Genes to ecosystems Flashcards

1
Q

What is Ecology

A

The scientific study of the interactions
between organisms and their environment
that determines the distribution and
abundance of organisms

The environment includes other individuals of the same species as well as member of other
species BUT it also includes physical factors,
e.g. Temperature, rainfall, wind etc.

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2
Q

The 3 Basic Problems and Approaches to Ecology

A

Descriptive – natural history, e.g. describes the
vegetation groups of the world (temperate
deciduous forests, tropical rain forests, grasslands
etc.)

Functional – dynamics and relationships, energy
flow in ecosystems, populations and communities
as they exist and can be measured now

Evolutionary – the historical reasons why natural selection has favoured the particular adaptations we now see.

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3
Q

What is an individual?

A

-Genetically distinct unit.

-May be unicellular (e.g., bacterium, diatom, ciliate)
or multicellular (e.g., lizard, mouse, human).

  • A bacterial colony (or diatom bloom) that arises by
    binary fission from a single cell is a clonal
    population.
  • A coral is a colony of hundreds or thousands of
    individual, genetically identical polyps.
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4
Q

What are Unitary & Modular Organisms?

A

Unitary organisms come as individual units.
– Most animals are unitary organisms.
–Unitary organisms have determinate form.
– Individuals are usually genetically distinct

Modular organisms have indefinite growth
forms.
– Individuals are composed of an indefinite
number of genetically identical modules.
– Includes most plants and some animals such
as corals or sponges.

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5
Q

Can you provide examples of Modular
Organisms?

A

Many plants & some
animals show great
variation in size and
structure.
* e.g. blades of grass
are connected by
underground
rhizomes.
* Modular organisms
are often branched

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6
Q

What is a population?

A

A population is a group of individuals of the same species occupying a particular space at a particular time.

  • Populations have attributes that
    transcend those of individuals
    –Age distribution
    –Genetic composition
    –Spatial distribution
    –Temporal distribution
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7
Q

What is a community?

A

Any assemblage of populations of different
species in a prescribed area or habitat.
* e.g., the community of plants in a
deciduous forest, or the community of
animals in a rotting log
* May be of any size (NB interactions)
* May be restricted to
–a taxonomic group (e.g., bird community
of a forest) or
–include many different taxonomic groups
(plankton community)

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8
Q

What is an ecosystem?

A

An interacting complex of plant, animal,
and micro-organism communities and
their non-living environment (Arthur
Tansley, 1935)
* e.g., all of the living organisms together
with topography, soil, underlying geology,
hydrology and atmosphere
(weather/climate)

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9
Q

What is Biodiversity?

A

“Biodiversity is the genetic, taxonomic and ecosystem variety in living organisms of a given area, environment, ecosystem or the whole planet” (McAllister, 1991). It can be divided into genetic, organismal and ecological diversity (Harper and Hawksworth, 1994). Genetic diversity is defined as the variety of genes within a species, organismal diversity is the variety of species within a community, and ecological diversity is the variety of biomes within a geographic area (Harper and
Hawksworth, 1994).

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10
Q

What are the general patterns in
ecology (do we have laws)?

A

Species Area Relationships

Species Abundance Distributions

Latitudinal diversity gradient

Diversity-function relationship(s)

Mass-abundance relationship(s): Big sized species have lower population densities than small sized species.

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11
Q

What is meant by the term biodiversity?

A

The term biological diversity is used in at least four
different ways to indicate:
* genetic diversity within a species
* species diversity within a community
* community or ecosystem diversity within a region
* functional diversity within an assemblage of species

Species diversity: The number of species in a community, weighted by their relative abundance.

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12
Q

What are the 4 Components of Species Diversity?

A

Species richness?
– The number of species in a community

Species evenness (equitability)?
– The relative abundance of different species in a community.

Species heterogeneity?
– A concept that combines both the number of species and their relative abundance in a single metric.

Diversity index?
– A quantitative measure of species heterogeneity.

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13
Q

What do you need to know to be able to assess species diversity?

A

Taxonomic information: ability to assign individuals to the
appropriate species.

  • A count of the number of species in the community.
  • A measurement of the relative abundance of the species in
    the community.
  • May be straightforward for some communities. (e.g., bird
    community of a small woodland)
  • May be difficult for many invertebrate groups for which
    there are a large number of species that have similar
    morphologies.
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14
Q

Why is biodiversity declining?

A

Loss of habitat
– Logging
– Farming
– Urbanization
* Habitat modification
– Water extraction
– Flood control
* Overexploitation
– Overfishing
– Hunting (e.g., bushmeat)
* Introduced species
– Invasive species
* Pollution
* Climate change

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15
Q

Why does biodiversity matter?

A

Ecosystem functions (processes) and ecosystem services depend on biodiversity.

  • Intergovernmental Science-Policy Platform for
    Biodiversity and Ecosystem Services (IPBES) has been
    established to
    – assess change (loss) of biodiversity
    – assess how these changes affect human wellbeing.
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16
Q

What is the difference between ecosystem functions and ecosystem services?

A

Ecosystem functions are
the biological, geochemical
and physical processes and
components that occur
within an ecosystem.
* Ecosystem functioning
affects nutrient cycles, the
water cycle and the carbon
cycles.
* Other ecosystem functions
affect population dynamics
(e.g., seed dispersal,
pollination).
—————————-

Ecosystem services are
ecosystem functions that
are directly beneficial to
humans.
* Provisioning services (e.g.,
food, fibre, fuel, minerals,
water)
* Regulating services (e.g.,
CO2
sequestration, waste
decomposition)
* Cultural services (e.g.,
ecotourism, heritage values)

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17
Q

Examples of ecosystem functions and
ecosystem services

A

Ecosystem functions:

Plants are primary
producers.
* Grazing and predation
balance plant and animal
populations.
* Plant seed dispersal.
* Animals find mates and
reproduce.
* Waste materials are
degraded and recycled back
into the soil.

Ecosystem services:

Bees pollinate crop plants.
* Animals provide protein for
human consumption.
* The watershed provides
water for human
consumption.
* Trees serve as buffers
against storms preventing
destruction of homes and
other structures.

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18
Q

DIVERSITY-PRODUCTIVITY
HYPOTHESIS

A

Niche Differentiation accounts for
increased productivity in more
diverse communities.

Habitat is heterogeneous.
* Different species have different
niches.
In the hypothetical case illustrated, each species has a circular radius in niche space
in which it is a good competitor.
* By occupying more of the habitat
space, diverse communities use
more of the available nutrients to
produce more total biomass.

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19
Q

What is ecological stability?

A

Response to change…

-Press perturbation: Sustained alteration to a system state variable, e.g. temp,
pH, or biological subsidy.

  • Pulse perturbation: temporary change to a system state variable that can then
    recover.

Four key aspects…

  1. Variability - the variation of community biomass over time
  2. Resistance - the degree to which community biomass is changed following a perturbation
  3. Resilience - how long it takes for community biomass to return to predisturbance or reference state levels following a perturbation
  4. Persistence - the length of time that biomass remains unchanged
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20
Q

Does diversity increase stability?

A

Charles Elton suggested that species diversity promoted
stability citing:
* Theoretical and laboratory experiments on 2-species systems
(Lotka-Volterra, Gause)
* Islands (which have lower biodiversity) are more vulnerable
to invading species than continents.
* Outbreaks of pests are found most often in simple
communities on cultivated or disturbed land.
* Tropical rain forests (which have very diverse plant
communities) do not have insect irruptions whereas
temperate forests do.
* Use of pesticides can lead to irruptions by eliminating insects
that are predators or parasites of “pest” species (by reducing
the biodiveristy of the predators).

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21
Q

DIVERSITY-STABILITY HYPOTHESIS:

A

Ecosystems that have more species
are more stable because diversity
promotes resistance to
disturbance.
* Species differ in their traits.
* More diverse communities
contain some species that can
thrive after a perturbation
(change in a biotic or abiotic
factor).
* These species can compensate
for competitors that are stressed
by the perturbation.

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22
Q

Latitudinal Diversity Gradient

A

Species diversity is greater in
tropics (23° N/S) than at high
latitudes.
* Tropical rainforests contain
>1,000 tree species. (around
800 species in 50ha)
* Northern Europe contains
only 50 tree species.

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23
Q

Latitudinal Diversity Gradients – Some
Exceptions

A

Exceptions to the typical
pattern.
* Puffins are more diverse at
higher latitudes in N.
hemisphere.
* Sea lions are more diverse at
high latitudes in both N. and
S. hemispheres.

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24
Q

Why are the tropics so diverse?

i.e. why does species richness increase towards the tropics and away from the poles across the majority of taxonomic groups?

A
  1. The time theory (tropics are old, more time for speciation)
  2. The theory of spatial heterogeneity (tropics are structurally
    complex more niches)
  3. The competition hypothesis (more competition drives
    narrower niches)
  4. The predation hypothesis (less competition via greater
    predation)
  5. The theory of climatic stability (easier to specialise)
  6. The productivity hypothesis (climate increases productivity)
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25
Q

Six factors have been advanced to account for
variations in species richness. These are:

A

Evolutionary speed
Geographic area
Interspecific interactions
Ambient energy
Productivity
Intermediate disturbance

More than one of the factors may be important – some
drivers and some maintainers.
* Importance varies amongst regions and/or taxonomic
groups.

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26
Q

Evolutionary Speed Hypothesis (1/3)

A
  • Explanation for why so many species arise – not why so many can coexist
  • Length of time tropics have existed, promoting speciation
  • Stability of the tropics reducing extinction (difficult to text)
  • Climate favours small bodied, fast generation time, taxa
  • UV exposure higher, could (little evidence) increase
    mutations
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27
Q

Evolutionary Speed Hypothesis (2/3)

A

Species diversity is the product of evolution.

Faunas and floras that have evolved for longer time
and/or at faster rate will be more diverse.

Tropics are more diverse because:
– Conditions are favourable
– Evolution has not been interrupted by glaciation.

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28
Q

Evolutionary Speed Hypothesis (3/3)

A

Species richness increases
over evolutionary time scales, unless interrupted by
catastrophes.
* Evolution brings new species into communities (and extinction removes extant
species).
* Ecological time scales are
much faster than evolutionary time scales, so
other processes must operate
as well.

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29
Q

Geographic Area Hypothesis

A

Hypothesis: More species can be supported in larger areas
because larger areas provide more niches.

Number of habitats may increase with area.
– more scope for speciation

Total population may increase with area.
– less likelihood of extinction

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30
Q

Diversity Hotspots

A

Hotspots are areas with high numbers of endemic
species.
* An endemic species is found in only one, relatively
small, geographic area.
* Species arise primarily by geographic isolation.
* On global scale, patterns of isolation are a
consequence of continental drift.
* Locally, topography can be important.
* Many, but not all, hotspots are in tropics.

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31
Q

Interspecific Interactions

A

Greater competition can increase diversity

Stronger predation may increase diversity.

Greater competition can increase diversity.
– More stable, less stressful environmental conditions may lead to greater competition.
– Greater competition leads to resource partitioning and
narrower niches (more specialist species).
– This leads to both greater habitat specificity (contributing to b-diversity) and within habitat diversity (a-diversity).

Stronger predation may increase diversity by
– reducing competition, allowing more species to share the same resource if predation controls prey abundance or
removes competitively superior species.

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32
Q

Interspecific Interactions: Competition

A

Competition in “equilibrium”
communities:
– the number of species that can
coexist is no greater than the
number of limiting resources.
* Where there is a range of
resource availability, species
can partition the resource to
avoid competitive exclusion.
* Species richness depends on
the average niche width and
extent of overlap.

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33
Q

Interspecific Interactions: Competition

A

Anolis are small, diurnal, insect eating lizards
* sit and wait predators that perch in trees or bushes
* food size is a critical niche dimension
* niche breadth decreases with increased species richness

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34
Q

Interspecific Interactions: Predation

A

Predation can lead to increased species richness by removing animals that are superior competitors,
because there is often a tradeoff between maximum
reproduction rate and ability to resist predation.
Removal of a keystone predator can lead to reduced diversity

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35
Q

Interspecific Interactions: Disease

A

Tropical forests have high tree diversity.
* Seed deposition is high, but
survival is low close to a mature
tree of the same species.
* Survival is reduced by host specific parasites or disease in
the immediate vicinity of
mature trees.
* Some seeds carried away from
the parent tree by fruitivores
are more likely to survive.

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36
Q

Ambient Energy Hypothesis

A

Hypothesis: Energy
availability generates and
maintains species richness
* because fewer species can
tolerate extreme
environments.
* Key variables are solar
radiation, temperature and
water availability.
* Annual evapotranspiration can
be used as an index of energy
balance.

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37
Q

Productivity Hypothesis

A

Hypothesis: greater
primary production results
in greater species diversity.
* In terrestrial systems, total
primary productivity
depends on
– area of habitat,
– sunlight and
– precipitation.

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38
Q

Counter examples to the Productivity
Hypothesis

A

Some of the most speciesrich plant communities
occur on nutrient poor
soils
– fynbos in South Africa
– heath scrublands in
south-eastern Australia
* Compare location of
biodiversity hotspots with
NPP map.

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39
Q

Intermediate Disturbance Hypothesis

A

Hypothesis: at local scales, competitive exclusion,
which should reduce species diversity, is prevented by
disturbance.
* Disturbance includes any event that disrupts
competition:
– fluctuations in physical/chemical factors
– catastrophes such as fires or erosion
– predation or herbivory

Species of low
competitive ability are
lost when disturbance is
infrequent.
* Species are lost
indiscriminately when
disturbance is severe.
* Maximum diversity
should occur at
intermediate disturbance.

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40
Q

Does Diversity Increase Productivity?

A

DIVERSITY-PRODUCTIVITY
HYPOTHESIS

Niche Differentiation accounts for increased productivity in more diverse communities.

Habitat is heterogeneous.
* Different species have different
niches.
In the hypothetical case illustrated, each
species has a circular radius in niche space
in which it is a good competitor.
* By occupying more of the habitat
space, diverse communities use
more of the available nutrients to
produce more total biomass.

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41
Q

Potential mechanisms (plant niche)

A

Below ground niche
complementarily due to resource
competition

The regulation of plant productivity
by soil microbiota

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42
Q

Potential mechanisms (plant niche)

A

Below ground niche
complementarily due to resource
competition

The regulation of plant productivity
by soil microbiota

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43
Q

Potential mechanisms (soil microbes)

A

Below ground niche
complementarily due to
resource competition

The regulation of plant
productivity by soil
microbiota

soil sterilisation treatments
also remove beneficial
organisms such as
saprotrophs and
mycorrhizae, and modify
nutrient availability

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44
Q

Diversity and Ecosystem Function.

A

Diversity-productivity hypothesis: Ecosystems containing more species are on average more productive or have greater total biomass because diversity allows more of the habitat space/resources to be occupied.

Diversity-stability hypothesis: Ecosystems that have more
species are more stable because more diverse communities
contain some species that can thrive after a disturbance
(change in a biotic or abiotic factor) and these can compensate
for competitors that are stressed by the disturbance.

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45
Q

What is ecological stability?

A

Response to change…

Press perturbation: Sustained alteration to a system state variable, e.g. temp,
pH, or biological subsidy.
* Pulse perturbation: temporary change to a system state variable that can then
recover.

Four key aspects…

Variability - the variation of community biomass over time
2. Resistance - the degree to which community biomass is changed following a
perturbation
3. Resilience - how long it takes for community biomass to return to predisturbance or reference state levels following a perturbation
4. Persistence - the length of time that biomass remains unchanged

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46
Q

Functional Traits

A

Examples of plant traits
– Phenology
– Height at maturity
– Root depth
– Seed size
– Maximum photosynthesis rate
– Water use efficiency
– Affinity for limiting nutrients

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47
Q

What is meant by the term functional diversity?

A

Functional diversity: the amount of trait variation in an assemblage.
* Species do not contribute equally to varied ecosystem
processes and delivery of services.
– Keystone predators
– Ecological engineers

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48
Q

Modern Molecular Ecology –
The Basic Method!

A

BIG ECOLOGICAL QUESTION FIRST!

Extract starting
material –
Nucleic Acids
DNA or RNA

-> Amplify
extracted DNA
or RNA material
via PCR

-> Downstream
processing of
product

-> Bioinformatics
and data
analysis

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49
Q

PCR Produces Large Amounts of
Nucleic Acid From Small Starting Templates

A

ds DNA separates into
ss DNA > ca. 94°C.
Causes DNA melting of
the DNA template by
disrupting the hydrogen
bonds between
complementary bases,
yielding single-stranded
DNA molecules

The reaction
temperature is lowered
to 50–65 °C for 20–40s.
Annealing of the
primers to the ss DNA
template.
annealing temperature
is ca 3-5 °C below the
Tm of the primers used.

Stable DNA-DNA
hydrogen bonds are
only formed when the
primer sequence very
closely matches the
template sequence. The
polymerase binds to
the primer-template
hybrid and begins DNA
synthesis.

The temperature
depends on the DNA
polymerase used
Taq polymerase has its
optimum activity
temperature at 75–80
°C (72 °C is used)

DNA polymerase
synthesizes new DNA
strand complementary
to template strand by
adding dNTPs in 5’ to 3’
direction
Extension time depends
both on the DNA
polymerase used and
length DNA fragment to
be amplified

DNA polymerase
synthesizes new DNA
strand complementary
to template strand by
adding dNTPs in 5’ to 3’
direction
≈1kb per min.

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50
Q

Quantitative PCR - qPCR

A

Used to quantify PCR product (commonly in real-time;
hence confusion with RT-PCR).
* Measures starting amounts of DNA, cDNA, or RNA.
* Used to determine whether a DNA sequence is present
in a sample and the number of its copies in the sample.
* Quantitative real-time PCR has a very high degree of
precision. One of the best methods for working out how
much DNA/RNA is in a sample.

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51
Q

Quantitative PCR – Basic Method

A

TaqMan probes:
A fluorophore is attached to the 5’
end of the probe (additional oligo to
primers) and a quencher to the 3’
end.
The fluorophore is excited by the
machine and passes its energy to
the quencher.
FAM as the fluorophore and TAMRA
as the quencher.

TaqMan probes:
FAM does not fluoresce as it passes
its energy onto TAMRA.
As TAMRA fluorescence is detected
at a different wavelength to FAM,
the background level of FAM is low.
The probe binds to the amplicon
during each annealing step of the
PCR.

TaqMan probes:
When the Taq polymerase extends
from the primer which is bound to
the amplicon, it displaces the 5’ end
of the probe, which is then
degraded by the 5’-3’ exonuclease
activity of the Taq polymerase.
Releases the fluorophore and
quencher into solution, leading to an
irreversible increase in fluorescence
from the FAM and a decrease in the
TAMRA.

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52
Q

ddPCR – Basic Method

A

qPCR: Inconsistent CT
* Data not comparable between
runs
* Nonspecific amplification

ddPCR: * No standard curve
* Data is comparable between
runs
* No replicate wells needed (?)

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53
Q

Uses for different PCR

A

Metagenetics: who is there? and number of species

qPCR: How many are there and abundance

Metagenomics: What can they do, abundance

Metatranscriptomics: What are they doing?, activity

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54
Q

Definitions in PCR practices (1/4)

A

Amplicon: The short DNA sequence products of polymerase chain
reaction (PCR) amplification using taxon- or gene-specific primers to target a particular region of the genome.

Biodiversity genomics: Biodiversity assessed using high-throughput
DNA-based methods or data from whole genomes integrated with a broad array of metadata describing biological and environmental
indicators.

Biomonitoring: Biodiversity analysis that is repeated across space and
time that may focus on a target organism such as invasive or at-risk
species, an assemblage such as the bioindicator groups (amphibians, birds, macroinvertebrates) as an indicator of ecosystem status.

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55
Q

Definitions in PCR practices (2/4)

A

DNA Barcoding: A minimal standardized signature DNA sequence is used for species identification, for example, a 658-bp region ofCO1
mtDNA is used for identification of animals. Other DNA barcode
markers have been proposed for fungi, plants and protists.16S rDNA
has been used for the identification of bacteria.

eDNA: Environmental DNA comprised of free degraded DNAs in the environment as well as DNA co-extracted from whole organisms such
as microscopic organisms, arthropods, nematodes; shed cells; faeces;
as well as the DNA contained within dead or dormant cells such as seeds or spores.

ESV: Exact sequence variant. Also known as an amplicon sequence variant (ASV), zero-radius OTU (ZOTU) or simply an OTU defined by
100% sequence similarity

56
Q

Definitions in PCR practices (3/4)

A

HPC: High-performance computing, computer clusters can be used to
run the same analysis for many samples in parallel, or splitting large jobs into many smaller ones for a quicker overall runtime. Available through private clusters or third-party cloud computing services.

HTS: High-throughput sequencing, sometimes referred to as nextgeneration sequencing or second-generation sequencing.
Distinguished by the high number of sequencing reactions that occur
in parallel.

Metadata: Supplementary data linked to DNA sequences that provide
information in a standard and searchable way such as organismal or bulk environmental sample description.

57
Q

Definitions in PCR practices (4/4)

A

Multiplex sequencing: The addition of a unique DNA sequence tag to each sample, such as when multiple samples are pooled and sequenced at the same time, allows sequences from different samples to be distinguished from each other during data analysis.

Oligonucleotides: Relatively short nucleotide molecules used as primers for PCR, as probes on microarrays, or baits during target
enrichment.

OTU: Operational taxonomic unit, a group of similar DNA sequences sometimes used as a proxy for “species” in diversity measures.

Primers: Short oligonucleotides that are complementary to a
particular region of the genome and are a starting point for DNA
replication by DNA polymerase during PCR.

Taxon: An organism identified to any taxonomic rank (e.g., species
to kingdom); plural taxa.

58
Q

how are eDNA metabarcoding (amplicon
sequencing etc) good?

A

Potential to revolutionize ecology
* Low cost, high throughput sampling
* Resolves biodiversity across levels
of organization
* Applicable in any environment with
globally comparable results
* Can capture difficult to identify
species
* Rapid low-cost biomonitoring etc
etc..
* But, each step has many pitfalls
and challenges to overcome….

59
Q

General and crude metabarcoding (amplicon sequencing) workflow:

A

Extract and isolate DNA from a sample (can be environmental
matrix, mix of whole organisms, eDNA etc)
2) Amplify via PCR the gene region of interest (phylogenetic marker
gene – e.g. 16S rRNA, COX1, ITS) for target taxa producing multiple
copies of the same region from each of the different taxa present
in your sample
3) (optional) Secondary PCR is used to add on a “tag” (multiplex
index, or barcode) that identifies which sample the PCR amplicons
came from
4) All samples are pooled (normally in equimolar concentrations) and
prepared for HTS (aka NGS) and sequenced
Raw sequences are processed via a bioinformatics pipeline, which
use the tags included in step #3 to de-multiplex sequences into
their original samples.
6) Sequence variability is used to cluster sequences in OTUs – i.e.
group all sequences that are within 3% similarity as an OTU
(analogous to species)
7) Count how many OTUs each sample has, and how many reads
come from the same OTU (measure of relative abundance)
8) Match OTUs to reference databases on known sequences types to
identify which species where present and have been recorded
9) Do some ecology…

60
Q

eDNA metabarcoding applications

A

Ancient Ecosystems

Plant-Pollinator Interactions

Diet Analysis

Invasive Species Detection

Pollution Response

Air Quality Monitoring

61
Q

eDNA metagenomics (shotgun
metagenome sequencing etc)

A

Potential to revolutionize ecology
* Costly, but produces large amounts
of useful data
* Resolves taxonomic and functional
diversity across levels of
organization
* Applicable in any environment with
globally comparable results
* Can capture difficult to identify species
* Same sample design considerations
as metabarcoding, but with
computational limits as well…

Also Essentially identical environmental sampling to used in metabarcoding studies

62
Q

General and crude metagenome (shotgun sequencing) workflow:

A

1) Extract and isolate DNA from a sample (can be environmental
matrix, eDNA, gut biome etc)

2) Quantify DNA, ensuring you have enough to sequence – requires a
larger amount of DNA extract than amplification-based approaches

3) Randomly fragment DNA into shorter reads appropriate for NGS
platform (e.g. 150x150bp PE) – not required for metabarcoding as
amplicons typically ~350-650bp in length

4) Tag all samples with multiplex identifier (or run one sample per
lane) and pool into equimolar concentrations before sequencing on
appropriate NGS platform

5) Raw sequences are processed via a bioinformatics pipeline, which use the tags included in step #4 to de-multiplex sequences into
their original samples.

6) Do some bioformatics….

7) Do some ecology…

63
Q

The virome:

A

Viruses are the most abundant biological entities in the biosphere

  • Can infect Bacteria, Archaea, and Eukaryotes
  • Virome is >10x more abundant than the microbiome with
    107 - 109 viruses per gram of sediments or soils
  • Important role in the genomic plasticity of their hosts, and species interactions.
  • Large regulator of dynamics of microbial populations
  • Difficult to isolate and study using targeted approaches
64
Q

Define population.

A

A population is a group of organisms of the same
species occupying a particular space at a particular
time.

  • Populations have attributes that transcend those of
    individuals…

– Age distribution
– Genetic composition
– Spatial distribution

  • Some simple models of population dynamics ignore
    these attributes.
65
Q

What is population size?

A

Population size, usually denoted N, is the number of
individual organisms in a population.
* Elephants
– 3-5 million African elephants roamed Africa in the
1930s.
– Today, the elephant populations in southern
Savannahs in Africa total 300,000 elephants.
* Ants
– E.O. Wilson estimated 10 million billion
(10,000,000,000,000,000 = 1016)
– However, this is amongst an estimated 22,000
species.

66
Q

What is population density?

A

Absolute population density is the number of individuals
per unit area or per unit volume.
* Population size is the absolute density multiplied by the
area (or volume) of the population’s range.
* Extremely wide range of densities, depending on
organism.

67
Q

How to work out population size and What factors need to be taken into account when measuring population size or density?

A

population size = (Population density) x (Area of Range)

Are the organisms motile or sessile?
* Anticipated size/density and patchiness of
distributions.
* Ease/difficulty of detection or collection.
* Efficiency of sampling method.
* Time and resources available to undertake a survey.
* Two broad approaches:
– absolute population size or density
– relative population size or density.

68
Q

the 3 Types of Spatial Distributions

A

Random

Even = Regular (uniform)

Clumped = Aggregated
= Patchy

69
Q

Random distribution

A

Random (unpredictable): Distance between individuals
is random.
– Position of an individual is
independent of the positions
of other individuals.

-Individuals do not interact!

  • Can arise during colonization
    from random dispersal in
    homogenous environments.
    – e.g., larvae (oysters) or seeds
    (dandelion).

Why are random
distributions rare in nature?
* Abiotic factors are variable:
climate, edaphic (soil)
* Biotic interactions: social
interactions (behaviour) lead
to clumping (e.g. herds or
swarms)

70
Q

Aggregated (patchy) distribution

A

Distance between individuals
is minimized
* Most common pattern in
nature

Patchy resources
* e.g., watering holes
* Social interactions that allow
* earlier detection of predators
* more effective defence
* increase hunting performance
(wolf pack)

71
Q

Uniform (regular = even) distribution

A

Distance between
individuals is maximized
* Minimizes competition
– Moisture: creosote bush
– Sunlight: even distribution of trees in a forest
* (Anti)Social interactions:
– Territoriality
* Alleopathy
– Sage (Salvia leucophylla)
releases terpenes that inhibit
growth of neighbouring
plants

72
Q

What is population dynamics

A

Population dynamics is
the study of how a given
population’s numbers
grow and shrink over
time.

Formally described using mathematical equations, which
form the bases for population models.
Many assumptions and considerations (“all models are wrong, but some are useful” – George Box)
– logistic vs exponential growth
- resource limitation vs no resource limitation
– closed vs open populations
- without immigration/emigration vs with
– discrete vs continuous generations
- regular new generations without overlap or not

Population size and
density change as a
result of
– births,
– deaths,
– immigration and
– emigration

73
Q

Population growth for discrete generations in
closed populations

A

Discrete generations consist of populations that do not
overlap.
– e.g., univoltine insects or annual plants have one
generation per year
* Closed populations are not affected by immigration or
emigration.
– This simplification is often applied in studying population
dynamics.

74
Q

How do we calculate the per capita growth
rate?

A

Realized per capita growth rate (R0 ) per
generation
– units for R0
are per generation
– R0 varies due to biotic and abiotic factors

1 + Proportion of population at time t+1 that are not present at time t.

Net growth, Birth > Death
No growth, Birth = Death
Net decline, Birth < Death

75
Q

exponential or geometric
growth

A

If unchecked, a given population will continue to increase in size at
an exponential rate.

This occurs when birth > death for closed populations; and when either birth > death and/or immigration > emigration for open
populations.

Populations may increase
exponentially during
initial stage of recovery
from overexploitation.
* e.g., whooping crane in
wintering grounds near
Aransas, Texas
* breeds in Canada, but
winters on Texas coast

76
Q

Population Regulation

A

Populations vary from place-to-place –
good habitats with high densities, poor
habitats with low densities

No populations increase indefinitely
without a limit, even
introduced/invasive species will eventually reach an asymptotic density

If population sizes do not increase pass a
limit, why not?

Consider a closed population. It will grow
until it reaches an equilibrium where:

per capita births = per capita deaths

It will remain at or around equilibrium if
either per capita births and/or per capita
deaths are density dependent.

77
Q

The principles of population regulation

A

First principle of population regulation:
No closed population stops increasing unless either the per capita birth rate or per capita death rate is density dependent

Second principle of population regulation:
Difference between two populations in equilibrium density can be caused by variation in either density-dependent or density-independent per capita birth and/or per capita death rates.

78
Q

Extrinsic versus intrinsic processes
influencing populations

A

Extrinsic processes
include the actions of
other species, and the
physical/chemical
environment

Intrinsic processes result
from actions and
interactions of the
individuals making up the
population.

Population regulation
results from interaction of
extrinsic and intrinsic
factors.

e.g., predators typically
take certain ages groups

e.g., size of territory
defended by many birds or
mammals can limit
population density

79
Q

Stable versus unstable populations

A

Stable populations do not show wide fluctuations
from equilibrium density.

Unstable populations vary widely in abundance.

Instability may arise from biotic instability
– e.g., predator-prey oscillation (snowshoe hare –
lynx).

Instability may also arise from environmental
fluctuations such as
– severe weather.

80
Q

How do open populations differ from
closed populations?

A

A population is a group of organisms of the same
species occupying a particular space at a particular
time.

Open populations can change in size due to
immigration and emigration as well as births and
deaths.

Closed populations are not subject to immigration or
emigration.
– Population dynamics in closed populations are
driven only by births and deaths.

81
Q

Metapopulations

A

Spatial scale is important
in stability of populations.
* Population may be stable
at regional scale, but
unstable locally.
* Local populations show
much more extreme
fluctuations, including
extinction, than regional
metapopulations.

82
Q

What is a metapopulation?

A

A collection of local populations that are linked
together by dispersal (immigration and emigration).
* Local populations arise from colonization.
* Local populations are more likely to become (locally)
extinct.

83
Q

Source and Sink Populations

A

Some habitats can support high population growth
rates.
* These can serve as sources of individuals to less
favourable habitats.
* Territoriality, for example, may led to emigration
(dispersal).
* In habitats where death rates exceed birth rates,
populations can still be maintained by immigration.

84
Q

What is mutualism?

A

Mutualism: Two species live in close association
with one another to the benefit of both.

  • Two examples related to terrestrial plants
    – Leaf cutter ants and fungi where the fungi relies on the ants. and the fungi produces stuff for the ants to eat
    – ants and ant cows (aphids) where the ants protect the aphids and in return eat the honey dew that the aphids produce.
85
Q

Mutualism: mycorrhizae

A

Almost all plants have
mycorrhizae growing on
root tips.

These fungi provide
nutrients (P, Fe) to plants
in exchange for sugars.

Plants with mycorrhizae
are
– more competitive in
infertile soil and
– better able to tolerate
environmental stress.

86
Q

Arbuscular Mycorrhizal (AM) Fungi

A

Ubiquitously distributed soil microbe
* Obligate plant-root endosymbiont
* Colonise ⅔ terrestrial plants species
* Acquire all their carbon from host plant
* Beneficial impacts on the plant include:
increased P & N uptake, protection from
pathogens and improved water relations

Arbuscular mycorrhizal (AM) fungi (Phylum:
Glomeromycota) form obligate root symbioses with the majority (≈ ⅔) of terrestrial plants.

In return for photosynthates, AM fungi provide host plant
species with increased phosphorus and nitrogen uptake and protection against soil pathogens.

87
Q

What is predation?

A

Predation occurs when one living organism (the predator) consumes all or part of another living organism (the prey).

  • Herbivory: One animal species (the predator) eats all or
    part of a plant species (the prey).
  • Herbivores consume plants, including seeds and fruits.
    – Often the plant is not killed, but may be damaged.
  • Carnivory: One animal species (the predator) eats all or
    part of a second animal species (the prey), often killing
    the prey.
88
Q

What other types of interactions are
included in predation?

A

Parasites are plants or animals that live in or on other organisms (the hosts) and depend on their hosts for nutrition, but do not kill their hosts.

Insect parasitoids lay eggs on or near the host insect, which is subsequently killed or eaten by the larvae

Cannibalism is a form of predation in which the prey
is a member of the same species

89
Q

How do predators affect other species?

A

Predators may restrict the distribution or reduce the abundance of prey.

  • Predators may compete by consuming the same prey (when in short supply).
  • Predators may consume different prey, which themselves compete for a common resource.
  • On short (ecological) time scales predation can affect community structure.
  • On evolutionary time scales, predation is a selection pressure that can lead to predator-prey coevolution.
90
Q

How does co-existence occur?

A

Predators and prey cannot co-exist in two-species “communities“ in a closed system.

  • Co-existence can occur provided that immigration and emigration are allowed.
  • Gauss (1934) achieved this by introducing
    immigrants at intervals to Didinium-Paramecium microcosms.
  • Huffaker (1958) achieved this by increasing
    environmental heterogenity (creating a patchy environment) Typhlodromus-Eotetranychus microcosms.
  • In both cases, the food supply to the prey was unlimited.

Also adding places for the species to hide.

91
Q

How do predator-prey systems in the real world differ from systems studied in laboratory microcosms?

A

Multiple prey species are eaten by multiple predator species.
* Habitat is more variable (spatially heterogeneous) for
both predator and prey .
* Prey have a greater range of refuges from predation.
* Time scale for laboratory experiments is limited,
precluding evolutionary changes.

92
Q

What is the Allee effect?

A

Inverse density
dependence of per
capita population
growth rate (r) at low
density.

Mortality rate increases
and birth rate decreases
as population density
declines.

When density drops too
low,
– mates may be
difficult to locate
– group defences
against predators
become less effective.

If size drops below a
critical threshold
density, the population
will go extinct.

93
Q

What is doomed surplus?

A

“doomed surplus” = excess of population growth over
that which can be supported by the habitat
* The doomed surplus would die due to exposure or disease,
if not killed by predators.
* To confirm, requires comparing populations of prey in
– experimental treatments where predators are removed
– versus controls where predators are present.

94
Q

Predation on large mammals in Serengeti Plains (Eastern Africa)

A

Predators (hyenas, wild dogs,
cheetahs, leopards, lions) appear
to have little effect on populations
of large mammal prey
(wildebeest, buffalo, zebra,
gazelle).
* Most prey are migratory, entering
the Serengeti Plains during the
wet season.
* Predators are resident, and their
populations are limited by prey
availability during the dry season.

95
Q

What is surplus killing in predators?

A

Surplus killing occurs when predators kill more prey than they
can immediately food requirements.
* May be an outcome of evolutionary selection for aggressive
behaviour towards prey.
– in particular, when confronted with agile prey that are
typically difficult to subdue
* Observed in many types of animals including foxes, wolves,
but also invertebrate predators.
* Surplus killing occurs when prey are particularly vulnerable.
– e.g., chickens in a hen house
– poor nutrition during severe winters in deer populations
– lack of defence mechanisms against introduced species
(e.g., red fox in Australia)
* Predators may store food for latter consumption.

96
Q

What are the components of the response of
predators to prey abundance?

A

Numerical response:
change in the numbers or
density of a predator
population in relation to
the size or density of its
prey species.

Functional response:
change in the feeding rate
of an average predator in
relation to the abundance
of its prey

97
Q

List the types of ecological interactions that
can occur between individuals

A

Competition
* Predation
– Carnivory or Herbivory
* Parasitism or Disease
* Mutualism
* Commensalism
* Amensalism

98
Q

Define the terms intraspecific competition,
interspecific competition and predation.

A

Intraspecific competition is an interaction in population ecology, whereby members of the same species compete for limited resources.
This leads to a reduction in fitness for both individuals.

Interspecific Competition: Two species use
the same limited resource or seek that
resource, to the detriment of one or both.

Predation: One animal species (the predator)
eats all or part of a second species (the prey),
often killing the prey.

99
Q

Define the terms mutualism,
commensalism, Amensalism and Symbiosis.

A

Mutualism: Two species interact with one another
to the benefit of both.

Commensalism: Two species interact with one
another to the benefit of one without harming or
benefitting the other

Amensalism: Two species interact with one another
to the benefit of one but to the detriment of the
other.

Symbiosis: interaction between two different
organisms living in close physical association such as in mutualism, commensalism or parasitism

100
Q

What are the 3 main categories for competition?

A

Exploitative (e.g., resource) competition

Interference (e.g., contest) competition

Indirect competition

  • Space
  • Mates
  • Nutrients, Light , Water
  • Food
101
Q

Describe and give an example of
exploitation competition.

A

Exploitation competition
occurs when organisms from
the same or different species
utilize a common resource
that is in short supply.
– They consume the resource, thereby reducing the amount
that is available.

Buffalo and grasshopper eat
the same grass, but do not
interfere with one another.

Trees compete for light, but do not directly harm each other.

102
Q

Define interference competition and an example.

A

Interference competition
occurs directly between
individuals.
– via aggression,
– or when the individuals
interfere with foraging,
survival, reproduction of
others,
– or directly prevent others
from occupying a portion of
the habitat.

Two species of birds do not eat the same food, but compete for a limited number of tree holes for nesting sites.

103
Q

Describe indirect competition.

A

Indirect competition occurs when two species
interact via a third species, for example via a
common predator.

  • Pheasants & rabbits do not compete directly for food
    or space, but may appear to interact when they are
    subject to a common predator (e.g., foxes).
  • An increase in the abundance of rabbits leads to in increase in the fox population.
  • The pheasant population then declines due to
    increased predation from the larger fox population.
  • This leads to an inverse relationship between
    population sizes of rabbits and pheasants.
104
Q

What is a niche? including Realised and fundamental niches

A

  • Define the term “fundamental niche.”
  • The set of resources that a species can use, and the
    range of habitats that it can occupy, in the absence of
    competition with or predation by other organisms.
    ———-
    Define the term “realized niche.”:
  • The observed resource use of a species in the presence
    of other organisms in the community.
105
Q

Outcomes of the Lotka-Volterra
competition equations.

A

Coexistence requires that
intraspecific competition
is greater than
interspecific competition.
* In the green area, species
1 increases at the expense
of species 2.
* In the orange area, species
2 increases to the
detriment of species 1.
* In the white area,
populations of both
species decline.

106
Q

Theories of resource competition.

A

Lotka-Volterra competition model considers
consumption of a single resource.
– It predicts competitive exclusion.
* Coexistence can occur if there is more than one limiting resources and different species have different requirements for these resources.
– The number of species that can coexist depends on the
number of limiting resources.
* Coexistence can also occur in nature if there is:
– heterogeneity in the environment,
– fluctuation in resource level,
– episodic resource availability, or
– competition is not the only type of interaction between
the species.

107
Q

Where, when and why might we expect
competitive exclusion not to occur in natural
communities?

A

Environments where resources are not limiting (e.g.,
where predation controls abundance of prey).

Environments where species do not compete for the same resources.

Both the Lotka-Volterra zero growth isoclines and Tilman’s competition model predict the outcomes of
competition at EQUILIBRIUM.

– Is equilibrium ever reached in the real world?

Fluctuating environments can reverse the direction of
competition.

108
Q

Competition in Warblers (Dendroica)
pronounced DEN-droy-kuh. (1/2)

A

Research on competitive exclusion has focused on taxonomically related species that inhabit the same
environments.

Much of this work has been done on birds.

Robert MacArthur’s (1958) studies of warblers
(Dendroica spp.) Ecology 39: 599-619 (available
electronically from the library)

5 species coexist in New England forests.

All eat insects and are comparable in size.

How is competitive exclusion prevented?

Warblers will eat at different parts on the tree, meaning they can co-exist. Some warblers occupy the same space and one is clearly a stronger competitor, however the other warbler will live off the boom and bust of the insect population of the more dominant warblers feeding niche.

109
Q

Competition in Warblers (Dendroica) (2/2)

A

These Dendroica species partition the forest by
– feeding at different positions in the canopy
– feeding in different manners
– moving in different directions through the trees

Conclusion: closely related species of warbler avoid
competition either by living in different places, or feeding in different ways on different types of food.

In addition, Cape May warbler is a poor competitor
(only feeds on tips of highest braches)
– Coexistence of this species depends on eruptions of
insects to provide superabundant food

110
Q

what is Character Displacement?

A

Divergence of species in
areas where they co-occur
to either maintain
reproductive isolation or
reduce interspecific
competition.

Observations of character
displacement support
Gause’s hypothesis.

111
Q

What can character displacement be used for?

A

Character Displacement can be used as evidence of evolutionary adaptations to reduce competition
provided that…

The pattern could not have occurred by chance.
* Sites should not differ greatly in environmental
conditions whether both species or only one of the
species is present.
* Morphological differences reflect differences in
resources used.
* There is other evidence for competition.
* Phenotypic differences have a genetic basis
* Trait results from actual evolutionary change.

112
Q

What 3 things must occur for natural selection to take place?

A

The essence of Darwin’s theory is that natural selection will occur if three conditions are met. These conditions, highlighted in bold above, are a struggle for existence, variation and inheritance. These are said to be the necessary and sufficient conditions for natural selection to occur.

113
Q

What is the ecological benefit of rarity.

A

Locally rare species are expected to have a survival advantage because rarity reduces their risk of damage from pathogens. This “rare-species advantage” may help maintain plant diversity in natural systems and explain how introduced plant species become invasive weeds.

There will also be less competition between species if they are rarer.

They will also have less predation pressure.

114
Q

Log-normal distribution in rarer species

A

In many studies, species of
intermediate abundance are more
common than very rare species.
* This is seen as a maximum in the
plot of number of species versus
geometric class.
* A log-normal distribution is the
expected statistical distribution
when the
– number of species is high, and
– relative abundances are
determined by a large number
of independently operating
factors.

115
Q

Explanations for the log-normal distribution in rarer animals

A

Sequential Niche Breakage Hypothesis:
– A community contains a total set of niche requirements.
– This niche space is broken up sequentially as new
species enter the community one at a time.

The log-normal distribution is a consequence of the
sequential RANDOM partitioning of the total niche space
by the component species.

  • A competitively superior species occupies more of the
    space.
116
Q

Sequential Breakage Hypothesis

A

Two possible ways for a 3 species community to arise by
subdividing total niche by sequential random partitioning.

In both cases, the niches are structured in a hierarchy.

117
Q

What is a heterogeneous sample vs a homogenous ecology

A

Homogenous means alike. Heterogenous means unalike or distinct from one another. Thus, a homogenous population has little variation. You could refer to a specific trait, such as hair color or you could refer to genetic diversity.

118
Q

what is habitat heterogeneity?

A

The habitat-heterogeneity hypothesis, developed initially by MacArthur and MacArthur (1961), proposes that an increase in number of different habitats can lead to an increase in species diversity.

The “habitat heterogeneity hypothesis” (MacArthur, 1972) states that the number of available ecological niches will increase as habitats become more complex, and that this will have positive effects on the ability of species to coexist (e.g. McClain & Barry, 2010; Stein, Gerstner, & Kreft, 2014; Tews et al., 2004).

119
Q

What is alpha, beta and gamma diversity?

A

Alpha diversity: the diversity within a particular area or
ecosystem.
– usually expressed as the number of species (i.e., species richness) in that ecosystem.

Beta diversity: a comparison of diversity between areas or ecosystems
– usually expressed as the number of different species between the ecosystems.
– rate of accumulation of diversity with an increasing number of sites sampled

Gamma diversity: a measure of the overall diversity within a large region.
– usually expressed as the total number of species in a
geographical area.

120
Q

Approximately equal numbers
of studies (before 2005)
reported increased and
decreased diversity (of
indicator taxa) following
selective logging in Southeast
Asia. Why?

A

Logging reduces habitat
heterogeneity
* Sample alpha diversity relatively
unchanged
* Between-sample beta diversity
deceases
* Thus – slope of SAR (The species–area relationship) decreases

121
Q

what is the neutral theory?

A

Neutral theory: relative abundance of different species within a community is determined by chance.

Neutral theory is a null hypothesis to niche theory.

All species in the community are assumed to be ecologically equivalent.
-all species have the same per capita birth rates, death rates and speciation rates.
-All species are equally competitive.

As individuals die, they are replaced by offspring of another individual, chose at random regardless of species.

The community is saturated with species and is in equilibrium (the total number of species is constant).

122
Q

Testable predictions: in the neutral theory

A

species abundances will better fit the ZSM distribution
than the log-normal.

  • changes in community composition will be related to
    solely to distance between samples (reflecting effects
    of dispersal limitation).
  • no relationship between community composition and
    either abiotic or biotic variables.
123
Q

What is a stochastic process?

A

A stochastic process means that one has a system for which there are observations at certain times, and that the outcome, that is, the observed value at each time is a random variable. This comprises essentially everything we speak about.

124
Q

metagenomics sequencing vs metabarcoding

A

In brief, metagenomics could be defined as the characterization of the vast number of genomes present in an environmental sample, using both a taxonomical and a functional analytical approach. DNA metabarcoding, on the other hand, principally focuses on taxonomically describing the species present within a sample.

125
Q

Define ecological efficiency and outline the processes that contribute to losses that occur during energy transfer between trophic levels.

A

Ecological efficiency describes the efficiency with which energy is transferred from one trophic level to the next. It is determined by a combination of efficiencies relating to organismic resource acquisition and assimilation in an ecosystem.

126
Q

Define secondary production and outline the information that is required to estimate the productivity of a vertebrate population.

A

The production of organic matter by the consumers is called secondary productivity. In secondary productivity, the energy is obtained by the transfer of energy through the food chain.

127
Q

The pattern and relative magnitudes of energy flow in a rainforest

A

The main energy source in an ecosystem is sunlight. This is absorbed by plants, called ‘producers’. This energy is then passed on to the animals through the plants they eat, these animals are called ‘primary consumers’.

128
Q

Describe how primary production can be affected by the activity of organisms in other trophic levels.

A

Autotrophs, the producers in a food web, convert the sun’s energy into biomass. Biomass decreases with each trophic level. There is always more biomass in lower trophic levels than in higher ones. Because biomass decreases with each trophic level, there are always more autotrophs than herbivores in a healthy food web.

So, the correct answer is ‘Net Primary Productivity’. Note: From one trophic level to the next trophic level only 10% of energy will be transferred and 90% of the energy gets lost. This is called the 10 percent law.

129
Q

Describe what happens during the succession of communities, using examples.

A

Ecological Succession. Ecological succession is the process by which a whole community of populations changes through time. It occurs following a disturbance that creates unoccupied areas for colonization.

During succession, some species colonies area and their population become more numerous, whereas, the population of other species declines and even disappears. It is a process of systematic progression of types of species invading an area. There are two main types of succession, primary and secondary.

In primary succession, newly exposed or newly formed rock is colonized by living things for the first time. In secondary succession, an area that was previously occupied by living things is disturbed, then re-colonized following the disturbance.

130
Q

Discuss what determines the species richness of different communities.

A

Plant species richness may vary with variation in local soil properties. Animal species richness may vary with the complexity of the habitat form, for example vegetation structure. Thus habitat heterogeneity is both context and species dependent. An obvious pattern of communities is the variation in species abundances.

Many factors affect small-scale species richness, including geographic (e.g. species pool, dispersal), biotic (e.g. competition, predation, facilitation) and abiotic (e.g. resource availability, environmental heterogeneity, disturbance frequency and intensity).

Heterogeneity is defined as the variation in biotic and abiotic conditions across space and through time

131
Q

What is facilitation?

A

Facilitation occurs when one species positively impacts the fitness of another, and has predominantly been studied in free-living species like plants. Facilitation can also occur among symbiont (mutualistic or parasitic) species or strains, but equivalent studies are scarce.

or example, pollinators, such as bees, butterflies, and hummingbirds, benefit because they eat the collect pollen and/or nectar that they collect from flowers. The plants also benefit because their pollen is dispersed to other plants, allowing them to reproduce.

132
Q

Describe how the individualist plant community concept differs from the organismic plant community concept.

A

Individualistic hypothesis The view, first proposed by H. A. Gleason in 1917, that vegetation is continuously variable in response to a continuously varying environment. Thus, no two vegetation communities are identical.

Clements’s Organismal community is a spatial concept: variety of plant and animal species interacting and influencing the overall structure. Gleason’s Continuum view is a population concept, focusing on the response of the component species to the underlying features of the environment.

133
Q

Animals affect plant communities by facilitating pollen dispersal (e.g., bees, bats and birds). 3 other ways by which animals affect plant communities either directly or indirectly, giving named examples.

A

Animals help plants by helping pollinate flowers or by dispersing seed. They also help supply nutrients when they die and decompose.

134
Q

What is the MacArthur-Wilson model of species richness.

A

MacArthur and Wilson thus assume that there will be an equilibrial point where the immigration rate equals the extinction rate. They further hypothesize that an increase in island size will lower extinction curves while a decrease in distance between the island and the source region will raise immigration curves.

135
Q

Terrestrial primary production varies widely in both space and time. Describe how primary production is measured and discuss the factors that determine terrestrial primary production.

A

Primary productivity is usually determined by measuring the uptake of carbon dioxide or the output of oxygen. Production rates are usually expressed as grams of organic carbon per unit area per unit time.

The type of terrestrial ecosystem found in a particular place is dependent on the temperature range, the average amount of precipitation received, the soil type, and amount of light it receives.

The niche will also affect the primary production for the different species in the ecosystem.

136
Q

Discuss the transfer of energy and materials between primary producers and other trophic levels in terrestrial ecosystems.

A

Primary producers use energy from the sun to produce their own food in the form of glucose, and then primary producers are eaten by primary consumers who are in turn eaten by secondary consumers, and so on, so that energy flows from one trophic level, or level of the food chain, to the next.

Energy can pass from one trophic level to the next when organic molecules from an organism’s body are eaten by another organism.