Energy and Environment Laboratory, RCE Curitiba Parana, Brazil

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Coordinator: Prof. Marcelo Risso Errera, Ph.D. UFPR – Federal University of Paraná Telefone: +55(41) 3361-3230 / 3030 E-mail: [email protected] Energy and Environment Laboratory Member of CRIE (RCE-Curitiba) Curitiba, Oct. 19, 2016

Transcript of Energy and Environment Laboratory, RCE Curitiba Parana, Brazil

Page 1: Energy and Environment Laboratory, RCE Curitiba Parana, Brazil

Coordinator: Prof. Marcelo Risso Errera, Ph.D.

UFPR – Federal University of ParanáTelefone: +55(41) 3361-3230 / 3030 E-mail: [email protected]

Energy and Environment Laboratory

Member of CRIE (RCE-Curitiba)

Curitiba, Oct. 19, 2016

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100 yearsUFPR – Federal University of Paraná

(historic building downtown Curitiba)

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100 years33.000 students and 2.500 faculty members

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Curitiba and its sustainability initiatives

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1st 3rd Curitba

http://grist.org/article/cities3/

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Ciclo vida website

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Theory to assess the contributions of zero emission vehicles (ZEV) in

paradigm shift in urban fleets: the effect of the effect of urban fleet size on automotive vehicles

emissions

Errera, Marin and Stanescu

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We love cars.

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We love cars

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Do Zero Emission Vehicles

(electric, hydrogen) contribute do

urban emissions ?

(in paradigm shift of urban fleets:

the effect of the effect of urban fleet size on automotive

vehicles emissions)

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Errera/set/09 28

Summary

Problem statement (factors) Urban mobility (needs, desires, choice criteria, ....) Modes (types, mass or individual transit) Infra-structure (city form, traffic management) Air quality conditions (emissions and dispersion)

Model types for traffic simulation First simulators (Lighthill and Whitman, 1955) Deterministic, statistic and automatons

Validation, calibration and limitations Usual traffic parameters Field data

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The problem

The matter of urban fleet emissions Factors that determine the emissions What is needed to control (stabilize or reduce)

Vehicles emissions Lab tests, summed emissions, scale, technology,

vehicle use, fuel, driving skills, traffic management

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Purpose of the Model

Purpose: To develop a model to estimate vehicle emissions

associated to traffic conditions (mainly fleet size) Model type:

Macroscopic, deterministic and empirical, saturated traffic, speed dependent emissions, unchanging infra-estructure

Adapted data

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The model

Fleet size (N ) Mean speed (v

)

Emission Factors (FE )

Fleet composition ( ) and average yearly mileage (x)

Total anual emissions (Et )

traffic data

Lab tests

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Present model (traffic)

k=N

route extension=

NL

Fundamental relations (Smit, R., 2006):

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v = -0,0277(k) + 30,725R 2 = 0,9703

0

5

10

15

20

25

30

0 100 200 300 400 500

k ( v e h i c l e s / k m )

V m

e a

n ( k

m /

h )

After data from CET, 2007

Estimative based on field data (traffic engineering company of The City of São Paulo) (L≈18 thousand km):

Curitiba (L = 4381km, IPPUC)

Present model (traffic)

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Present model (emissions)

Average speed varies solely with traffic conditions

Fuel burning pollutants (CO, NOx, HC, pm) Category (diesel and gasoline) Grouped by category and fuels Engine @ hot regime Stop-go traffic not detailed

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Lab tests Chassi dinamometer

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Gasoline vehicles (passenger cars)

CETESB / IPEA, 1998

Diesels vehicles (bus and trucks)

Present model (emissions)

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Present model (emissions)

Total yearly emissions [ton poll / year]

Pollutant, k; category j, period (year) i Mean Yearly Traveled distance, xj Category (j) fleet size nj EFj average speed and pollutant dependent

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Goal: To estimate fleet size effect on the overall yearly emissions [ton pollt / year]

Scenario: Curitiba Registered fleet Average mileage Average speed profile adapted from São Paulo vfree = 40 km/h

CO e NOx emissions Parametric variation

respect to fleet size

After DETRAN ref. 1996-2005

Grouped categories

Composition (aj ) typical, %

Year mileage, xj , km/yr

Automobiles 82,84 12.000

Bus + Trucks 17,16 80.000

Others 0,0 -

Total 100,00 -

Data input

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0

500000

1000000

1500000

2000000

2500000

3000000

3500000

0,0 0,5 1,0 1,5 2,0 2,5 3,0fleet size, Ni in vehicles [ millions ]

ETa

,CO

, E

Ta,

NO

x [

ton

/ yea

r ]

CO

____ with congestion effects - - - - without congestion effects

NOx

Variation of the overall yearly emissions according to fleet expasion

Traffic saturation effects

results

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0

500

1000

1500

2000

2500

3000

3500

4000

0,0 0,5 1,0 1,5 2,0 2,5 3,0fleet size, Ni in vehicles [ millions ]

dE

Ta,k

/ dN

[ to

n / 1

000

veh.

]

CO

____ with congestion effects - - - - without congestion effects

NOx

results

Emissions variation rate with fleet size

Traffic saturation effect

Marginal emissions

Equivalent to emissions caused by ZEVs in the fleet

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Conclusion

The model captured marginal pollution phenomena and provided estimates under simplified conditions

Marginal pollution would be present even for ZEVs That is ZEVs create traffic that in turn creates marginal emissions

from other conventional fuel cars Validation, calibration for each city is needed

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Agradecimentos

Marcelo Risso ErreraEnergy and Environment Lab / GEANEXEnvironmental Engineering Department – UFPRUniversidade Federal do Paraná

[email protected]