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Warm Mix Asphalt Observations from the WSDOT I-90 Job (June 2008). Where are we with WMA? What do we know and not know? Life cycle assessment I-90 Observations. Where are we at with WMA technology?. - PowerPoint PPT Presentation
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Warm Mix AsphaltObservations from the WSDOT I-90 Job (June 2008)
1. Where are we with WMA?
2. What do we know and not know?
3. Life cycle assessment
4. I-90 Observations
Where are we at with WMA technology?
WMA has been around in its current iteration since about the mid 1990s but has existed in some for or another for at least 30 years.
1995 2009
current WMA starts
1970s
Older WMA-like productsBoeing and others
WMA standard use starts in some places
Plant foaming methods
MAXAM AquaBlack Foaming attachment
Terex Roadbuilding
Warm mix asphalt sys.
Foaming attachment
Astec Industries Double Barrel Green Foaming attachment
Gencor Industries Green Machine Foaming attachment
Kolo Veidekke WAM Foam Foaming process
Material foaming
Aspha-min Aspha-min Zeolite powder
PQ Corporation Advera Zeolite powder
Additives
Sasol Wax Sasobit Wax pellets
McConnaughay Low energy asphalt Chemical process
LEA CO Low energy asphalt Chemical process
Akzo Nobel Rediset WMX Surfactant pellets
Arkema Group CECABASE RT Surfactant chemicals
Meadwestvaco Evotherm Surfactant chemicals
The classic WMA benefits are enticing.
1. Reduced plant fuel consumption2. Reduced emissions
– At the plant– Fugitive emissions
3. Reduced viscosity during construction– Better compaction– Longer haul distances– Cold weather paving
4. Same viscosity during operation– Some have greater viscosity
What do we know and not know?
Based on published reports and presentations, here’s what we think we know.
Item Evidence Results
FieldPerformance
Older jobs: Europe (some > 10 yrs)Newer jobs: Europe and U.S.APT: NCAT, Caltrans PRC, others
≥ HMA(not positive yet)
Laboratory Performance
NCAT, State DOTs, Europe •Some moisture issues•Can be overcome
Energy Use Europe, U.S. trials 10-30% less
Emissions Europe, U.S. trials(far fewer data points)
10-70% reduction depending upon compound
Fumes/smell Europe (experiment)U.S. (mostly visual)
30-50% PAH reduction
Compaction EuropeNumerous U.S. trials
≥ HMA
Aging Some lab work, some speculation
Less aging
What do we not yet know to our satisfaction?
Item Unknown Help
FieldPerformance
Long-term performance APT (NCAT, Caltrans PRC)NCHRP Project 09-47
Laboratory Performance
Mix designCharacterization tests
NCHRP Project 09-43NCHRP Project 09-47
Energy Use Good protocol for quantification Life cycle assessment (LCA)NCHRP Project 09-47
Emissions Good protocol for quantification Life cycle assessment (LCA)NCHRP Project 09-47
Fumes/smell Quantification is very complex Simple method neededNCHRP Project 09-47
Compaction EuropeNumerous U.S. trials
≥ HMANCHRP Project 09-47
Aging Aging effects of WMA Less aging
Specification Best way(s) of doing it TWGLeader states (e.g., TX)
A “life cycle assessment” can help assess the energy, environmental and materials picture.
Life cycle assessment (LCA) is a good tool to assess the overall life cycle impact of WMA.
Life cycle assessment (LCA)A protocol to assess the environmental, economic, and social impacts of an industrial system.
The life cycle of the industrial system extends from cradle-to-grave: from materials acquisition and production, through manufacturing, system use and maintenance, and finally through the end of the system’s life.
Essentially an accounting tool.
oil extraction
Aggregate Quarry
transport refinery transport
transport
placement transport
emissions waste hazardouswaste
other outputs
water fuel
other inputs
hma plant
An example of LCA processes, inputs and outputs to consider for
HMA paving.
For a given unit of production (e.g., 1 lane-mile of pavement) a typical LCA gives a range of outputs.
• Amount of materials used (tonnes)• Total energy use (MJ)• Water consumption (kg)• Emissions
– Global warming potential (tonnes of CO2 equivalent)– Nitrogen oxides – NOx (kg)– Sulfur dioxide – SO2 (kg) – Particulate matter – PM10 (kg)– Carbon Monoxide – CO (kg)
• Toxic things– Human toxicity potential – Mercury – Hg (g)– Lead – Pb (g)– Hazardous waste (kg)– Polycyclic aromatic hydrocarbons (PAHs)
0 1 2 3 4
CRCP
HMA
Pav
emen
t
Total Energy Consumed (TJ)
Raw Materials Extraction
Manufacturing
Placement
Amount of energy consumed by 100 US households in a year (4 TJ) - On average, a US household consumes 11,000 KWh of energy per year - Does not include anything outside of the house (e.g., cars, fuel, etc.)
An example of a LCA output relating to energy consumption in pavement construction.
Data from: Zapata and Gambatese, Energy Consumption of Asphalt and Reinforced Concrete Pavement Materials and Construction, J. of Inf. Sys., vol. 11, issue 1, p. 9-20.
Amount of Energy Required to Build 1 Lane-Mile of Pavement
Notes:•90%+ from manufacturing•Numbers change a lot depending on assumption
9-inch CRC Pavement(6 inches base material)
12-inch HMA Pavement(6 inches base material)
94%3% 3%
91%7% 2%
3.7 TJ
3.0 TJ
4.0 TJ
An example of a LCA output relating to the contribution of different processes to environmental outcomes.
Contribution of Main Processes on Environmental Impacts of HMA
Hassan, M.M. (2009). Life-Cycle Assessment of Warm-Mix Asphalt: An Environmental and Economic Perspective. Presentation at the 88th Annual Meeting of the Transportation Research Board, Washington, D.C., 11-15 January, 2009.
0 500 1,000 1,500 2,000 2,500 3,000
Waste Generated (Tons)
Extraction Manufacturing Construction End of Life
Waste from 1,000 average US households/yr- On average 2 tons/household/yr
An example of a LCA output relating to waste production in roadways.
Data from: Rajendran and Gambatese, Solid Waste Generation in Asphalt and Reinforced Concrete Roadway Life Cycles, J. of Inf. Sys., vol. 13, issue 2, p. 88=96.
Waste Generated by 1 Lane-Mile of PavementNotes:•Most from manufacturing and EOL•Numbers change a lot depending on assumption
9-inchCRC Pavement(6 inches base)
10-inch HMA Pavement(15 inches base)
41% 52%6%1%
38% 59%2%1% 2,852 tons
2,225 tons
2,000 tons
0.200.64
1.801.48
2.782.88
1.99
2.05
1.68
0.05
0.970.78
1.05
2.17
2.21
0
1
2
3
4
5
6
7
Zapata, Gambetese (2005) Mroueh, et al. (1999) Hoang et al. (2005) Athena (2006) Athena (2006) 20% RAP
Tota
l Ene
rgy
(TJ)
maintenance
placement
manufacturing
extraction
3.03
3.85
5.37
6.02
4.46
Total Energy Use for 1 lane-mile of HMA pavementSt
ruct
ure
(inch
es)
0
12
24
= HMA= Base= Subbase
LCAs are a defensible protocol for quantifying the energy, environmental and materials aspects of WMA.
• Account for all processes associated with HMA– Include WMA additive production/transport– Include human health benefits beyond criteria pollutants
• Isolate improvements attributable to WMA
But…there are issues with the way we do LCA.
• Functional unit– describes the function and performance of the
subject of the product or process being studied – Example: 1 lane-mile of pavement capable of
supporting 100 million ESALs over 50 years
Implies1.Structural design2.Traffic measurement3.Defining maintenance/rehabilitation methods4.Performance standard
And…we are missing a good chunk of the data we need to calculate a good LCA and it is expensive to get this data.
Process Data Source
Issues
Fuel/Energy GREET Generic vehicle types
Transport GREET Generic vehicle types
Asphalt Production Eurobitume Dated European data
Aggregate Production
Eurobitume Dated European data
HMA Production EPA AP-42Eurobitume
Only data for average plantCannot differentiate by process
Laydown EPA NONROAD
Uses generic engine hp sizes
WMA Additive None No good information
GREET: Greenhouse Gases, Regulated Emissions, and Energy Use in Transportation Model from Argonne National LaboratoriesEurobitume: LCI report for Eurobitume (European-type Asphalt Institute)EPA NONROAD: EPA emissions model for non-road vehiclesEPA AP-42: EPA emissions factors (emissions tied to quantity of material)
The I-90 Sasobit WMA job (June 2008)
12,500 tons½-inch Superpave0.25-ft mill-and-fill
Right lane only
Key ParametersHMA Class ½-inch WMA Class ½-inch
Binder content
5.2% 5.2%
Binder type PG 76-28 PG 76-28 (83-28 w/Sasobit)
Gyrations 100 100
RAP content 20% 20%
Tonnage 7,781 tons 4,724 tons
Sasobit 0 2% by binder weight
Cost/ton $58.00 $64.10
Production temp
340-350°F 300°F
Laydown temp
300-330°F 270-300°F
CPF 1.03 1.04
Compaction PF
1.02-1.05 1.03-1.05
Average density
93.60% of Rice 93.67% of Rice
Fuel usage 1.4 gal/ton (diesel) 1.07 gal/ton (diesel)23.5% less
Roller pattern 5-8 passes in 30 min
same
HMA: 12 June 2008
HMA: 12 June 2008
WMA: 23 June 2008
WMA: 23 June 2008
Open Path FTIR
Preliminary LCA results from I-90
Grant County power mix. This is one of the cleanest mixes in the nation.
Other (Solar, Wind,Biomass, etc.)
1.35%
Nuclear5.52%
Natural Gas3.06%
Coal8.21%
Hydro82.84%
A few observations.
• Mix temperature drives everything– We can gather less data and get same value
• How to simplify– Report mix temperature
• Temperature vs. criteria pollutants for types of plants• Temperature vs. vapor pressure for HMA compounds• Temperature vs. vapor pressure is NOT linear• The first 50°F is bigger than the second 50°F
– Report burner performance– Report fuel usage
Summary
• We have learned a lot about WMA• LCA can provide a defensible protocol for
analyzing environmental/energy factors• Need to gather a few pieces of information
to reduce the environmental data needed– HMA temperature vs. criteria pollutants– HMA temperature vs. asphalt fumes