meta data for this page
  •  

Differences

This shows you the differences between two versions of the page.

Link to this comparison view

Both sides previous revisionPrevious revision
Next revision
Previous revision
sector:energy:fugitive:flaring:start [2023/03/21 12:02] – [Table] kotzullasector:energy:fugitive:flaring:start [2023/03/21 12:09] (current) – [1.B.2.c - Venting and Flaring] kotzulla
Line 11: Line 11:
 . .
  
-Pursuant to general requirements of the Technical Instructions on Air Quality Control TA Luft (2002), gases, steam, hydrogen and hydrogen sulphide released from pressure valves and venting equipment must be collected in a gas-collection system. Wherever possible, gases so collected are burned in process combustion. Where such use is not possible, the gases are piped to a flare. Flares used for flaring of such gases must fulfill at least the requirements for flares for combustion of gases from operational disruptions and from safety valves. For refineries and other types of plants in categories 1.B.2, flares are indispensable safety components. In crude-oil refining, excessive pressures can build up in process systems, for various reasons. Such excessive pressures have to be reduced via safety valves, to prevent tanks and pipelines from bursting. Safety valves release relevant products into pipelines that lead to flares. Flares carry out controlled burning of gases released via excessive pressures. When in place, flare-gas recovery systems liquify the majority of such gases and return them to refining processes or to refinery combustion systems. In the process, more than 99 % of the hydrocarbons in the gases are converted to CO₂ and HO. When a plant has such systems in operation, its flarehead will seldom show more than a small pilot flame.+Pursuant to general requirements of the Technical Instructions on Air Quality Control TA Luft (2002), gases, steam, hydrogen and hydrogen sulphide released from pressure valves and venting equipment must be collected in a gas-collection system. Wherever possible, gases so collected are burned in process combustion. Where such use is not possible, the gases are piped to a flare. Flares used for flaring of such gases must fulfill at least the requirements for flares for combustion of gases from operational disruptions and from safety valves. For refineries and other types of plants in categories 1.B.2, flares are indispensable safety components. In crude-oil refining, excessive pressures can build up in process systems, for various reasons.  
 + 
 +Such excessive pressures have to be reduced via safety valves, to prevent tanks and pipelines from bursting. Safety valves release relevant products into pipelines that lead to flares. Flares carry out controlled burning of gases released via excessive pressures. When in place, flare-gas recovery systems liquify the majority of such gases and return them to refining processes or to refinery combustion systems. In the process, more than 99 % of the hydrocarbons in the gases are converted to CO<sub>2</sub> and H<sub>2</sub>O. When a plant has such systems in operation, its flarehead will seldom show more than a small pilot flame.
  
 __Table 1: Activity data applied for 1.B.2.c__ __Table 1: Activity data applied for 1.B.2.c__
Line 23: Line 25:
 |          Value  ^ |          Value  ^
 ^  NMVOC  |  0.005  | ^  NMVOC  |  0.005  |
-^  NOₓ     1.269  | +^  NO<sub>x</sub>     1.269  | 
-^  SO₂     8.885  |+^  SO<sub>2</sub>     8.885  |
 ^  CO      0.726  | ^  CO      0.726  |
  
 __Table 3: Emission factors applied for flaring emissions at petroleum production facilities__ __Table 3: Emission factors applied for flaring emissions at petroleum production facilities__
 |        Unit  ^  Value  ^ |        Unit  ^  Value  ^
-^  NOₓ   kg/t  |  0.008  | +^  NO<sub>x</sub>   kg/t  |  0.008  | 
-^  SO₂   kg/t  |  0.010  |+^  SO<sub>2</sub>   kg/t  |  0.010  |
 ^  CO    g/t    0.1    | ^  CO    g/t    0.1    |
  
Line 37: Line 39:
 ^  NMVOC  |  kg/m³  |  0.004  | ^  NMVOC  |  kg/m³  |  0.004  |
 ^  CO      kg/m³  |  0.001  | ^  CO      kg/m³  |  0.001  |
-^  SO₂     kg/m³  |  0.003  | +^  SO<sub>2</sub>     kg/m³  |  0.003  | 
-^  NOₓ     g/m³    0.4    |+^  NO<sub>x</sub>     g/m³    0.4    |
  
 __Table 5: Emission factors applied for flaring emissions at at refineries: disruptions of flaring operations, in [kg/t]__ __Table 5: Emission factors applied for flaring emissions at at refineries: disruptions of flaring operations, in [kg/t]__
Line 44: Line 46:
 ^  NMVOC  |  0.001  | ^  NMVOC  |  0.001  |
 ^  CO      0.001  | ^  CO      0.001  |
-^  SO₂     0.007  | +^  SO<sub>2</sub>     0.007  | 
-^  NOₓ     0.004  |+^  NO<sub>x</sub>     0.004  | 
 + 
 +The emission factors have been derived from the 2004 and 2008 emissions declarations Theloke et al. 2013 [(THELOKE2013)]. In 2019, they were updated for CH<sub>4</sub>, N<sub>2</sub>O, CO, NMVOC, NO<sub>x</sub> and SO<sub>2</sub>, on the basis of Bender & von Müller, 2019 [(BENDER2019)].
  
-The emission factors have been derived from the 2004 and 2008 emissions declarations Theloke et al. 2013 [(THELOKE2013)]. In 2019, they were updated for CH₄, N₂O, CO, NMVOC, NOₓ and SO₂, on the basis of Bender & von Müller, 2019 [(BENDER2019)]. 
 Venting emissions are taken into account in category 1.B.2.b.iii. The SO₂ emissions are obtained from the activity data for the flared natural gas (Table 178) and an emission factor of 0.140 kg / 1,000 m³, a factor which takes account of an average H₂S content of 5 % by volume. Venting emissions are taken into account in category 1.B.2.b.iii. The SO₂ emissions are obtained from the activity data for the flared natural gas (Table 178) and an emission factor of 0.140 kg / 1,000 m³, a factor which takes account of an average H₂S content of 5 % by volume.
 The emission factors are determined on the basis of emissions reports, crude-oil-refining capacity and total capacity utilisation at German refineries. The guide for this work consists of the evaluation assessment of Theloke et al. (2013) [(THELOKE2013)]. The emission factors are determined on the basis of emissions reports, crude-oil-refining capacity and total capacity utilisation at German refineries. The guide for this work consists of the evaluation assessment of Theloke et al. (2013) [(THELOKE2013)].
Line 53: Line 56:
 ===== Recalculations ===== ===== Recalculations =====
  
-Please refer to overarching chapter [[sector:energy:fugitive:start|1.B - Fugitive Emissions from fossil fuels]] +<WRAP center round info 60%> 
 +For more details please refer to the super-ordinate chapter [[sector:energy:fugitive:start|1.B - Fugitive Emissions from fossil fuels]] 
 +</WRAP>
 ===== Planned improvements ===== ===== Planned improvements =====