by any object, whereas passive infrared (PIR) sensors have a broad or narrow detection area but only detect moving objects that differ in temperature from the environment.


Once animals have been fitted with radio or satellite telemetry units, these devices may be used to locate animals during key life stages (e.g., denning bears), access carcasses to document causes of mortality, and learn about habitat use based on movement and survival and mortality rates. These data may be combined with information obtained from the analyses of biologic samples collected noninvasively in the field to provide a more comprehensive understanding of the biology and ecology of certain species.

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Aug 27, 2016 | Posted by in EXOTIC, WILD, ZOO | Comments Off on Noninvasive Techniques to Assess Health and Ecology of Wildlife Populations

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