Population Dynamics 1 Outline • • • • • • Dynamics of Population Growth Exponential vs. Arithmetic Growth Malthusian vs. Logistic Growth Population Increase Population Decrease Survivorship Regulating Population Growth Density Dependence vs. Independence Conservation Biology 2 What caused the demise of Easter Island’s human population? 3 Major Characteristics of a Population Populations are dynamic Change in response to environmental pressures Changes include 1. Size (# of individuals) 2. Density (# of individuals in certain space 3. Dispersion (spatial pattern such as clumping, uniform dispersion, or random dispersion) 4. Age distribution (proportion of individuals of each age in a population) 4 Spatial Distribution of Populations for Plants Regular Random Aggregated Regular – seen with trees. Occurs because of light patterns on the forest floor are determined by tree canopy Random – based on wind, animal or other forms of seed dispersal Aggregated – plants occur in “clumps”; plants may aggregate to survive 5 Population Dynamics Changes are referred to as population dynamics Respond to • Environmental stress • Changes in environmental conditions 6 FACTORS THAT INCREASE OR DECREASE POPULATIONS • • Natality - Production of new individuals. Referred to also as births or B Fecundity - Physical ability to reproduce. Fertility - Measure of actual number of offspring produced. Immigration - Organisms introduced into new ecosystems. Referred to by letter I 7 Mortality, Survivorship, and Emigration • • Mortality - Death Rate or D Survivorship - Percentage of cohort surviving to a certain age. Life expectancy - Probable number of years of survival for an individual of a given age. - Increases as humans age. Life Span - Longest period of life reached by a given type of organism. Emigration - Movement of individuals out of a population. Emigration usually applies to humans; few species actually leave the group if they are a herd animal. Represented by letter E. 8 FACTORS THAT REGULATE POPULATION GROWTH • • • • Intrinsic factors - Operate within or between individual organisms in the same species. Extrinsic factors - Imposed from outside the population. Biotic factors - Caused by living organisms. Abiotic factors - Caused by non-living environmental components. 9 Biotic Potential and Carrying Capacity • • Biotic Potential Maximum reproductive rate of an organism. Intrinsic rate of increase (r) – rate at which a population would grow if it had unlimited resources 10 Organisms with high r 1. 2. 3. 4. Reproduce early in life Have short generation times (time between successive generations) Can reproduce many times (long reproductive life) Have many offspring every time they reproduce 11 Environmental Resistance and Carrying Capacity • Environmental Resistance Any environmental factor that reduces population growth. • Biotic potential + environmental resistance = the carrying capacity of a given population • Carrying Capacity Maximum number of individuals of any species that can be indefinitely supported in a given area. 12 Population Viability Analysis • Minimum Viable Population is the minimum population size required for long-term viability of a species. 13 Minimum Viable Population If population declines below MVP needed to support a breeding population: 1. Certain individuals may not be able to locate mates 2. Genetically-related individuals may interbreed and produce weak/malformed offspring 3. Genetic diversity may be too low to enable adaptation to new environmental conditions Intrinsic rate of increase will fall and extinction likely 14 Endangered Species Act of 1973 • • • • Purposes of this Act are to provide a means whereby 1. the ecosystems upon which endangered species and threatened species depend may be conserved, 2. to provide a program for the conservation of such endangered species and threatened species, and 3. to take such steps as may be appropriate to achieve the purposes of the treaties and conventions set forth in subsection (a) of this section. 15 Examples of Threatened or Endangered Species under protection • • http://ecos.fws.gov/tess_public/Boxscore.do Why would an organism be counted more than once? Tennessee Yellow-eyed Grass Florida panther Mead’s Milkweed Four petal Paw Paw Short-tailed albatross Pig footed Bandicoot Quino Checkerspot Butterfly 16 First “declared” casualty of Global Warming • • • • • • • • • • • • The Polar Bear (Ursus maritimus) Maturation at 3 to 5 years old Females give birth to one or two cubs Cubs remain with female for 2 1/4 years Females breed every third year Males travel long distances to find females Eat seal and walrus Need ice pack to hunt Current estimated population 20,000 to 25,000 globally Are under protection of Marine Mammal Protection Act of 1972 U.S. shares protection responsibilities with Norway, Russia, Denmark (Greenland) and Canada under international conservation agreement in 1976 Shared, unified management with Federation of Russia, which involves Native Peoples 17 Population Count • • Counting ALL of the members of a population is next to impossible Therefore, you need to develop a method that will give you an estimation of the size of the population 18 Estimation of Population Size • • • Mark and recapture Used by wildlife biologists to determine number of animals in a population for a given community Tagging, tattooing, leg bands, subdermal radio transmitters, paint or other marking substance to mark captured organisms 19 Mark and Recapture By performing a number of mark and recaptures, the field biologist can use the data to estimate the number of organisms in a given population Depending on the species, can take one year or more 20 Estimating Population Laboratory • • • Use washable pen to mark beans (blow on ink to dry it before placing bean back into bag) When lab is completed, remove all beans from bag and wipe off marks with dampened paper towel. Place beans back in the bag. 21 Estimating Population Size • Estimate of total population = (total # captured) x (number marked) total number recaptured with mark Show the math! Then see Ms. P. for the actual number in the bag Continue with the analysis 22 Consider this… • • You take a job where the boss offers you $15.00/hour. You decline, asking the boss to pay you $1.00 the first day, $2.00 the second, and so on, doubling your pay each day you work. Calculate what you would receive for pay on Day 30. Should your boss take this deal? Why or why not? 23 Solve it! • • The deer population in Maryland is doubling at a rate of 5.2% per year Using the equation below, calculate the five year estimated growth for the Maryland deer population if the annual percentage growth rate is 5.2%. The population currently stands at an estimated 250,000 - 70/annual percentage growth rate 24 Rule of 70 • • A quantity grows exponentially when its increase is proportional to what is already there You boss would be a fool to take your request! 25 Density Dependent Factors • • Higher proportion of population is affected as population density increases. Tend to reduce population size by decreasing natality or increasing mortality. Interspecific Interactions - Predator-Prey oscillations Intraspecific Interactions - Territoriality Stress and Crowding - Stress-related diseases 26 DYNAMICS OF POPULATION GROWTH • • Exponential Growth - Growth at a constant rate of increase per unit time. (Geometric) Arithmetic/Logistic Growth - Growth at a constant amount per unit time. 27 Growth to a Stable Population • Logistic Growth - Growth rates regulated by internal and external factors until coming into equilibrium with environmental resources. Growth rate slows as population approaches carrying capacity. S curve 28 Exponential Growth and Doubling Times • Number of individuals added to a population at the beginning of exponential growth is relatively small. But numbers increase quickly as the population, and thus the given percentage of that population, grows. J curve What is an example of a J curve population? 29 Rule of 70 • Doubling Time of a population: 70_____________ annual percentage growth rate. Keep this mind! 30 Money • A common example is compound interest, where $100 invested at 7% per year annual compound interest will double in 10 years! Exponential growth applies to populations, too -- if a population grows at 7% per year, it, too, will double in 10 years. 70/7 = 10 years to double your money! 31 Rule of 70 • • However, to really make some money, it takes time to actually get to a point where you are making real money! Populations are like this too – they start small and then take off! 32 Problem is… • • Unfortunately, exponential growth works against us, too. When populations continue to grow, the impact of growth becomes increasingly significant over time. In other words, because of the nature of exponential growth, "when things get bad, they get bad in a hurry". Example: Maryland Deer population 33 Overpopulation! • Consider a deer population with 100 deer, growing at 7% per year. In 10 years, the population will double to 200 deer, in another 10 years it will double again to 400 people, and ten years after that it will double again to 800 deer. 34 Density Dependent Factors • • Higher proportion of population is affected as population density increases. Tend to reduce population size by decreasing natality or increasing mortality. Interspecific Interactions - Predator-Prey oscillations Intraspecific Interactions - Territoriality Stress and Crowding - Stress-related diseases 35 Example of Intraspecific Competition • • • • • • • • • In the summer of 1980, much of southern New England was struck by an infestation of the gypsy moth (Porthetria dispar). As the summer wore on, the larvae (caterpillars) pupated; the hatched adults mated, and the females laid masses of eggs (each mass containing several hundred eggs) on virtually every tree in the region. In early May of 1981, the young caterpillars that hatched from these eggs began feeding and molting. The results were dramatic: In 72 hours, a 50-ft beech tree or a 25-ft white pine tree would be completely defoliated. Large patches of forest began to take on a winter appearance with their skeletons of bare branches. In fact the infestation was so heavy that many trees were completely defoliated before the caterpillars could complete their larval development. [View!] The result: a massive die-off of the animals; very few succeeded in completing metamorphosis. Here, then, was a dramatic example of how competition among members of one species for a finite resource — in this case, food — caused a sharp drop in population. http://home.comcast.net/~john.kimball1/BiologyPages/P/Populations2.html 36 Stress and Crowding • • Stress causes cortisol to increase in the body This increases blood pressure, heart rate Causes body to age faster, increasing rate of illness Crowding increases probability of being infected by transmissible diseases also increases stress on immune system, lowering immunity - Example: Black Plague epidemic more prevalent in major cities then in smaller villages 37 Density-dependent factors are impacted by Biotic Factors Reproductive rate Niche type (generalized or specialized) Food supply Habitat Competition for resources Ability to hide or defend against predators Ability to resist disease and parasites Ability to migrate and live in other habitats Ability to adapt 38 Density Independent Factors • • • Constant proportion of the population is affected regardless of population density. Tend to be abiotic components. light temperature chemical environmental (optimal level of critical nutrients) Do not directly regulate population size. 39 Density-independent checks on population growth Include: • Tornados • Hurricanes • Droughts • Floods • Freezes 40 Increase or Decreasing Population Size • • Depends on both biotic and abiotic factors Consider this: the snowfall in Colorado is higher than normal, causing problems for humans, animals and plant life. However, how will this snowfall prove auspicious come spring? 41 Population Oscillations • • Overshoot - Measure of extent to which population exceeds carrying capacity of its environment. Ex. Easter Island Dieback - Negative growth curve. Severity of dieback generally related to the extent of overshoot. 42 Population Curves found in Nature • Four general types: Stable Irruptive Irregular Cyclic 43 Stable Growth • • • Population fluctuates slightly above and below it’s carrying capacity Characteristic of many species in undisturbed tropical rain forests where there is very little variation in avg. temp and rainfall Most organisms that enter a new habitat 44 Irruptive Growth • Malthusian Growth (Irruptive) - Population explosions followed by population crashes. Malthus concluded human populations tend to grow until they exhaust their resources and then crash. Example: Easter Island, Lemmings 45 Irregular Growth • • • No recurring pattern of population size change Considered “chaotic” May be caused by chaos in the environment • 46 Cyclic Growth • • • Can be due to top-down control or bottom-up control Here, depends on number of lynx for topdown or availability of food for hares for bottom-up Ex: Fir-Moose-Wolf populations on Isle Royale 47 Growth Rate Study of Sea Pines Deer • • • • Expanding populations of deer affected by shrinking habitats due to human development Only controls are parasites, lack of feed and auto collisions *Deer affected by parasites such as ticks Culling populations important to stop dramatic increases in populations People dislike the selective “culling” by sharpshooters and bow hunters, said as natural reserve cannot do this Use of immunocontraception PGF2a Court case to save the deer still pending 48 Growth Rate Studies • • • • Determine population size of Sea Pines Deer Growth expected Compare your data to published projections Evaluate data/analyze/conclusion 49 Calculation Formulae Part 1 • • • • • • • • r = intrinsic rate of increase r = ((lnP2 – lnP1)/t) x 100 Where P1 = population at time one P2 = population at time two ln refers to natural log t = number of years Doubling time t = 0.693/r 50 Example • • • • • r = ((lnP2 – lnP1)/t) x 100 = ((ln120-ln70)/50 x 100 = ((4.487 – 4.248)/50) x 100 = 0.53/50 x 100 = 1.0779 or 1.08% 51 Calculation Formulae Part 2 • P = P0 ert where P = final population P0 = initial population e = don’t worry about this r = rate of increase for 1998 – 1999, which is 33.6% or 0.0336 t = time (for this, number of years) 52 Example for years 0 to 1 P = 500 e(.3364)(1) • = 500 .3364 Now punch in .3364, then punch INV, then ln (that is, you are taking the inverse of the natural log of .3364) = 500 ( 1.399) = 699.949 or 700 (round up or down to nearest whole number) • 53 • • • • • • • Malthusian Strategies – r Strategy (Barrons 164 Short life • Adapted to unstable environment. Rapid growth • Pioneers, colonizers Early maturity Many small offspring • Niche generalists • Prey Less parental care • Regulated mainly by Little investment in extrinsic factors. individual offspring. OpportunisticAble to • Low trophic level colonize new areas • Type III survivorship rapidly curve 54 Examples of r strategists • • • • • • • • • • Bacteria Most fish species (ID a fish that is a r strategist) Mollusk species Amphibian species Most reptile species Rodents Rabbits Most insects (grasshoppers, flies, butterflies, etc.) Weeds Trees 55 Logistic Strategies or K strategy (Barrons 164) • • • • • • Long life Slower growth Late maturity Fewer large offspring High parental care and protection. High investment in individual offspring. • • • • • • • Adapted to stable environment. Later stages of succession. Niche specialists Predators Regulated mainly by intrinsic factors. High trophic level Type I or III survivorship curve Considered a more “progressive” evolutionary strategy 56 Examples of K strategists • • • • Primates, including humans, gorillas, chimpanzees Elephants and Rhinos Turtles Orchids 57 Query • • Which type of organisms, r or K, will benefit from global warming? Consider the following in your answer Change in climate Change in habitat Effects on organisms Nature of r and K strategists 58 Survivorship Curves (Barrons 161) • Four general patterns: Full physiological life span. Probability of death unrelated to age. Mortality peaks both early and late in life. Mortality peaks early in life. 59 Survivorship Curves • • • Type I or a – seen in elephants and humans; K strategists; lower death rate; fewer offspring, high degree of parental care Type II or b – amphibians; death is likely no matter what the age Type III or d – seen in fish and oysters; r strategists; high death rate due to form of reproduction (usually external) and lack of parental care in early formation 60 • • • • • The vertical axis gives the fraction of survivors at each age. Curve A is characteristic of organisms that have low mortality until late in life when aging takes its toll. Cure B is typical of populations in which such factors as starvation and disease obscure the effects of aging, and infant mortality is high. Curve C is a theoretical curve for organisms for which the chance of death is equal at all ages. This might be the case for organisms that do not age (some fishes) or those (e.g., many songbirds) that suffer severe random mortality throughout life. K-strategists usually have survivorship curves somewhere between A and C. Curve D is typical of organisms, oysters for example, that produce huge numbers of offspring accompanied by high rates of infant mortality. Many r-strategists have such a curve. Comparision of Survivorship Curves 61 Life Tables and Organisms • • Life tables – give information on the survivorship of organisms at each part of life Used by insurance companies to determine the relationship of a client’s age and likelihood they will pay enough in insurance premiums to cover the cost of the policy. Can also be used to create age-sex diagrams, calculate age-dependency ratios, and other information that gives a “picture” of a species “life history” 62 Human Population Ecology: Demography In this laboratory you will calculate, analyze research differences in mortality rates in the human population before and after 1950. Use of cemetery data for laboratory, because humans keep data records of their natalities and mortalities. 63 Reasons for Human Mortalities Before and After 1950 Before 1950 After 1950 64 Develop a Hypothesis Regarding Mortality based on Time Period of Death and Gender 65 Select one of these cemeteries to obtain data! • • • • http://www.interment.net/us/ Select a county in Maryland (each person take a different one) Select a cemetery (you may need more than one cemetery to collect all your data) Write down data for 80 people in the specific data table based on Females who died before 1950 Females who died after 1950 Males who died before 1950 Males who died after 1950 Each student will collect data for 80 individuals! Calculate age at death (Year of death – Year of Birth) Do not collect information for people who actually died in 1950!!! (Why?) We will use this information to calculate the data for Table 2 AND to create a graph of the data for the ENTIRE CLASS. 66 Calculating Survivorship Column A Mortality –number of deaths for that age cohort or interval from everyone; make sure to tally the total number of deaths at the bottom of the column 2. Column B Alive – subtract the number who died in A from the number of individuals alive at the beginning of the age interval. You need to get this info from everyone and tally the number up. 3. Column C Survivorship – leave empty. We will calculate this once we have collated everyone’s data. 1. 67 Raw Data • • • • • • You will be given a master sheet for each gender and death time (before or after 1950) Write down all the data from the individuals from the computer screen Add up information for each age cohort Total up Column A for each master sheet Calculate Column C – Divide total for age cohort in Column B by the TOTAL at the bottom of column A. This is the Survivorship for that age cohort. 68 Graphing the data • • Make a graph with Y axis as survivorship and each age cohort as the X axis. There will be 4 separate lines on the graph Females who died before 1950 Females who died after 1950 Males who died before 1950 Males who died after 1950 69 When you are finished Both the graph and the essay for this lab will be part of your exam grade: • Answer the five questions from the laboratory in an ESSAY format. • Use good thinking and writing skills. • Directly address the data from the lab • Work MUST be original • Email your essay to www.turnitin.com by midnight, 1/21 • Hand in the graph, with your name on it, before the exam begins on Monday, 1/22. 70 Questions to Address 71 Conservation Genetics • • • Genetic Drift Random reduction in gene frequency. Changes gene pool of population Founder Effect Few individuals start a new population. Smaller gene pool. Limits genetic differences Can see increased effects of mutations Demographic Bottleneck Few individuals survive catastrophe. - Inbreeding Mating between related individuals. 72 Genetic Drift • • • " Random change in gene frequency within a population" (Meffe et al.) Not necessarily adaptive Stronger in small populations 73 Founder Effect • • • • • "The establishment of a new population by a few original founders which carry only a small fraction of the total genetic variation of the parental population." (Ernst Mayr) Over time, the unique traits become found throughout the population Amish Fugate family Can also occur in genetic drift, although without the new population 74 Demographic Bottleneck • • • • • • • Population suffers reduction in size and then recovers Random losses of genetic diversity Usually associated with catastrophic events or diseases Genetic variation doesn't rebound from a decrease as quickly as population size. Examples: Irish Potato famine emigrations and deaths changed the population of Ireland Mass wasting disease in deer populations 75 Metapopulations • A collection of populations that have regular or intermittent gene flow between geographically separate units. Bay Checkerspot Butterfly - Source - Sink Model 76 Source-Sink Model • • Some habitats become sources from which surplus population migrates to less suitable habitats that act as sinks for the surplus populations. To a certain degree, some countries (e.g., Italy) with a human reproductive rate below the replacement rate are serving as sinks for countries (especially those nearby) with expanding populations and increasingly scarce resources. 77 Conservation Biology • • • • Science of protecting and managing Earth's biological diversity First seen in 18th and 19th C. Germany and India The term conservation came into use in the late 19th cent. and referred to the management, mainly for economic reasons, of such valuable natural resources as timber, fish, game, topsoil, pastureland, and minerals, and also to the preservation of forests (see forestry), wildlife (see wildlife refuge), parkland, wilderness, and watershed areas. In recent years the science of ecology has clarified the workings of the biosphere; i.e., the complex interrelationships among humans, other animals, plants, and the physical environment. 78 Conservation Biology • • • • Species can be considered to have an intrinsic value. That is, the survival of a species may be viewed to be in the interest of the species itself, without regard for the utilitarian benefits to humans. In this view, non-human populations are perceived to have interests, including an interest in their own continued survival. This view is espoused by deep ecology, which shifts emphasis away from the anthropocentric reasons for conservation and species survival. 79 CONSERVATION BIOLOGY • Island biogeography - Small islands far from a mainland have fewer terrestrial species than larger, closer islands. MacArthur and Wilson proposed that species diversity is a balance between colonization and extinction rates. 80 Introduction of Non-native Species • On islands, can devastate the delicate balance within a community, upsetting the food web. Rabbits in Australia Rats and cats on the Galapagos Islands Rats, snakes and mongooses on Hawai’I 81 Removing Exotic Species • • • Very costly to remove exotic species once they are established May take a long time for re-establishment of the original community May never be the same as before the exotic species 82 Extinction of Species • • • • Extinction of a species is irreversible. An extinct species represents a lost resource of unknown value. Although the net value of any one species is virtually impossible to represent in pure numerical or monetary figures, financial incentives for conservation of many individual species can be demonstrated. Ex: Tropical rain forest plant species that could be used for medicines can be conserved by preserving the forest. 83 Summary • • • • • • Dynamics of Population Growth Exponential vs. Arithmetic Growth Malthusian vs. Logistic Growth Population Increase Population Decrease Survivorship Regulating Population Growth Density Dependence vs. Independence Conservation Biology 84 85