stoveguy2esw said:
but the charge that is used is used to determine not only the efficiency of the unit as far as percentage of efficiency ,
its not a "trade secret" or something that the industry tries to hide. (if it is , they didn't tell me so I'll spit it right out if asked)
Mike, two questions....
1. You say "the efficiency of the unit", yet EPA says on their own web site:
"Efficiencies shown are default efficiencies. These stoves have not been laboratory tested for efficiency."
Are you saying that the ACTUAL operating efficiency is tested and available to the customer from the hang tag or EPA?
2. The enclosed table shows three EPA tested stoves - all non-cats with similar technology. All have similar size fireboxes (within 10%) and similar low burns. But the high burn varies vastly....and so does the GPH.
One reason is that the manufacturer and the Test Lab technicians are allowed to manipulate certain parts of the testing procedure. I have listed those below......anyway, as to the "trade secrets", it would appear that there are many, and that these have been used by some manufacturers so that they appear to have an advantage, while there actually may be none at all (or the other way around, the higher GPH stove may burn better or cleaner with oak cordwood).....
I have listed some of the ways that Omni (the test lab) states that the tests can be manipulated - totally legally and within spec.
Anyway, let me know if your info is different on the efficiency testing. EPA says:
"There is currently no strong impetus to improve or test wood stove efficiency. There is a well documented efficiency test method published as a proposed method by the U.S. EPA" (but it is neither required nor used).
-------list of legal ways to change the EPA "numbers"
Using higher or lower average moisture content fuel loads ranging from 19% to 25% (dry basis) to increase or decrease burn rates and/or emissions rates,
Placing higher or lower moisture content fuel pieces at different locations within
the firebox (e.g., bottom/top or back/front) to control the timing, location, and
temperature regimes of pyrolysis products and volatile gas releases into secondary
combustion zones,
Placing higher or lower fuel density pieces at different locations within the firebox
to control the timing, location, and temperature regimes of pyrolysis products and
volatile gas releases into secondary combustion zones. There are no Method 28
fuel density specifications and Douglas fir wood densities vary up to 60% from
low to high density fuel pieces,
Starting the test at the high or low end of the allowed coal-bed size range (i.e.,
20% to 25% of the test fuel load weight) to affect the start-up pattern and the
ultimate average burn rate and emissions characteristics for the fuel load,
Starting the test at high or low average firebox/stove temperatures which also
affects the start-up pattern and ultimately the average burn rate for the fuel load.
The desired relative firebox/stove temperature can be obtained by both managing
how much of the coal bed is present at test start-up and managing how the stove is
operated before the required one-hour, no-adjustment pre-burn period is started,
and,
Using fuel load weights at the high or low end of the Method-28-allowed fuel
weight limits (i.e., 7 pounds per cubic foot of firebox volume, plus or minus 10%).
Fuel load weight differences of 10% can affect burn rates and measured emissions
rates. It is well known that smaller fuel loads produce lower emissions rates at any
burn rate.
Although the effects of these factors have not been quantified,
the overall concern is that EPA
NSPS testing can be manipulated and a practiced technician can prepare custom results