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Biodiversity, Species Interactions, and Population Control Chapter 5 Core Case Study: Southern Sea Otters: Are They Back from the Brink of Extinction? Habitat Hunted: early 1900s Partial recovery Why care about sea otters? • Ethics • Keystone species • Tourism dollars 5-1 How Do Species Interact? Concept 5-1 Five types of species interactions—competition, predation, parasitism, mutualism, and commensalism—affect the resource use and population sizes of the species in an ecosystem. Species Interact in Five Major Ways Interspecific Competition Predation Parasitism Mutualism Commensalism Most Species Compete with One Another for Certain Resources Competition Competitive exclusion principle 4. Competition & Predation Interspecific competion results because of niche overlap = overlap in requirements for limited resources. Types of Competition: interference competition: one species limits another species' access to a resource; e.g., hummingbirds defending feeding territories. exploitation competition: competing species both have access to a limited resource, but one exploits the resource more quickly or efficiently. Principle of Competitive Exclusion G.P. Gausse, in a classical experiment (1934), showed that two species with identical niches can not coexist indefinitely. This is called the principle of competitive exclusion. Note that when grown together, Paramecium aurelia outcompetes Paramecium caudatum. Most Consumer Species Feed on Live Organisms of Other Species (1) Predators may capture prey by • Walking • Swimming • Flying • Pursuit and ambush • Camouflage • Chemical warfare Predators & Prey What features characterize them? Predators tend to evolve characteristics for efficient capture of prey (keen eyesight, speed, etc.). Prey tend to evolve chacteristics to avoid being eaten (camoflauge, chemical defenses, behaviors that startle predators, etc.). Most Consumer Species Feed on Live Organisms of Other Species (2) Prey may avoid capture by • Camouflage • Chemical warfare • Warning coloration • Mimicry • Deceptive looks • Deceptive behavior Science Focus: Why Should We Care about Kelp Forests? Kelp forests: biologically diverse marine habitat Major threats to kelp forests • Sea urchins • Pollution from water run-off • Global warming Predator and Prey Species Can Drive Each Other’s Evolution Intense natural selection pressures between predator and prey populations Coevolution Types of Species Interactions major types of biotic interactions (continued): symbiosis: a long–lasting relationship in which species live together in intimate association: parasitism: one organism (parasite) lives on part of another organism (host), e.g., flea living on a dog mutualism: two species interacting in a way that benefits both, e.g., lichens consist of algae & fungi that benefit each other (in this example can't live apart); commensalism: one organism benefits from another, but neither helps nor harm that other organism, e.g., epiphyte growing on a tree (epiphyte benefits & tree not effected, unless there are many epiphytes). Some Species Feed off Other Species by Living on or in Them Parasitism Parasite-host interaction may lead to coevolution Parasitism can be viewed as a special type of predation wherein the parasite: 1) is usually smaller than the prey, 2) remains closely associated with the prey over time, & 3) rarely kills its host. 5. Symbiotic Species Interactions Endoparasites live inside their host, e.g., tapeworm living in the gut of a mammal; plasmodium living inside a vertebrate & causing malaria. Ectoparasites live outside their host, e.g., mosquito feeding on the blood of mammal; lamprey attaching to outside of a host fish (see Fig. 9–13). In Some Interactions, Both Species Benefit Mutualism Nutrition and protection relationship Gut inhabitant mutualism Mutualism Mutualism involves a relationship in which two interacting species benefit. obligatory mutualism results when two organisms can not live without each other; example: in lichens an algae provides photosynthesis & a fungi provides a home for the algae; example: Rhizobium bacteria, in legume plant root nodules, fix nitrogen & legume provides carbohydrates & home; example: termites have gut organism that can digest cellulose. In other mutualisms the organisms can live apart, but there is strong mutual benefit in the relationship; example: flowering plants & their pollinators, plant gets pollinated, pollinator gets nectar or pollen to eat; Mutualism There are many more classic examples of mutualism. example: oxpeckers, a type of bird, feeds on the parasitic tics of various large mammals in Africa, such as the black rhinoceros (see Fig. 9–14); example: mycorrhizal fungi live in the roots of various plants; the fungus gets carbohydrates & the plant gets better absorption of nutrients by the fungal mat that extends beyond the roots (see Fig. 9–15); example: the clownfish in the coral reefs of Australia lives among the tentacles of sea anemones; the clownfish gains protection from the stinging tentacles & food scraps when the anemone feeds; the anemone gains protection from various fish that feed on sea anemones (see Fig. 9–16); example: certain species of stinging ants live in acacias; the ants get a home and food in the form of nectar; the acacias get © Brooks/Cole Publishing Company / ITP protection from various herbivores. In Some Interactions, One Species Benefits and the Other Is Not Harmed Commensalism Epiphytes Birds nesting in trees Commensalism Commensalism involves a symbiotic relationship in which one species beneifits while another is neither helped not harmed to a significant degree. example: redwood sorrel, a small herbaceous plant, benefits from growing in the shade of tall redwoods, but the redwoods are not affected; example: epiphytes (such as orchids & bromeliads) that grow on trunk & branches of trees in the tropical rain forest gain a favorable place to live; whereas, at least when epiphytes are not overly abundant, the tree is not affected (see Fig. 9–17). Note that if epiphytes become sufficiently abundant to block light, the tree can be negatively affected, and this becomes an example of competition. © Brooks/Cole Publishing Company / ITP 5-2 How Can Natural Selection Reduce Competition between Species? Concept 5-2 Some species develop adaptations that allow them to reduce or avoid competition with other species for resources. Some Species Evolve Ways to Share Resources Resource partitioning Reduce niche overlap Use shared resources at different • Times • Places • Ways Resource Partitioning Species with similar resource requirements can coexist because they use limited resources at different times, in different ways, or in different places. For example, specialized feeding niches of various birds of coastal wetland enable coexistence of many species. Resource Partitioning © Brooks/Cole Publishing Company / ITP Resource Partitioning Five species of insect–eating warblers are able to coexist in spruce forest of Maine. Each species minimizes competition with others for food by spending at least half its feeding time in a distinct portion of spruce trees (shaded areas); each also consumes somewhat different insect species. Fig. 9–5 © Brooks/Cole Publishing Company / ITP Resource Partitioning Fig. 9–5 (continued) © Brooks/Cole Publishing Company / ITP Character Displacement Over many years coexisting species with similar niches tend to evolve physical & behavioral adaptations to minimize competition. For example on islands where they co–ocurr, species of Darwin's finch have evolved different bill sizes & eat different size prey. 5-3 What Limits the Growth of Populations? Concept 5-3 No population can continue to grow indefinitely because of limitations on resources and because of competition among species for those resources. 1. Characteristics of Populations population dynamics population size population density Dispersion age structure . is the number of individuals in a population at a given time; is the number of individuals per unit area in terrestrial ecosystems or per unit volume in aquatic ecosystems; is the proportion of individuals in each age group (e.g., prereproductive, reproductive, & postreproductive) of a population. is the spatial patterning individuals; Changes in population size, density, dispersion, & age distribution are known as Populations Have Certain Characteristics (1) Populations differ in • Distribution • Numbers • Age structure Population dynamics Populations Have Certain Characteristics (2) Changes in population characteristics due to: • Temperature • Presence of disease organisms or harmful chemicals • Resource availability • Arrival or disappearance of competing species Most Populations Live Together in Clumps or Patches (1) Population distribution • Clumping • Uniform dispersion • Random dispersion Most Populations Live Together in Clumps or Patches (2) Why clumping? • Species tend to cluster where resources are available • Groups have a better chance of finding clumped resources • Protects some animals from predators • Packs allow some to get prey • Temporary groups for mating and caring for young Characteristics of Populations What is the difference between clumped, uniform & random dispersion? Fig. 10–2 © Brooks/Cole Publishing Company / ITP Populations Can Grow, Shrink, or Remain Stable (1) Population size governed by • • • • Births Deaths Immigration Emigration Population change = (births + immigration) – (deaths + emigration) 2. Population Dynamics & Carrying Capacity Population size is governed by births, deaths, immigration, and emigration: [Population Change] = [Births + Immigration] – [Deaths + Emigration] If the number of individuals added by births & immigration are balanced by those lost by deaths & emigration then there is zero population growth; populations vary in their capacity for growth, also known as biotic potential; the intrinsic rate of growth (r) is the rate at which a population will grow if it had unlimited resources. Population Dynamics What are the most important factors that tend to increase or decrease population size? Fig. 10–3 © Brooks/Cole Publishing Company / ITP Carrying Capacity There are always limits to population growth in nature. carrying capacity (K) is the number of individuals that can be sustained in a given space; the concept of carrying capacity is of central importance in environmental science; if the carrying capacity for an organism is exceeded, resources are depleted, environmental degradation results, & the population declines. Populations Can Grow, Shrink, or Remain Stable (2) Age structure • Pre-reproductive age • Reproductive age • Post-reproductive age No Population Can Grow Indefinitely: J-Curves and S-Curves (1) Biotic potential • Low • High Intrinsic rate of increase (r) Individuals in populations with high r • • • • Reproduce early in life Have short generation times Can reproduce many times Have many offspring each time they reproduce No Population Can Grow Indefinitely: J-Curves and S-Curves (2) Size of populations limited by • • • • • Light Water Space Nutrients Exposure to too many competitors, predators or infectious diseases No Population Can Grow Indefinitely: J-Curves and S-Curves (3) Environmental resistance Carrying capacity (K) Exponential growth Logistic growth Exponential vs. Logistic Growth What’s the difference between Exponential & Logistic Growth? Exponential growth occurs when resources are not limiting. Logistic growth occurs when resources become more and more limiting as population size increases. Exponential Population Growth Exponential growth occurs when resources are not limiting. during exponential growth population size increases faster & faster with time; currently the human population is undergoing exponential growth; exponential growth can not occur forever because eventually some factor limits population growth. Logistic Population Growth Logistic population growth occurs when the population growth rate decreases as the population size increases. note that when the population is small the logistic population growth curve looks like exponential growth; over time, the population size approaches a carrying capacity (K). Exceeding the Carrying Capacity During the mid–1800s sheep populations exceeded the carrying capacity of the island of Tasmania. This "overshoot" was followed by a "population crash". Numbers then stabilized, with oscillation about the carrying capacity. Exceeding the Carrying Capacity Reindeer introduced to a small island off of Alaska in the early 1900s exceeded the carrying capacity, with an "overshoot" followed by a "population crash" in which the population was totally decimated by the mid–1900s. Population Curves in Nature Natural populations display a broad diversity of population curves. Stable populations are relatively constant over time. Cyclic curves are often associated with seasons or fluctuating resource availability. Irruptive curves are characteristic of species that only have high numbers for only brief periods of times (e.g., seven–year cicada). Population Curves in Nature Population cycles for the snowshoe hare & Canadian lynx are believed to result because the hares periodically deplete their food, leading to first a crash of the hare population & then a crash of the lynx population. Science Focus: Why Are Protected Sea Otters Making a Slow Comeback? Low biotic potential Prey for orcas Cat parasites Thorny-headed worms Toxic algae blooms PCBs and other toxins Oil spills When a Population Exceeds Its Habitat’s Carrying Capacity, Its Population Can Crash Carrying capacity: not fixed Reproductive time lag may lead to overshoot • Dieback (crash) Damage may reduce area’s carrying capacity Species Have Different Reproductive Patterns r-Selected species, opportunists K-selected species, competitors 3. Reproductive Strategies & Survival Organisms can be divided into two categories of "strategies" for reproduction & survival: r–strategist species, tend to live in recently disturbed (early successional) environments where resources are not limiting; such species tend to have high intrinsic rates of growth (high r); K–strategist species tend to live in environments where resources are limiting (later succession) & tend to have lower intrinsic rates of growth and characteristics that enable them to live near their carry capacity (population size near K). r–Strategist Species Characteristics of r– strategists, including production of many small & unprotected young, enable these species to live in places where resources are temporarily abundant. These species are typically "weedy" or opportunistic. K–Strategist Species Characteristics of K–strategists, including production of few large & well cared for young, enable these species to live in places where resources are limited. These species are typically good competitors. Survivorship Curves Three kinds of curves: late loss (usually K–strategists), in which high mortality is late in life; constant loss (such as songbirds), in which mortality is about the same for any age; early loss (usually r– strategists), in which high mortality is early in life. Genetic Diversity Can Affect the Size of Small Populations Founder effect Demographic bottleneck Genetic drift Inbreeding Minimum viable population size Under Some Circumstances Population Density Affects Population Size Density-dependent population controls • • • • Predation Parasitism Infectious disease Competition for resources Several Different Types of Population Change Occur in Nature Stable Irruptive Cyclic fluctuations, boom-and-bust cycles • Top-down population regulation • Bottom-up population regulation Irregular Humans Are Not Exempt from Nature’s Population Controls Ireland • Potato crop in 1845 Bubonic plague • Fourteenth century AIDS • Global epidemic Case Study: Exploding White-Tailed Deer Population in the U.S. 1900: deer habitat destruction and uncontrolled hunting 1920s–1930s: laws to protect the deer Current population explosion for deer • Lyme disease • Deer-vehicle accidents • Eating garden plants and shrubs Ways to control the deer population 5-4 How Do Communities and Ecosystems Respond to Changing Environmental Conditions? Concept 5-4 The structure and species composition of communities and ecosystems change in response to changing environmental conditions through a process called ecological succession. Communities and Ecosystems Change over Time: Ecological Succession Natural ecological restoration • Primary succession • Secondary succession Some Ecosystems Start from Scratch: Primary Succession No soil in a terrestrial system No bottom sediment in an aquatic system Early successional plant species, pioneer Midsuccessional plant species Late successional plant species Primary Succession Primary succession occurs with time in lifeless areas. examples include succession newly formed islands & succession after the retreat of a glacier; • typically lichens & mosses first colonize bare rock; • later small herbs & shrubs colonize; • finally tree species colonize; • the first species to colonize are termed pioneer species; • the progression of species that colonize with time are commonly termed early, mid, & late successional species. © Brooks/Cole Publishing Company / ITP Primary Succession Generalized physical appearance showing the types, relative sizes, and stratification of plant species in various terrestrial communities or ecosystems. Fig. 9–18 © Brooks/Cole Publishing Company / ITP Primary Succession Primary succession over several hundred years on bare rock exposed by a retreating glacier on Isle Royal in northern Lake Superior. Fig. 9–19 © Brooks/Cole Publishing Company / ITP Primary Succession Greatly simplified view of primary succession in a newly created pond in a temperate area. Nutrient rich bottom sediment is shown in dark brown. Fig. 9–20a © Brooks/Cole Publishing Company / ITP Some Ecosystems Do Not Have to Start from Scratch: Secondary Succession (1) Some soil remains in a terrestrial system Some bottom sediment remains in an aquatic system Ecosystem has been • Disturbed • Removed • Destroyed Secondary Succession Secondary succession occurs where the natural community of organisms has been disturbed, removed, or destroyed. example: "old field succession" in eastern North America, where agricultural fields go through succession from herbaceous plants, to shrubs & early successional trees, to mid–successional forest, to oak– hickory forest; •according to the classic view, succession proceeds until an area is occupied by a climax community, however recent views recognize that succession is influenced by variability & chaotic events such that a single climax is not predictable. © Brooks/Cole Publishing Company / ITP Secondary Succession Secondary succession over 150–200 years in an abandoned farm field in North Carolina. Fig. 9–21 © Brooks/Cole Publishing Company / ITP Secondary Succession Successional changes in the animal community accompany successional changes in the plant community. Fig. 9–22 © Brooks/Cole Publishing Company / ITP Some Ecosystems Do Not Have to Start from Scratch: Secondary Succession (2) Primary and secondary succession • Tend to increase biodiversity • Increase species richness and interactions among species Primary and secondary succession can be interrupted by • • • • • Fires Hurricanes Clear-cutting of forests Plowing of grasslands Invasion by nonnative species Disturbance What is the role of disturbance in succession? disturbance: a discrete event that disrupts an ecosystem or community; examples of natural disturbance: fires, hurricanes, tornadoes, droughts, & floods; examples of human–caused disturbance: deforestation, overgrazing, plowing; disturbance initiates secondary succession by eliminating part or all of the existing community, & by changing conditions & releasing resources. © Brooks/Cole Publishing Company / ITP Science Focus: How Do Species Replace One Another in Ecological Succession? Facilitation Inhibition Tolerance Mechanisms of Succession Both primary & secondary succession are driven by three mechanisms: facilitiation: a process by which an earlier successional species makes the environment suitable for latter successional species; e.g., legumes fixing nitrogen can enable later successional species; inhibition: a process whereby one species hinders the establishment & growth of other species; e.g., shade of late successional trees inhibits the growth of early successional trees; tolerance: a process whereby later successional species are unaffected by earlier successional species. © Brooks/Cole Publishing Company / ITP Changes During Succession During succession species diversity & stratification tend to increase, while growth rates & primary productivity tend to decrease. Fig. 9–23 © Brooks/Cole Publishing Company / ITP Ecosystem Changes During Succession Characteristic Plant size Species diversity Trophic structure Early Succession small low mostly producers Ecological niches few, more generalized low Late Succession large high mixture of producers, consumers, & decomposers many, more specialized high low high high low simple low complex high low high Community organization (# links) Biomass Net Primary Productivity Food web Efficiency for nutrient cycling Efficiency of energy use © Brooks/Cole Publishing Company / ITP Secondary Succession Successional changes in the animal community accompany successional changes in the plant community. Fig. 9–22 © Brooks/Cole Publishing Company / ITP Succession Doesn’t Follow a Predictable Path Traditional view • Balance of nature and a climax community Current view • Ever-changing mosaic of patches of vegetation • Mature late-successional ecosystems • State of continual disturbance and change Living Systems Are Sustained through Constant Change Inertia, persistence • Ability of a living system to survive moderate disturbances Resilience • Ability of a living system to be restored through secondary succession after a moderate disturbance Tipping point 8. Stability & Sustainability Stability has three aspects: inertia (or persistence): the ability of a system to resist being disturbed or altered; constancy: the abilty of a living system to maintain a certain size or state; resilience: the ability of a living system to recover after a disturbance; Signs of poor health or stressed ecosystems: decrease in primary productivity; increased nutrient losses; decline or extinction of indicator species; increased populations of pests or disease organisms; decline in species diversity; •presence of contaminants. Through an understanding of ecology we can grapple with what it means to have sustainable ecosystems. © Brooks/Cole Publishing Company / ITP