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Ecosystems and Restoration Ecology

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1 Ecosystems and Restoration Ecology
Chapter 55 Ecosystems and Restoration Ecology

2 Overview: Cool Ecosystem
An ecosystem consists of all the organisms living in a community, as well as the abiotic factors with which they interact An example is the unusual community of organisms, including chemoautotrophic bacteria, living below a glacier in Antarctica © 2011 Pearson Education, Inc.

3 Figure 55.1 Figure 55.1 Why is this Antarctic ice blood red? 3

4 Ecosystems range from a microcosm, such as an aquarium, to a large area, such as a lake or forest
© 2011 Pearson Education, Inc.

5 Figure 55.2 Figure 55.2 A desert spring ecosystem. 5

6 Energy flows through ecosystems, whereas matter cycles within them
Regardless of an ecosystem’s size, its dynamics involve two main processes: energy flow and chemical cycling Energy flows through ecosystems, whereas matter cycles within them © 2011 Pearson Education, Inc.

7 Concept 55.1: Physical laws govern energy flow and chemical cycling in ecosystems
Ecologists study the transformations of energy and matter within ecosystems © 2011 Pearson Education, Inc.

8 Conservation of Energy
Laws of physics and chemistry apply to ecosystems, particularly energy flow The first law of thermodynamics states that energy cannot be created or destroyed, only transformed Energy enters an ecosystem as solar radiation, is conserved, and is lost from organisms as heat © 2011 Pearson Education, Inc.

9 The second law of thermodynamics states that every exchange of energy increases the entropy of the universe In an ecosystem, energy conversions are not completely efficient, and some energy is always lost as heat © 2011 Pearson Education, Inc.

10 Conservation of Mass The law of conservation of mass states that matter cannot be created or destroyed Chemical elements are continually recycled within ecosystems In a forest ecosystem, most nutrients enter as dust or solutes in rain and are carried away in water Ecosystems are open systems, absorbing energy and mass and releasing heat and waste products © 2011 Pearson Education, Inc.

11 Energy, Mass, and Trophic Levels
Autotrophs build molecules themselves using photosynthesis or chemosynthesis as an energy source Heterotrophs depend on the biosynthetic output of other organisms © 2011 Pearson Education, Inc.

12 Energy and nutrients pass from primary producers (autotrophs) to primary consumers (herbivores) to secondary consumers (carnivores) to tertiary consumers (carnivores that feed on other carnivores) © 2011 Pearson Education, Inc.

13 Prokaryotes and fungi are important detritivores
Detritivores, or decomposers, are consumers that derive their energy from detritus, nonliving organic matter Prokaryotes and fungi are important detritivores Decomposition connects all trophic levels © 2011 Pearson Education, Inc.

14 Figure 55.3 Figure 55.3 Fungi decomposing a dead tree. 14

15 Microorganisms and other detritivores Secondary and tertiary consumers
Figure 55.4 Sun Key Chemical cycling Energy flow Heat Primary producers Primary consumers Detritus Figure 55.4 An overview of energy and nutrient dynamics in an ecosystem. Microorganisms and other detritivores Secondary and tertiary consumers 15

16 Concept 55.2: Energy and other limiting factors control primary production in ecosystems
In most ecosystems, primary production is the amount of light energy converted to chemical energy by autotrophs during a given time period In a few ecosystems, chemoautotrophs are the primary producers © 2011 Pearson Education, Inc.

17 Ecosystem Energy Budgets
The extent of photosynthetic production sets the spending limit for an ecosystem’s energy budget © 2011 Pearson Education, Inc.

18 The Global Energy Budget
The amount of solar radiation reaching Earth’s surface limits the photosynthetic output of ecosystems Only a small fraction of solar energy actually strikes photosynthetic organisms, and even less is of a usable wavelength © 2011 Pearson Education, Inc.

19 Gross and Net Production
Total primary production is known as the ecosystem’s gross primary production (GPP) GPP is measured as the conversion of chemical energy from photosynthesis per unit time Net primary production (NPP) is GPP minus energy used by primary producers for respiration NPP is expressed as Energy per unit area per unit time (J/m2yr), or Biomass added per unit area per unit time (g/m2yr) © 2011 Pearson Education, Inc.

20 NPP is the amount of new biomass added in a given time period
Only NPP is available to consumers Standing crop is the total biomass of photosynthetic autotrophs at a given time Ecosystems vary greatly in NPP and contribution to the total NPP on Earth © 2011 Pearson Education, Inc.

21 TECHNIQUE 80 60 40 20 Snow Clouds Vegetation Percent reflectance Soil
Figure 55.5 TECHNIQUE 80 60 40 20 Snow Clouds Vegetation Percent reflectance Soil Figure 55.5 Research Method: Determining Primary Production with Satellites Liquid water 400 600 800 1,000 1,200 Visible Near-infrared Wavelength (nm) 21

22 Tropical rain forests, estuaries, and coral reefs are among the most productive ecosystems per unit area Marine ecosystems are relatively unproductive per unit area but contribute much to global net primary production because of their volume © 2011 Pearson Education, Inc.

23 Net primary production (kg carbon/m2yr)
Figure 55.6 Net primary production (kg carbon/m2yr) 3 2 1 Figure 55.6 Global net primary production. 23

24 Net ecosystem production (NEP) is a measure of the total biomass accumulation during a given period
NEP is gross primary production minus the total respiration of all organisms (producers and consumers) in an ecosystem NEP is estimated by comparing the net flux of CO2 and O2 in an ecosystem, two molecules connected by photosynthesis The release of O2 by a system is an indication that it is also storing CO2 © 2011 Pearson Education, Inc.

25 Float surfaces for 6–12 hours to transmit data to satellite.
Figure 55.7 Float surfaces for 6–12 hours to transmit data to satellite. Total cycle time: 10 days Float descends to 1,000 m and “parks.” O2 concentration is recorded as float ascends. Figure 55.7 Impact: Ocean Production Revealed Drift time: 9 days 25

26 Primary Production in Aquatic Ecosystems
In marine and freshwater ecosystems, both light and nutrients control primary production © 2011 Pearson Education, Inc.

27 Light Limitation Depth of light penetration affects primary production in the photic zone of an ocean or lake © 2011 Pearson Education, Inc.

28 Nutrient Limitation More than light, nutrients limit primary production in geographic regions of the ocean and in lakes A limiting nutrient is the element that must be added for production to increase in an area Nitrogen and phosphorous are the nutrients that most often limit marine production Nutrient enrichment experiments confirmed that nitrogen was limiting phytoplankton growth off the shore of Long Island, New York © 2011 Pearson Education, Inc.

29 Phytoplankton density (millions of cells per mL)
Figure 55.8 RESULTS 30 24 18 12 6 Ammonium enriched Phosphate enriched Unenriched control Phytoplankton density (millions of cells per mL) Figure 55.8 Inquiry: Which nutrient limits phytoplankton production along the coast of Long Island? A B C D E F G Collection site 29

30 Experiments in the Sargasso Sea in the subtropical Atlantic Ocean showed that iron limited primary production © 2011 Pearson Education, Inc.

31 Table 55.1 Table 55.1 Nutrient Enrichment Experiment for Sargasso Sea Samples 31

32 Upwelling of nutrient-rich waters in parts of the oceans contributes to regions of high primary production The addition of large amounts of nutrients to lakes has a wide range of ecological impacts © 2011 Pearson Education, Inc.

33 This has led to the use of phosphate-free detergents
In some areas, sewage runoff has caused eutrophication of lakes, which can lead to loss of most fish species In lakes, phosphorus limits cyanobacterial growth more often than nitrogen This has led to the use of phosphate-free detergents © 2011 Pearson Education, Inc.

34 Video: Cyanobacteria (Oscillatoria)
© 2011 Pearson Education, Inc.

35 Primary Production in Terrestrial Ecosystems
In terrestrial ecosystems, temperature and moisture affect primary production on a large scale Primary production increases with moisture © 2011 Pearson Education, Inc.

36 Net annual primary production (above ground, dry g/m2 yr)
Figure 55.9 1,400 1,200 1,000 800 600 400 200 Net annual primary production (above ground, dry g/m2 yr) Figure 55.9 A global relationship between net primary production and mean annual precipitation for terrestrial ecosystems. 20 40 60 80 100 120 140 160 180 200 Mean annual precipitation (cm) 36

37 It is affected by precipitation, temperature, and solar energy
Actual evapotranspiration is the water transpired by plants and evaporated from a landscape It is affected by precipitation, temperature, and solar energy It is related to net primary production © 2011 Pearson Education, Inc.

38 Nutrient Limitations and Adaptations That Reduce Them
On a more local scale, a soil nutrient is often the limiting factor in primary production In terrestrial ecosystems, nitrogen is the most common limiting nutrient Phosphorus can also be a limiting nutrient, especially in older soils © 2011 Pearson Education, Inc.

39 Various adaptations help plants access limiting nutrients from soil
Some plants form mutualisms with nitrogen-fixing bacteria Many plants form mutualisms with mycorrhizal fungi; these fungi supply plants with phosphorus and other limiting elements Roots have root hairs that increase surface area Many plants release enzymes that increase the availability of limiting nutrients © 2011 Pearson Education, Inc.

40 Concept 55.3: Energy transfer between trophic levels is typically only 10% efficient
Secondary production of an ecosystem is the amount of chemical energy in food converted to new biomass during a given period of time © 2011 Pearson Education, Inc.

41 Production Efficiency
When a caterpillar feeds on a leaf, only about one-sixth of the leaf’s energy is used for secondary production An organism’s production efficiency is the fraction of energy stored in food that is not used for respiration Production efficiency Net secondary production  100% Assimilation of primary production © 2011 Pearson Education, Inc.

42 Plant material eaten by caterpillar
Figure 55.10 Plant material eaten by caterpillar 200 J 67 J Figure Energy partitioning within a link of the food chain. Cellular respiration 100 J Feces 33 J Not assimilated Growth (new biomass; secondary production) Assimilated 42

43 Figure 55.10a Figure Energy partitioning within a link of the food chain. 43

44 Fishes have production efficiencies of around 10%
Birds and mammals have efficiencies in the range of 13% because of the high cost of endothermy Fishes have production efficiencies of around 10% Insects and microorganisms have efficiencies of 40% or more © 2011 Pearson Education, Inc.

45 Trophic Efficiency and Ecological Pyramids
Trophic efficiency is the percentage of production transferred from one trophic level to the next It is usually about 10%, with a range of 5% to 20% Trophic efficiency is multiplied over the length of a food chain © 2011 Pearson Education, Inc.

46 Approximately 0.1% of chemical energy fixed by photosynthesis reaches a tertiary consumer
A pyramid of net production represents the loss of energy with each transfer in a food chain © 2011 Pearson Education, Inc.

47 Tertiary consumers 10 J Secondary consumers 100 J Primary consumers
Figure 55.11 Tertiary consumers 10 J Secondary consumers 100 J Primary consumers 1,000 J Primary producers Figure An idealized pyramid of net production. 10,000 J 1,000,000 J of sunlight 47

48 In a biomass pyramid, each tier represents the dry mass of all organisms in one trophic level
Most biomass pyramids show a sharp decrease at successively higher trophic levels © 2011 Pearson Education, Inc.

49 Dry mass (g/m2) Dry mass (g/m2)
Figure 55.12 Trophic level Dry mass (g/m2) Tertiary consumers Secondary consumers Primary consumers Primary producers 1.5 11 37 809 (a) Most ecosystems (data from a Florida bog) Figure Pyramids of biomass (standing crop). Trophic level Dry mass (g/m2) Primary consumers (zooplankton) Primary producers (phytoplankton) 21 4 (b) Some aquatic ecosystems (data from the English Channel) 49

50 Turnover time is the ratio of the standing crop biomass to production
Certain aquatic ecosystems have inverted biomass pyramids: producers (phytoplankton) are consumed so quickly that they are outweighed by primary consumers Turnover time is the ratio of the standing crop biomass to production © 2011 Pearson Education, Inc.

51 Dynamics of energy flow in ecosystems have important implications for the human population
Eating meat is a relatively inefficient way of tapping photosynthetic production Worldwide agriculture could feed many more people if humans ate only plant material © 2011 Pearson Education, Inc.

52 Concept 55.4: Biological and geochemical processes cycle nutrients and water in ecosystems
Life depends on recycling chemical elements Nutrient cycles in ecosystems involve biotic and abiotic components and are often called biogeochemical cycles © 2011 Pearson Education, Inc.

53 Biogeochemical Cycles
Gaseous carbon, oxygen, sulfur, and nitrogen occur in the atmosphere and cycle globally Less mobile elements include phosphorus, potassium, and calcium These elements cycle locally in terrestrial systems but more broadly when dissolved in aquatic systems © 2011 Pearson Education, Inc.

54 All elements cycle between organic and inorganic reservoirs
A model of nutrient cycling includes main reservoirs of elements and processes that transfer elements between reservoirs All elements cycle between organic and inorganic reservoirs © 2011 Pearson Education, Inc.

55 Burning of fossil fuels Formation of sedimentary rock
Figure 55.13 Reservoir A Organic materials available as nutrients Reservoir B Organic materials unavailable as nutrients Fossilization Living organisms, detritus Peat Coal Oil Respiration, decomposition, excretion Burning of fossil fuels Assimilation, photosynthesis Reservoir D Inorganic materials unavailable as nutrients Reservoir C Inorganic materials available as nutrients Figure A general model of nutrient cycling. Weathering, erosion Atmosphere Minerals in rocks Water Formation of sedimentary rock Soil 55

56 In studying cycling of water, carbon, nitrogen, and phosphorus, ecologists focus on four factors
Each chemical’s biological importance Forms in which each chemical is available or used by organisms Major reservoirs for each chemical Key processes driving movement of each chemical through its cycle © 2011 Pearson Education, Inc.

57 The Water Cycle Water is essential to all organisms
Liquid water is the primary physical phase in which water is used The oceans contain 97% of the biosphere’s water; 2% is in glaciers and polar ice caps, and 1% is in lakes, rivers, and groundwater Water moves by the processes of evaporation, transpiration, condensation, precipitation, and movement through surface and groundwater © 2011 Pearson Education, Inc.

58 Movement over land by wind
Figure 55.14a Movement over land by wind Evaporation from ocean Precipitation over land Precipitation over ocean Evapotranspira- tion from land Figure Exploring: Water and Nutrient Cycling Percolation through soil Runoff and groundwater 58

59 The Carbon Cycle Carbon-based organic molecules are essential to all organisms Photosynthetic organisms convert CO2 to organic molecules that are used by heterotrophs Carbon reservoirs include fossil fuels, soils and sediments, solutes in oceans, plant and animal biomass, the atmosphere, and sedimentary rocks © 2011 Pearson Education, Inc.

60 CO2 is taken up and released through photosynthesis and respiration; additionally, volcanoes and the burning of fossil fuels contribute CO2 to the atmosphere © 2011 Pearson Education, Inc.

61 Burning of fossil fuels and wood
Figure 55.14b CO2 in atmosphere Photosynthesis Photo- synthesis Cellular respiration Burning of fossil fuels and wood Phyto- plankton Consumers Figure Exploring: Water and Nutrient Cycling Consumers Decomposition 61

62 The Nitrogen Cycle Nitrogen is a component of amino acids, proteins, and nucleic acids The main reservoir of nitrogen is the atmosphere (N2), though this nitrogen must be converted to NH4+ or NO3– for uptake by plants, via nitrogen fixation by bacteria © 2011 Pearson Education, Inc.

63 Denitrification converts NO3– back to N2
Organic nitrogen is decomposed to NH4+ by ammonification, and NH4+ is decomposed to NO3– by nitrification Denitrification converts NO3– back to N2 © 2011 Pearson Education, Inc.

64 Decomposition and sedimentation
Figure 55.14c N2 in atmosphere Reactive N gases Industrial fixation Denitrification N fertilizers Fixation Runoff Dissolved organic N NO3– Terrestrial cycling N2 NH4+ NO3– Aquatic cycling Denitri- fication Figure Exploring: Water and Nutrient Cycling Decomposition and sedimentation Assimilation Decom- position NO3– Fixation in root nodules Uptake of amino acids Ammonification Nitrification NH3 NH4+ NO2– 64

65 Decomposition and sedimentation
Figure 55.14ca N2 in atmosphere Reactive N gases Industrial fixation Denitrification N fertilizers Fixation Runoff Dissolved organic N NO3– NH4+ NO3– Terrestrial cycling Figure Exploring: Water and Nutrient Cycling Aquatic cycling Decomposition and sedimentation 65

66 Fixation in root nodules
Figure 55.14cb Terrestrial cycling N2 Denitri- fication Assimilation Decom- position NO3– Uptake of amino acids Fixation in root nodules Figure Exploring: Water and Nutrient Cycling Ammonification Nitrification NH3 NH4+ NO2– 66

67 The Phosphorus Cycle Phosphorus is a major constituent of nucleic acids, phospholipids, and ATP Phosphate (PO43–) is the most important inorganic form of phosphorus The largest reservoirs are sedimentary rocks of marine origin, the oceans, and organisms Phosphate binds with soil particles, and movement is often localized © 2011 Pearson Education, Inc.

68 Wind-blown dust Geologic uplift Weathering of rocks Runoff Consumption
Figure 55.14d Wind-blown dust Geologic uplift Weathering of rocks Runoff Consumption Decomposition Plant uptake of PO43– Plankton Dissolved PO43– Uptake Leaching Figure Exploring: Water and Nutrient Cycling Sedimentation Decomposition 68

69 Decomposition and Nutrient Cycling Rates
Decomposers (detritivores) play a key role in the general pattern of chemical cycling Rates at which nutrients cycle in different ecosystems vary greatly, mostly as a result of differing rates of decomposition The rate of decomposition is controlled by temperature, moisture, and nutrient availability © 2011 Pearson Education, Inc.

70 Mean annual temperature (C)
Figure 55.15 EXPERIMENT Ecosystem type Arctic Subarctic Boreal Temperate Grassland Mountain A G M B,C D P T H,I S E,F U N L O J K Q R RESULTS 80 70 60 50 40 30 20 10 Figure Inquiry: How does temperature affect litter decomposition in an ecosystem? R U Percent of mass lost K O Q T J P D S N F C I M L A H B E G –15 –10 –5 5 10 15 Mean annual temperature (C) 70

71 EXPERIMENT Ecosystem type Arctic Subarctic Boreal Temperate Grassland
Figure 55.15a EXPERIMENT Ecosystem type Arctic Subarctic Boreal Temperate Grassland Mountain A G M D B,C P T H,I Figure Inquiry: How does temperature affect litter decomposition in an ecosystem? E,F S O U N L J K Q R 71

72 Mean annual temperature (C)
Figure 55.15b RESULTS 80 70 60 50 40 30 20 10 U R O Q K T Percent of mass lost J P S D N F C I M L H Figure Inquiry: How does temperature affect litter decomposition in an ecosystem? A B E G –15 –10 –5 5 10 15 Mean annual temperature (C) 72

73 Decomposition is slow in anaerobic muds
Rapid decomposition results in relatively low levels of nutrients in the soil For example, in a tropical rain forest, material decomposes rapidly, and most nutrients are tied up in trees other living organisms Cold and wet ecosystems store large amounts of undecomposed organic matter as decomposition rates are low Decomposition is slow in anaerobic muds © 2011 Pearson Education, Inc.

74 Case Study: Nutrient Cycling in the Hubbard Brook Experimental Forest
The Hubbard Brook Experimental Forest has been used to study nutrient cycling in a forest ecosystem since 1963 The research team constructed a dam on the site to monitor loss of water and minerals They found that 60% of the precipitation exits through streams and 40% is lost by evapotranspiration © 2011 Pearson Education, Inc.

75 Nitrate concentration in runoff (mg/L) Completion of tree cutting
Figure 55.16 (a) Concrete dam and weir (b) Clear-cut watershed 80 60 40 20 Deforested Figure Nutrient cycling in the Hubbard Brook Experimental Forest: an example of long-term ecological research. Nitrate concentration in runoff (mg/L) Completion of tree cutting 4 3 2 1 Control 1965 1966 1967 1968 (c) Nitrate in runoff from watersheds 75

76 (a) Concrete dam and weir
Figure 55.16a Figure Nutrient cycling in the Hubbard Brook Experimental Forest: an example of long-term ecological research. (a) Concrete dam and weir 76

77 In one experiment, the trees in one valley were cut down, and the valley was sprayed with herbicides
© 2011 Pearson Education, Inc.

78 (b) Clear-cut watershed
Figure 55.16b Figure Nutrient cycling in the Hubbard Brook Experimental Forest: an example of long-term ecological research. (b) Clear-cut watershed 78

79 These results showed how human activity can affect ecosystems
Net losses of water were 3040% greater in the deforested site than the undisturbed (control) site Nutrient loss was also much greater in the deforested site compared with the undisturbed site For example, nitrate levels increased 60 times in the outflow of the deforested site These results showed how human activity can affect ecosystems © 2011 Pearson Education, Inc.

80 Nitrate concentration in runoff (mg/L) Completion of tree cutting
Figure 55.16c 80 60 40 20 Deforested Nitrate concentration in runoff (mg/L) Completion of tree cutting 4 3 2 1 Control Figure Nutrient cycling in the Hubbard Brook Experimental Forest: an example of long-term ecological research. 1965 1966 1967 1968 (c) Nitrate in runoff from watersheds 80

81 Concept 55.5: Restoration ecologists help return degraded ecosystems to a more natural state
Given enough time, biological communities can recover from many types of disturbances Restoration ecology seeks to initiate or speed up the recovery of degraded ecosystems Two key strategies are bioremediation and augmentation of ecosystem processes © 2011 Pearson Education, Inc.

82 (a) In 1991, before restoration
Figure 55.17 Figure A gravel and clay mine site in New Jersey before and after restoration. (a) In 1991, before restoration (b) In 2000, near the completion of restoration 82

83 (a) In 1991, before restoration
Figure 55.17a Figure A gravel and clay mine site in New Jersey before and after restoration. (a) In 1991, before restoration 83

84 (b) In 2000, near the completion of restoration
Figure 55.17b Figure A gravel and clay mine site in New Jersey before and after restoration. (b) In 2000, near the completion of restoration 84

85 Bioremediation Bioremediation is the use of organisms to detoxify ecosystems The organisms most often used are prokaryotes, fungi, or plants These organisms can take up, and sometimes metabolize, toxic molecules For example, the bacterium Shewanella oneidensis can metabolize uranium and other elements to insoluble forms that are less likely to leach into streams and groundwater © 2011 Pearson Education, Inc.

86 Concentration of soluble uranium (M)
Figure 55.18 6 5 4 3 2 1 Concentration of soluble uranium (M) Figure Bioremediation of groundwater contaminated with uranium at Oak Ridge National Laboratory, Tennessee. 50 100 150 200 250 300 350 400 Days after adding ethanol 86

87 Figure 55.18a Figure Bioremediation of groundwater contaminated with uranium at Oak Ridge National Laboratory, Tennessee. 87

88 Biological Augmentation
Biological augmentation uses organisms to add essential materials to a degraded ecosystem For example, nitrogen-fixing plants can increase the available nitrogen in soil For example, adding mycorrhizal fungi can help plants to access nutrients from soil © 2011 Pearson Education, Inc.

89 Restoration Projects Worldwide
The newness and complexity of restoration ecology require that ecologists consider alternative solutions and adjust approaches based on experience © 2011 Pearson Education, Inc.

90 Figure 55.19a Equator Figure Exploring: Restoration Ecology Worldwide 90

91 Kissimmee River, Florida
Figure 55.19b Figure Exploring: Restoration Ecology Worldwide Kissimmee River, Florida 91

92 Truckee River, Nevada Figure 55.19c
Figure Exploring: Restoration Ecology Worldwide Truckee River, Nevada 92

93 Tropical dry forest, Costa Rica
Figure 55.19d Figure Exploring: Restoration Ecology Worldwide Tropical dry forest, Costa Rica 93

94 Rhine River, Europe Figure 55.19e
Figure Exploring: Restoration Ecology Worldwide Rhine River, Europe 94

95 Succulent Karoo, South Africa
Figure 55.19f Figure Exploring: Restoration Ecology Worldwide Succulent Karoo, South Africa 95

96 Figure 55.19g Figure Exploring: Restoration Ecology Worldwide Coastal Japan 96

97 Maungatautari, New Zealand
Figure 55.19h Figure Exploring: Restoration Ecology Worldwide Maungatautari, New Zealand 97

98 Microorganisms and other detritivores Secondary and tertiary consumers
Figure 55.UN01 Sun Key Chemical cycling Energy flow Heat Primary producers Primary consumers Detritus Figure 55.UN01 Summary figure, Concept 55.1 Microorganisms and other detritivores Secondary and tertiary consumers 98

99 Formation of sedimentary rock
Figure 55.UN02 Reservoir A Organic materials available as nutrients: Living organisms, detritus Reservoir B Organic materials unavailable as nutrients: Peat, coal, oil Fossilization Respiration, decomposition, excretion Burning of fossil fuels Assimilation, photosynthesis Figure 55.UN02 Summary figure, Concept 55.4 Reservoir D Inorganic materials unavailable as nutrients: Minerals in rocks Reservoir C Inorganic materials available as nutrients: Atmosphere, water, soil Weathering, erosion Formation of sedimentary rock 99

100 Figure 55.UN03 Figure 55.UN03 Appendix A: answer to Concept Check 55.4, question 1 100

101 Figure 55.UN04 Figure 55.UN04 Appendix A: Answer to Test Your Understanding, question 9 101


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