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Textile Mill - Northeastern US
Particulate Emissions Test Results Summary: WESP Outlets |
| Date | Unit | Equipment | Gas Flow ACFM | Temperature
(Fahrenheit) |
GR/DSCF |
| 8/8/89 | 1 | 2 Dryers | 24,280 | 117 | *0.009 |
| **0.002 | |||||
| 8/11/89 | 2 | 2 Dryers | 22,768 | 105 | **0.006 |
| **0.002 | |||||
| 9/20/89 | 3 | 2 Ovens | 9,390 | 98 | *0.005 |
| **0.001 | |||||
| 9/19/89 | 4 | 1 Oven | 12,030 | 105 | *0.007 |
| **0.002 |
* Filterable and condensable particulate - ** Filterable particulate only.
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Roaster Off Gas Scrubbing Plant
Western Canada WESP Test Results: |
| Design:
Particulate
Less than 100 mg/m3 |
Actual: 54 mg/m3 |
| Design:
Gas Flow Rate:
11.8 m3/sec |
Actual: 11.97 m3/sec |
|
|
| Test Date: | March 9, 1994 |
| Emission Source: | Molybdenite roaster off gas scrubbing plant |
| Emission Constituents: | Dust, sulfuric acid mist |
| Test Objective: | Measure particulates and gas flow in scrubbing plant exhaust |
| Process: | Molybdenite (MoS2) oxidation to MoO3 by roasting |
| Roaster Capacity: | 1460 kg/hr |
| Sampling Location: | Roaster off gas scrubbing plant exhaust duct |
| Test Time: | 1:46 P.M. |
|
Pulp and Paper Plant
Western United States Test Results: |
| Dryer ON Test Results: | WESP Outlet | Without Controls |
| Particulate Average: | 0.13 gr/DSCF | Approx. 0.4 gr/DSCF |
| Formaldehyde: | .007 lb/hr | Approx. 0.1 lb/hr |
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| Process: | Wood Fired Boiler / Particle Board Dryer | |||||||||
| Volume: | 26,000 ACFM | |||||||||
| APC System: |
|
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| WESP Wash System: | Counter current
wash headers
Wash with hot alkaline water (boiler blow-down) Wash 2 times/shift - 2-3 min/wash with dryer on |
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P |
Hazardous Waste Incineration
Southwestern United States Test Burn Emission Summary: |
| (Limit) | *Average Condition I | **Average Condition II | ***Average Condition III | |
| Gas
Flow,
Wet, ACFM |
- | 58,550 | 57,600 | 60,790 |
| DRE % | ||||
| PCB | (99.9999) | 99.999995 | 99.999943 | 99.999994 |
| MCB | (99.9999) | 99.999919 | 99.999918 | 99.999969 |
| HCE | (99.9999) | 99.999988 | 99.999983 | 99.999978 |
| Metals Removal % | (Limit) | *Average Condition I | **Average Condition II | ***Average Condition III |
| Antimony | - | 99.9914 | 99.7464 | 99.8274 |
| Arsenic | - | 99.9973 | 99.9943 | 99.9781 |
| Barium | - | 99.9939 | 99.9961 | 99.9974 |
| Beryllium | - | 99.9912 | 99.9960 | 99.9966 |
| Cadmium | - | 99.9971 | 99.3688 | 99.5516 |
| Chromium | - | 99.9967 | 99.9684 | 99.9822 |
| Lead | - | 99.9985 | 99.9716 | 99.9971 |
| Mercury | - | 95.676 | 91.3541 | 98.1065 |
| Silver | - | 99.9803 | 98.9819 | 99.7859 |
| Thallium | - | 99.9087 | 99.7334 | 99.6372 |
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| Particulate
gr/DSCF |
(0.02) | 0.0006 | 0.0009 | 0.0003 |
*Maximum liquid and direct burn
** Maximum sludge burn
*** Maximum bulk solids burn
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Mid Western US
Particulate Emissions Test Results |
| Process: | ABS Plastic Extruding - Monomer Vapors, Plastics, DOP, Pigments | ||||||||||||||||
| APC System: |
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| WESP Wash System: | Steam heated to
start
Co-current and counter current wash headers Wash with hot water (no detergent required) |
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| Test Results: | Particulate | ||||||||||||||||
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North Eastern US
Municipal Incinerator Emission Test Summary |
| Process: | Sewage Sludge Fluidized Bed Incinerator | |||
| APC System: |
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| Average Volume: | 9575 ACFM | |||
| Test Results: | Particulate |
| Evaluation of Emission Test Results for Gases and Particulates | |||||||
| Feed
Rate
Dry Solids #/hr |
Parameter | Allowable Emission Rate | Actual
Emission Rate
(7% O2, 0% Moisture)
|
Compliance | |||
| 3191 avg. | HCL (ppmv) | 30 | 1.00 | 0.55 | YES | ||
| 3191 | CO (ppmv) | 100 | 24.64 | 12.59 | YES | ||
| 3233 | SO2 (ppmv) | 30 | 21.64 | YES | |||
| 3233 | SO2 + SO3 (ppmv) | 22.38 | |||||
| 3191 | NO2 (ppmv) | 300 | 12.5 | 11.97 | YES | ||
| 3191 | THC (ppmv as propane) | 30 | 2.22 | 1.43 | YES | ||
| 3118 | Particulates
(gr/scf, dry) |
0.015 | 0.0076 | YES | |||