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GENERAL40898
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Last modified
8/24/2016 8:00:00 PM
Creation date
11/23/2007 10:55:22 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1999002
IBM Index Class Name
General Documents
Doc Date
7/22/1999
Doc Name
FINAL ENVIRONMENTAL IMPACT STATEMENT VOL 1 CHAPTER 5 AND 6
Media Type
D
Archive
No
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CNAPTERFIVE D~'eit EIS Reulslons <br />o,.r.,.ace io..vi.. ,.f.,,.c,.:ce ,. ..,........,c.. n~nr~~ .eco.,~oa .,. ,r.o .,,..,,.~~' <br />based on recent analyses, the project h:cs quantified <br />potential hydrocazbon (VOC) emissions from the wellhead gas sepazators, they stripper system, <br />and the combustion sources to be 38.5 tpy. This level was calculated using conservative <br />assumptions and the maximum production rate of 1.4 million tpy. The CDPF[E-APCD has <br />proposed requiring quarterly monitoring of VOCs and I-IAPs (benzene, toluene, ethyl benzene <br />and xylene; or BTEX) from the process stream as part of their air pollutant emissions operating <br />permrt⢠<br />The Proposed Action includes several environmental protection measures as ~~art of the project <br />design. Specific to air quality, fugitive dust control is considered in the estimate of impacts from <br />construction activities, including unpaved roads. Process emission sources include air pollution <br />control and pollution prevention in the design. These control measures have been taken into <br />consideration in this impact assessment, as well as in the modeling. In addition, once the <br />CDPHE-Air Pollution Control Division has reviewed the permit application :submitted for the <br />project, periodic federal sampling requirements (in accordance with methods specified in 40 <br />CFR 60), and additional State of Colorado monitoring procedures would be required to <br />demonstrate emissions permit compliance. <br />Page 4-23; Meteorological Data <br />The simulation of both short-term and annual average impacts was performed using the ISCST3 <br />dispersion model. This model requires hourly values of temperature, wind slreed, wind direction <br />and atmospheric stability class. Monitoring stations in the general region were surveyed for the <br />availability of data. For the Parachute Site, one yeaz of data obtained by Unocal in 1989 at the <br />Parachute Creek Oil Shale Upgrade Facility was selected. For the Piceance Mite, one year of data <br />from the Cathedral Bluffs Project Tract Cb collected during 1984, was selected. A wind rose <br />portraying the wind speed and direction for the Piceance and Parachute Sites is provided in <br />Figures D-3 and D-4, respectively (Appendix D). One yeaz of site specific data generally <br />represents the typical conditions that would be encountered. The CDPHE ha<s approved the use of <br />the one-yeaz of meteorological data for the Yankee Gulch facilities New Source Review PSD <br />permit analysis. Similazly, the BLM has determined that these data are adequate for preparing <br />the EIS arrguality impact analysis. Further detail regazding the meteorological data is presented <br />in the av oualiri construction <br />Modeling Results/Analysis <br />Piceance and Parachute Sites <br />An arr modeling analysis was performed for the Proposed Action as part of the air quality <br />construction permit application. The modeling analysis included a National Ambient Air Quality <br />Standards (NAAQS) analysis, comparisons to the PSD Class I and II increments, visibility <br />analyses, and Class I water analyses. <br />5-20 <br />
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