VOCA Emissions InventoryÑFebruary 2010 Release

Scott N. Spak and Marcelo Mena

 

Downloads

 

Sectoral CSV and netCDF files: voca_emissions.zip (15 MB)

Temporally and vertically allocated speciated combined netCDF file: voca_emis.nc (2.5 GB)

 

Description: This inventory represents anthropogenic and limited volcanic emissions for South America, through a combination of the most recent Chilean emissions inventory with a gridded global emissions inventory. The Chilean inventory is based on the Comisi—n Nacional del Medio Ambiente (CONAMA) 2008 reported point source emissions (including the 2008 Pollution Prevention Plan smelter emissions) and estimated municipal mobile and residential inventories. Outside of Chile, anthropogenic area emissions are derived from the combination of the 1¼ x 1¼ EDGAR FT 2000 gaseous inventory (Olivier and Berdowski, 2001) with Tami Bond's present-day black carbon and organic carbon inventory (Bond et al., 2004), gridded through the LandScanTM 2006 Global Population distribution and resampled to a 0.10833¼ (roughly 12 km) latitude-longitude grid. Sulfur dioxide emissions for Peruvian smelters and volcanoes in Peru, Ecuador, and Colombia, were estimated by replicating the analysis of Carn et al. (2007) for daily OMI SO2 PBL retrievals during the VOCALS REx experimental period (10/15/2008 - 11/15/2008).

 

File format: Raw sectoral-level mobile, anthropogenic area (residential and industrial), and large point source emissions are provided in comma-separated value (CSV) and gridded netCDF files. The combined netCDF file includes the sum of all three sectors with vertical, temporal, and speciation profiles applied. See the RETRO software tools page for mass-conserving emissions regridding options.

 

Projection: The data are not projected, but can be used as a ÒGeographicÓ projection with GIS software packages. The data are referenced by latitude/longitude (WGS84) coordinates.

 

Units: All emissions are in metric tons per year

 

Species: Emissions are estimated for NOx, SO2, VOCs, CO, and NH3 in the gas phase, with PM2.5 and PM10 for Chile only and black carbon and primary organic carbon outside Chile. 

 

Per EDGAR conventions,

NOx = tons NO2

SO2 = tons SO2

Black carbon = tons carbon

Organic carbon = tons carbon (not organic mass)

VOCs = total VOC mass (not just C) across all compounds. For emissions processing, assume 1 gVOC = 0.07246 mol = average molecular composition of C + 1.8 H.

 

Particle speciation: Particles are not speciated in the Chilean inventory. Suggested PM2.5 speciation:

 

Species

% of PM2.5 Mass

Primary organic carbon

20%

Black carbon

10%

Crustal materials

70%

 

We assume all coarse mode emissions (PM10 not included in PM2.5) are crustal in origin.

 

VOC speciation: is model dependent. We allocate VOC mass to the lumped SAPRC-99 mechanism independent of sector, as an example:

 

SAPRC Species

% of VOC Mass

ACET

0.0117

ALK3

0.0767

ALK4

0.0982

ALK5

0.0945

ARO1

0.0718

ARO2

0.0516

C2H2

0.0454

C2H6

0.1498

C3H6

0.0342

C3H8

0.0921

CCHO

0.0048

CRES

0.0006

ETHENE

0.1455

HCHO

0.0344

MEK

0.0085

OLE1

0.0293

OLE2

0.0476

RCHO

0.0033

 

Allocating VOC mass by emissions activity using the US EPA SPECIATE database could improve speciation.

 

Vertical Profiles: Stack height for large point sources were available for only the largest sources, and ranged from 50 m to 152 m; where they were not available, we assume a static distribution that accounts for plume rise:

 

Height AGL

Point Sources

Volcanoes

Area Sources

<30 m

 

10%

70%

30-80 m

30%

20%

30%

80-120 m

50%

40%

 

120-250 m

20%

20%

 

>250 m

 

10%

 

 

Diurnal Profiles: Point source emissions are assumed constant. Area source diurnal cycle (as a % of total) from 0:00 to 23:00 local time is estimated as

0.0389, 0.0303, 0.0282, 0.0282, 0.0282, 0.0282, 0.0389, 0.0476, 0.058,0.043,0.0387, 0.0387, 0.0429, 0.0429, 0.0387, 0.0387, 0.045, 0.054, 0.058, 0.052, 0.0476,0.0476, 0.041, 0.0389

 

Caveats

- biogenic emissions are not included.

- biomass burning emissions are not yet included. We recommend GFED monthly 1¼ x 1¼ emissions or daily estimates from MODIS fire detection and intensity products. However, South American biomass burning levels during VOCALS REx were relatively low.

- fumarolic emissions estimates for six volcanoes (Galeras, Guagua Pichincha. L‡scar, Lastarria, Nevado del Ruiz, and Reventador). Although Villarrica was active during the REx campaign, emissions were carried eastward and did not impact the VOCALS region.

- the only Peruvian smelters included in the large point source inventory are Ilo and La Oroya. All other Peruvian emissions come from EDGAR.

 

Status: Barring bug fixes, this is the final release for VOCA modeling. However, development is ongoing, and user contributions are greatly appreciated.

 

Questions: Scott N. Spak (scott-spak@uiowa.edu)

 

References

 

Bond, T.C., et al. (2004), A technology-based global inventory of black and organic carbon emissions from combustion," J. Geophys. Res., 109, D14203, doi:10.1029/2003JD003697.

 

Carn, S.A., N.A. Krotkov, A.J. Krueger, K. Yang, and P.F. Levelt (2007). Sulfur dioxide emissions from Peruvian copper smelters detected by the Ozone Monitoring Instrument, Geophys. Res. Lett. 34, L09801, doi:10.1029/2006GL029020.

 

Olivier, J.G.J. and J.J.M. Berdowski (2001). Global emissions sources and sinks. In: Berdowski, J., Guicherit, R. and B.J. Heij (eds.) The Climate System, pp. 33-78. A.A. Balkema Publishers/Swets & Zeitlinger Publishers, Lisse, The Netherlands. ISBN 905809 255 0.