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DROVE: An algorithm for the disaggregation of on-road mobile source emission inventories

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DROVE: An algorithm for the disaggregation of on-road

mobile source emission inventories

C a r l o s D . G ó m e z ,

C a r l o s M . G o n z á l e z

, F r a n c i s c o J . G a r c ía , B e a t r i z H . A r i s t i z á b a l

G r u p o d e Tr a b a j o A c a d é m ic o e n I n g e n i e r ía H i d r á u l ic a y A m b i e n t a l

U n i v e r s i d a d N a c i o n a l d e C o l o m b i a S e d e M a n i z a le s

(2)

Latin America and Caribbean region:

81%

of people living in urban areas

(

North America:

82%

.)

In

Colombia

,

90%

of people are going to live in urban areas to year

2050

(UN projection)

Mobile source emissions

:

Main problem in cities in terms of

air quality

It is necessary to improve

Air Quality

Management Plans (PGCA):

Identification and estimation of emissions

from pollutant sources.

(3)

MADS, 2010; SIAC, 2011.

Air Quality Management Plans

(4)

Vehicular emissions disaggregation in medium-sized cities

Few studies in South America

=> Cities with

population less than 1 million

inhabitants

In

Colombia:

studies have focused on principal cities (Bogotá, Medellín) and few

medium-sized areas (e.g. Manizales, Envigado, CAR Municipalities).

Problems such as the

lack of available information

:

Road network distribution,

vehicular traffic data.

Peñaloza, 2010; Gómez et al., 2018; Dávila, 2015; Londoño et al., 2011.

DROVE (Disaggregation of on-ROad Vehicle Emissions)

(5)

DROVE model structure

Required input

Optional input

Defined by user

DROVE internal estimation

Final product

Road

Network

Grid

Based on a desired

domain, e.g. cells of

1 km x 1 km.

Additional

information

If available, road

classification, traffic

flows.

Splitted Road

Network

Split the road segments

using the grid

Gridded

emissions

Dissagregation

Factor

Total

Emissions

Outputs

- Graphical

- Text file

(6)

DROVE model structure

Required input

Optional input

Defined by user

DROVE internal estimation

Final product

Road

Network

Grid

Based on a desired

domain, e.g. cells of

1 km x 1 km.

Additional

information

If available, road

classification, traffic

flows.

Splitted Road

Network

Split the road segments

using the grid

Gridded

emissions

Dissagregation

Factor

Total

Emissions

Outputs

- Graphical

- Text file

(7)

DROVE model structure

Required input

Optional input

Defined by user

DROVE internal estimation

Final product

Road

Network

Grid

Based on a desired

domain, e.g. cells of

1 km x 1 km.

Additional

information

If available, road

classification, traffic

flows.

Splitted Road

Network

Split the road segments

using the grid

Gridded

emissions

Dissagregation

Factor

Total

Emissions

Outputs

- Graphical

- Text file

(8)

DROVE model structure

Disaggregation factor:

Normalized data for each grid-cell or road segment, which represents the

magnitude of emission.

𝐷𝐹

𝑗,𝑘,𝑚,𝑡

=

𝛾

𝑗,𝑘,𝑚,𝑡

∗ 𝑙

𝑖,𝑗,𝑚

σ

0

𝑖

𝛾

𝑗,𝑘,𝑚,𝑡

∗ 𝑙

𝑗,𝑚

𝐷𝐹

: Disaggregation factor

𝑙

: Length of road segment

𝑗

: Road segment or grid-cell id

𝛾

: Weighting factor

𝑘

: Vehicular category

𝑡

: Time (hour of the day)

(9)

DROVE model structure

Disaggregation factor:

Normalized data for each grid-cell or road segment, which represents the

magnitude of emission.

𝐷𝐹

𝑗,𝑘,𝑚,𝑡

=

𝛾

𝑗,𝑘,𝑚,𝑡

∗ 𝑙

𝑖,𝑗,𝑚

σ

0

𝑖

𝛾

𝑗,𝑘,𝑚,𝑡

∗ 𝑙

𝑗,𝑚

𝐷𝐹

: Disaggregation factor

𝑙

: Length of road segment

𝑗

: Road segment or grid-cell id

𝛾

: Weighting factor

𝑘

: Vehicular category

𝑡

: Time (hour of the day)

This first version of DROVE contains 3 approximations:.

Length of road segments

Length of road segments weighted by type of road

Length of road segments weighted by vehicular flow

(10)

DROVE. Available types of code

Base model build in ArcGis using

ModelBuilder

R code

Phyton

(11)

Application in the Andean medium-sized Manizales city

Altitude (m.a.m.s.l.) 2150

54 km

2

urban area

400436 inhab.

44.1 vehicles/100 inhabitants

(12)

MODELING

Biogenic volatile organic compounds in Colombia: First specialized model and

determining emission factors

(GEC G2 / Thursday, August 15 / 11:30

– 11:45)

MONITORING

Concentrations

and

gas-particle

partition

of

polycyclic

aromatic

hydrocarbons.

(GEC G2 / Thursday,

August 15 / 10:15

– 10:30)

Exposure to particulate matter in

microenvironments

related

to

transportation in Manizales

(Poster

session)

Study of the historical behavior of

particulate matter in Manizales and

analysis

of

the

relationship

PM

2.5

/PM

10

(Poster session)

EMISSION

SOURCES

Update

of

the

atmospheric

emission inventory

– year 2017

(Auditorium / Thursday, August

15 / 16:00

– 16:15)

Estimation of PM

2.5

and Black

Carbon emissions from on-road

vehicular sources

(Auditorium /

Thursday, August 15 / 16:30

16:45)

Grupo de Trabajo Académico en Ingeniería Hidráulica y Ambiental
(13)

Application in the Andean medium-sized Manizales city

Emissions per grid-cell

Some applications

Emission hotspots

(14)

Application in the Andean medium-sized Manizales city

Emissions per grid-cell associated

with a lat-lon centroid

Some applications

Input file for air quality models

Compatible with the emissions

preprocessor:

Another Assimilation

System for WRF-Chem (AAS4WRF)

(15)

Application in the Andean medium-sized Manizales city

Road level emissions

Some applications

Emission hotspots

Analysis with ambient air quality data

Integration of environmental and

transport policies

(16)

Ongoing work

Final tests of temporal disaggregation algorithm

R and Phyton code with QGIS

Official publication: Open source code

(17)

Acknowledgments

CONVENIO INTERADMINISTRATIVO 107-2018

Corporación Autónoma Regional de Caldas, CORPOCALDAS

Grupo de Trabajo Académico en Ingeniería Hidráulica y Ambiental

Universidad Nacional de Colombia Sede Manizales

(18)

Borge, R., Lumbreras, J., Pérez, J., de la Paz, D., Vedrenne, M., de Andrés, J.M., Rodríguez, M.E., 2014. Emission inventories and modeling requirements for the development of air quality plans. Application to Madrid (Spain). Sci. Total Environ. 466–467, 809–819. https://doi.org/10.1016/j.scitotenv.2013.07.093

Davis, N., Lents, J., Osses, M., Nikkila, N., Barth, M., 2005. Development and Application of an International Vehicle Emissions Model Transportation Research Board 81st Annual Meeting. Transp. Res. 1–20.

Gómez, C.D., González, C.M., Osses, M., Aristizábal, B.H., 2018. Spatial and temporal disaggregation of the on-road vehicle emission inventory in a medium-sized Andean city. Comparison of GIS-based top-down methodologies. Atmos. Environ. 179, 142–155. https://doi.org/10.1016/j.atmosenv.2018.01.049

González, C.M., Gómez, C.D., Rojas, N.Y., Acevedo, H., Aristizábal, B.H., 2016. Relative impact of on-road vehicular and point-source industrial emissions of air pollutants in a medium-sized Andean city 152, 279–289. https://doi.org/10.1016/j.atmosenv.2016.12.048

González, C.M., Ynoue, R.Y., Vara-Vela, A., Rojas, N.Y., Aristizábal, B.H., 2018. High-resolution air quality modeling in a medium-sized city in the tropical Andes: Assessment of local and global emissions in understanding ozone and PM10 dynamics. Atmos. Pollut. Res. 9, 934–948. https://doi.org/10.1016/j.apr.2018.03.003

Loibl, W., Orthofer, R., Winiwarter, W., 1993. Spatially disaggregated emission inventory for anthropogenic NMVOC in Austria. Atmos. Environ. Part A. Gen. Top. 27, 2575– 2590. https://doi.org/10.1016/0960-1686(93)90031-S

Mangones, S.C., Jaramillo, P., Fischbeck, P., Rojas, N.Y., 2019. Development of a high-resolution traffic emission model: Lessons and key insights from the case of Bogotá, Colombia. Environ. Pollut. 253, 552–559. https://doi.org/10.1016/j.envpol.2019.07.008

Ossés de Eicker, M., Zah, R., Triviño, R., Hurni, H., 2008. Spatial accuracy of a simplified disaggregation method for traffic emissions applied in seven mid-sized Chilean cities. Atmos. Environ. 42, 1491–1502. https://doi.org/10.1016/j.atmosenv.2007.10.079

Parra, R., Jiménez, P., Baldasano, J.M., 2006. Development of the high spatial resolution EMICAT2000 emission model for air pollutants from the north-eastern Iberian Peninsula (Catalonia, Spain). Environ. Pollut. 140, 200–219. https://doi.org/10.1016/j.envpol.2005.07.021

Saide, P., Zah, R., Osses, M., Ossés de Eicker, M., 2009. Spatial disaggregation of traffic emission inventories in large cities using simplified top-down methods. Atmos. Environ. 43, 4914–4923. https://doi.org/10.1016/j.atmosenv.2009.07.013

Shu, Y., Lam, N.S.N., 2011. Spatial disaggregation of carbon dioxide emissions from road traffic based on multiple linear regression model. Atmos. Environ. 45, 634–640. https://doi.org/10.1016/j.atmosenv.2010.10.037

Thunis, P., Clappier, A., Tarrason, L., Cuvelier, C., Monteiro, A., Pisoni, E., Wesseling, J., Belis, C.A., Pirovano, G., Janssen, S., Guerreiro, C., Peduzzi, E., 2019. Source apportionment to support air quality planning: Strengths and weaknesses of existing approaches. Environ. Int. 130, 104825. https://doi.org/10.1016/j.envint.2019.05.019 Tuia, D., Ossés de Eicker, M., Zah, R., Osses, M., Zarate, E., Clappier, A., 2007. Evaluation of a simplified top-down model for the spatial assessment of hot traffic emissions in mid-sized cities. Atmos. Environ. 41, 3658–3671. https://doi.org/10.1016/j.atmosenv.2006.12.045

United Nations, 2019. World Urbanization Prospects 2018. New York.

(19)

THANKS

GRACIAS

Carlos David Gómez

[email protected]

Carlos Mario González

[email protected]

[email protected]

References

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