The EPA considers a dry scrubber (SDA) system to be comprised of both the lime slurry injection
system and the particulate control device (e.g., fabric filter, electrostatic precipitator). Inlet testing should
be conducted at a suitable location in the ductwork prior to the lime slurry being injected into the flue
gas stream. Outlet testing should be conducted at a suitable location following the particulate control
device. This location may be in the stack or in ductwork prior to the stack as long as there is no other
control device following the test location.
8. What do I do if I have a sampling location that does not meet Method 1 requirements? What if I have
multiple ducts around the control device to be tested?
There are a number of conditions that would cause a sampling location to be unsuitable according
to the requirements of Method 1 and, ordinarily, indicate that such a location be rejected or cause
increased costs to be incurred. However, because of the nature of the constituent being investigated in
this information collection effort (i.e., speciated mercury), the Agency believes that there are approaches
available that will allow sampling locations to be used that are consistent with the intent and data quality
requirements and that do not cause additional costs to be incurred.
Where the ductwork leading to the control device to be tested does not meet the Method 1 criteria, this
should be noted in the proposed draft site-specific test plan. However, since little can reasonably be
done to correct the situation, sampling may be performed at the most accessible inlet location without
conducting the three-dimensional flow testing that may be needed at several inlet locations to find a
suitable location. This is because (a) mercury is primarily in the gaseous phase and is not impacted by
uncertainties in the gas flow and the isokinetic sampling rate, and (b) stratification of mercury species is
not expected.
In situations where multiple ducts are found and it is believed infeasible to simultaneously sample all of
the ducts because of the additional incurred costs, sampling may be conducted in only one duct so long
as appropriate process conditions are monitored for all ducts. In this event, the proposed draft
site-specific test plan should fully describe the situation. This is because, again, mercury speciation is
not expected to be stratified. If this situation occurs at the outlet, however, it is preferred (although not
required) that the sampling occur at the stack where there is only one duct.
If the depth of the duct to be sampled is large (e.g., greater than 16 feet) and traversing from opposite
sides is not possible or practicable, sample traversing may be done only to a depth of 16 feet. This will
alleviate problems incurred with the use of longer probes and, again, results from the fact that the
mercury species do not stratify in the ductwork.
In all cases, the specifics (e.g., procedures employed to obtain a representative sample; number of
sampling points used) should be detailed in the proposed draft site-specific test plan and, later, in the
final emission test report.
OMB Control Number 2060-0396
Last Update:
24 March 1999
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