Lecture 14 Biomes Flashcards
Ecosystem function measured by
Net primary productivity - biomass produced by primary producers
Nutrient mineralisation
(available N in soil)
Carbon sequestration (C sinks)
Decomposition
Seagrass meadow (Posidonia oceanica)
Stores the most carbon in top m of soil. Living material reduces water movement and captures drifting detritus. Dead material resistant to decomposition. Seagrass “mattes” retain sediments and protect beach from erosion
Other environments with high C storage
Tundra, boreal forest, salt marshes
All due to low decomposition rates
Role of biodiversity in ecosystems
Co-occurring species occupy diff niches
E.g. access diff types and depths of soil Nitrogen
More species - more individuals accessing resources
Total plant cover increases w/greater species richness (as seen in cedar creek grass plots USA) available N used more efficiently and remaining N in soil declines
Niche packing
Niche complementarity
Sampling effects
Can contribute to pos BD(biodiversity) to EF (ecosystem function) relationship
More species added to system
Relationships between biodiversity and ecosystem function BD-EF
Vary among species and measure of function
Positive high redundancy - lots of species doing the same thing - loss of diversity at high level does not lead to large reduction in function until critical low reached
Positive low redundancy - loss of diversity at high levels leads to large reduction in function - further loss has less effect (as monoculture establishes)
Positive proportional loss - each species loss leads to equal loss in function (no compensation)
Negative relationship - common in observational studies w/realised diversity
No relationship
Negative proportional - every species lost leads to proportional increase in function.
Faster growing species
Faster growing species outcompete others have neg diversity increased productivity
Large impact species
Keystone
Strong ecosystem wide effects disproportionate to their size e.g. wolves in Yellowstone NP
Foundation
Large and abundant so have large ecosystem effects e.g. trees and seagrass
Engineering species
Physically alter environment e.g. beavers
Keystone and foundation species control net primary production through food web.
Keystone predators top down. Resources affect primary producers bottom up. Trophic cascade pattern in Yellowstone could also be bottom up from aspen recovery - more manipulative experiments required
Sea otters and kelp forests
Sea otters consume urchins that graze kelp maintaining kelp populations
Loss of otters leads to urchin overrun areas known as urchin barrens where kelp is unable to establish itself - effectively an urchin desert
Alternative stable states
Diff self replacing communities in ecosystem can dominate
Shifts between them occur at large perturbations
Once shifted state is stable and only a large perturbation can shift system back - phase may be discontinuous
Kelp state maintained: predator abundance controlled by otters limiting urchin migration and grazing
Barren state maintained: predator abundance urchins settle fertilise and recruit their destructive grazing prevents successful kelp recruitment
Alternate stable state
Diff states of ecosystem as a theoretical landscape. In the kelp/barren example sea otters are a system variable. Shifting the system to a new state - over a ‘peak’ to a new ‘hollow’
community can also be shifted to another state if the landscape itself changes (parameter/enviro factor) changing the curve
Eutrophication
Eutrophication in shallow lakeside to nitro/phospho fertilisers:
Overabundance of nutrient in water leading to algal bloom
Hysterisis
Past effects influence future trajectory, return to initial state cannot be achieved simply by reversing initial perturbation - the ‘trough’ may be too deep to return from
Ecosystem summary
Defined as : all interacting organisms in an area and their abiotic environment
Assimilation, production and trophic efficiency set limits on energy higher up trophic levels and biomass that can be supported: limits special abundance
Function influenced by biodiversity
Can shift to alt stable state after perturbation
Hysteresis : shift back to former state not possible w/ simple reversal of perturbation