Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities

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Jun. 11, 2013
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities
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Particulate Matter Adjacent to Cattle Deep-Bedded Monoslope Facilities

Editor's Notes

  1. The primary monoslope air quality project is funded by a USDA AFRI Air Quality Grant that includes researchers from South Dakota State University, Iowa State University, the Livestock Poultry and Environmental Learning Center, and the USDA Agricultural Research Service in Clay Center, NE. The project that will be discussed today is a sub-project of the overall grant and included ARS researchers from the USDA Cotton Production and Processing Research Unit in Lubbock, TX, who study particulate matter associated with cotton ginning.
  2. Currently CERCLA reports use a single value for ammonia and hydrogen sulfide based on summertime measurements from open feedlots in four states (some Southern). This probably is not reflective of deep-bedded barns. Beef cattle barns were not included in the original NAEMS project so accurate emission data is not available for beef cattle confinement barns. Manure handling systems include: weekly total scrape (no deep pack) vs deep-pack/clean around edges weekly
  3. Monitoring was continuous every other month over 2 years to get at seasonal trends and changes in the animal growth cycle. There were be two pens monitored per barn. PM 10 is what can get into esophagus. PM 2.5 is what can settle at the bottom of the lungs.
  4. To monitor particulate matter, Minivols were used periodically at both South Dakota barn sites to collect baseline emission data. We did not have sufficient equipment to monitor the Iowa sites using Minivols. But we did want to gather some baseline data from the bedpack barns and to evaluate particulate matter concentration relative to management events such as bedding. That lead to this sub-project in collaboration with our colleagues at the ARS Cotton Production and Processing Research Unit in Lubbock, TX.
  5. This consists of three Lo-Vol units placed at the front and3 Lo-Vol units placed back of the barn. Air was drawn into the unit and dust captured on a pre-weighed filtered paper within the unit. These filters are then weighed back and calculated to determine the level of PM 10 and PM 2.5
  6. Shown on this data slide are the TSP concentrations for each of the six sampling locations during the April 28 – May 5 sampling period. Samplers located on the north side of the barn are shown in blue and those located on the south side of the barn are shown in red. Average concentration over the 24 hour normal operation period are shown on April 28, May 4, and May 5 th . Three hour bedding events are shown on April 29 and May 2. The concentration of TSP during the 3 hr bedding event are clearly higher than during hours of normal operation. The average windspeed on April 29 th was 6.49 m/s. On May 2, average wind speed through the barn was 7.01 m/s.
  7. This is a chart of the TSP concentrations during the June 24 – July 1 sampling event. Bedding events occurred on June 24 and June 28. Twenty-four hour samples during hours of normal operation occurred on June 29, June 30, and July 1 st . As with the previous sampling period, we see significantly higher TSP concentrations during the bedding events compared to the hours of normal operation. On June 24 th , there was a slight south wind at only about 1.9 m/s moving through the barn. June 28 th was an interesting sampling day. The wind happened to changed direction during the 3 hour sampling period. On interesting thing to note about the bedding events, is that these elevated concentrations of TSP are very short-lived. Observe the June 29 th sampling period, less than 24 hours after bedding has been added to the barn, there is very little TSP emitted from the barns.
  8. Typical openlot feedlot particulate matter is 410 ug/m3.