- Page 1 and 2: EPA-453/R-94-004 ALTERNATIVE CONTRO
- Page 3 and 4: ALTERNATIVE CONTROL TECHNOLOGY DOCU
- Page 5 and 6: Chapter Page 4.1 MECHANISMS OF NO F
- Page 7 and 8: TABLE OF CONTENTS (con.) Chapter Pa
- Page 9 and 10: LIST OF TABLES Number Page 2-1 UNCO
- Page 11 and 12: CHAPTER 1 INTRODUCTION Congress, in
- Page 13 and 14: CHAPTER 2 SUMMARY This chapter pres
- Page 15 and 16: 2.2 NO EMISSION CONTROL TECHNOLOGIE
- Page 17 and 18: TABLE 2-2. ACHIEVABLE NO REDUCTIONS
- Page 19 and 20: TABLE 2-4. CAPITAL AND ANNUAL COSTS
- Page 21 and 22: TABLE 2-5. COST EFFECTIVENESS OF NO
- Page 23 and 24: eductions ranged from 470 tons/year
- Page 25 and 26: CHAPTER 3 INDUSTRY DESCRIPTION 3.1
- Page 27 and 28: Type II. Moderate-heat-of-hardening
- Page 29 and 30: 3 a TABLE 3-2. UNITED STATES CEMENT
- Page 31 and 32: Figure 3-1. U.S. Portland cement pl
- Page 33: Table 3-3. (con.) Rank Clinker 3 (1
- Page 37 and 38: Figure 3-3. New technology in dry-p
- Page 39 and 40: substantial levels of silica and al
- Page 41 and 42: are achieved by clinker coolers of
- Page 43 and 44: 126,000 to 963,000 tons/year with a
- Page 45: such as crushing and grinding opera
- Page 48 and 49: 4.1.1 Thermal NO Formation x Therma
- Page 50 and 51: temperatures are on the order of 16
- Page 52 and 53: 4-6
- Page 54 and 55: expected to produce more fuel NO th
- Page 56 and 57: introduce a large proportion of com
- Page 58 and 59: will also mean a somewhat lower sec
- Page 60 and 61: ILC systems: In these systems, the
- Page 62 and 63: which indicates an average and the
- Page 64 and 65: 4-18
- Page 66 and 67: Uncontrolled NO x emissions Plant c
- Page 68 and 69: from 2 to 9 lb/ton of clinker, and
- Page 70 and 71: Capacity Heat in NO x emissions Met
- Page 72 and 73: TABLE 4-3. (con.) Capacity Heat in
- Page 74 and 75: TABLE 4-3. (con.) Capacity Heat in
- Page 76 and 77: TABLE 4-3. (con.) Capacity Heat in
- Page 78 and 79: in estimating uncontrolled and cont
- Page 80 and 81: 13. Letter from Sheridan, S.E., to
- Page 82 and 83: 44. Chemecology Corporation Source.
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73. Letter and attachments from Smi
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NO control approaches applicable to
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5.1.2.2 Kiln Fuel Changing the prim
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oxygen content of the primary air m
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tend to recirculate hot combustion
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e about 15 to 38 percent depending
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combustion system shown in Figure 5
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5-14
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Figure 5-3. Schematic of hazardous
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5-18
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higher than typical cement kiln flu
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window is in the middle of a kiln.
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Figure 5-4. Application of the sele
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in Section 5.1.2 is usually difficu
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5.4 REFERENCES 1. Helmuth, R.A., F.
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25. Letter from Wax, J., Institute
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TABLE 6-1. CEMENT KILN MODEL PLANTS
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6-4
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6-6
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The total capital cost is the sum o
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TABLE 6-3. ANNUALIZED COST ELEMENTS
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6-12
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6.1.3.7 Administrative Charges. The
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At this time only three installatio
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6-18
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The annualized costs for low NOx bu
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No additional costs for utilities o
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20 percent PEC cost for contingenci
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TABLE 6-7. ANNUALIZED COSTS FOR RET
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6-28
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PEC for model plant 300,000 ' Heat
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TABLE 6-9. ANNUALIZED COSTS FOR MID
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6-34
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TABLE 6-10. CAPITAL COSTS FOR A URE
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TABLE 6-11. ANNUAL OPERATING COSTS
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6-40
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TABLE 6-12. CAPITAL COSTS FOR AN AM
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TABLE 6-13. ANNUAL OPERATING COSTS
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6-46
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costs range from $9.9 million for t
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The estimated annualized costs for
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6.3 COST EFFECTIVENESS OF NOx CONTR
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emoved. Cost effectiveness were det
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TABLE 6-17. COST EFFECTIVENESS OF R
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6-58
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TABLE 6-18. COST EFFECTIVENESS OF M
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TABLE 6-19. COST EFFECTIVENESS OF U
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6.3.4 Selective Catalytic Reduction
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6-66
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TABLE 6-21. COST EFFECTIVENESS OF S
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6-70
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11. Letter and attachments from Nov
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Tables 7-1 7-2
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TABLE 7-2. REDUCTION IN NO x EMISSI
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model plants described in Section 6
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temperature and excess air may be u
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NOxemissions will form. The heater
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equirement for the flue gas reheati