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PRINCIPLES OF TOXICOLOGY

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548 CONTROLLING OCCUPATIONAL AND ENVIRONMENTAL HEALTH HAZARDS<br />

those of the cans. In short, acceptable TWA sampling results can be obtained at low cost by using bags<br />

followed by on-site analysis using short-term detector tubes.<br />

The results of the sampling in all three plants showed that the highest concentrations were found<br />

in the holding coolers, and that they can exceed the IDLH level of 50,000 ppm. In one plant, workers<br />

spent nearly the entire shift working on a palletizing operation inside a relatively large holding cooler.<br />

In another plant, entry into a smaller holding cooler was confined to forklift drivers, whose time inside<br />

was relatively short. Ventilation in both areas was relatively poor, since incursion of fresh outdoor air<br />

was minimized to maintain proper refrigeration.<br />

The rate of generation of carbon dioxide gas from dry ice in these settings is dependent upon a<br />

number of variables, including the quantity of dry ice present, the temperature, the degree of outdoor<br />

air infiltration, the size of the room, and the length of time the meat packages are held before being<br />

loaded onto trucks. Table 22.4 shows that exposures can be highly variable when measuring concentrations<br />

with short-term detector tubes. Table 22.5 shows the results of TWA exposure measurements.<br />

All workers were exposed to levels above the TLV ® of 5000 ppm, and excursions well above the<br />

allowable levels were commonplace.<br />

Several control alternatives were considered. Substitution of other methods of quick freezing offer<br />

the best method of controlling the hazard, since no carbon dioxide is present. Freeze tunnels or blast<br />

tunnels which use low-temperature air or nitrogen can be used. The meat is frozen and then packaged;<br />

this method requires more rigorous control of temperatures inside holding coolers and trucks, since<br />

no refrigerant is present inside the package itself. Nitrogen poses the potential hazard of displacement<br />

of oxygen, although it is preferable to carbon dioxide, since it poses no toxicity other than acting as<br />

an asphyxiant. The chief drawback to blast tunnels is that they occupy a great deal of floor space, and<br />

are thus difficult to fit into existing facilities. Spiral tunnels, which occupy less floor space are now<br />

available.<br />

Another control method involves the use of local exhaust ventilation to exhaust fugitive carbon<br />

dioxide emissions from the machines that deliver the dry ice (which actually is applied in a pressurized<br />

liquid form) to the poultry package. Determination of the adequacy of the exhaust ventilation system<br />

often can be determined visually, since the cold CO 2 gas is visible. The local exhaust systems found<br />

in the three plants studied all had inadequate hood designs and airflow rates that failed to capture the<br />

TABLE 22.4 Initial Short-Term Detector Tube Sampling at Four Poultry Processing Plants<br />

Concentration (ppm)<br />

Plant Area Number of Employees Range Average<br />

1 Breathing zone inside freezer 9 8,000–29,000 18,000<br />

Loading dock 2 5,000–6,500 5,750<br />

Dry Ice delivery to poultry<br />

packages<br />

3 8,000–11,000 8,000<br />

2 Holding cooler and<br />

palletizing area<br />

3 12,000 12,000<br />

Loading dock 2 12,000–13,000 12,500<br />

Dry ice delivery to poultry<br />

packages<br />

6 5,000–8,000 6,400<br />

3 Holding cooler 5 23,000–60,000 33,000<br />

Dry Ice delivery to poultry<br />

packages (local exhaust<br />

present)<br />

6 2,700–5,000 3,700<br />

4 Holding cooler 3 5,000–26,000 18,000<br />

Palletizing area 2 11,000–30,000 21,000<br />

Dry ice delivery to poultry<br />

packages<br />

4 8,000–22,000 12,000

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