Release Characterization Case Study. Major Emission Sources Venting from the feed and product...
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![Page 1: Release Characterization Case Study. Major Emission Sources Venting from the feed and product storage tanks Off-gases from the scrubbers Liquid wastes.](https://reader035.fdocuments.in/reader035/viewer/2022062401/5a4d1b237f8b9ab059996274/html5/thumbnails/1.jpg)
Release Characterization
Case Study
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Major Emission Sources• Venting from the feed and product storage tanks• Off-gases from the scrubbers• Liquid wastes from the scrubbers• Emissions from the decanting and purification
columns• Emissions from the boilers• Fugitive emissions• Feed and product loading and off-loading emissions
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Emission from Reactors, Stripper, Decanting and Purification Columns• Table 8.3-2: 1.5kg/1000 kg throughput (reactor vent),
0.2 kg/1000 kg throughput (stripper), 0.02 kg/ 1000 kg throughput (decanter), 0.7 kg/ 1000 kg throughput (distillation column vents).
• Assume (1) half of the emissions from reactor are cyclohexane (reactant) and half are ketone and alcohol (products) and (2) all of the emissions of the other units are products.
• Emission estimates: 0.8 kg cyclohexane/ 1000 kg throughput and 1.6 kg ketone and alcohol/100 throughput.
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Emissions from Boilers• Rudd et al. (1981) suggested 1 value of 0.5 metric tons of fuel oil used per
metric ton of product.• Assume #6 fuel oil with 1% sulfur is used.
3 3
32
3 3
33
3
19 kg/10 L fuel oil 0.8 L/kg 500 kg fuel oil/ 10 kg product
= 7.6 kg SO /10 kg product
0.69 kg/10 L fuel oil 0.8 L/kg 500 kg fuel oil/ 10 kg product
= 0.3 kg SO /10 kg product
8 kg/10 L fuel oil 0.8 L/k
3
3x
3 3
3
g 500 kg fuel oil/ 10 kg product
= 3.2 kg NO /10 kg product
1.5 kg/10 L fuel oil 0.8 L/kg 500 kg fuel oil/ 10 kg product
= 0.6 kg PM/10 kg product
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Fugitive Emissions
• Rough estimates are made on the basis of experience. Typical values: 0.5 – 1.5 kg per 1000 kg product.
• Use 0.5 kg/ 1000 kg throughput.• Emissions are evenly split between products
and reactants.
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Emission Loss from Liquid Loading
L L 12.46
0.6 (4.1 14.7/760) 98 = 12.46530
= 0.1 lb/1000 gal = 0.15 kg/1000 kg throughput
S P MT
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Losses from Tanks• Assume an annual production rate of 100 million pounds
per year.• A typical tank should hold 2-3 days of production capacit
y.• A tank 35 ft in diameter and 20 ft high with a fixed roof is
reasonable.• The tank is 80% full.• If the facility is located in Houston, TX, the data and proc
edure described in appendix C lead to an estimate of 0.5 kg emitted/1000 kg product for standing and working losses.
• We will assume that these are emissions of the feed material (cyclohexane) also.
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Hedley et al. (1975)
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Environmental Performance
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Performance Indicators• Energy consumed from all sources within the
manufacturing or delivery process per unit of manufactured output.
• Total mass of material used directly in the product, minus the mass of the product, per unit of manufactured output.
• Water consumption per unit of manufactured product.• Emissions of targeted pollutants (those listed in TRI)
per unit of manufactured output.• Total pollutants per unit of manufactured output.
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Material UseBased on data of Rudd et al. (1981) and Hedley et al. (1975). Rudd reports th
at the manufacture of 1 ton of cyclohexanol requires 1.64 tons of cyclohexane and 0.13 ton of NaOH. Cyclohexanone is produced at a rate of 0.38 tons per tons of cyclohexanol.
1.64 0.13 1.38Material Intensity 0.28
1 0.38
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Water Use
• According to Hedley et al. (1975), 5000 gpm of cooling water and 10 gpm of process water are used for a 85000000 pounds per year facility.
• This leads to an estimate of 30 gallons of water per pound of product.
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Energy Intensity and Pollutant Generation
• From literature, 0.4 fuel oil per kg product. On the basis of 150000 BTU per gallon fuel oil, the energy intensity is 7 kBTU per pound of product.
• From Table 8.3-12, pollutant generation is 0.3 lb/ lb product.
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The performance indicators of the example process are at the high ends of the rangereported here. Improvements are needed!!!