Basic Terms And Concepts Flashcards

1
Q

ecosystem

A

community of biotic and abiotic components which are linked by nutrient and energy cycles and interacting as a system

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2
Q

food web

A

the totality of interacting food chains in an ecosystem. It describes how the energy flows in the system.

Food web A diagram or model that shows the feeding connections between all major groups of organisms in an ecosystem.

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3
Q

population

A

group of individuals of the same species, which live in the same demographic region, time and are genetically connected over generations

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4
Q

abundance

A

density of organisms per unit of area/volume

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5
Q

biomass

A

mass of organisms per unit of area/volume, includes all parts of living organisms but not dead organisms or parts thereof

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6
Q

production

A

characteristic of the community, rate of C/energy is fixed, or new biomass is built over time

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7
Q

productivity

A

characteristic of the habitat, says how great the production could be (not community or population)

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8
Q

excretion

A

the elimination of waste products produced by the metabolism (e.g. urine, faces)

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9
Q

exudation

A

diffusive excretion of small molecular compounds (e.g. amino acids, monosaccharides) by plants or phytoplankton

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10
Q

ingestion

A

uptake of material into the digestive system I= A+E

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11
Q

assimilation

A

the incorporating of nutrients into the individual; A=R+P

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12
Q

gross growth efficiency

A

to quantify the efficiency with which organisms convert the energy they acquire through feeding into new biomass. It represents the ratio of the increase in biomass (growth) to the total energy assimilated.

relation between production and ingestion; K1=P/I

higher values indicate more efficient energy conversion and allocation to growth, while lower values suggest a greater proportion of energy is utilized for other purposes.

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13
Q

net growth efficiency

A

to assess the efficiency with which organisms convert assimilated energy into new biomass after accounting for energy losses through respiration and other metabolic processes.

often expressed as a percentage and reflects the effectiveness of an organism in utilizing energy for growth and reproduction

relation between production and assimilation; K2=P/A

higher values indicate a higher proportion of assimilated energy being allocated to net growth, lower values suggest a larger portion of energy is lost through metabolism

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14
Q

efficiency of energy transfer between trophic levels

A

refers to the amount of energy that is transferred from one trophic level to the next in a food chain or food web.

between 0-30%,
Generally, energy transfer becomes less efficient as it moves up the trophic levels, resulting in a pyramid-shaped energy distribution with higher energy levels at lower trophic levels.
the higher organised an organism is, the lower the TTE → lower TL – higher TTE (very generalised)
𝑇𝑇𝐸 = 𝑃𝑝𝑟𝑒𝑑𝑎𝑡𝑜𝑟/𝑃𝑝𝑟𝑒𝑦
(P- Production)

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15
Q

efficiency of assimilation

A

assimilation efficiency AE=A/I

to quantify the proportion of ingested energy (I) that is assimilated by an organism. it is calculated by dividing the assimilated energy (A) by the ingested energy (I).
Assimilated energy represents the portion of ingested energy that an organism is able to digest, absorb, and utilize for metabolic processes, growth, and reproduction. In contrast, the energy that is not assimilated is typically lost as undigested material or through metabolic processes such as respiration or excretion.

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16
Q

necromass

A

mass of dead organic matter, that accumulates within an ecosystem (bark, hardwood…)

  • Included as a component of biomass
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17
Q

primary production (PP)

A

rate at which C is fixed (photosynthetically) (=GPP) or new biomass built (=NPP)

forms the foundation of energy flow and nutrient cycling in ecosystems

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18
Q

secondary production

A

rate of production of heterotrophic organisms per unit of area/volume per time
(can be used for somatic growth/ reproduction)

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19
Q

P:B ration

A

production per biomass: growth rate at population or community level.

The P:B ratio provides insights into the productivity and growth efficiency of organisms or ecosystems and can vary depending on factors such as environmental conditions, species composition, and resource availability.

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20
Q

autochthonous

A

materials produces within the system (einheimisch/ortsständig)

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21
Q

allochthonous

A

material produced outside the system and transported into it (i.e. definition depends on system boundaries)
e.g. leaves or organic matter from trees falling into a freshwater ecosystem from the surrounding terrestrial environment.

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22
Q

gross primary production

A

(GPP) total amount of energy or biomass produced by autotrophic organisms via photosynthesis or chemosynthesis in an ecosystem

total of C fixed

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23
Q

net primary production

A

(NPP) = gross primary production (GPP) - losses due to respiration + exudation/excretion

the amount of energy or biomass that remains after autotrophic organisms have used some of the energy for their own metabolic needs through respiration, representing the available energy for consumption by heterotrophic organisms and for storage in an ecosystem.

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24
Q

gross population growth rate (µ)

A

The gross population growth rate (µ) represents the overall rate of increase or decrease in the size of a population over a specific time period, without accounting for factors such as births, deaths, immigration, or emigration.

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25
Q

Which factors determine the trophic transfer efficiency how and why?

A

(The higher an organism is organised, the higher are the losses due to respiration. Good food quality raises the TTE, because the needed quantity shrinks.

Trophic transfer efficiency: The fraction of total production at a given trophic level that is converted to production at the next trophic level.)

Trophic transfer efficiency (TTE) is influenced by multiple factors. Firstly, TTE generally decreases with higher trophic levels due to energy losses at each transfer. Additionally, prey quality, foraging efficiency of predators, metabolic rates of organisms, temperature, and environmental conditions such as resource availability all play a role in determining TTE. These factors collectively shape the efficiency of energy transfer between trophic levels, impacting the flow of energy and nutrients within ecosystems.

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26
Q

osmotrophy

A

a form of nutrition in which organisms obtain nutrients by absorbing dissolved organic matter or particulate organic matter through osmosis or active transport across their cell membranes.

used by certain protist and fungi

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27
Q

mixotrophy

A

ability to assimilate carbon dioxide (photosynthesis and chemosynthesis) and ingest and digest organic particles (phagotrophy) and dissolved material (osmotrophy).
Mixotrophic organisms have the ability to switch between autotrophy and heterotrophy depending on environmental conditions and resource availability

28
Q

omnivory

A

Ability of organism to consume both plant matter (as a herbivore) and animal matter (as a carnivore).

the trophic position of omnivores is dynamic and can vary based on their diet and the specific ecosystem they inhabit

examples of omnivorous animals include humans, bears, raccoons, and pigs

29
Q

allometry

A

body size correlates with weight specific metabolic rates (ingestion, production, respiration, excretion)

larger organisms generally have lower metabolic rates per unit of body mass compared to smaller organisms (“negative allometry”)

30
Q

Metabolic Theory of Ecology (MTE)

A

Very short: the metabolic rate of organism serve as the fundamental biological rate, which is the base for the most observed pattern in ecology

31
Q

grazing chain/ Grazer food chain

A

Components of a food web that begin with photoautotrophs (in pelagic systems: cyanobacteria, algae, aquatic vascular plants) and pass through herbivores to carnivores.

32
Q

detritus chain/ Detrital food chain

A

Food-web components that begin with particulate organic matter (detritus/dead biodegradable material) or dissolved organic matter, and pass through detritivores (detritus eating bacteria and other microorganisms) to other consumers.

33
Q

grazing vs detritus chains in pelagic/terrestrial habitats

A
  • pelagic: grazing chain more important, because the majority of the NPP is consumed by herbivores (usually complete swallowing of the prey) – less detritus occurs

*terrestrial: detritus chain is more important, because herbivores consume only a small part of the NPP, especially in forests, more detritus occurs. (after beraking it down and releasing nutriets back in the soil, these nutrients are used by the NPPs again.)

34
Q

trophic cascade (HSS)

A

A trophic cascade is a phenomenon in which changes in the abundance or behavior of organisms at one trophic level in a food chain or food web can have cascading effects on multiple other trophic levels. This can occur when the manipulation of top predators or primary producers leads to indirect effects that propagate through the trophic levels, altering community structure and ecosystem dynamics.

35
Q

trophic level

A

integer, says how often substance got assimilated since the last fixation by the primary production

A group of organisms that obtain their food from sources of equal distance from the original source. Autotrophs equal level 1, herbivores equal level 2, primary carnivores equal level 3, and secondary carnivores equal level 4. Species feeding from more than one level may be assigned a fractional trophic level called trophic position based on their diet composition.

36
Q

trophic position

A

determined by the TL/TP the population is feeding on, doesn’t have to be an integer

a species must be assigned to fractional trophic levels, called trophic positions that reflect their diet. For example, an omnivore (e.g., a bear or a crayfish) feeding 50% on level 1 (e.g., autotrophs) and 50% on level 2 (e.g., herbivores) would be assigned a trophic position of 2*0.5 + 3 *0.5=2.5. Thus, models can take into account proportionate differences in the diet composition.

warum trophic level 2 und 3?

37
Q

bottom-up-control

A

regulation of higher trophic levels by the abundance or productivity of lower trophic levels.

38
Q

top-down-control

A

regulation of lower trophic levels by the abundance or activity of higher trophic levels
(many predators → little prey, negative correlation)

39
Q

upper limit to the size ratio between predator and prey

A

max ratio terrestrial: 1000:1,
pelagic: 1.000.000:1 (This larger ratio is partly due to the different dynamics and energy availability in aquatic environments, where smaller prey items, such as plankton or microorganisms, can sustain larger predators through more efficient energy transfer and the abundance of prey resources.)

If the predator is getting to big, the uptake of the prey is not energetically worthwhile anymore

40
Q

„stability” of an ecological system

A

There isn’t one definition of THE stability in ecology. There are just stability properties like persistence, resistance and resilience.
The stability of an ecological system refers to its ability to maintain its structure, function, and overall dynamics in the face of internal or external disturbances. A stable ecosystem can resist and recover from perturbations, maintaining relatively constant population sizes, species composition, and ecological processes over time. Stability can be measured through various indicators, such as resilience (the ability to bounce back after a disturbance) and resistance (the ability to withstand disturbances without significant changes). A more stable ecosystem is generally characterized by balanced trophic interactions, robust food webs, and efficient nutrient cycling, promoting long-term sustainability and biodiversity.

41
Q

Persistence

A

Outlast/Survival of an ecological system over time, including e.g. preservation of the species inventory

Beständigkeit

42
Q

Resistance

A

remain essentially unchanged despite potential disorders/ in response to disturbance or cahnged enviromental conditions

Resistenz

43
Q

Resilience

A

return to the initial/stable state after a change due to temporary disturbances (subsumes elasticity (=speed of return to the initial state) & area of attraction (= all the states from which the initial state is reached again)

Resilienz

44
Q

taxonomic diversity

A

‘Simpson-Index:’

𝐷=1−Σ𝑝𝑖^2𝑠𝑖 =1 (p…proportion of specie)
𝐷𝑚𝑎𝑥=1−𝐷𝑠 (s…specie number)
𝐸=𝐷/𝐷𝑚𝑎𝑥 (E…evenness)
Simpson – relies more on evenness than specie number

‘Shannon-Wiener:’

𝐻′=−Σ(𝑝𝑖log(𝑝𝑖))𝑠𝑖=1
𝐻′=log (𝑠)
E = 𝐻′/𝐻′𝑚𝑎𝑥
SW relies more on species number than evenness

Therefore, the Simpson Index focuses on evenness in species proportions, while the Shannon-Wiener Index places greater importance on the number of species present in the calculation of diversity.

45
Q

The recycling of resources from dead org. material occurs mostly via bacteria and fungi (almost only relevant in terrestrial systems → why?!)

A
  • The most fungi are obligate aerobe
  • There is more dead organic matter in terrestrial systems
  • In terrestrial system fungi are the main decomposers of lignin, in open water ecosystems there isn’t lignin, → white rot

Lignin: phenolisches Makromolekül aus verschiedenen Monomerbausteinen, ein fester, farbloser Stoff, der in die pflanzliche Zellwand eingelagert wird und dadurch die Verholzung der Zelle bewirkt

46
Q

Define biodiversity. How is it measured?

A

Biodiversity is the variety or richness of genes, species, populations and their interactions.
You can measure it with different indices (Simpson, Shannon-Wiener etc.) to compare different ecosystems, habitats etc…

47
Q

How does biodiversity influence ecosystem functions and their spatial-temporal variability? What are the mechanisms?

A

Stability of ecosystem function increases with diversity, at first linear, then weaker → high biodiversity → low variability of ecosystem functions

The reasons are buffer mechanisms:
Compensatory mechanism between individual populations, positive covariance → less stable; negative covariance → more stable

Portfolio effect: the more individual populations the higher the probability of asynchronous fluctuations → negative covariance

Insurance Hypothesis: with high diversity the probability of an occurrence of different species with the same functions increases (negative covariance)

Facilitation: one species benefits from another

Complementarity: different niches

Jansen-Cornell effect: Probability of survival for seedlings of a plant (this hypothesis was postulated for tropic trees) increases with the distance to the next adult individual… one reason for the species richness in the tropes

48
Q

factors influencing biodiversity: latitude

A

diversity is decreasing from the tropics to the poles

49
Q

factors influencing biodiversity: extreme habitats

A

extreme habitats are low on species number, but (with enough productivity) rich in individuals and vice versa, temperate habitats are more diverse and often have fewer individuals per species

50
Q

factors influencing biodiversity: productivity

A

productivity of the habitat: unimodal curve, maximum at medium productivity, with low productivity only specialist survive, with high productivity strong competition for light → plants grow very big → fewer individuals/area, with medium productivity the diversity is the highest, because different species are limited by different resources (Tilman model)

51
Q

factors influencing biodiversity: IDH (Intermediate Disturbance Hypothesis)

A

IDH suggests that ecosystems experiencing intermediate levels of disturbance will have higher species diversity compared to ecosystems with low or high disturbance levels

the diversity is highest (measured by the duration of the generation) at mean interference frequency and Interference intensity;

very frequently and strong disturbances → r-strategists;
very seldom and weak disturbances → K-strategists;
mediate frequency and intensity → both strategists are alternating, new niche dimensions arise

R-strategists are characterized by high reproductive rates and minimal parental care
K-strategists exhibit slower reproduction, extended parental care, and higher investment in fewer offspring

52
Q

factors influencing biodiversity: Temporal fluctuations

A

caused by external influences like seasons, weather, climate; or endogenous processes like predator-prey cycles; change competitive relationships, create new niche dimensions trough adaption

53
Q

factors influencing biodiversity: spatial heterogeneity

A

spatial heterogeneity and unequal access to resources: gradients in resource availability, resource concentration can differ on very small spatial scales → strong building of niches

54
Q

factors influencing biodiversity: Patchiness

A

metapopulation dynamics or source-sink-dynamics; regional coexistence, while local competitive exclusion; migration inhibits extinction

55
Q

factors influencing biodiversity: Insular biogeography

A

Insular biogeography (on near and big islands – highest diversity)

56
Q

factors influencing biodiversity: seed dormancy

A

Seed dormancy, can raise diversity, because of the outlast of bad periods, resettlement after extinction

57
Q

factors influencing biodiversity: predation

A

Predation can increase diversity (parasitism) or decrease it (predator-mediated completion, intraguild predation)

58
Q

Why do we find typically a unimodal relationship between the productivity of a habitat (e.g. determined by nutrient concentrations, precipitation) and biodiversity but a saturating function between production (of new biomass) and biodiversity?

saturating- sättigend

A

‘Different objects’: productivity (=characteristic of the habitat, says how great the production could be) and production (= characteristic of the community, rate of C/energy is fixed, or new biomass is built over time)
‘Different scales’: In experiments we measure the production, there is a positive relationship between biomass production and diversity (complementary mechanism, dominance mechanism and facilitation → overyielding)
Observation of the productivity over different locations get averaged
‘Different dependency’: experiments – total production depends on diversity
observations - diversity depends on abiotic factors and the competition relationships

long story short: they are different things
Unimodal relation between productivity and biodiversity because: with medium productivity the diversity is the highest, because different species are limited by different resources (e.g. Tilman model)
Saturating function between production and biodiversity because: Stability of ecosystem function increases with diversity, at first linear, then weaker → high biodiversity → low variability of ecosystem functions

59
Q

What do bacteria feed on in soil and open water?

A

open water: bacterioplankton - osmotrophy of organic content from other organisms, play an important role in the microbial loop and remineralisation of organic compounds (C, N)

some bacteria are autotrophs, or mixing energy sources (mixotrophs)

soil: decomposers, feed on plant material,
lithotrophs & chemoautotrophs, obtain energy from N, S, FE, H,
many of them are nitrogen fixing bacteria, important for N- cycle

60
Q

Trophic guild

A

A group of organisms that share common food sources and common predators

61
Q

Trophic transfer efficiency

A

The fraction of total production at a given trophic level that is converted to production at the next trophic level.

62
Q

Ecological stoichiometry

A

Study of element ratios within biomass in relation to element ratios within food or in the surrounding environment.

study of the balance and flow of elements, particularly carbon, nitrogen, and phosphorus, in ecological systems and how their ratios influence ecological processes, nutrient cycling, and the structure and functioning of ecosystems.

63
Q

Different shape of the trophic pyramid (pelagic vs. terrestrial)

A

When based on biomass, such a diagram takes a pyramidal shape for terrestrial environments whereas it resembles more a column for pelagic ecosystems at least for the lower trophic levels. That is, the laws of nature do not require the pyramidal shape, and a higher trophic level may have the same or even more biomass than a lower trophic level adjacent to it.

In both terrestrial and pelagic ecosystems, exceptions to the pyramidal shape can occur, with higher trophic levels potentially having comparable or even greater biomass than adjacent lower trophic levels.

pelagic: higher biomass in higher TL, terrestrial: higher in lower TL

adjacent- angrenzend

64
Q

POM

A

particulate organic matter (POM, detritus)

also designated as particulate organic carbon (POC)

65
Q

DOM

A

dissolved organic matter (DOM)

also designated dissolved organic carbon (DOC)

66
Q

efficiency of consumption

A

Consumtion Efficiency = In / Pn-1 (n=Trophic level)

calculated by dividing the ingested energy at a particular trophic level (In) by the production at the previous trophic level (Pn-1).
A higher consumption efficiency value suggests that a larger proportion of energy produced at the lower trophic level is being consumed and utilized by organisms at the higher trophic level.

67
Q

I = A + E = P + R + E

A

Ingestion( I ) = Assimilation A + Excretion E = Production P + Respiration R + Excretion E