Chromium VI Air Monitoring in Kansas City, Kansas
Background
As part of the Mineral Wool Production and Wool Fiberglass Manufacturing
rulemaking, EPA sent requests to 29 fiberglass manufacturing plants across
the nation, asking them to provide emissions data. From this information,
EPA learned that the CertainTeed plant in the Fairfax Industrial
District of Kansas City, Kansas, showed chromium VI emissions that
were higher than any other facility in the industry. It is
believed that refractory bricks used in CertainTeed’s manufacturing
process are the source of the facility’s chromium VI emissions.
To determine if these emissions may pose health concerns for local
residents, EPA Region 7 decided to conduct air monitoring at John
Garland Park, located between the facility and nearby residential
areas.
For more details on the sampling plan, see:
Quality Assurance Project Plan - Chromium VI Air Study, Kansas City, Kansas (PDF) (86 pp, 15.17MB, About PDF)
Preliminary Results
For more details on the sampling plan, see:
Quality Assurance Project Plan - Chromium VI Air Study, Kansas City, Kansas (PDF) (86 pp, 15.17MB, About PDF)
Results of air monitoring show that the chromium VI levels in air do
not indicate a health concern. Region 7 placed monitoring
equipment in John Garland Park in December 2011 to measure chromium
VI concentrations in the air and to determine whether further action,
if any, is necessary. Chromium VI air sample results for December 2011
through March 2012 are summarized below.
The CertainTeed plant normally operates two furnaces (K1 and K2). K2 has temporarily ceased operations. Only the K1 furnace was operating during the air monitoring conducted after Dec. 11, 2011. Chromium VI air sampling has been suspended due to the low levels detected in the outdoor air samples. If operation of the K2 furnace resumes, EPA will re-evaluate the need to resume chromium VI air monitoring.
Air Sampling Results
in nanograms per cubic meter (ng/m3)The CertainTeed plant normally operates two furnaces (K1 and K2). K2 has temporarily ceased operations. Only the K1 furnace was operating during the air monitoring conducted after Dec. 11, 2011. Chromium VI air sampling has been suspended due to the low levels detected in the outdoor air samples. If operation of the K2 furnace resumes, EPA will re-evaluate the need to resume chromium VI air monitoring.
December 2011 |
|||||||||||
Sample Date | 12/8 | 12/11 | 12/14 | 12/17 | 12/20 | 12/23 | 12/27 | 12/29 | |||
Monitor C1 | 0.015 | *ND | 0.0327 | 0.0128 | 1.05 | 0.0132 | 0.0503 | 0.0126 | |||
Monitor C2 | 0.0162 | *ND | 0.0291 | 0.0129 | 1.02 | 0.0121 | **NA | 0.0138 | |||
Wind Direction | N | SSW | SSW | SW | NE | SW | NW | SW | |||
January 2012 |
|||||||||||
Sample Date | 1/1 | 1/4 | 1/7 | 1/11 | 1/13 | 1/16 | 1/19 | 1/22 | 1/25 | 1/28 | 1/31 |
Monitor C1 | *ND | 0.0195 | 0.0593 | 0.0171 | *ND | 0.022 | 0.0411 | *ND | 0.0471 | *ND | 0.0162 |
Monitor C2 | *ND | 0.0183 | 0.0568 | 0.0411 | 0.0146 | 0.0094 | 0.037 | *ND | 0.0447 | *ND | 0.011 |
Wind Direction | NW | NW | NE | NW | WNW | SSW | NNE | S | ENE | SW | SW |
February 2012 |
|||||||||||
Sample Date | 2/3 | 2/6 | 2/9 | 2/12 | 2/15 | 2/18 | 2/21 | 2/24 | 2/27 | ||
Monitor C1 | 0.0952 | 0.0079 | 0.0142 | 0.0173 | 0.0909 | 0.087 | *ND | *ND | 0.0284 | ||
Monitor C2 | 0.105 | 0.0132 | 0.0176 | 0.0199 | 0.111 | 0.0963 | *ND | *ND | 0.028 | ||
Wind Direction | ENE | NW | SW | SSE | ENE | NE | NW | SW | N | ||
March 2012 |
|||||||||||
Sample Date | 3/1 | 3/4 | 3/7 | 3/10 | 3/13 | 3/16 | 3/19 | ||||
Monitor C1 | 0.0272 | 0.0078 | *ND | 0.0202 | 0.0843 | 0.0086 | 0.0089 | ||||
Monitor C2 | 0.0314 | 0.0078 | *ND | 0.0167 | 0.0833 | 0.0093 | 0.0081 | ||||
Wind Direction | N | ENE | NW | SSE | S | SSE | SSE |
* ND – Non detect | ** Monitor malfunction
EPA also used computer modeling on stack test emissions
data in reaching its initial conclusions that there are no
immediate health concerns. The stack test emissions data were
provided to EPA by CertainTeed as part of the rulemaking and
additional tests ordered by the Agency. A second round of stack
test sampling by all 29 U.S. fiberglass plants has been requested
by EPA’s Office of Air Quality Planning and Standards (OAQPS).
OAQPS has also asked manufacturers to provide the amount of chromium
VI in their refractory bricks.
Recent soil samples taken by EPA as part of another project in the Garland Park Landfill area also did not indicate chromium levels that would be of health concern.
Chromium VI (Hexavalent Chromium)
Recent soil samples taken by EPA as part of another project in the Garland Park Landfill area also did not indicate chromium levels that would be of health concern.
Chromium occurs naturally in rocks, animals, plants, and soil. It
can exist in several different forms. Depending on the form it takes,
it can be a liquid, solid, or gas. The form of chromium of most concern
from a health perspective is chromium VI, also called hexavalent
chromium. Inhalation of chromium VI at high levels can damage the
respiratory system and cause cancer. Other forms of chromium are
chromium (0) and chromium (III). Chromium (0) is the metal form of
chromium. It is used in steel manufacturing. Chromium VI and chromium
(III) are used for chrome plating, dyes and pigments, refractory bricks,
leather tanning, and wood preserving. Chromium (III) is an essential
nutrient that helps the body use sugar, protein, and fat.
Exposure to chromium occurs from ingesting contaminated food or drinking water or breathing contaminated air. It is odorless and tasteless. Air emissions of chromium are predominantly of chromium (III), and in the form of small particles or aerosols. The largest industrial sources of chromium in the atmosphere are those related to ferrochrome production. Ore refining, chemical and refractory processing, cement-producing plants, automobile brake lining and catalytic converters for automobiles, leather tanneries, and chrome pigments are also sources of chromium emissions to ambient air.
For more information, please contact: Exposure to chromium occurs from ingesting contaminated food or drinking water or breathing contaminated air. It is odorless and tasteless. Air emissions of chromium are predominantly of chromium (III), and in the form of small particles or aerosols. The largest industrial sources of chromium in the atmosphere are those related to ferrochrome production. Ore refining, chemical and refractory processing, cement-producing plants, automobile brake lining and catalytic converters for automobiles, leather tanneries, and chrome pigments are also sources of chromium emissions to ambient air.
David Bryan
Environmental Protection Agency
Office of Public Affairs
901 N. 5th Street
Kansas City, Kansas 66101
Phone: 913-551-7433
bryan.david@epa.gov
Environmental Protection Agency
Office of Public Affairs
901 N. 5th Street
Kansas City, Kansas 66101
Phone: 913-551-7433
bryan.david@epa.gov