Title: Basics of Research with Emphasis on
1Basics of Research with Emphasis on Estimating
Abundance and Habitat
2Objectives
- The first major failure of most conservation
research is the lack of a clear objective - The second major failure of research is failure
to establish specific objective - The third major failure is to then completely
ignore those objectives
3Objectives
- Action Plans provide direction, but cover
objectives in more general terms need to refine - For example there is a PQFAP objective for the
Hainan hill partridge relative to forest
management and reserves. - Review work done by Gao Yu-ren
- Determine extant habitat
- Specific objectives
- Always keep the terms TIME and SPACE in the
back of your mind
4Objectives
- Best approach is to describe in terms of question
- For example
- Is purpose to describe present distribution of
species in a country? - Is purpose to describe present distribution of
species in a reserve? - Is purpose to estimate abundance of species
in a particular locality? - Is purpose to make comparisons of abundance
among different reserves or among
different types of management?
5Objectives
- Is purpose to describe dynamics (trends) to
assess changes in populations or distributions? - Is the purpose to establish causal relationships
eg. Habitat destruction, mushroom collection,
hunting? - Keep in mind that the purpose of a research
project is NOT to develop conservation
assessments of a species. - Conservation assessments might be an outcome,
but they are not a conclusion
6Objectives
- Approach to our research
- Next question to ask ourselves is the type of
approach 3 major types - Correlational studies most common approach
- Experimentation strongest inference
- Adaptive Resource Management may be the
future for our research direction
(Walters 1986)
7Sampling
What is the need?
- We sample because we can rarely do a complete
census in fact even for humans a complete
census often produces poorer data - Sampling means a subset of your study population
selection of elements of the population,
collection of data on those, and using that data
to draw conclusions about the population
8Sampling
- First thing to define Your POPULATION!!
- Is it the Sichuan HP in a reserve?
- Is it the SHP in the western Sichuan?
- Is it the SHP in Sichuan?
- Is it the SHP in the China?
9Sampling
- Second thing to define REPRESENTATION
- Does your sample represent your target
population? - For example
10Sampling
- We define our target population as the population
of quail in a 10,000 ha reserve - Our objective is to undertake an assessment of
the population of this quail eg What is the
population of the quail in the reserve? - Biologist A comes up with the following quadrat
sampling design -
11Sampling
10,000 ha reserve
Road
Biased sampling
12Sampling
10,000 ha reserve
Random Sampling
13Sampling
10,000 ha reserve
Habitat C
Habitat A
Stratified Sampling
Habitat B
14Sampling
10,000 ha reserve
Systematic Sampling
15Sampling
- Key is to decide design and sample number
- Sample size of ONE and ALL are both wrong because
they are either producing no data or are a waste
of resources
The latter in abundance monitoring is actually a
true census!!!!!
16Unit of Measure
- Key issue to be defined at the beginning
- Commonly it is the animal
- Or the group of animals
- Or a spatial unit
- Or a unit in time
- Often very poorly defined resulting in some of
the common research mistakes
17Unit of Measure Some Definitions
- Census complete count e.g. number of biologists
in this room---no error estimate - Population Estimate Estimate of numbers of
animals on a study area e.g. 228 orange necked
hill partridge in Cat Tien National Park,
VN---must have error estimate - Density estimate Estimate of number of animals
per unit area e.g. 15 western tragopans per km2
in Nepal---must have error estimate
18Unit of Measure Some Definitions
- Index
- Number of calls per point
- Number of birds observed per km of transect
- Does not usually provide a population or density
estimate - Can provide provide an estimate of population or
density if combined with a quantitative technique
19Variability in Sampling
A sample is comprised of two things?
- A measure of central tendency!!!!!!
- A measure of statistical error!!!!!!
- Statistical error is not a measure of bias!!!!!!
Do not ever present a mean or median or any
measure of central tendency without a measure of
error!!!!!!!!!!!!!!!!!
20Scale
- Critically important Always ask if you have the
scale right - Best analogy Are you trying weigh elephants to
the nearest gram and trying to weigh mice to the
nearest kilogram - Common mistake is to try to apply techniques
designed for fine scale to very coarse scale
projects
21Concept of Detectability
- Probably most overlooked issue in research
- What is it???
- It is the relationship between our count of our
sample units (birds) and the number that are
actually present
22Concept of Detectability
- Remember that good estimates of populations are
not possible simply by increasing the sample size
in fact extra sampling for the sake of larger
sample size is not warranted or a good use of
limited resources - Any counts, or calls, or other observations must
have some connection (hopefully measurable )with
either absolute or relative populations
unbiased estimates
23Concept of Detectability
- For example
- 1,000 ha study area
- Divided into 10 100-ha plots
- We sample all 10 plots and find a mean of 12.5
birds per plot ( 1.5 SD) - What is our population estimate?
24Concept of Detectability
N 125 (15)
25Concept of Detectability
- Now suppose
- I am All Seeing and I know that our ability to
detect birds in each plot is only 0.7. - What then is our true population estimate?
N 179 22
26Concept of Detectability
- Obviously we are not All Seeing !!!!!!
- However, there are numerous techniques that allow
us to estimate detectability (b) - For example double sampling
- For example using radio-tagged or tagged birds to
verify - Use of absolute estimates which include estimates
of detectability
27Concept of Detectability
- This is true even when we are doing INDICES
- Why?
- Because indices can even have problems if we
cannot meet the assumption that the index does
not vary with space and time independent of the
population we are measuring
28Application to Habitat Analysis
- Finding birds in the field
- In conjunction with population surveys
- Radio-telemetry
29Variation in Detectability
- Are there more detections of SHP in Primary
Forest because there are more birds or because
they are easier to see? - Can create biases in habitat analysis
30Analysis techniques
Design I studies
- Logistic regression
- Log-linear modeling
- Simple c2 analysis (Neu et al. 1974)
31Telemetry analysis techniques
Design II - IV studies
- Design II Animals marked, but only study area
habitat assessed - Design III Resource use and habitat available
defined for each animal - Design IV Resource use and habitat available
defined for each observation of each animal
32Telemetry analysis techniques
Design II - IV studies
- Scale and Resource Availability are key issues
impacting all Designs - Once again sampling is a key issue individuals
radio-tagged, temporal variation in data
collection, non-random loss of observations,
autocorrelation
33Telemetry analysis techniques
Defining Resource Availability
- Formal Framework provided by Johnson (1980)
- First Order Geographic range of species
- Second Order Home range location within
distribution - Third Order Selection of particular areas
within a home range - Fourth Order Microhabitat or food selection
34Telemetry analysis techniques
- Radio-telemetry studies fit Second and Third
Order Resources Studies - Friedmans Test
- Johnson Method
- Compositional Analysis
- Discrete Choice Modeling
- Logistic Regression
- Log-linear Modeling
- Multiple Regression