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HP’s emissions to air from our facility operations are relatively small, and we have equipment and processes in place to control those that do occur. In prior years, we reported estimated emissions from our seven largest manufacturing sites for several conventional air quality parameters. We have since concluded that the scope and nature of these reported emissions are not significant from a companywide viewpoint, and we have not included an update in this report. Local reporting to authorities of these and other indicators will continue where required.
The main substances emitted to air are shown in the table.
| Air emissions, 2004-2006 [Tonnes] |
 |
| Pollutant |
Americas |
Europe,
Middle
East and Africa |
Asia
Pacific and Japan |
| 2004 |
2005 |
2006 |
2004 |
2005 |
2006 |
2004 |
2005 |
2006 |
| Particulate
matter (20 microns or less) |
4.75 |
4.54 |
4.69 |
1.58 |
1.58 |
1.58 |
0.00 |
0.00 |
0.01 |
| Carbon
Monoxide (CO)1 |
38.00
|
36.80 |
16.90 |
15.80 |
15.80 |
15.80 |
0.00 |
0.00 |
0.10 |
| Volatile
organic compounds (VOCs) |
30.40 |
23.80 |
21.60 |
3.21 |
3.21 |
3.21 |
2.34 |
1.91 |
1.75 |
| Nitrogen
Oxides (NOx)1,2 |
74.20 |
71.30 |
37.90 |
63.10 |
63.10 |
63.10 |
0.00 |
0.04 |
0.10 |
| Sulfur
Oxides (SOx) |
6.68 |
5.03 |
2.26 |
15.80 |
15.80 |
15.80 |
0.00 |
0.00 |
0.12 |
The U.S. Environmental Protection Agency (EPA) Toxics Release Inventory (TRI) is a mandatory annual report on specified chemicals used in our operations in the United States. HP’s operations, primarily in the manufacture of our imaging and printing products, require the use of several TRI chemicals. Because we have long considered this to be an important measure, we extend TRI reporting criteria to the seven manufacturing sites worldwide that account for the vast majority of HP’s TRI emissions.
Overall, HP’s TRI emissions decreased 3 percent between 2005 and 2006, primarily because of lower use of our largest production solvent, n-methyl pyrrolidone, and reductions in nitric acid and its treatment byproducts, nitrates. Production ramp-up at one of our facilities was responsible for an increase in our use and emissions of xylene.
 |
| Disposition by type of TRI material,
2004-20061 [Tonnes] |
 |
| Chemical |
Emitted to Air |
Discharged to Water
(to sewer/off-site treatment facility) |
Shipped Off-Site for Recycle/Energy Recovery |
Shipped Off-Site for Treatment or Disposal |
Total |
| |
2004 |
2005 |
2006 |
2004 |
2005 |
2006 |
2004 |
2005 |
2006 |
2004 |
2005 |
2006 |
2004 |
2005 |
2006 |
| N-methyl pyrrolidone |
0.1 |
0.1 |
0.1 |
0.0 |
0.0 |
0.0 |
657.2 |
618.8 |
605.4 |
4.2 |
4.6 |
4.2 |
661.5 |
623.5 |
609.7 |
| Ethylene glycol |
0.4 |
0.4 |
0.7 |
0.0 |
0.2 |
0.0 |
0.0 |
0.0 |
0.0 |
67.8 |
67.5 |
62.7 |
68.2 |
67.8 |
63.4 |
| Nitrates |
0.0 |
0.0 |
0.0 |
31.0 |
42.4 |
32.6 |
6.0 |
0.0 |
0.0 |
0.4 |
0.0 |
0.0 |
37.4 |
42.4 |
32.6 |
Lead |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
19.0 |
14.3 |
10.1 |
0.0 |
0.0 |
0.0 |
19.0 |
14.3 |
10.1 |
Xylene |
0.0 |
0.1 |
5.2 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.4 |
0.6 |
5.9 |
0.4 |
0.7 |
11.1 |
Ethylene glycol |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
4.7 |
1.9 |
3.2 |
4.7 |
1.9 |
3.2 |
All others |
0.3 |
0.6 |
0.4 |
0.0 |
0.1 |
0.1 |
0.0 |
0.0 |
0.0 |
0.0 |
0.0 |
0.6 |
0.3 |
0.7 |
1.1 |
Total |
0.8 |
1.1 |
6.4 |
31.1 |
42.7 |
32.7 |
682.1 |
633.1 |
615.5 |
77.4 |
74.6 |
76.7 |
791.4 |
751.3 |
731.3 |
1 The substances with global totals greater than 1 tonne are shown. TRI reports are due July 1 each year, so the most recently completed reporting year is 2006.
2 2004 and 2005 data for nitric acid discharged to water are restated (previous table did not account for on-site treatment process).
Since eliminating ozone depleting substances (ODS) from HP manufacturing
in 1993, we only use ODS at HP facilities in cooling and air conditioning
systems. Although these systems are sealed, leaks during operation and
maintenance can cause emissions. HP continues to reduce the ozone depleting
potential of its cooling and air conditioning systems by replacing chlorofluorocarbons
(CFCs) with hydrofluorocarbons (HFCs). HFCs do not deplete ozone but are
greenhouse gases.
We do not measure ODS emissions, but estimate leakage using information
from the Third Assessment Report published by the Intergovernmental Panel
on Climate Change. We estimate that our ODS releases decreased 10% in
2006 compared with 2005 and 21% compared with 2004, due to replacing old
air conditioning systems with more efficient units that use gases with
a lower global warming potential.
Of particular note, we reduced Dichlorodifluoromethane (CFC-12) by 65%
and Bromotrifluoromethane (Halon 1301) by 12%. The CFC-12 reduction has
an additional benefit as well, since it has one of the highest global
warming potentials of all refrigerants, 10,600 times that of carbon dioxide.
See performance data, including regional breakdown, in the data
table.
1 Changes in CO and NOx for the Americas from
2005 to 2006 are largely due to a change in the calculation methodology
in Boise, Idaho.
2 Our Asia Pacific and Japan operations did not measure nitrogen
oxides (NOx) emissions in 2004.
3 2004 data restated due to calculation errors.
4 2004 Nitric Acid corrected due to a calculation error found
during our audit process.
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