Exam Flashcards
(41 cards)
“50-500” rule
The 50/500 rule was made in 1980 by Australian geneticists to define a minimum lower threshold to prevent genetic loss (viable effective population size (N(e)). 50= minimum population size to combat inbreeding, a minimum. Of 500 individuals needed to reduce genetic drift. Population size is extremely important in evaluating conservation priorities for a species. Small populations are at risk of going extinct because of demographic stochasticity and genetic drift.
Theoretical application: When attempting to recover extremely depleted populations, there is direct conservation efforts to get the adult population above 50 (>50), and continue recovery efforts until populations is above 500.
“SLOSS” debate
The SLOSS is a ecology and conservation debate during the 1970 and 1980 regarding weather single large or several small reserves are superior in conserving biodiversity in a fragmented habitat.
Why is it relevant?
Biological corridors
Wildlife corridors are connections across the landscape that link up areas of habitat. They support natural processes that occur in a healthy environment, including the movement of species to find resources, such as food and water.
They are very important for conservation of biodiversity and ecosystems, as they allow species to reproduce and ensure exchange of individuals and genes between several populations. They contribute to genetic diversity of species and recolonisation of environments in the event of a disturbance. Ne = Population now. Difficult to use in marine concervation because we don’t know larval dispersal.
Population viability analysis
PVA is mathematical/ ecological models that estimate changes in population size (N) over time based on life history and demographic rates, environmental factors, population pressures (threats) and genetic factors. It is applied in conservation biology to predict future scenarios for population growth and decline, as well as compare alternative options for their management. PVAs can be used as a basis for listing species as threatened and endangered under IUCN red list.
Critically endangered species
A taxon is “Critically Endangered” when it is facing an extremely high risk of extinction in the wild in the immediate future, as defined by any of the following criteria:
Population reduction:
- Observed population reduction of 80-90 % over the last 10 years or 3 generations.
- The species is found than less than 100 km2 area or 10 km2.
- Less than 250 mature individuals in the population
- Quantitve analysis showing the probability of extinction in the wild is at least 50 % over 10 years or three generations.
Phylogenetic diversity
Diversity that includes how long the genetic distance is between species (Phylogenetic tree). Areas that have high phylogenetic differences (owl and fox) will also be an area with high species diversity. High species diversity supports better and more ecosystem function. Focusing on maximising phylogenetic diversity in conservation because it on average maximizes the protection many taxa
Triple jeopardy
Triple jeopardy is a combination of social and biological factors that increase an animals extinction risk. Fish is particularly prone to extinction if it has a small range, is not abundant were it is found, and has specialised dieter, habitat, physiological or reproductive requirements. Some marine animals like sharks and rays face triple jeopardy due to their marine habitat. Large animals are typically more comen in this category as they take a long time to reproduce and mature, they can be hunted at a faster rate than they can reproduce. Whale shark example.
Congruency
Similarity between difrent taxa, what might be good for one taxa might not be good for everyone. To make efffcent concervation you need congurancy (overlap) of taxas.
Bioaccumulation
Bioaccumulation is a process of accumulation of chemicals in an organism that takes place if the rate of intake exceeds the rate of excretion. Chemicals are introduced into the organism through exposure to the abiotic environment (soil, water, air) or as dietary intake (trophic transfer). Marine organisms that are filter feeders such as mussels are used to measure and monitor the consequences of industrial discharge as they are placed out in cages (they respond rapidly to changes in water quality and rapidly absorbs heavy metals etc.).
mBACI” sampling design
Multiple before and after control Impact (mBACI), The purpose of which is to determine whether a particular disturbance (natural or human induced) causes a change in the population or assemblage. The method involves 2 or more controls and 2 or more impact sites. Good because of special replication
Representative area
Identifying the main geographic gradients in an area (Species composition, habitat type etc.), and then choosing sites from the different habitat types. By establishing reserves at the different locations that represent different habitat types and species composition, a range of different communities and a greater biodiversity are protected.
o This require that we have a great deal of information to describe the major spatial patterns in community structure.
o Strategies used in reserving at the GBR
The Representative Areas Program (RAP) aims to enhance protection of the region’s biodiversity by developing a network of no-take areas that represents the range of habitats and communities within the Marine Park.
Recruitment overfishing
Taking such a high proportion of the breeding stock that there is no longer enough juvenile recruitment to sustain the fishery or allow it to recover. Bigger K selected species are especially exposed to recruitment overfishing as they have few offspring and take a long time to reach maturity, so they cannot reproduce enough to replenish the population. The result of this is collapsed fisheries and species populations. This is an important focus area within conservation to put regulation on harvest amounts and have oversight of how much fish is being fished to monitor the abundance and regulate thereafter.
Eutrophication
Accumulation of nutrients in the water results in algae dominating because of high nutrient availability. Fertilizer runoff to marine ecosystems can lead to algae bloom that now dominates. This can lead to bottom-up control. It results in deterioration of water quality and the depletion of dissolved oxygen in water, Algal blooms limit light penetration, reducing growth and causing die-offs of plants in littoral zones while also lowering the success of predators that need light to pursue and catch prey. Bacterial metabolism increases as benthic plants die, leading to conditions of hypoxia (low oxygen) and in extreme cases, anoxia (oxygen too low to support animals = dead zones). Eutrophication areas can eventually become dead zones.
Dispersal kernel
Dispersal distance, (Distance and probability of dicpersal) the Euclidian distance between ‘start’ and ‘end’ points of a dispersal event, is recog-nized as a fundamental characteristic of the dispersal process and defined as the movement of dispers-ers (diaspores, propagules, gametes, or dis-persing) to where they establish.
Dispersal kernels are useful to MPA design (i.e. how far apart should MPA’s be?) and fisheries management as they can inform potential of population replenishment to surrounding unprotected or open fishing areas. For threatened species, they can also inform ‘rescue effect’ potential.
Ecological extinction
Ecological extinction is the reduction of population densities to the point that the species no longer plays the same ecological role in communities. This is probably the most widespread and serious form of extinction in the marine environment. However, ultimately the ecosystem will collapse as the system runs out of ecologically equivalent species.
Local extinction
Local extinction is the disappearance of a species in certain areas or loss of sub- populations, particularly in relation to exploitation and/or local pollution. Local extinction may not be a problem, provided that there is a source of juveniles for recovery. However, it can be a major problem when it concerns keystone species.
Ecological traps
Species with complex and hard-wired life cycles can fall into what has become known as “ecological traps” in changing environments (Fig. 43). For example, the African penguin in South Africa evolved to migrate to locations that were the perfect temperatures for food production to the north. However, due to rising temperatures, the migration cues are now mis-matched with productivity. Their evolved habitat selection cues are now an ecological trap leading them to places they will suffer a high mortality.
Umbrella species
Umbrella species are those species whose protection, because of their large area requirements, will automatically provide protected areas for a large number of small range species. Most umbrella species are large mammals and birds.
Indicator species
Organisms having certain characteristics which make them suitable for detecting and forecasting impacts at some level of biological organization. Indicators species can be defined in what their effect does such as ecological factors, keystone species, umbrella species, flagship species, vulnerable species,
Sentinel species
Sentinel species are often animals used to detect risks to humans by providing advance warning of danger. When a sentinel population changes (Increase or decrease) they will indicate population changes in other species as well. These species are high sensitive to environmental disturbances and are sometimes used in aquatic biological assessments to provide an early warning that more severe water quality conditions are likely to occur unless mitigation measures are taken. Species such as polar beers, bald eagles and dolphins because they accumulate persistent pollutants. Butterfly indicates the health of coral reefs
Metapopulation
A collection of Subpopulations that are separated in space but connected by dispersal.
Immigration and emigration are key elements of population dynamics. Metapopulations are characterized by repeated extinctions and colonization of the small individual populations, but the metapopulation persists. Some are source and some are sink populations.
Stock-recruitment relationship
The stock-recruitment (S/R) relationship is fundamental to the management of natural resources, especially fish and shellfish stocks. The nature of this relationship is used to determine to what extent a population may be harvested by either commercial or sport fisheries. Relationship between spawning biomass and the recruits that can be exploited.
The SRR is used to predict the average number of recruits that would be produced at different population sizes. R- selected species have a higher reproductive rate than K selected species and can therefore be harvested more. The spawning stock is defined, normally, as the number of female organisms in the population of reproductive age and able to reproduce in any one year. The recruits are defined as those young who survive to either maturity, or to be captured by the fishery.
Trophic cascade
Trophic cascades are powerful indirect interactions that can influence and change entire ecosystems. They occur when predators limit the density and/or behaviour of their prey and by that enhance the survival of the next lower trophic level. This is important for conservation efforts as the reduction of key predators can change the entire species composition and abundance in a ecosystem.
Complementarity
Complementarity is used as a criteria for selecting sites to maximize biodiversity in MPAs. It involves choosing sites with contrasting species composition (i.e. sites that are most different from those already chosen). This ensures that as much values biodiversity as possible is represented for conservation within constraints. Evidence suggests that biodiversity supports ecosystem functioning. Yet, the mechanisms driving this relationship remain unclear. Complementarity is one common explanation for these positive biodiversity–ecosystem functioning relationships.