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ecosystem ecology
how energy and elements flow, considering both biotic and abiotic factors
trophic pyramid
autotrophs- primary producers—capture ambient energy. they are at the bottom of the energy pyramid
primary consumers- eat autotrophs, 2nd from bottom
secondary consumers- 3rd from bottom
tertiary consumers- top
more energy available at the base of the pyramid
a lot of this energy is lost to physiological maintenance and activity (5-20% survives each level)
animals are less metabolically efficient than palnts so a lot of energy may be lost to movement or high metabolic rates
Decomposers and scavengers use energy NOT consumed by higher trophic levels
Parasites- use energy of host, not conventionally considered at higher trophic levels
animals can eat at multiple trophic levels
predators at higher trophic levels
require high productivity habitats
forage over huge areas
are less abundant than species at lower trophic levels
assimilation efficiency
ratio of assimilation (energy gained) to ingestion (total energy in food)
prey is higher than plants/seeds
net production efficiency
ratio of energy contained in production (growth and offspring) to total assimilated energy
Higher net production efficiency means higher biomass production
ectotherms have larger efficiency
higher metabolic rates = lower effiiciency
lower temperature = greater efificiency, higher = lower (so temperate plants have higher efficiency compared to tropical)
Deritus
dead biomass
going up the trophic pyramid, decomposition of deritus returns energy and nutrients back into a form usable by primary producers
is really hard to digest, so it slows energy movement
allochthonous input
energy/nutrients that is produced outside an ecosystem and is transported in
very useful in low-productivity environments
plants deposit carbon underground by
dying → their roots die and remain in soil
Plants’ carbon is taken by mutualists and parasites in the soil
recalcitrant carbon
organic carbon that resists breakdown, mostly found in soil but also some in ocean sediment
is not involved in carbon cycle
labile carbon
organic carbon that is readily metabolized and moved along the carbon cycle
Sources of CO2
CO2 can dissolve in ocean to become carbonic acid, lowering pH of sea water
it can exist in minerals such as CaCO3 (calcite and limestone) and MgCO3 (dolomite) → releases out from these into environment
Photosynthesis moves CO2 into the ground
Respiration decomposition moves CO2 out via fires, harvesting/herbivory, and pathogen
photosynthesis
converts light energy into chemical energy
rubisco- enzyme linked to photosynthesis
Plants control photosynth. by opening and closing their stromata (takes energy so it is a tradeoff)
by opening their stromata, they can absorb CO2 and emit O2 + H2O
resources controls- CO2, water, light, nutrients
Conditions controls- temperature
net carbon gain
measures the energy sequestered from carbon in plant tissue
used in place of NPP for an individual plant or area of ecological habitat
units- mass/unit area*year
varies with climate
carbon use efficiency
fraction of photosynthesized C that goes into NPP
decreases with stand age (age of the plant) and amount of non-photosynthetic tissue (less leaves = less photosynthesis)
ranking for net primary production in ecosystems (high to low)
wetland- not limited by water or temp
tropical wet forest, cultivated land
temperate forest
tropical dry forest
tropical woodland
boreal forest
temperate steppe
tundra
desert (limited by water and temperature)
NPP is controled by
temperature -growing season length and nutrient supply
precipitation- water supply
vegetation type
soil type- water and nutrient supply
decomposition
physical and chemical breakdown of dead organic matter (litter and soil)
mostly occurs through microbial respiration
main decomposers-bacteria, archea, fungi, soil fauna
decompsition controls
temperature
moisture
pH
Soil biota
Litter chemistry- defensive compounds, C:N ratio (rubsico), lignin (wood that breaks down slowly), traits to reduce water loss
synergistic
permafrost
soil that never thaws
is where a lot of carbon is locked up
as temperatures rise, it thaws and releases CH3 into the atmosphere, which causes climate warming (positive feedback system)
nitrogen cycle
N2 is. 78% of atmosphere, is innert.
N2 reaches soil or water through nitrogen fixation by microbes
plants and algae absorb nitrogen as either NO3 or NH3
ammonification
breakdown of proteins, creating NH3 or NH4 as a product
all organisms do some degree of ammonification, but soil fungi and microbes do a lot of it in nutrient cycling
nitrification
the 2 separate reactions going from NH3 to NO2 and NO2 to NO3
NH3 by nitrosomonas in soil, Nitrosococcus in ocean
NO2 by nitrobacter in soil, Nitrosococcus in ocean
denitrification
occurs under anaerobic conditions, where gaseous NO forms from NO3
NO can then become N2
NO and N2 denitrify soil or water because they are unusable nitrogen sources for primary producers
Immobilization
take up of N by microbes, locking up N in organic forms inaccessible to plants
soil microbes require both C and N, given the high C:N ratio
Microbes may metabolize soil nitrogen and lock it into their own biomass
controls over litter decomposition
high nitrogen:carbon means it will break down fast, low breaks down slow
nitrogen cycles rapidly
nitrogen can get stuck in leaf litter, less available for standing plants
Haber bosch process
N2 + 3H2 = 2NH3
used for fertilizer production
largest source of reactive nitrogen (followed by biological N fixation and then fossil fuel burning)
terrestial ecosystems
land based community of organisms and the interactions between biotic and abiotic components in a given area
nutrient enrichment decreases plant diversity in these ecosystems
gulf of mexico
Gulf is a semi-enclosed basin, acting as a sink for the draining terrestrial ecosystems across 31 states
agricultural run off from terestrial ecosystems flow into the gulf, causing eutrophication (seasonal deadzone- no O2)
sediment flow- rivers carry sediment from inland to coast
deadzones
nitrogen saturation / biological deserts
excess NO3 washes out of soil, pulling essential nutrients out of soil
areas may be high in competitive exclusion, species loss, leading to silent zone
denitrification cycle is imbalanced in these areas because of saturation of nitrogen
turns into nitrous oxide rather than N2
total nitrogen deposition
reactive nitrogen is related to high population density, intensive agriculture, and industrial activity
causes loss of biodiversity
soil acidification
leaks into deadzones
to improve-
Reduce input- make N use more efficient
reduce transport of reactive N to rivers and ground water
maximize denitrification to its N2 end product
richness
number of species present
when there is imperfect detection, you’d use species accumulation curves
evenness
equity of relative abundances
estimated through formulas
high evenness- the species that are present have similar abundances
low evenness- large skew in abundances of species
detection
used to quanti
species accumulation curves
show relationship between sampling intensity on x-axis and species/taxonomic richness on y-axis
Sampling intensity increases = probability of finding more species initially increases but it levels off since the possibility of finding more species is rare
rarefraction
interpolates to standardize comparisons of species richness to a common number of individuals
compares richness given diffeerent sampling intensities among communties
asymptotic estimators
extrapolate to estimate species richness given imperfect detection
estimates richness of communities by extrapolating relationship between number of individuals collected
competition
reduces biological diversity
superior competitors can eliminate inferior
intensity of competition depends on number of either competitor
predation facilitates coexistence in guilds where competition alone causes inferior competitors to be eliminated
apparent competition
effect whereby two noncompeting prey support the predator population
either prey supporting predator population can indirectly increase predation on other species
apparent mutualism
effect whereby two noncompeting prey overwhelm the predator numerically
possible when predator exhibits negative density dependence (predator interference)
Keystone predators
predators that have a large impact on the ecological community (species richness, abundances) or ecosystem (energy, elemental flow)
keystone species
any species that has disproportionately large impact on a community or ecosystem relative to its own abundance
trophic cascade- “domino effect”
indirect species interactions that originate with predators and spread downward through food webs
doesn’t require prey consumption
effect cascade- species on lower trophic that aren’t directly consumed are affected by organism, causing cascade at higher trophic level
predators regulate ecological community
loss of top predator: shift in plant community composition
loss of predator causes lower level population to grow high
that population does selective grazing- avoids plants that are well defended
well defended plants grow more abundant → affects ecosystem
loss of top predator- mesopredator release hypothesis
mesopredator- intermediate predator
top predator and mesopredator control population of shared prey
Green world hypothesis
asks, if everything on earth is trying to eat and reproduce, why is the world still green?
plants aren’t limited by herbivores-but light, water, nutrients.
Herbivores are controled by predators → they can’t over-consume vegetation
goes back to the idea of trophic cascades
odd vs even levels
odd levels- each level is controlled by the next level. So, this allows more plants to grow, resisting environmental changes. This is more representative of the green world theory
even levels- there is an intermediate player that is eaten so the herbivores aren’t being depleted enough to keep them from overgrazing. As a result, plants are more depleted.
bottom up effects
opposite of trophic cascade
occurs when there is an abundance of food → limits population size at and above the trophic level
food abundance is tied to primary productivity → can cause spike in prey that is unrelated to primary productivity
top-down and bottom up effects visibility
trophic cascades aren’t visible until researchers remove the predator or the predator goes extinct
bottom-up effects aren’t observable until researchers experimentally increase primary productivity, primary productivity naturally increases in a burst, or if human activity incidentally increases primary productivity
redundancy
multiple species have similar characteristics in a community
affects competition for non-food resources, intraguild predation, ability of prey to avoid predators, and abiotic stress
food chains
show linear relationships linking primary producers to apex predators
used to describe simple ecological communities
food webs
describe complex relationships
used to describe complex interactions with many species
difficult to interpret
simpson index
measure of richness and eveness
probability that 2 randomly chosen individuals belong to different species
D=1/ sum of p²
p is the proportion of ecological community made of i
when community is even D=species richness
alpha, beta, gamma diversity
alpha diversity is within a sampling unit (ecological community)
local diversity, ie. a quadrat, a stream, island
evaluated by richness and evenness
beta measures biodiversity turnover (between sampling units)
change across space or time
Bray Curtis distance/dissimilarity
gamma is across all communities/samples (region)
evaluated by richness and evenness
Bray-Curtis Distance
BC=1-(2Cij/Si+Sj)
Cij- sum of lesser counts (lower abundance) of species shared by both communities
Si- sum of abundances across all communities in i
Sj— sum of abundances across all species in j
higher means more dissimilar while lower means more similar
presence absencee B-diversity
less informative without abundance
turnover- difference in species found in neighboring areas
looks at who is there rather than how many of each species there is
disproportionately driven by presence/absence of widespread species
dispersal
movement of individuals from one area to another
between or within a population
in fungi- passive transportation of spores, plants- seeds or spores, animals- transport in different life stages or active dispersion
helps explain alpha and beta diversity
ways to study dispersal
capture-mark-recapture- capture animal, mark it, release and try to find later
scat of dispersers- collect poop, they know the range of the animal’s existence
wind tunnel experiments- measures how far seeds are strewn as a result of wind turbulence
radiotracking- following animals real time using a transmitter-direct path
drones- real time tracking- direct path
dispersal kernel
probability distribution that characterizes frequency of dispersal to different distances by an organism
experimental or observed
dispersal limitation
inability of species to reach all suitable habits in a defined area
results in poor ability to move very far and/or low connectivity of habitat
dispersal impact on biodiversity
sometimes negative effect on competitive ability
worst competitors can become best dispersers by reaching evnironment that suits them, but then they can die out once species disperses
Janzen Connell Effects
combine dispersal kernels with natural elements to understand the distribution of forest trees
hypothesis- natural enemies prevent recruitment of offspring near their parents, facillitating coexistence among species
gives rise to negative density-dependence, higher population size leads to greater aggregation to natural enemies and regulates tree species
negative density-dependence allows for many competiting trees to coexist (creating higher biodiversity)
observations- most seeds land directly under parent tree. Those are eaten, the seeds that land further are more likely to survive. Predators crowd around the tree → tradeoff
hump is where the maximum recruitment happens → higher survival, far enough to hide from predators but close enough to have seeds
effect prevents one species from taking over a patch of forest
Immediate disturbance hypothesis
immediate frequencies of disturbance events will prevent competitively dominant species from eliminating competitively subordinate species
assumes that populations of competitively dominant species grow slower than ruderal species
assumes that ruderals are better dispers
high disturbance means tha ruderals (sturdiest/fastest growing species) dominate (low diversity) while low means best competitors dominate (low diversity) → we want a happy medium
local species diversity is maxed when ecological disturbance isn’t too rare or frequent
disturbance
an abrupt reduction in biomass due to some environmental change
anything that rapidly kills
metapopulations
network of populations that undergo extinction and recolonization events in a spatial array of habitat patches
source habitats
high quality patches of habitat
large population size, unlikely to go extinct, individuals disperse to other patches and can recolonize empty patches/inc pop size
sink habitats
low quality patches of habitat
small population size
b < d - high extinction risk without immigration from other patches
long term persistence is only possible through rescue effects
landscape ecology
types of habitats in a landscape
areas of different habitat types
spatial arrangement of habitat types
how organisms use and move through dif. habitats
patch
area of fairly homogenous habitat that differs from surrounding area
used to emphasize where organisms may spend most time or reproduce
corridor
area that facillitates dispersal, often connects different patches
matrix
large background area where patches and corridors are embedded
edge effects
change in population or community structure at the boundary of two habitats
some populations can’t really survive at the center of a habitat, so they live towards the edge, where things are milder
spatial autocorrelation
closer things are more related than distant things
makes it difficult to find out how things are related because basically everything is spatially related
metacommunities
set of communities linked by dispersal of their constituent species
habitate differences among ecological communities
greater differences among habitat characteristics leads to greater beta diversity
greater variety of habitats increase gamma diversity by increasing range of species that can persist there
higher dispersal of species causes
decreased beta diversity because species become more similar with more movement
increased alpha diversity- species reaches more communities, increasing local diversity
concept maps
plot how ideas are related
can show causality, similarities, or strength of relationships
types of maps
range maps- characterize distribution of organisms
outline map- encircle known range
dot map- points where individuals have been found
species distribution modeling and ecological niche modeling
establishes correlation between when species occurs and the environments in the locations
helps estimate index of environmental suitability
species distribution modeling focuses on the geography and realized niche, often used to estimate decrease in range size and shifts in ranges
ecological niche modeling focuses on the niche and defines fundamental niche
pros- easy to implement
cons- uses circular logic and ignores biotic interactions
Buffon’s law
distinct regions that are environmentally similar have distinct biological organisms
challenges idea that environmentally similar but isolated regions have distinct assemblages of mammals and birds
ecological niche modeling
tells you about biological needs of species
historical biogeography
looks at how change in earth’s geography influences modern day distributions and patterns of biodiversity
extended periods of isolation can facilitate distinct organisms
tectonic theory
describes movement of tectonic plates of Earth’s crust in geographic space
the connection of the land allowed the animals to move and distribute, which is why we see simialarities in land even though they are so far apart
Great American Interchange
3 million years ago
mostly movement from north america to south via Panama canal. South American used to be island contient
warmer and easier to thrive in south
pleistocene climate
a lot colder
drier in most of the world
water locked up in ice - lower sea level
latiitudinal biodiversity gradient
species richness usually declines going from the equator to the poles
exceptions- salamander, mariine taxa
hypotheses for why- ecological, historical, etc.
Ahistorical hypothesis for LDG
more energy towards the equator due to solar radiation near the equator, stimulates greater primary productivity, leading to greater plant diversity, longer food chains, and greater consumer diversity
more intense competition is associated with narrow resource use (niche partitioning). Competition among many diverse species keeps competitor abundances low and avoid competitive exclusion
greater kheystone predation
epiphyte load- greater diversity of trees facilitates greater diversity of epiphytes
greater diversity of hosts facilitates greater diversity of parasites
historical hypotheses for LDG
higher speciation rates in tropical habitat (species have formed faster in tropical regions compared to poleward regions)
Lower extinction rates in tropical habitats- they’re more stable environments, lower climate change near equator
tropical habitat is more stable over both short and long time periods
short time period = low seasonality = greater specialization
long time period = tropical habitat remains same over long period = lower extinction rates and greater specialization
tropical conservatism hypothesis vs out-of-the-tropics hypothesis
tropical conservatism hypothesis vs out-of-the-tropics hypothesis
TCH- tropical habitats have been occupied longer for many groups of organisms, and dispersal and adaptation to nontropical envrionments is really rare because they are comfortable
Species will accumulate over time in tropical regions while no colonization occurs in temperate regions
OTT- tropics are a cradle (high rates of speciatioin) and a museum (low rates of extinction)
species are always bubbling over-they originated in the tropics and then expanded towards the poles.
Tropical cradle and museum can be competiting or non competing.
tropical cradle
tropics are a source of new species that then disperse and adapt to non-tropical regions.
tropical museum
tropical taxa have low extinction rate.