CH2_ECOLOGY ENGINEERING rev.pdf
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CHAPTER II
ECOLOGICAL ENGINEERING AND ECOSYSTEM
RESTORATION
A. Definition of ecological engineering
Ecological engineering is defined as the design of sustainable ecosystems that
integrate human society with its natural environment for the benefit of both (Mitsch
and Jrgensen, 2004). It involves the restoration of ecosystems that have been
substantially disturbed by human activities such as environmental pollution or land
disturbance; and the development of new sustainable ecosystems that have both human
and ecological value. While there was some early discussion of ecological engineering
in the 1960s, its development was spawned later by several factors, including loss ofconfidence in the view that all pollution problems can be solved through technological
means and the realization that with technological means, pollutants are just being
moved from one form to another. Such approaches require massive resources to solve
problems, that, in turn, perpetuate carbon and nitrogen cycle problems, for example.
Restoration ecology was described as the full or partial [re]placement of structural or
functional characteristics that have been extinguished or diminished and the
substitution of alternative qualities or characteristics than the ones originally present
with the proviso that they have more social, economic, or ecological value than existed
in the disturbed or displaced state (Cairns, 1988). A definition of ecological restoration
established as part of a National Academy of Science study in the early 1990s was thereturn of an ecosystem to a close approximation of its condition prior to disturbance
(NRC, 1992). Several restoration fields have developed somewhat independently, and
all appear to have the design of ecosystems as their theme. Although related to
ecological engineering or even a part of it, several of these approaches seem to lack one
of the two important cornerstones of ecological engineering, namely: 1) recognizing the
self-designing ability of ecosystems, or 2) basing the approaches on a theoretical base,
not just empiricism.
The development of ecological engineering was given strong impetus in the last decade
with the publication of a textbook, the publication of the journal Ecological
Engineering and the formation of two professional ecological engineering societies.
The five principles defining ecological engineering are: 1) It is based on the self-
designing capacity of ecosystems; 2) It can be the acid test of ecological theories; 3)
It relies on system approaches; 4) It conserves non-renewable energy sources; and 5) It
supports biological conservation. Ecology as a science is not routinely integrated into
engineering curricula, even in environmental engineering programs. Likewise,
ecologists, environmental scientists, and managers are missing important training in
their professionproblem solving. These two deficiencies were addressed in the
integrated field of ecological engineering.
One way to view ecological engineering and ecosystem restoration, since they coversuch a wide varieties of fields, is to consider the various fields on a spectrum of how
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much conventional engineering (and, hence, reliance on human structures and our
fossil fuel economy are involved; see Figure 2.1). On the right side of this spectrum are
traditional ecological approaches such as prairie restoration or wetland restoration
where quite often only a small effort of conventional engineering is needed. In some
cases, wetlands (at least the hydrology) can almost be restored in a few hours or days if
a drainage tile is broken or blocked, allowing the return of the original hydrology. Inthe middle of the spectrum are approaches such as biomanipulation or wetland creation
where clearly more management and engineering are required. This is probably also
true for wetlands built for wastewater or nonpoint source pollution control or for
developing multi-species agroecosystems. At the far left of the theoretical spectrum are
examples that involve significant amounts of energy and engineering. Intensely
engineered systems such as Biosphere 2, clearly ecological engineering in the sense
that ecosystems are being created, quite often are enormously subsidized, yet might fall
within the definition of ecological engineering.
Biosphere 2 Biomanipulation Prairie Restoration
Soil Bioremediation Wetland Restoration
Solar Aquatics Mineland Restoration
Agroecological Engineering
Wastewater Wetlands
Wetland Creation
more lesshuman engineering
highlowreliance on self-design
sustainability potential
low high
Fig. 2.1. Spectrum of ecological engineering and ecosystem restoration (Mitsch
and Jrgensen, 2004)
B. Principles of ecological engineering
While ecological engineering and ecosystem restoration might prove that some
ecological theories are not rigorous enough to survive real world tests, the principles
below are based on ecological concepts that have a strong record of field verification.
Principle 1Ecosystem structure and function are determined by the forcing
functions of the system.
Principle 2Energy inputs to the ecosystems and available storage of matter
are limited.
Principle 3Ecosystems are open and dissipative systems.
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Principle 4Attention to a limited number of factors is most strategic in
preventing pollution or restoring ecosystems.
Principle 5Ecosystems have some homeostatic capability that results in
smoothing out and depressing the effects of strongly variable inputs.
Principle 6Recycling pathways must be matched to the loading rates to
ecosystems to reduce the effect of pollution.
Principle 7Design for pulsing systems wherever possible.
Principle 8Ecosystems are self-designing systems.
Principle 9Processes of ecosystems have characteristic time and space scales
that should be accounted for in environmental management.
Principle 10Biodiversity should be championed to maintain an ecosystems
self-design capacity.
Principle 11Ecotones, or transition zones, are as important for the ecosystems
as the membranes are for cells.
Principle 12Couplings between ecosystems should be utilized wherever
possible.
Principle 13 The components of an ecosystem are interconnected, interrelated
and form a network, implying that direct as well as indirect effects of ecosystemdevelopment need to be considered.
Principle 14An ecosystem has a history of development.
Principle 15Ecosystems and species are most vulnerable at their geographical
edges.
Principle 16Ecosystems are hierarchical systems and are parts of a larger
landscape.
Principle 17Physical and biological processes are interactive. It is important
to know both physical and biological interactions and interpret them properly.
Principle 18Ecotechnology requires a holistic approach that integrates as far
as possible all the interacting parts and processes.
Principle 19Information in ecosystems is stored in structures.
References:
Cairns, J., Jr. 1988. Restoration ecology: The new frontier. Pages 1-11 In: J. Cairns, Jr.,ed.,Rehabilitating Damaged Ecosystems, Volume I. CRC Press, Boca Raton, FL.
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Mitsch, W. J., S. E. Jrgensen. 1989. Ecological Engineering: An Introduction to
Ecotechnology. John Wiley & Sons, New York. 472 pp.
Mitsch, W. J. 1993. Ecological engineeringa cooperative role with the planetary life
support systems. Environmental Science & Technology 27:438-445.
Mitsch, W. J. 1998. Ecological engineeringthe seven-year itch. Ecological
Engineering 10: 119-138.
Mitsch, W. J., S. E. Jrgensen. 2003. Ecological engineering: A field whose time has
come.Ecological Engineering 20: 363-377.
Mitsch, W. J., S. E. Jorgensen. 2004. Ecological Engineering and Ecosystem
Restoration. Wiley, New York.
National Research Council. 1992. Restoration of Aquatic Ecosystems. NationalAcademy Press, Washington, DC.
Internet resources:
Ecological Engineering (the journal), Volumes 1-23 (1991 present) published by
Elsevier. Journal content and other journal information published at:
http://www.elsevier.com/locate/ecoleng.
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Slides
1 & 4
Madan, or Marsh Arabs,Mesopotamian Marshlandssouthern Iraq
With permission from National Geographic; first published
in textbook: Mitschand Gosselink, 1986, Wetlands. Van
Nostrand Reinhold, New York Richardson 2004
Drainage of the Mesopotamian Marshlands
Slides2 & 5Drainage of the Mesopotamian Marshlands
Slides
3 & 6Drainage of the Mesopotamian Marshlands
Olentangy River Wetland Research Park
The Ohio State University
ExperimentalWetlands
Oxbow Wetland
Bottomland Hardwood ForestRestoration
MesocosmCompound Sandefur
Wetland Pavilion
Heffner Wetland
Building
CityBikepath
OlentangyRiver
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Slides
7 & 10
EDUCATION AND RESEARCH ARE
MOST IMPORTANT TO ENHANCE OUR KNOWLEDGE AND
WISE USE OF WETLANDS
Slides
8 &11
Olentangy River Wetland Research Park, Ohio S tate University
Slides
9 & 12
Ecological Engineering
and
Ecosystem Restoration
Restoring the Florida Everglades
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Slides
13 & 16
Restoring the Florida Everglades
Treatment Wetlands
Slides
14 & 17
restoredbottomland
forest
createdwetlandinterceptingtiledrainage
Restoring the Mississippi River Basin
Restoring Coastal Marshes in New J ersey
Slides
15 & 18
Restoring the Skjern River, Denmark
Restoring Coastal Marshes in New J ersey
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Slides
19 & 22
Biosphere 2 - the most costly ecological engineering of all
impacts andemissions
ECOSYSTEMSIndustrialization
andurbanization
ECOSYSTEMS
Environmentaltechnology
Ecologicalmodelling
Strategy for environmental managementEarly 1970s
Slides
20 & 23
Biosphere 2 - the most costly ecological engineering of all
Ecologicalmodelling
ECOSYSTEMS
Environmentaltechnology
HUMANS
Environmentallegislation
Ecologicalengineering
and
ecosystemrestoration
Global environmental problems
Climate change
Ozone depletion
Acid deposition Rain forestl oss
Cleanertechnology;
Sustainabledevelopment
Strategy for environmental managementtoday
Slides
21 & 24
Biosphere 2 - the most costly ecological engineering of all
CLEANERTECHNOLOGY
CLIFE CYCLEANALYSIS
L
RAW MATERIAL ENERGY
TRANSPORT
APPLICATION
DISPOSAL
ECOSYSTEMS
E
ENVIRONMENTALTECHNOLOGY
T
ECOLOGICALENGINEERING
ANDECOSYSTEM
RESTORATION
E
RECYCLINGC
RECYCLINGC T
E
T
E
L
L
L
T
E
T
E
USE OF WASTE HEATC
PRODUCTIONC
PRODUCT
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Slides
25 & 28
21002000190018000
2
4
6
8
10
Change in population 1805-1999 and an op-
timistic (but realistic) prognosis 1999-2050
Human
population(billions)
Year
Goals of Ecological Engineering
1. the restoration of ecosystems that have beensubstantially disturbed by human activitiessuch as environmental pollution or landdisturbance; and
2. the development of new sustainableecosystems that have both human andecological value.
Slides
26 & 29
100
80
60
40
20
01900 1920 1940
Year
Atmospheric CO2
Global Nitrogen Fixation
1960 1980 2000
PercentChange
Ecological Restoration
the return of an ecosystem to a
close approximation of its
condition prior to disturbance
Source: NRC, 1992
Slides
27 & 30 Ecological Engineering
the design of sustainable
ecosystems that integrate
human society with its natural
environment for the benefit of
both
Source: Mitsch and Jrgensen, 2004
Termsthatare synonyms, subdisciplines, or fields similar toecological engineering______ ________ ______ _______ _______ _______ _______ ______
synthetic ecology biomanipulation
restoration ecology riverand lake restoration
bioengineering wetland restoration
sustainableagroecology reclamation ecology
habitat reconstruction nature engineering
ecohydrology ecotechnology
ecosystem rehabilitation engineering ecology
biospherics solar aquatics
______ ________ ______ _______ _______ _______ _______ ______
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Slides
31 & 34 History of Ecological Engineering
H.T. Odum(1960s) mention of ecological engineering inseveral publications
Ma Shijun (1960s-70s in China; 1985 in Westernliterature) father of ecological engineering in China
Mitsch -t aught course at IIT in 1975 called Ecologicalengineering and systems ecology
Ecotechnology of Uhlmann, Straskraba and Gnauek(1983-1985)
Mitsch and Jrgensen ecological engineering book (1989)
ECOLOGICAL ENGINEERINGECOLOGICAL ENGINEERING
ANNUAL MEETINGANNUAL MEETING
MAY 1, 2001MAY 1, 2001
UNIVERSITY OF GEORGIAUNIVERSITY OF GEORGIA
ATHENSATHENS
Slides
32 & 35 History of Ecological Engineering First ecological engineering meeting in Trosa Sweden (1991)
followed by Etnier and Guterstambook (1991, 1997)
Ecological Engineeringjournal started (1992)
Ecological engineering workshop in Washington DC atNational Academy of Sciences (1993)
IEES started in 1993 in Utrecht, The Netherlands
SCOPE project in ecological engineering and ecosystemrestoration established in Paris, 1994 - 2002
Discussions of American ecological engineering society inColumbus, 1999; AEES first meeting April 2001 Athens, GA
Mitsch and Jrgensen (2004) and Kangas (2004) textbookscompleted
Seriesof 4 workshops andsubsequent specialissue publicationsof SCOPE(ScientificCommittee on Problemsof the Environment) project EcologicalEngineering and EcosystemRestoration
______________________________________________________________________________Workshop Title Workshop Location Special Issue
And Date Publication of Ecol Eng______________________________________________________________________________Ecological engineeringin Tallin,Estonia Mitsch andMander (1997)Ce ntra l a nd Ea ste rn Europ e: No vember 6 -8, 1 995Remediationof ecosystemsdamaged by environmentalcontamination
Ecologicalengineer ingin developing Beijing,China R.Wanget al. (1998)countries October 7-11, 1996
Ecologicalengineer ingapplied tor iver Par is,France Lefeuvre et al. (2002)and wetland restoration July 29-31, 1998
Ecology ofpost-mining landscapes Cottbus, Germany HttlandBradshaw(2001)March 15-19,1999
______________________________________________________________________________
Slides
33 & 36
ECOLOGICAL ENGINEERINGECOLOGICAL ENGINEERING
WORKSHOPWORKSHOP
MARCH 15MARCH 15--16, 199916, 1999
THE OHIO STATE UNIVERSITTHE OHIO STATE UNIVERSIT
COLUMBUSCOLUMBUS
Self-design
The application of self-organization
in the design of ecosystems
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Slides
37 & 40Systems categorized by types of organization (modified from Pahl-Wostl, 1995)
____ _____ _____ ____ _____ _____ _____ _____ _____ _____ _____ _____ ____ _____ ___Characteris tic Imposed organization Self-organization
____ _____ _____ ____ _____ _____ _____ _____ _____ _____ _____ _____ ____ _____ ___
Control externally imposed; endogenously imposed;
centralized control distributed control
Rigidity rigid networks flexible networks
Potential for adaptation little potential high potential
Application conventional engineering ecological engineering
Examples machine organism
fascist or socialist society democratic society
agriculture natural ecosystem
____ _____ _____ ____ _____ _____ _____ _____ _____ _____ _____ _____ ____ _____ ___
A Systems Approach
Slides
38 & 41
Nonrenewable Resource
Conservation
Slides
39 & 42
The Acid Test
ConventionalEngineer
FossilFuels
Natu ralEnergies
Servicesto Societ
Conventional EngineeringConventional Engineering
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Slides
43 & 46
Na tur alEnergies
self
design
FossilFuels
Servicesto Societ
EcologicalEngineer
Mitsch (1998)
Ecological EngineeringEcological Engineering
Comparison of ecotechnology and biotechnology
_____________________________________________________________
Characteristi c Ecotechnology Biot echno logy
_____________________________________________________________Basic unit Ecosystem Cell
Basic principles Ecology Genetics; cell biology
Control Forcing fun ctions, Genetic structure
organisms
Design Self-design with some Human design
human help
Biotic diversity Protected Changed
Maintenance and Reasonable Enormousdevelopment costs
Energy b asis Solar based Fossil fuel based
________________________ _______________________________ ______
Slides
44 & 47
Ecosystem Conservation
To keep every cog and wheel is the first precaution
of intellegent tinkering.
Aldo Leopold
Contrasts with Other Fields
Environmental engineering
Biotechnology
Ecology
Slides
45 & 48 Contrasts with Other Fields
Environmental engineering
Biotechnology
TheoreticalEco logy
Ap pl ie dEco logy
Eco log ica lEngineering
The design, restoration andcreat ion o f ecosys tems
Resource Mgt.
Ecotoxicology
Environ. Monitoring
Ecosystems
Community
EcologicalEconomics
Landscape Eco logy Ri sk Ass es sm en t
Impact AssessmentPopulation
Evolutionary
The design, restoration, and creation of ecosystems
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Slides
49 & 52 Contrasts with Other Fields
Environmental engineering
Biotechnology
Ecology
Ecotechniques/Cleaner Technology
Industrial Ecology
Functional classification
Ecosystems are used to reduce or solve a pollutionproblem
Ecosystems are imitated or copied to reduce aresource problem
The recover of ecosystems is supported
Existing ecosystems are modified in anecologically sound way
Ecosystems are used for the benefit of humankindwithout destroying the ecological balance
Slides
50 & 53
Classification of Ecological
Engineering
Examples of ecological engineering approaches for terrestrial and aquatic systemsaccordingtotypesof applications.
________________________ ______________________________ _____________________EcologicalEngineering Approaches Terrestrial Examples Aquatic Examples________________________ ______________________________ _____________________1 .Ecosystemsareusedtosolvea pollu tion Phytoremediation Wastewaterwetlandproblem
2.Ecosystemsare imitated or copied to Forest restoration
3 .Th e re co very o fan ec os ys tem is Mine lan d res to ra tion Lak e r es to rat io nsupportedafter disturbance
4.Existing ecosystems are modified Selectivetimber harvest Biomanipulationin an ecologicallysound way
5. Ecosystems are used for b enefit Sustainable Multi-specieswithoutdestroyingecological balance a gr oe cosys tem s aq uacu lt ur e________________________ _______________________________ ____________________
Replacement wetland
reduce or solve a problem
Slides
51 & 54
Biosphere 2 Biomanipulation Prairie Restoration
Soil Bioremediation Wetland Restoration
Solar Aquatics Mineland Restoration
Agroecological Engineering
Wastewater Wetlands
Wetland Creation
more lesshuman engineering
highlowreliance on self-design
sustainability potentiallow high
Solving or reducing a pollution problem
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Slides
55 & 58Solving or reducing a pollution problem
Imitating or copying
ecosystems
Slides
56 & 59
Solving or reducing a pollution problem
Supporting ecosystem recovery
Slides
57 & 60
Imitating or copying ecosystems
Supporting ecosystem recovery
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Slides
61 & 64Modifying
existing
ecosystems in an
ecologically
sound way
Biomanipulation
Source: Hosper
and Meijer, 1992
_____________________________________________________________________________________________________________Ecological Engineering Project Location Purpose References
_____________________________________________________________________________________________________________
Createdflow-through riverine Columbus, Ohio to experimentallydeterminethelong-termeffects Mitsch et al.,1998;wetlands of planting on ecosystem function in progress
Root -zon ewetlan ds f o r S no ger d, S weden to inv es tiga te u se o f r o ot -zon ewetlan ds to G um br icht , 1 99 2wastewater treatment provide tertiary treatment of wastewater from
smalltown
Non-pointsource control central and southern to estimate theinteraction betweenwetland retention Braskerud,2002a,bwetlands Norway efficiencyand nutrient loss from agricultural
watersheds
Surface-waterwetlandsfor HoughtonLake,Michigan to use natural peatlandstotreat wastewater Kadlecand Knight,wastewater treatment from municipality to prevent lake pollution 1996
Renovation ofcoal-minedrainage AthensCounty,Ohio to studyiron retention fromcoal mine drainage Mitsch andWise,1998
withTypha wetland
R iv er p oll ut io n co nt rol S uz hou, C hi na t o us e wat er h ya ci nt hs (Eichhornia crassipes) Ma a nd Ya n, 198 9systemsforwaterpollution controland
production offodder
Nonpointsource pollution control central Illinois to create wetlandstoremove nutrientsfromMidwest Kovacicet al., 2000agricultural runoff Larsonet al., 2000
Intertidal sediment fences southern Louisiana to constructintertidal fencesmadefromrecycled Boumanset al.,1997Christmast reestorevegetationon mudflatsandincreasedsedimenttrapping
Examples of ecological engineering at different scales (cont.)
Ecosystem Scale
Slides
62 & 65
Classification According to Scale
______________________________________________________________________________________________________________Ecological Engineering Project Location Purpose References
______________________________________________________________________________________________________________
Restoration ofriparianlandscape Lake County,Illinois to restoreMidwestern U.S.riverfloodplain Heyetal., 1989anddeterminedesign proceduresforrestored Mitsch,1992wetlands Sanville andMitsch,
1994
Reg io na l lan ds cape r es to ra tion Cen tr al F lo rida to r econs tr uc tw et land /u plan d land scape Bro wn e ta l. , 1 99 2at phosphate mine
Agro-ecologicalengineering severalthousandsites to havemultiple-product farmingwithextensive R.Zhanget al.,1998in China recycling
Fishproduction/wetlandsystems YixingCounty, to producefisheriessynchronizedto Phragmites Mitsch,1991JiangsuProvince,China wetlandproductionandharvesting
Sa lt m ar sh c re at io n C hi na s e as t coa st , es p, t o de ve lo pSpartinama rs he s o nf or me r C hu ng, 1 98 5, 1 98 9Wenling,Zhejiang barrencoastline forshorelineprotection and Qinetal. ,1997Province food and fuel product ion
Saltmarshrestoration Delaware Bay, NewJerseyto restoresaltmarshesfromsalthayfarmsand Weinstein et al. ,1997,AndPhragmites- domi na te d ma rs he s 20 01; T eal an d
Weinstein,2002
River backwater restoration RhoneRiver,central to restoreandenhanceriver andriverbackwater Henry andAmoros,France connectivity 1995; Henry et al.,
2002______________________________________________________________________________________________________________
Examples of ecological engineering at different scales (cont.)
RegionalScale
Slides
63 & 66_____________________ ________________________ __________________________ ___________________________ ________________Ecological Engineering Project Location Purpose References
_____________________ ________________________ __________________________ ___________________________ ________________
Treatmentofseptagewastes Harwich,Massachuset ts to producecleanwater(drinkingwater standards) Guterstam andTodd,
f rom s e pt age i na n un li ned l a nd fi ll l a goon 1990 ; Te a l and Peterson,1991
S ca le m ode ls o f E ve r gl ade s W as hi ngt on , D C t o s im u la te phys ic a l andb io log ic al f unc ti on A de ya ndL ove la nd ,
and Chesapeake Bay of large-scale ecosystems 1991
Bi os ph er e 2 C at alin a Mo un ta in s, 1 .5 h a gl as s-e nc lo se ds ys te m to in ve sti ga te Ma ri no a nd O du m,
Arizona ecology and humans in enclosed systems 1999
W et la nd m es oc os ms S an D ie go , C al if or ni a t o i nv es ti ga te t h e ro le o f h yd ro pe ri od s on B us na rd o e t a l. , 19 92m a rs h r et en ti ono f nu tr ie nt s a ndme ta ls S in i cr ope e t a l. , 1992
W et la nd m es oc os ms C ol um bu s, O h io t o c om pa re c o mp et it iv e gr ow th o f tw o w et la nd S ve ng so uk a nd M it sc h,macrophytespeciesinlowandhigh nutr ients 2001
W et la nd m es oc os ms C ol um bu s, O h io t o i nv es ti ga te t he u s e o f su lf ur s cr ub be r ma te ri al A hn e t a l. , 20 01 ;
A s lin er s fo r tr eat me nt w et la nd s Ah n an d Mit sc h, 2 00 2b
Peat landrestorationplots Waikatoregion,North to determinethe roleoffer t il izer ,seedaddit ions Schipperetal . ,2002
Island,NewZealand andcult ivat ion techniquesforpeat landrestorat ion
E xpe ri me nt al e s tuar ine ponds M or ehe adC i ty , N or th t o i nves ti ga te e st uar ine ponds r ec ei v inga O dum, 1985 , 1989bC ar ol in a m ix tu re o f wa st ew ate r a nd s alt wa te r
Forestedwet landsforrecycling Gainesvi lle,F lorida to experimental lyinvest igateforested cypress Odum etal. ,1974;domesforwastewaterrecyclingand conservation EwelandOdum,1984;
Dierbergand Brezonik,
Mesocosm Scale
Ecosystem Scale
Examples of ecological engineering at different scales
When to Use Ecotechnology
1. The parts of nature affected, directly and indirectly, mustbe determined.
2. Quantitative assessment of impact of all alternatives mustbe carried out.
3. Project needs to include entire system, including humanimpacts and affected ecosystem.
4. Optimization should include short and long-term effects.
5. Renewable and nonrenewable resource use should bequantified.
6. Uncertainty should be accounted for in ecological andeconomic components.
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Slides
67 & 69
Ecological Design Principles
Ecological Design Principles
_________________________________________________ _____
7. Design for pulsing systems whenever possible.
8. Ecosystems are self-designing systems.
9. Processes of ecosystems have characteristic time and sp acescales that should be accounted for in environmental
management.
10.Biodiversity should be championed to maintain an
ecosystems self-design capacity.
11.Ecotones, transition zones, are as important for ecosystems asmembranes are for cells.
12.Coupling between ecosystems should be utilized whereverpossible.
Slides
68 & 70
Ecological Design Principles______________________________________________________
1.Ecosystem structure and function are determined by theforcing functions of the system.
2.Energy inputs to the ecosystem and available storage ofmatter are limited.
3.Ecosystems are open and dissipative systems.
4.Attention to a limited number of factors is most strategic inpreventing pollution or restoring ecosystems.
5.Ecosystems have some homeostatic capability that results insmoothing out and depressing the effects of strongly variableinputs.
6.Match recycling pathways to the rates to ecosystems toreduce the effect of pollution.
Ecological Design Principles__________________________________________________________
13. The components of an ecosystem are interconnected, interrelated,
and form a network, implying that di rect as well as indirecteffects of ecosystem development need to be considered.
14. An ecosystem has a history of development.
15. Ecosystems and species are most vulnerable at their geographicaledges.
16. Ecosystems are hierarchical systems and are parts of a largerlandscape.
17. Physical and biol ogical processes are interactive. It is importantto know both physical and biological interactions and to interpre tthem properly.
18. Ecotechnology requires a holistic approach that integrates allinteracting parts and processes as far as possible.
19. Information in eco systems is stored in structures.
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