summary of sustainability work of the brook byers ... · design attributes only single family...
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Summary of Sustainability Work of the
Brook Byers Institute for Sustainable Systems
Junchen Yan, Thomas Igou, Osvaldo Broesicke,
Yongsheng Chen, John C. Crittenden
Department of Civil and Environmental Engineering
Georgia Institute of Technology
Aug 9th, 2018
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Roadmap to Develop Sustainable Cities
• We need to recreate the anthroposphere to exist within the means of nature
• Use resources that nature provides
• Generate waste that nature can assimilate without overwhelming natural cycles
• Must examine interactions between the environmental, engineered, social and
economic systems.
• Research Directions:
Infrastructure Ecology
Sustainability Toolbox
Ecosystem Services
Life Cycle Assessment
Models
Predict consumer behavior and demand for
sustainable infrastructure
Optimize technology choice depending on
community structure and climate
Identify network mechanisms of
interdependent infrastructures
Sustainable
Systems
Analysis
Social Decision Making
Predicting the Demand for
Urban Infrastructure
Identifying Sustainable &
Resilient Alternatives
Evaluate the Sustainability & Resilience Performance
Build the Infrastructure
& Assess Actual
Performance
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Our Work on Sustainable Systems Analysis
Infrastructure Ecology views the city as an ecosystem and integrates the urban infrastructure as a system of systems.
This allows us to alter and reorganize energy and resource flows and consider the potential synergistic effects arising from
infrastructure symbiosis. [1]
– Improve diversity of infrastructure, and improve energy and material flow to mimic real ecosystems.
Interconnectedness within the urban infrastructure system (UIS) and the
interrelation of the UIS with natural environmental systems and socio-
economic systems.
12 Principles of Infrastructure Ecology
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Our Work on Sustainable Systems Analysis
Work in progress
Used Topic Modeling to analyze 12,526
abstracts
• Identified 30 topics
– Research Themes (23/30)
– Sustainability Tools (7/30)
• Toolbox covers:
– Solution development
– System evaluation
– Decision making
Sustainability Toolbox [2]
Source: Lu et al. (In Progress)
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Land use and ecosystem services in Atlanta [3]
Carbon storage (108 tons)
1985 1992 1999 2005 2012
0
1
2
3
4
Water yield (1010
m3)
1985 1992 1999 2005 2012
0.0
.5
1.0
1.5
2.0
Nitrogen export (106 kg)
1985 1992 1999 2005 2012
0
2
4
6
8
10
Phosphorus export (106
kg)
1985 1992 1999 2005 2012
0.0
.5
1.0
1.5
2.0
2.5
Sediment export (105
tons)
1985 1992 1999 2005 2012
0
2
4
6
8
10
Habitat quality index (107)
1985 1992 1999 2005 2012
0.0
.5
1.0
1.5
2.0
Recreation opportunity index (106)
1985 1992 1999 2005 2012
0
2
4
6
8
10
Food supply (1011
kcal)
1985 1992 1999 2005 2012
0.0
.2
.4
.6
.8
1.0
1.2
1.4
• Forest and wetland had the greatest proportion of decreases, which were
42% and 34%, respectively.
• From 1985 to 2012, the forest accounted for the largest proportion in
Atlanta.
• Low and high intensity developed land increased most, by 157% and
394%, respectively.
Indicators Change rates
Carbon storage -23%
Water yield -22%
Nitrogen export +28%
Phosphorus export +49%
Sediment export +17%
Habitat quality index -27%
Recreation opportunity -35%
Food supply -36%
Our Work On Sustainable Systems Analysis
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Our Work On Sustainable Systems Analysis
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3,258 Person Per Square Mile1.07 metric ton per capita per year
Structural Fractal Dimension = 2.80
1,378 Person Per Square Mile1.52 metric ton per capita per year
Structural Fractal Dimension = 3.36
The geometric form of road networks is similar between Washington DC and Atlanta. The difference in the hierarchy of transportation networks accounts for 30% of density difference and 20% of carbon difference between Washington DC and Atlanta.
0.6
0.8
1.0
1.2
1.4
1.6
2.4 2.8 3.2 3.6 4.0
Carb
on
Pe
r C
ap
ita
(Me
tric
to
nn
es
20
05
)
Structural Fractal Dimension
2 miles
42% More Water For Transportation!
The Impact of the Hierarchy of Transportation Network On Carbon Emissions
from Land Development and Transportation
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Our Work On Sustainable Energy Systems Analysis
Combined Cooling, Heating, and Power combined with Renewable Generation and Energy Storage [4,5]
The big goal of this research is to develop a tool that can evaluate the social, environmental and economic impact of theproposed power system via several sustainability metrics.
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Our Work On Sustainable Systems Analysis
Parametric Life Cycle
Assessment [6]
Combined Cooling Heating Power Energy Demand• Electricity• Hot water• Heating• Cooling
Parameterization
Result Interpretation and Decision Support
ElectricityStorage
Electricity
Thermal Storage
Hot Water Cold Water
Environmental, Social and Economic Life Cycle Impact Assessment
Life Cycle Inventory
Water Energy CO2 CO CH4 N2O NO NO2 SO2 NOX NH3 VOC PM2.5 PM10 (Variety of Chemicals from batteries)
TechnologiesCCHP Generation• Microturbines• Reciprocating Engines• Sterling Engine• Fuel Cells• Solid Oxide Fuel Cells
Renewables• Solar• Wind
Electricity Storage• Solid State Batteries• Flow Batteries• Flywheels• Compressed Air Energy
Storage• Hydrogen• Pumped Hydro-power
storage• Thermal• Hydraulic Rock Storage• Electric Cars
Thermal Storage• Heat stored as sensible heat• Heat stored as latent heat• Heat stored as chemical energy
Centralized Heat and Powersupply backup
• Electricity from central grid• Hot water from furnace
feedback
Options
Energy Demand ScenariosClimate Change Heating Degree Days Cooling Degree DaysBuilding Types Building OrientationsBuilding Energy Loss Rate and Efficiency
Energy Supply ScenariosLocation Resource Limitations Operational ModeEfficiency Heat to Power Ratio PolicySubsidy Net metering Resource PriceLife time Degradation Weather PatternFuel Consumption Pattern
Energy Backup ScenariosResource Price Type of Centralized Power PlantFurnace Type Electricity Price Water HeaterPolicy Carbon Cost Efficiency
Socialan
dPo
liticalDecisio
n&
Plan
nin
g
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Our Work On Sustainable Systems Analysis
Big Data for Social Decision and Urban Complexity Modeling [7]
Collect Analyze ModelingSocial MediaBlogsTwitterNewsProduct Reviews
Enrich and prepare social media content with metadata
Agent-based urban model and visualization
Topic Modeling
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• Demand reduced by harvesting rainwater and reclaiming greywater.
• LID techniques can reduce centralized water use for non-potable uses by up to 65% in Atlanta.
• LID and greywater reclamation can reduce centralized water demand by up to 84% for non-potable uses in Atlanta.
A
Water
SuppyWastewater
Treatment
Stormwater
Management
Rainwater
Harvesting
Low Impact
Development
10
Our Work On Sustainable Systems Modeling
Decentralized Water Systems [13-15]
Greywater
Reclamation
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Agent-Based Modeling: Simulating Adoption Rate for More Sustainable Urban Development [8]
Our Work On Sustainable Systems Modeling
Principal Agents: Prospective
Homebuyer, Homeowners, Developers,
Government
Impact fee for Low Impact Development
non-compliance penalty:
• $13,000 per unit for single-family
house
• $1,500 per unit for apartment home
Implemented Policy Tool
After 30 years:
• 40% reduction in potable water demand
from centralized plant in MSD as compared
to BAU
• 36% increase in net property tax revenue
generation in MSD as compared to BAU
Policy Implementation Effect
65%
35%
0%
20%
40%
60%
80%
100%
0 5 10 15 20 25 30Year
Percentage of households as compared to total households after30 yearsPercentage of households in single-family houses as compared tototal households after 30 yearsPercentage of households in apartments as compared to totalhouseholds after 30 years
41%
59%
0%
20%
40%
60%
80%
100%
0 5 10 15 20 25 30Year
Business As Usual
(BAU)
More Sustainable Development
(MSD)
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Our Work On Sustainable Systems Modeling
Latent-Class Model for Choice Simulation [7]
Conventional sprawling community Smart growth neighborhood
Design
Attributes
Only single family houses on large lots.
No sidewalks.
A few miles to shopping, restaurants, a
library, and a school and you have to drive to
most.
Public transportation is distant or unavailable.
A mix of housing choice.
Sidewalks are provided.
A few blocks to shopping, restaurants, a library, and a school and you can either walk or
drive
Public transportation, is nearby.
A few blocks to parks, playground, and recreational area you can either walk or drive.
Commute time to work is less than 20 minutes.
Add more desirable attributes (red color in the above table)
Use community preference survey data (National Association of Realtors) to calibrate decision-making equations in an agent-based model
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Our Work On Sustainable Systems Modeling
Urban Farming: Hydroponic systems modeling [10,11]
Work in progress
• Global agriculture is supported by unsustainable, largely unidirectional flows of water, fertilizer and energy
• Recovery of nutrients, water and energy is feasible from primary domestic wastewater by integration of membrane filtration and granular
activated carbon with high-rate anaerobic treatment (below)
• Anaerobically treated domestic wastewater provides an excellent feedstock for hydroponic agriculture as solids are completely removed,
energy is produced (biogas), and micro- and macronutrients (fertilizers) are retained
Pilot-scale performances [11]
En
erg
y p
ote
nti
al
(kW
h/m
3)
Energy-Positive:
Max: +0.287 kWh m-3
Min: +0.193 kWh m-3
CAS: –0.450 kWh m-3
• High COD removal (94%)
COD <25 mg/L
BOD5 <10 mg/L
• 54-59% of COD converted to CH4 0.42 kWh m-3
• Low biosolids production
0.051 gVSS gCODR-1
• Complete solids removal
>99% TSS & VSS removal
• HRT: 4.6 6.8 hours
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Our Work On Sustainable Systems Modeling
Urban Farming: Aquaponic systems modeling [9]
Work in progress
• Symbiotic aquaculture and hydroponic cultivation in closed, recirculating system
• Combining techniques improves productivity and nutrient utilization efficiency
• Currently developing a model to simulate water quality, food productivity, energy demand and appropriate implementation scales in cities (in progress, below)
• Model is based on experimental greenhouse at GT Structures Laboratory (right)
Fish Tanks Bioreactor Grow Beds
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Calculate emissions (CO2 and NOX), water consumption, and potential
cost savings for energy production within each building and Metro Atlanta
Model electrical and thermal
load to meet demand for
each building type
Model electrical
output from alt
energy sources
Model thermal &
electrical output
from CCHP system
Model energy
demand for 5
building types
Three studies
1. Water, air emissions, and cost impacts of air-cooled microturbines for combined cooling, heating and power systems: A case study in the Atlanta region
2. Impact of land use & technology policies on water demand and emissions of a rapidly growing urban region
3.heating and power systems
Decentralized Energy Generation [4,5]
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Our Work On Sustainable Systems Modeling
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By 2030, implementation of CCHP in all new and existing residential and commercial buildings could reduce CO2 emissions by ~0.016 Gt, NOX emissions by ~24 kt, and decrease water-for-energy consumption by 315 MGD per year for the Metro Atlanta region with More Compact Development [5]
CO2 (106 tonnes) NOX (103 tonnes) Water Consumption (mgd )
0
5
10
15
20
25
30
No
CCHP
CCHP CCHP
w/ netmet
2005 level
-90%-63%
0
5
10
15
20
25
30
35
No CCHP CCHP CCHP
w/ netmet
2005 level
-50%
-8%
0
50
100
150
200
250
300
350
400
No
CCHP
CCHP CCHP w/
netmet
2005 level
-74% -93%
16
Decentralized Energy Generation [4,5]
Our Work On Sustainable Systems Modeling
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Our Work On Sustainable Systems Modeling
Optimize building composition with infrastructure demands
• Analyzing how different combined cooling, heating, and
power (CCHP) systems can match thermal and electric
demands
• Analyzing the demands of 15 reference building types
within 16 different climate zones, analyzed by the
Department of Energy.
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Our Work On Sustainable Systems Modeling
• Urban infrastructure systems can be represented by a multilayer network
• Can be studied by tensor representation
• Limits the loss of interaction data of monolayer network representation, which requires one common currency
Multilayer Network Analysis of Infrastructure Systems
Figure taken from Derrible, S., (2017) [12]
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References
1. Pandit, A., Minné, E.A., Li, F., Brown, H., Jeong, H., James, J.A.C., Newell, J.P., Weissburg, M., Chang, M.E., Xu, M., Yang, P., Wang, R., Thomas, V.M., Yu, X., Lu, Z., Crittenden, J.C., 2015. Infrastructure ecology: An evolving paradigm for sustainable urban development. J. Clean. Prod. 1–9. doi:10.1016/j.jclepro.2015.09.010
2. Lu, Z., Broesicke, O., Xu, M., Newell, J., Keoleian, G., Derrible, S., Mihelcic, J., Schwegler, B., Zhou, T., Chang, M., Crittenden, J., In Progress. Synthesis and Evaluation of Sustainability Toolbox for Managing Complex Human-Nature Systems
3. Sun, X., Crittenden, J. C., Li, F., Lu, Z. & Dou, X. Urban expansion simulation and the spatio-temporal changes of ecosystem services, a case study in Atlanta Metropolitan area, USA. Sci. Total Environ. 622–623, 974–987 (2018).
4. James, J.-A., Thomas, V.M., Pandit, A., Li, D., Crittenden, J.C., 2016. Water, Air Emissions, and Cost Impacts of Air-Cooled Microturbines for Combined Cooling, Heating, and Power Systems: A Case Study in the Atlanta Region. Engineering 2, 470–480. doi:10.1016/J.ENG.2016.04.008
5. James, J.-A., Sung, S., Jeong, H., Broesicke, O.A., French, S.P., Li, D., Crittenden, J.C., n.d. Impacts of Combined Cooling, Heating, and Power Systems and Rainwater Harvesting on Water Demand, Carbon Dioxide and NOx Emissions for Atlanta. Environ. Sci. Technol. In Review.
6. Lee, D. Parametric Approach to Life cycle Assessment. (Georgia Institute of Technology, 2016).7. Lu, Z., Southworth, F., Crittenden, J. C. & Dunhum-Jones, E. Market potential for smart growth neighbourhoods in the USA: A
latent class analysis on heterogeneous preference and choice. Urban Stud. 52, 3001–3017 (2015).8. Lu, Z., Noonan, D., Crittenden, J.C., Jeong, H., Wang, D., 2013. Use of impact fees to incentivize low-impact development and promote compact
growth. Environ. Sci. Technol. 47, 10744–10752. doi:10.1021/es304924w9. Debrota, K. H. Mechanistic Modeling of an Aquaponic Controlled Environment Agriculture System: Nutrient and Water Dynamics, Harvest
Productivity, and Waste Treatment (2017).10. Chen, Y., Crittenden, J. C., Igou, T. K., and Broesicke, O. A. Use of Domestic Wastewater for Food Production International Conference on Resource
Sustainability, June 27-29 (2018), Beijing, CN.11. Shin, C. and Bae, J. Current Status of the Pilot-Scale Anaerobic Membrane Bioreactor Treatments of Domestic Wastewaters: A Critical Review
Bioresource Technology 247, (2018): 1038–1046. doi:10.1016/J.BIORTECH.2017.09.002,
12. Derrible, S. Complexity in future cities: the rise of networked infrastructure. Int. J. Urban Sci. 21, 68–86 (2017).
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References
13. Jeong, H., Minne, E., Crittenden, J.C., 2015. Life cycle assessment of the City of Atlanta, Georgia’s centralized water system. Int. J. Life Cycle Assess. 20, 880–891. doi:10.1007/s11367-015-0874-y
14. Jeong, H., Broesicke, O.A., Drew, B., Li, D., Crittenden, J.C., 2016. Life cycle assessment of low impact development technologiescombined with conventional centralized water systems for the City of Atlanta, Georgia. Front. Environ. Sci. Eng. 10. doi:10.1007/s11783-016-0851-0
15. Jeong, H., Broesicke, O.A., Drew, B., Crittenden, J.C., 2017. Life cycle assessment of small-scale greywater reclamation systems combined with conventional centralized water systems for the City of Atlanta, Georgia. J. Clean. Prod. (In Review).
16. Crittenden, J.C., Lu, Z., Pandit, A., 2015. Water for everything and the transformative technologies to improve water sustainability, in: National Water Research Institute: Clarke Prize Lecture. Huntington Beach, CA, pp. 1–23.
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Supplementary Slides
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Potential CO2 And NOX Impacts Of CCHP In Atlanta
By 2030, implementation of CHP in all residential and commercial and buildings will reduce the CO 2
and NOX emissions in the Metro Atlanta region. [6]
w/CCHPs in existing (2005) and new buildings
BAU – CO2 MCG – CO2 BAU – NOX MCG – NOX
Base Year (2005)
0
5
10
15
20
25
30
35
NoCCHP CCHP CCHP
w/ netmet
CO
2E
mis
sions
(10
6to
nnes
)
0
5
10
15
20
25
30
NoCCHP CCHP CCHP
w/ netmet
NO
XE
mis
sions
(10
3to
nnes
)
50%
90%
22
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Potential Water-for-energy Impacts Of CCHP In Atlanta
By 2030, implementation of CCHP in all residential and commercial and buildings will reduce water consumption in the Metro Atlanta region. [6]
0
50
100
150
200
250
300
350
400
No CCHP CCHP CCHP w/
netmet
Co
nsu
mp
tio
n (
10
6g
al p
er d
ay)
0
500
1,000
1,500
2,000
2,500
3,000
3,500
4,000
No CCHP CCHP CCHP w/
netmet
Wit
hd
raw
als
(10
6g
al p
er d
ay) w/CCHPs in existing (2005) and new buildings
MCGBAU Base Year (2005)
93%
23
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Examples of Emergent Properties: Power Laws
Source: Bettencourt 2013
Infrastructure Measures: Road
miles: Exponent=.85
Doubling
Urban
Populaion
Results in 1.8
times
Roadway50% Reduction
of roadway for
10M people as
compare to
100K people.
24
Our Work On Sustainable Systems Analysis
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Urban Agriculture [8,16]
Urban Agriculture (Aquaponics,
Urban Farming, Greenhouse Farm)
Stormwater Management
with Low-Impact Development
More Concentrated Wastewater
Sou
rce of Fertilizer Harvested Rainwater
Stormwater treated through LID
Heat and Energy
Fertilizer for Farms, Food for Aquaponics
Heat
Na
tura
l Ga
s from
An
aero
bic D
igestio
n
Natural Gas from Compost
CO2 Injection
Natural Gas from Landfill
Combined Carbon Capture, Cooling, Heating and Power (Air-cooled microturbines)
On-site Energy and Nutrient Recovery
Local Composting
Landfill
Heat and Energy
Water
Fertilizer
Natural Gas
CO2
LEGEND
Close the loop in urban infrastructure systems
Urban system as a Circular Economy
Developing model for aquaponics productivity
25
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Life Cycle Assessments On Decentralized Energy
Generation (DG)
Quantifying the impacts for DG as a result of generation and storage technologies as well as policy.
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Multidisciplinary Decision Optimization
• Looking to identify the optimum combinations of technologies for given objectives
• Identify interactions among Water-Energy-Transportation infrastructures
• Develop the Pareto space– Visualization of optimum
combinations
Sample of alternative technologies and developmental strategies that may interact with centralized infrastructure
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