lb/hr lb/day ton/yrlb/hr lb/day ton/yrlb/hr lb/day ton/yrlb/hr lb/day ton/yrlb/hr lb/day ton/yrlb/hr lb/day ton/yrlb/hr lb/day ton/yrPM27 641 20 27 653 35 14 343 20 11 261 21 13 317 30 12 298 21 27 653 35PM1026 646 19 25 602 32 11 267 17 10 248 20 11 271 25 12 285 20 26 646 32PM2.526 635 19 25 599 32 11 262 19 10 249 20 11 271 25 11 256 20 26 635 32NOx608 14597 1036 624 14978 1334 617 14803 1078 597 14318 1124 615 14754 1363 61814839 1126 624 14978 1363CO1091 26172 455 809 19406 540 220 5283 406 235 5647 458 210 5047 466 240 5759 4591091 26172 540VOC388 9323 112 277 6655 121 44 1066 78 46 1094 82 45 1071 87 47 1136 82 388 9323 121Pb5.80E‐03 1.39E‐01 1.34E‐02 6.71E‐03 1.61E‐01 1.73E‐02 7.57E‐03 1.82E‐01 1.40E‐02 7.92E‐03 1.90E‐01 1.51E‐02 7.36E‐03 1.77E‐01 1.62E‐02 8.07E‐03 1.94E‐01 1.51E‐02 8.07E‐03 1.94E‐01 1.73E‐02SO21.80E+00 4.32E+01 8.49E‐01 1.36E+00 3.26E+01 1.02E+00 4.18E‐01 1.00E+01 7.74E‐01 4.38E‐01 1.05E+01 8.34E‐01 4.07E‐01 9.76E+00 8.97E‐01 4.46E‐01 1.07E+01 8.34E‐01 1.80E+00 4.32E+01 1.02E+00H2SO49.89E‐03 2.37E‐01 2.32E‐02 1.15E‐02 2.75E‐01 2.98E‐02 1.31E‐02 3.14E‐01 2.42E‐02 1.37E‐02 3.28E‐01 2.61E‐02 1.27E‐02 3.05E‐01 2.80E‐02 1.39E‐02 3.34E‐01 2.61E‐02 1.39E‐02 3.34E‐01 2.98E‐02GHG3.25E+05 7.79E+06 9.66E+04 2.32E+05 5.58E+06 1.11E+05 4.26E+04 1.02E+06 7.88E+04 4.44E+04 1.07E+06 8.44E+04 4.14E+04 9.94E+05 9.14E+04 4.52E+04 1.08E+06 8.45E+04 3.25E+05 7.79E+06 1.11E+05HAPs12 283 13 10 248 13 7 175 12 7 175 12 7 175 12 7 176 12 12 283 13Note:The	Potential	To	Emit	calculation	includes	the	sum	of	emissionsfrom	the	following	emission	sources:*Drillship	Main	Propulsion	Engines*Cement	and	Mud	Mixing	Dust	collectors*Mud	Degasser	Vent*Painting	Operations*Welding	Operations*Third	Party	Well	Evaluation	Engines*Flowback	Boiler*Boomflare*Condensate	Tanks*Support	Vessels*Drillship	Diesel	and	Jet	Fuel	Tanks*Drillship	Fugitive	ComponentsAnadarko Petroleum CorporationPotential To Emit (PTE) SummaryPollutantGasFlowback OilFlowback StimulationVessel Completion WellEvaluationVesselDrillingScenario PotentialtoEmitScenario1 Scenario2 Scenario3 Scenario4 Scenario5Anadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet1	of	192PTEUnits/hr Units/day Units/year Units/hr Units/day Units/year Units/hr Units/day Units/year Units/hr Units/day Units/year Units/hr Units/day Units/year Units/hr Units/day Units/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐01m3 4 95 18438 3 82 18438 4 86 18438 5 123 18438 4 103 18438 5 123 18438Emergency	Air	Compressor	 DR‐AC‐01hours 0.5 0.5 100 0.5 0.5 100 0.5 0.5 100 0.5 0.5 100 0.5 0.5 100 0.5 0.5 100Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐06hours* 1.0 1.00 100 1.00 1.00 100 1.00 1.00 100 1.00 1.00 100 1.00 1.00 100 1.00 1.00 100Fast	Rescue	Craft DR‐FR‐01hours 1.0 1.00 100 1.00 1.00 100 1.00 1.00 100 1.00 1.00 100 1.00 1.00 100 1.001.00 100Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐03hours* 1.0 24.0 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐18hours* 1.0 24.0 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800Drillship	Fugitive	Emissions DR‐FE‐01hours 1.0 24.0 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800Mud	Degasser	Vent DR‐VG‐01hours 1.0 24.0 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800Painting	(paint	+	thinner)	Operations DR‐PO‐01 gals2.1 50.0 6500 2.1 50 6500 2.1 50 6500 2.1 50 6500 2.1 50 6500 2.1 50 6500Welding	Operations DR‐WE‐01lbs 3.3 80.0 16000 3.3 80 16000 3.3 80 16000 3.3 80 16000 3.3 80 16000 3.3 80 16000EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐03hours 1.0 24.0 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐17hours 1.0 24.0 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800 1.0 24 4800Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐16hours* 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 24 125EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐05hours* 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 24 4800EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐19hours* 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 24 4800EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐07hours* 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 24 4800EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐20hours 0 0 0 0 0 0 0 0 0 1 24 4800 0 0 0 0 0 0EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐21hours 0 0 0 0 0 0 1 24 4800 1 24 4800 0 0 0 0 0 0EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐09hours 0 0 0 0 0 0 0 0 0 1 24 4800 0 0 0 0 0 0Flowback	Boiler DR‐TP‐22MMBtu 8.0 192 1152 8.0 192 1152 0 0 0 0 0 0 0 0 0 0 0 0Boom	Flare DR‐TP‐23MMscf 2.5 60 360 1.7 40 240 0 0 0 0 0 0 0 0 0 0 0 0EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐01hours 0 0 0 0 0 0 0 0 0 1 24 4800 0 0 0 0 0 0EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐02hours 0 0 0 0 0 0 0 0 0 1 24 4800 0 0 0 0 0 0EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐11hours* 0 0 0 0 0 0 0 0 0 1 24 4800 0 0 0 0 0 0Condensate	Tanks DR‐TP‐25	to	DR‐TP‐27hours* 1 24 4800 1 24 4800 0 0 0 0 0 0 0 0 0 0 0 0Stimulation	Vessel	Engines Variousbbl 0 0 0 0 0 0 9 225 4725 0 0 0 0 0 0 0 0 0Barges BG‐LP‐01	to	BG‐LP‐03hours 0 0 0 1 24 4800 0 0 0 0 0 0 0 0 0 0 0 0Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐02bbl 0 0 0 5 125 25000 0 0 0 0 0 0 0 0 0 0 0 0Well	Evaluation	Vessel Variousbbl 0 0 0 0 0 0 0 0 0 0 0 0 6 144 28800 0 0 0Supply	Boats Variousbbl 4.2 100.0 20000 4.2 100 20000 4 100 20000 8 200 40000 4 100 20000 8 200 40000*	Hours	per	unit.Anadarko Petroleum CorporationMatrix CalculatorDrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselScenario1 Scenario2 Scenario3 Scenario4 Scenario5EPNAirEmissionSources UnitDrillShipTemporaryThirdPartyEnginesSupportVesselsAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet2	of	192Matrix	Calculatorlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	and	DR‐GE‐01100.1 395 9484 923 342 8202 923 358 8587 923 513 12303 923 431 10347 923 513 12303 923Emergency	Air	Compressor	 DR‐AC‐010.24 0.1 0.1 0.01 0.1 0.1 0.01 0.1 0.1 0.01 0.1 0.1 0.01 0.1 0.1 0.01 0.1 0.1 0.01Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐067.63 8 7.63 0.38 7.63 7.63 0.38 7.63 7.63 0.38 7.63 7.63 0.38 7.63 7.63 0.38 7.63 8 0.38Fast	Rescue	Craft DR‐FR‐010.68 0.68 0.68 0.03 0.68 0.68 0.03 0.68 0.68 0.03 0.68 0.68 0.03 0.68 0.68 0.03 0.68 0.68 0.03Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 00000000 0000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 00000000 0000000000Drillship	Fugitive	Emissions DR‐FE‐010 00000000 0000000000Mud	Degasser	Vent DR‐VG‐010 00000000 0000000000Painting	(paint	+	thinner)	Operations DR‐PO‐010 00000000 0000000000Welding	Operations DR‐WE‐010 00000000 0000000000EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐033.26 3 78 7.82 3 78 7.82 3 78 7.82 3 78 7.82 3 78 7.82 3 78 7.82EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐171.37 1 33 3.28 1 33 3.28 1 33 3.28 1 33 3.28 1 33 3.28 1 33 3.28Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐1621.7000000000 00 0 0 0 0 0 22 5211.36EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐056.5200000000 00 0 0 0 0 0 7 15615.64EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐192.7400000000 00 0 0 0 0 0 3 666.57EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐076.5200000000 00 0 0 0 0 0 7 15615.64EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐201.370 0 0 0 0 0 0 0 0 1 333.28000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐211.370 0 0 0 0 0 1 333.28 1 33 3.28000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐096.520 0 0 0 0 0 0 0 0 7 15615.64000000Flowback	Boiler DR‐TP‐220.14 1 27 0.08 1 27 0.08 0 0 0000000000Boom	Flare DR‐TP‐2367.97 170 4078 12.24 113 2719 8.16 0 0 0000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐019.050 0 0 0 0 0 0 0 0 9 21721.72000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐029.050 0 0 0 0 0 0 0 0 9 21721.72000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐116.520 0 0 0 0 0 0 0 0 7 15615.64000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270 00000000 0000000000Stimulation	Vessel	Engines Various23.150 0 0 0 0 0 2175209 54.70000000000Barges BG‐LP‐01	to	BG‐LP‐0342.41 0 0 0 42 1018 101.78 0 0 0000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐0216.03 0 0 0 84 2004 200.41 0 0 0000000000Well	Evaluation	Vessel Various23.610 0 0 0 0 0 0 0 0 0 0 0 1423399 339.92 0 0 0Supply	Boats Various10.1 42 1008 100.75 42 1008 100.75 42 1008 100.75 84 2015 201.51 42 1008 100.75 84 2015 201.51608 14597 1036 624 14978 1334 617 14803 1078 597 14318 1124 615 14754 1363 61814839 1126Anadarko Petroleum CorporationNOXEmissions MatrixTotalAirEmissionSourcesSupportVesselsThirdPartyEnginesEPNDrillShipNOxScenario2 Scenario3 Scenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselScenario1NOx NOx NOx NOx NOxAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet3	of	192NOx	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐011.55E+00 6.1 147 14.29 5 127 14.29 5.5 133 14.29 8 190 14.29 7 160 14.29 8 190 1.43E+01Emergency	Air	Compressor	 DR‐AC‐011.92E‐02 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐065.41E‐01 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02Fast	Rescue	Craft DR‐FR‐013.62E‐02 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐031.49E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 0000000000000000.00 0.00 0.00Drillship	Fugitive	Emissions DR‐FE‐010 0000000000000000.00 0.00 0.00Mud	Degasser	Vent DR‐VG‐010 0000000000000000.00 0.00 0.00Painting	(paint	+	thinner)	Operations DR‐PO‐011.25E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01Welding	Operations DR‐WE‐015.70E‐02 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01EPA	Tier	II	Third	Party	Engines≤300	HPDR‐TP‐039.88E‐02 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐176.22E‐02 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐161.54E+000000000000000001.54E+00 3.70E+01 9.63E‐02EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐051.98E‐010000000000000001.98E‐01 4.74E+00 4.74E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐191.24E‐010000000000000001.24E‐01 2.98E+00 2.98E‐01EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐071.98E‐010000000000000001.98E‐01 4.74E+00 4.74E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐206.22E‐020000000006.22E‐02 1.49E+00 1.49E‐01 000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐216.22E‐020000006.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐091.98E‐010000000001.98E‐01 4.74E+00 4.74E‐01 000000Flowback	Boiler DR‐TP‐222.36E‐02 1.89E‐01 4.53E+00 1.36E‐02 1.89E‐01 4.53E+00 1.36E‐02000000000000Boom	Flare DR‐TP‐237.45E+00 1.86E+01 4.47E+02 1.34E+00 1.24E+01 2.98E+02 8.94E‐01000000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐012.83E‐010000000002.83E‐01 6.79E+00 6.79E‐01 000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐022.83E‐010000000002.83E‐01 6.79E+00 6.79E‐01 000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐111.98E‐010000000001.98E‐01 4.74E+00 4.74E‐01 000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270 000000000000000000Stimulation	Vessel	Engines Various0.740 0 0 0 0 0 7 1681.76000000000Barges BG‐LP‐01	to	BG‐LP‐033.010 0 0 3 727.22000000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&TG‐GE‐01	to	TG‐GE‐020.870 0 0 5 10910.87000000000000Well	Evaluation	Vessel Various0.790 0 0 0 0 0 0 0 0 0 0 0 5 11411.42 0 0 0Supply	Boats Various0.28 1 28 2.81 1 28 0 1 28 2.81 2 56 5.62 1 28 2.81 2 56 5.6227 641 20 27 653 35 14 343 20 11 261 21 13 317 30 12 298 21Anadarko Petroleum CorporationPM Emissions MatrixScenario1 Scenario2 Scenario3PMAirEmissionSources EPNDrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselPM PM PMScenario4 Scenario5PM PM PMDrillshipSupportVesselsThirdPartyEnginesTotalAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet4	of	192PM	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐011.55 6.12E+00 1.47E+02 1.43E+01 5.29E+00 1.27E+02 1.43E+01 5.54E+00 1.33E+02 1.43E+01 7.94E+00 1.90E+02 1.43E+01 6.67E+00 1.60E+02 1.43E+01 7.94E+00 1.90E+02 1.43E+01Emergency	Air	Compressor	 DR‐AC‐010.02 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 4.81E‐06 9.62E‐03 9.62E‐03 4.81E‐06 1.85E‐05 9.62E‐03 4.81E‐06Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐060.54 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 2.71E‐01 5.41E‐01 2.71E‐04 2.71E‐01 5.41E‐01 2.71E‐04 1.46E‐02 5.41E‐01 2.71E‐04Fast	Rescue	Craft DR‐FR‐010.04 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 1.81E‐02 3.62E‐02 1.81E‐05 1.81E‐02 3.62E‐02 1.81E‐05 6.54E‐05 3.62E‐02 1.81E‐05Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 0 0 0000000000000000Drillship	Fugitive	Emissions DR‐FE‐010 0 0 0000000000000000Mud	Degasser	Vent DR‐VG‐010 0 0 0000000000000000Painting	(paint	+	thinner)	Operations DR‐PO‐010.13 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01Welding	Operations DR‐WE‐010.0570 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐011.90E‐01 4.56E+00 4.56E‐01EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐030.10 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 1.19E‐03 9.88E‐02 2.37E+00 1.19E‐03 2.34E‐02 2.37E+00 1.19E‐03EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐170.06 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 7.46E‐04 6.22E‐02 1.49E+00 7.46E‐04 9.28E‐03 1.49E+00 7.46E‐04Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐161.54 0 000000000000001.54E+00 3.70E+01 9.63E‐02EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐050.20 0 000000000000001.98E‐01 4.74E+00 4.74E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐190.12 0 000000000000001.24E‐01 2.98E+00 2.98E‐01EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐070.20 0 000000000000001.98E‐01 4.74E+00 4.74E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐200.06 0 000000006.22E‐02 1.49E+00 1.49E‐01000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐210.06 0 000006.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐090.20 0 000000001.98E‐01 4.74E+00 4.74E‐01000000Flowback	Boiler DR‐TP‐220.02 1.89E‐01 4.53E+00 1.36E‐02 1.89E‐01 4.53E+00 1.36E‐02000000000000Boom	Flare DR‐TP‐237.45 1.86E+01 4.47E+02 1.34E+00 1.24E+01 2.98E+02 8.94E‐01000000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐010.16 0.00E+00 000000001.62E‐01 3.89E+00 3.89E‐01000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐020.16 0.00E+00 000000001.62E‐01 3.89E+00 3.89E‐01000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐110.20 0 000000001.98E‐01 4.74E+00 4.74E‐01000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270.00 0 00000000000000000Stimulation	Vessel	Engines Various0.43 0 000004.00E+00 9.60E+01 1.01E+00000000000Barges BG‐LP‐01	to	BG‐LP‐033.01 0 0 0 3.01E+00 7.22E+01 7.22E+00000000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐020.50 0 0 0 2.60E+00 6.23E+01 6.23E+00000000000000Well	Evaluation	Vessel Various0.53 0 000000000003.18E+00 7.64E+01 7.64E+00 0 0 0Supply	Boats Various0.23 9.71E‐01 3.38E+01 2.33E+00 9.71E‐01 2.33E+01 2.33E+00 9.71E‐01 2.33E+01 0.00E+00 1.94E+00 4.66E+01 4.66E+00 9.71E‐01 2.33E+01 2.33E+00 1.94E+00 4.66E+01 4.66E+002.65E+01 6.46E+02 1.92E+01 2.51E+01 6.02E+02 3.22E+01 1.11E+01 2.67E+02 1.65E+01 1.03E+01 2.48E+02 1.98E+01 1.13E+01 2.71E+02 2.51E+01 1.19E+01 2.85E+02 1.99E+01Anadarko Petroleum CorporationPM10Emissions MatrixTotalDrillshipAirEmissionSources EPNPM10ThirdPartyEnginesSupportVesselsPM10DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselPM10PM10PM10PM10PM10Scenario1 Scenario2 Scenario3 Scenario4 Scenario5Anadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet5	of	192PM10	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐011.55 6.12E+00 1.47E+02 1.43E+01 5.29E+00 1.27E+02 1.43E+01 5.54E+00 1.33E+02 1.43E+01 7.94E+00 1.90E+02 1.43E+01 6.67E+00 1.60E+02 1.43E+01 7.94E+00 1.90E+02 1.43E+01Emergency	Air	Compressor	 DR‐AC‐010.02 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04 9.62E‐03 9.62E‐03 9.62E‐04Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐060.54 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02 5.41E‐01 5.41E‐01 2.71E‐02Fast	Rescue	Craft DR‐FR‐010.04 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03 3.62E‐02 3.62E‐02 1.81E‐03Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030.15 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01 1.49E‐01 3.56E+00 3.56E‐01Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 000000000000000000Drillship	Fugitive	Emissions DR‐FE‐010 000000000000000000Mud	Degasser	Vent DR‐VG‐010 000000000000000000Painting	(paint	+	thinner)	Operations DR‐PO‐010.125 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01 2.61E‐01 6.26E+00 4.07E‐01Welding	Operations DR‐WE‐010.0570 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐01 1.90E‐01 4.56E+00 4.56E‐011.90E‐01 4.56E+00 4.56E‐01EPA	Tier	II	Third	Party	Engines≤300	HPDR‐TP‐030.10 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01 9.88E‐02 2.37E+00 2.37E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐170.06 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐160.310000000000000003.08E‐01 7.39E+00 1.93E‐02EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐050.200000000000000001.98E‐01 4.74E+00 4.74E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐190.120000000000000001.24E‐01 2.98E+00 2.98E‐01EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐070.200000000000000001.98E‐01 4.74E+00 4.74E‐01EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐200.060000000006.22E‐02 1.49E+00 1.49E‐01000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐210.060000006.22E‐02 1.49E+00 1.49E‐01 6.22E‐02 1.49E+00 1.49E‐01000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐090.200000000001.98E‐01 4.74E+00 4.74E‐01000000Flowback	Boiler DR‐TP‐220.02 1.89E‐01 4.53E+00 1.36E‐02 1.89E‐01 4.53E+00 1.36E‐02000000000000Boom	Flare DR‐TP‐237.45 1.86E+01 4.47E+02 1.34E+00 1.24E+01 2.98E+02 8.94E‐01000000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐010.160000000001.57E‐01 3.77E+00 3.77E‐01000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐020.160000000001.57E‐01 3.77E+00 3.77E‐01000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐110.200000000001.98E‐01 4.74E+00 4.74E‐01000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270 000000000000000000Stimulation	Vessel	Engines Various0.410000003.88E+00 9.31E+01 9.78E‐01000000000Barges BG‐LP‐01	to	BG‐LP‐033.01 0 0 0 3.01E+00 7.22E+01 7.22E+00000000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐020.48 0 0 0 2.52E+00 6.04E+01 6.04E+00000000000000Well	Evaluation	Vessel Various0.520000000000003.12E+00 7.49E+01 7.49E+00 0 0 0Supply	Boats Various0.22 9.17E‐01 2.20E+01 2.20E+00 9.17E‐01 2.20E+01 2.20E+00 9.17E‐01 2.20E+01 2.20E+00 1.83E+00 4.40E+01 4.40E+00 9.17E‐01 2.20E+01 2.20E+00 1.83E+00 4.40E+01 4.40E+002.64E+01 6.35E+02 1.91E+01 2.49E+01 5.99E+02 3.19E+01 1.09E+01 2.62E+02 1.87E+01 1.04E+01 2.49E+02 1.99E+01 1.13E+01 2.71E+02 2.52E+01 1.07E+01 2.56E+02 1.99E+01Anadarko Petroleum CorporationPM2.5Emissions MatrixScenario1 Scenario2 Scenario3 Scenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselPM2.5PM2.5PM2.5PM2.5PM2.5PM2.5ThirdPartyEnginesTotalEPNAirEmissionSourcesDrillshipSupportVesselsAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet6	of	192PM2.5	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐0134.56 136 3275 319 118 2832 319 124 2965 319 177 4248 319 149 3573 319 177 4248 319Emergency	Air	Compressor	 DR‐AC‐010.18 8.82E‐02 8.82E‐02 8.82E‐03 8.82E‐02 8.82E‐02 8.82E‐03 8.82E‐02 8.82E‐02 8.82E‐03 8.82E‐02 8.82E‐02 8.82E‐03 8.82E‐02 8.82E‐02 8.82E‐03 8.82E‐02 8.82E‐02 8.82E‐03Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐061.64 1.64E+00 1.64E+00 8.22E‐02 1.64E+00 1.64E+00 8.22E‐02 1.64E+00 1.64E+00 8.22E‐02 1.64E+00 1.64E+00 8.22E‐02 1.64E+00 1.64E+00 8.22E‐02 1.64E+00 1.64E+00 8.22E‐02Fast	Rescue	Craft DR‐FR‐010.45 4.52E‐01 4.52E‐01 2.26E‐02 4.52E‐01 4.52E‐01 2.26E‐02 4.52E‐01 4.52E‐01 2.26E‐02 4.52E‐01 4.52E‐01 2.26E‐02 4.52E‐01 4.52E‐01 2.26E‐02 4.52E‐01 4.52E‐01 2.26E‐02Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 000000000000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 000000000000000000Drillship	Fugitive	Emissions DR‐FE‐010 000000000000000000Mud	Degasser	Vent DR‐VG‐010 000000000000000000Painting	(paint	+	thinner)	Operations DR‐PO‐010 000000000000000000Welding	Operations DR‐WE‐010 000000000000000000EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐031.73 1.73E+00 4.15E+01 4.15E+00 1.73E+00 4.15E+01 4.15E+00 1.73E+00 4.15E+01 4.15E+00 1.73E+00 4.15E+01 4.15E+00 1.73E+00 4.15E+01 4.15E+00 1.73E+00 4.15E+01 4.15E+00EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐171.04 1.04E+00 2.49E+01 2.49E+00 1.04E+00 2.49E+01 2.49E+00 1.04E+00 2.49E+01 2.49E+00 1.04E+00 2.49E+01 2.49E+00 1.04E+00 2.49E+01 2.49E+00 1.04E+00 2.49E+01 2.49E+00Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐164.680000000000000004.68E+00 1.12E+02 2.92E‐01EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐053.460000000000000003.46E+00 8.30E+01 8.30E+00EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐192.070000000000000002.07E+00 4.97E+01 4.97E+00EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐073.460000000000000003.46E+00 8.30E+01 8.30E+00EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐201.040000000001.04E+00 2.49E+01 2.49E+00000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐211.040000001.04E+00 2.49E+01 2.49E+00 1.04E+00 2.49E+01 2.49E+00000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐093.460000000003.46E+00 8.30E+01 8.30E+00000000Flowback	Boiler DR‐TP‐220.04 2.86E‐01 6.86E+00 2.06E‐02 2.86E‐01 6.86E+00 2.06E‐02000000000000Boom	Flare DR‐TP‐23370 9.25E+02 2.22E+04 6.66E+01 6.16E+02 1.48E+04 4.44E+01000000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐014.950000000004.95E+00 1.19E+02 1.19E+01000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐024.950000000004.95E+00 1.19E+02 1.19E+01000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐113.460000000003.46E+00 8.30E+01 8.30E+00000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270.00000000000000000000Stimulation	Vessel	Engines Various7.200000006.75E+01 1.62E+03 1.70E+01000000000Barges BG‐LP‐01	to	BG‐LP‐039.14 0 0 0 9.14E+00 2.19E+02 2.19E+01000000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&TG‐GE‐01	to	TG‐GE‐026.83 0 0 0 3.56E+01 8.54E+02 8.54E+01000000000000Well	Evaluation	Vessel Various5.380000000000003.23E+01 7.74E+02 7.74E+01 0 0 0Supply	Boats Various6.99 29 699 70 29 699 70 29 699 70 58 1398 140 29 699 70 58 1398 1401091 26172 455 809 19406 540 220 5283 406 235 5647 458 210 5047 466 240 5759 459Anadarko Petroleum CorporationCO Emissions MatrixSupportVesselsTotalAirEmissionSources EPNScenario1 Scenario2 Scenario3 Scenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselCO CO CO CO CO CODrillshipThirdPartyEnginesAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet7	of	192CO	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐014.03 1.59E+01 3.82E+02 3.72E+01 1.38E+01 3.30E+02 3.72E+01 1.44E+01 3.46E+02 3.72E+01 2.06E+01 4.96E+02 3.72E+01 1.74E+01 4.17E+02 3.72E+01 2.06E+01 4.96E+02 3.72E+01Emergency	Air	Compressor	 DR‐AC‐010.05 2.45E‐02 2.45E‐02 2.45E‐03 2.45E‐02 2.45E‐02 2.45E‐03 2.45E‐02 2.45E‐02 2.45E‐03 2.45E‐02 2.45E‐02 2.45E‐03 2.45E‐02 2.45E‐02 2.45E‐03 2.45E‐02 2.45E‐02 2.45E‐03Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐060.62 6.18E‐01 6.18E‐01 3.09E‐02 6.18E‐01 6.18E‐01 3.09E‐02 6.18E‐01 6.18E‐01 3.09E‐02 6.18E‐01 6.18E‐01 3.09E‐02 6.18E‐01 6.18E‐01 3.09E‐02 6.18E‐01 6.18E‐01 3.09E‐02Fast	Rescue	Craft DR‐FR‐010.14 1.38E‐01 1.38E‐01 6.91E‐03 1.38E‐01 1.38E‐01 6.91E‐03 1.38E‐01 1.38E‐01 6.91E‐03 1.38E‐01 1.38E‐01 6.91E‐03 1.38E‐01 1.38E‐01 6.91E‐03 1.38E‐01 1.38E‐01 6.91E‐03Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 00000000000000000 0Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 0 0 6.93E‐0100000000000000 0Drillship	Fugitive	Emissions DR‐FE‐010.01 1.08E‐02 2.60E‐01 2.60E‐02 1.08E‐02 2.60E‐01 2.60E‐02 1.08E‐02 2.60E‐01 2.60E‐02 1.08E‐02 2.60E‐01 2.60E‐02 1.08E‐02 2.60E‐01 2.60E‐02 1.08E‐02 2.60E‐01 2.60E‐02Mud	Degasser	Vent DR‐VG‐012 2.23E+00 5.36E+01 5.36E+00 2.23E+00 5.36E+01 5.36E+00 2.23E+00 5.36E+01 5.36E+00 2.23E+00 5.36E+01 5.36E+00 2.23E+00 5.36E+01 5.36E+00 2.23E+00 5.36E+01 5.36E+00Painting	(paint	+	thinner)	Operations DR‐PO‐018.72 1.82E+01 4.36E+02 2.84E+01 1.82E+01 4.36E+02 2.84E+01 1.82E+01 4.36E+02 2.84E+01 1.82E+01 4.36E+02 2.84E+01 1.82E+01 4.36E+02 2.84E+01 1.82E+01 4.36E+02 2.84E+01Welding	Operations DR‐WE‐010.0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐030.75 7.54E‐01 1.81E+01 1.81E+00 7.54E‐01 1.81E+01 1.81E+00 7.54E‐01 1.81E+01 1.81E+00 7.54E‐01 1.81E+01 1.81E+00 7.54E‐01 1.81E+01 1.81E+00 7.54E‐01 1.81E+01 1.81E+00EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐170.32 3.16E‐01 7.59E+00 7.59E‐01 3.16E‐01 7.59E+00 7.59E‐01 3.16E‐01 7.59E+00 7.59E‐01 3.16E‐01 7.59E+00 7.59E‐01 3.16E‐01 7.59E+00 7.59E‐01 3.16E‐01 7.59E+00 7.59E‐01Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐161.76 0 0 00000000000001.76E+00 4.22E+01 1.10E‐01EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐051.51 0 0 00000000000001.51E+00 3.62E+01 3.62E+00EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐190.63 0 0 00000000000006.33E‐01 1.52E+01 1.52E+00EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐071.51 0 0 00000000000001.51E+00 3.62E+01 3.62E+00EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐200.32 0 0 000000008100000 0EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐210.32 0 0 0 0 0 0 3.16E‐01 7.59E+00 7.59E‐01 3.16E‐01 7.59E+00 7.59E‐0100000 0EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐091.51 0 0 00000001.51E+00 3.62E+01 3.62E+0000000 0Flowback	Boiler DR‐TP‐221.43E‐03 1.14E‐02 2.74E‐01 8.23E‐04 1.14E‐02 2.74E‐01 8.23E‐0400000000000 0Boom	Flare DR‐TP‐23140 3.50E+02 8.40E+03 2.52E+01 2.33E+02 5.60E+03 1.68E+0100000000000 0EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐010.55 0 0 00000005.52E‐01 1.32E+01 1.32E+0000000 0EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐020.55 0 0 00000005.52E‐01 1.32E+01 1.32E+0000000 0EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐111.51 0 0 00000001.51E+00 3.62E+01 3.62E+0000000 0Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270.00 0 0 9.65E+00 0 0 9.65E+0000000000000 0Stimulation	Vessel	Engines Various0.78 0 0 0 0 0 0 7.32E+00 1.76E+02 1.84E+0000000000 0Barges BG‐LP‐01	to	BG‐LP‐033.44 0 0 0 3.44E+00 8.25E+01 8.25E+0000000000000 0Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐020.8 0 0 0 4.15E+00 9.96E+01 9.96E+0000000000000 0Well	Evaluation	Vessel Various0.77 0 0 00000000004.60E+00 1.10E+02 1.10E+01 0 0 0Supply	Boats Various0.54 2.25E+00 5.40E+01 5.40E+00 2.25E+00 5.40E+01 5.40E+00 2.25E+00 5.40E+01 5.40E+00 4.50E+00 1.08E+02 1.08E+01 2.25E+00 5.40E+01 5.40E+00 4.50E+00 1.08E+02 1.08E+013.88E+02 9.32E+03 1.12E+02 2.77E+02 6.65E+03 1.21E+02 4.44E+01 1.07E+03 7.81E+01 4.56E+01 1.09E+03 8.17E+01 4.46E+01 1.07E+03 8.74E+01 4.73E+01 1.14E+03 8.18E+01Anadarko Petroleum CorporationVOC Emissions MatrixScenario1 Scenario2 Scenario3VOCScenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselVOC VOC VOC VOC VOC VOCThirdPartyEnginesTotalEPNAirEmissionSourcesDrillshipSupportVesselsAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet8	of	192VOC	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐011.28E‐03 5.04E‐03 1.21E‐01 1.18E‐02 4.36E‐03 1.05E‐01 1.18E‐02 4.56E‐03 1.09E‐01 1.18E‐02 6.53E‐03 1.57E‐01 1.18E‐02 5.49E‐03 1.32E‐01 1.18E‐02 6.53E‐03 1.57E‐01 1.18E‐02Emergency	Air	Compressor	 DR‐AC‐013.96E‐06 1.98E‐06 1.98E‐06 1.98E‐07 1.98E‐06 1.98E‐06 1.98E‐07 1.98E‐06 1.98E‐06 1.98E‐07 1.98E‐06 1.98E‐06 1.98E‐07 1.98E‐06 1.98E‐06 1.98E‐07 1.98E‐06 1.98E‐06 1.98E‐07Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐064.99E‐05 4.99E‐05 4.99E‐05 2.50E‐06 4.99E‐05 4.99E‐05 2.50E‐06 4.99E‐05 4.99E‐05 2.50E‐06 4.99E‐05 4.99E‐05 2.50E‐06 4.99E‐05 4.99E‐05 2.50E‐06 4.99E‐05 4.99E‐05 2.50E‐06Fast	Rescue	Craft DR‐FR‐011.12E‐05 1.12E‐05 1.12E‐05 5.58E‐07 1.12E‐05 1.12E‐05 5.58E‐07 1.12E‐05 1.12E‐05 5.58E‐07 1.12E‐05 1.12E‐05 5.58E‐07 1.12E‐05 1.12E‐05 5.58E‐07 1.12E‐05 1.12E‐05 5.58E‐07Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 00000000 0 000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 00000000 0 000000000Drillship	Fugitive	Emissions DR‐FE‐010 00000000 0 000000000Mud	Degasser	Vent DR‐VG‐010 00000000 0 000000000Painting	(paint	+	thinner)	Operations DR‐PO‐010 00000000 0 000000000Welding	Operations DR‐WE‐010 00000000 0 000000000EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐036.09E‐05 6.09E‐05 1.46E‐03 1.46E‐04 6.09E‐05 1.46E‐03 1.46E‐04 6.09E‐05 1.46E‐03 1.46E‐04 6.09E‐05 1.46E‐03 1.46E‐04 6.09E‐05 1.46E‐03 1.46E‐04 6.09E‐05 1.46E‐03 1.46E‐04EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐172.56E‐05 2.56E‐05 6.14E‐04 6.14E‐05 2.56E‐05 6.14E‐04 6.14E‐05 2.56E‐05 6.14E‐04 6.14E‐05 2.56E‐05 6.14E‐04 6.14E‐05 2.56E‐05 6.14E‐04 6.14E‐05 2.56E‐05 6.14E‐04 6.14E‐05Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐161.42E‐04 0 0 0 0 0 0 0 0 00000001.42E‐04 3.41E‐03 8.88E‐06EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐051.22E‐04 0 0 0 0 0 0 0 0 00000001.22E‐04 2.92E‐03 2.92E‐04EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐195.12E‐05 0 0 0 0 0 0 0 0 00000005.12E‐05 1.23E‐03 1.23E‐04EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐071.22E‐04 0 0 0 0 0 0 0 0 00000001.22E‐04 2.92E‐03 2.92E‐04EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐202.56E‐05 0 0 0 0 0 0 0 0 0 2.56E‐05 6.14E‐04 6.14E‐05000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐212.56E‐05 0 0 0 0 0 0 2.56E‐05 6.14E‐04 6.14E‐05 2.56E‐05 6.14E‐04 6.14E‐05 000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐091.22E‐04 0 0 0 0 0 0 0 0 0 1.22E‐04 2.92E‐03 2.92E‐04000000Flowback	Boiler DR‐TP‐220.0000 7.20E‐05 1.73E‐03 5.18E‐06 7.20E‐05 1.73E‐03 5.18E‐06 0 0 0000000000Boom	Flare DR‐TP‐230.00 0 0 0 0 0 0 0 0 0000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐011.75E‐04 0 0 0 0 0 0 0 0 0 1.75E‐04 4.19E‐03 4.19E‐04000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐021.75E‐04 0 0 0 0 0 0 0 0 0 1.75E‐04 4.19E‐03 4.19E‐04000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐111.22E‐04 0 0 0 0 0 0 0 0 0 1.22E‐04 2.92E‐03 2.92E‐04000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270.00 0 0 0 0 0 0 0 0 0000000000Stimulation	Vessel	Engines Various2.47E‐04 0 0 0 0 0 0 2.32E‐03 5.56E‐02 5.84E‐04000000000Barges BG‐LP‐01	to	BG‐LP‐032.78E‐04 0 0 0 2.78E‐04 6.66E‐03 6.66E‐04 0 0 0000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&TG‐GE‐01	to	TG‐GE‐022.52E‐04 0 0 0 1.31E‐03 3.15E‐02 3.15E‐03 0 0 0000000000Well	Evaluation	Vessel Various1.95E‐04 0 0 0 0 0 0 0 0 0 0 0 0 1.17E‐03 2.81E‐02 2.81E‐03 0 0 0Supply	Boats Various1.67E‐04 6.94E‐04 1.67E‐02 1.67E‐03 6.94E‐04 1.67E‐02 1.67E‐03 6.94E‐04 1.67E‐02 1.67E‐03 1.39E‐03 3.33E‐02 3.33E‐03 6.94E‐04 1.67E‐02 1.67E‐03 1.39E‐03 3.33E‐02 3.33E‐035.80E‐03 1.39E‐01 1.34E‐02 6.71E‐03 1.61E‐01 1.73E‐02 7.57E‐03 1.82E‐01 1.40E‐02 7.92E‐03 1.90E‐01 1.51E‐02 7.36E‐03 1.77E‐01 1.62E‐02 8.07E‐03 1.94E‐01 1.51E‐02Anadarko Petroleum CorporationPb Emissions MatrixAirEmissionSources EPNDrillshipThirdPartyEnginesPbScenario2 Scenario3 Scenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselScenario1Pb Pb Pb Pb PbSupportVesselsTotalAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet9	of	192Pb	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐017196 28416 681989 66356 24576 589828 66356 25728 617476 66356 36857 88456666342 30998 743957 66342 36857 884566 66342Emergency	Air	Compressor	 DR‐AC‐0122.33 11 11 1.12 11 11 1.12 11 11 1.12 11 11 1.12 11 11 1.12 11 11 1.12Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐06281.72 282 282 14.09 282 282 14.09 282 282 14.09 282 282 14.09 282 282 14.09 282 282 14.09Fast	Rescue	Craft DR‐FR‐0162.99 63 63 3.15 63 63 3.15 63 63 3.15 63 63 3.15 63 63 3.15 63 63 3.15Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 000000000000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 000000000000000000Drillship	Fugitive	Emissions DR‐FE‐010 000000000000000000Mud	Degasser	Vent DR‐VG‐01113 113 2714 271 113 2714 271 113 2714 271 113 2714 271 113 2714 271 113 2714 271Painting	(paint	+	thinner)	Operations DR‐PO‐010 000000000000000000Welding	Operations DR‐WE‐010 000000000000000000EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐03347.58 348 8342 834 348 8342 834 348 8342 834 348 8342 834 348 8342 834 348 8342834EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐17144.30 144 3463 346 144 3463 346 144 3463 346 144 3463 346 144 3463 346 144 3463346Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐16801.650000000000000008.02E+02 1.92E+04 5.01E+01EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐05695.160000000000000006.95E+02 1.67E+04 1.67E+03EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐19288.600000000000000002.89E+02 6.93E+03 6.93E+02EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐07695.160000000000000006.95E+02 1.67E+04 1.67E+03EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐20144.300000000001.44E+02 3.46E+03 3.46E+02000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐21144.300000001.44E+02 3.46E+03 3.46E+02 1.44E+02 3.46E+03 3.46E+02000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐09695.160000000.00E+00 0.00E+00 0.00E+00 6.95E+02 1.67E+04 1.67E+03000000Flowback	Boiler DR‐TP‐226.82 5.45E+01 1.31E+03 3.93E+00 5.45E+01 1.31E+03 3.93E+00000000000000Boom	Flare DR‐TP‐23116957 2.92E+05 7.02E+06 2.11E+04 1.95E+05 4.68E+06 1.40E+04000000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐01984.890000000009.85E+02 2.36E+04 2.36E+03000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐02984.890000000009.85E+02 2.36E+04 2.36E+03000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐11695.160000000006.95E+02 1.67E+04 1.67E+03000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270 000000000000000000Stimulation	Vessel	Engines Various1393.9000000013068 313627 3293000000000Barges BG‐LP‐01	to	BG‐LP‐031566.66 0 0 0 1567 37600 3760000000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐021423 0 0 0 7410 177846 17785000000000000Well	Evaluation	Vessel Various1099.390000000000006596 158313 15831 0 0 0Supply	Boats Various889.76 3707 88976 8898 3707 88976 8898 3707 88976 8898 7415 177952 17795 3707 88976 8898 7415 177952 17795324,683 7,792,395 96,581 232,356 5,576,544 111,108 42,616 1,022,793 78,818 44,392 1,065,408 84,422 41,421 994,107 91,356 45,194 1,084,647 84,472Anadarko Petroleum CorporationGHG Emissions MatrixScenario1 Scenario2 Scenario3EPNScenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselGHG GHG GHG GHG GHG GHGThirdPartyEnginesTotalAirEmissionSourcesDrillshipSupportVesselsAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet10	of	192GHG	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐017.05E‐02 2.78E‐01 6.68E+00 6.50E‐01 2.41E‐01 5.78E+00 6.50E‐01 2.52E‐01 6.05E+00 6.50E‐01 3.61E‐01 8.66E+00 6.50E‐01 3.04E‐01 7.29E+00 6.50E‐01 3.61E‐01 8.66E+00 6.50E‐01Emergency	Air	Compressor	 DR‐AC‐012.19E‐04 1.09E‐04 1.09E‐04 1.09E‐05 1.09E‐04 1.09E‐04 1.09E‐05 1.09E‐04 1.09E‐04 1.09E‐05 1.09E‐04 1.09E‐04 1.09E‐05 1.09E‐04 1.09E‐04 1.09E‐05 1.09E‐04 1.09E‐04 1.09E‐05Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐062.76E‐03 2.76E‐03 2.76E‐03 1.38E‐04 2.76E‐03 2.76E‐03 1.38E‐04 2.76E‐03 2.76E‐03 1.38E‐04 2.76E‐03 2.76E‐03 1.38E‐04 2.76E‐03 2.76E‐03 1.38E‐04 2.76E‐03 2.76E‐03 1.38E‐04Fast	Rescue	Craft DR‐FR‐016.17E‐04 6.17E‐04 6.17E‐04 3.08E‐05 6.17E‐04 6.17E‐04 3.08E‐05 6.17E‐04 6.17E‐04 3.08E‐05 6.17E‐04 6.17E‐04 3.08E‐05 6.17E‐04 6.17E‐04 3.08E‐05 6.17E‐04 6.17E‐04 3.08E‐05Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 00000000 0000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 00000000 0000000000Drillship	Fugitive	Emissions DR‐FE‐010 00000000 0000000000Mud	Degasser	Vent DR‐VG‐010 00000000 0000000000Painting	(paint	+	thinner)	Operations DR‐PO‐010 00000000 0000000000Welding	Operations DR‐WE‐010 00000000 0000000000EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐033.36E‐03 3.36E‐03 8.08E‐02 8.08E‐03 3.36E‐03 8.08E‐02 8.08E‐03 3.36E‐03 8.08E‐02 8.08E‐03 3.36E‐03 8.08E‐02 8.08E‐03 3.36E‐03 8.08E‐02 8.08E‐03 3.36E‐03 8.08E‐02 8.08E‐03EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐171.41E‐03 1.41E‐03 3.39E‐02 3.39E‐03 1.41E‐03 3.39E‐02 3.39E‐03 1.41E‐03 3.39E‐02 3.39E‐03 1.41E‐03 3.39E‐02 3.39E‐03 1.41E‐03 3.39E‐02 3.39E‐03 1.41E‐03 3.39E‐02 3.39E‐03Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐167.85E‐0300000000 00000007.85E‐03 1.88E‐01 4.91E‐04EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐056.73E‐0300000000 00000006.73E‐03 1.62E‐01 1.62E‐02EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐192.83E‐0300000000 00000002.83E‐03 6.78E‐02 6.78E‐03EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐076.73E‐0300000000 00000006.73E‐03 1.62E‐01 1.62E‐02EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐201.41E‐0300000000 01.41E‐03 3.39E‐02 3.39E‐03000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐211.41E‐030000001.41E‐03 3.39E‐02 3.39E‐03 1.41E‐03 3.39E‐02 3.39E‐03000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐096.73E‐0300000000 06.73E‐03 1.62E‐01 1.62E‐02000000Flowback	Boiler DR‐TP‐221.52E‐03 1.22E‐02 2.92E‐01 8.76E‐04 1.22E‐02 2.92E‐01 8.76E‐04 0 0 0000000000Boom	Flare DR‐TP‐235.88E‐01 1.47E+00 3.53E+01 1.06E‐01 9.80E‐01 2.35E+01 7.06E‐02 0 0 0000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐019.65E‐0300000000 09.65E‐03 2.31E‐01 2.31E‐02000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐029.65E‐0300000000 09.65E‐03 2.31E‐01 2.31E‐02000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐116.73E‐0300000000 06.73E‐03 1.62E‐01 1.62E‐02000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270 00000000 0000000000Stimulation	Vessel	Engines Various1.37E‐020000001.28E‐01 3.07E+00 3.23E‐02000000000Barges BG‐LP‐01	to	BG‐LP‐031.53E‐02 0 0 0 1.53E‐02 3.68E‐01 3.68E‐02 0 0 0000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐021.39E‐02 0 0 0 7.26E‐02 1.74E+00 1.74E‐01 0 0 0000000000Well	Evaluation	Vessel Various1.08E‐0200000000 0 0006.46E‐02 1.55E+00 1.55E‐01 0 0 0Supply	Boats Various9.21E‐03 3.84E‐02 9.21E‐01 9.21E‐02 3.84E‐02 9.21E‐01 9.21E‐02 3.84E‐02 9.21E‐01 9.21E‐02 7.67E‐02 1.84E+00 1.84E‐01 3.84E‐02 9.21E‐01 9.21E‐02 7.67E‐02 1.84E+00 1.84E‐01Total1.80E+00 4.32E+01 8.49E‐01 1.36E+00 3.26E+01 1.02E+00 4.18E‐01 1.00E+01 7.74E‐01 4.38E‐01 1.05E+01 8.34E‐01 4.07E‐01 9.76E+00 8.97E‐01 4.46E‐01 1.07E+01 8.34E‐01Anadarko Petroleum CorporationSO2Emissions MatrixAirEmissionSources EPNDrillshipThirdPartyEnginesSO2Scenario2 Scenario3 Scenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselScenario1SO2 SO2 SO2 SO2 SO2SupportVesselsAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet11	of	192SO2	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐012.20E‐03 8.69E‐03 2.09E‐01 2.03E‐02 7.52E‐03 1.80E‐01 2.03E‐02 7.87E‐03 1.89E‐01 2.03E‐02 1.13E‐02 2.71E‐01 2.03E‐02 9.48E‐03 2.28E‐01 2.03E‐02 1.13E‐02 2.71E‐01 2.03E‐02Emergency	Air	Compressor	 DR‐AC‐016.83E‐06 3.42E‐06 3.42E‐06 3.42E‐07 3.42E‐06 3.42E‐06 3.42E‐07 3.42E‐06 3.42E‐06 3.42E‐07 3.42E‐06 3.42E‐06 3.42E‐07 3.42E‐06 3.42E‐06 3.42E‐07 3.42E‐06 3.42E‐06 3.42E‐07Life	Boat	Diesel	Engines	no.	1	to	6 DR‐LB‐01	to	DR‐LB‐068.62E‐05 8.62E‐05 8.62E‐05 4.31E‐06 8.62E‐05 8.62E‐05 4.31E‐06 8.62E‐05 8.62E‐05 4.31E‐06 8.62E‐05 8.62E‐05 4.31E‐06 8.62E‐05 8.62E‐05 4.31E‐06 8.62E‐05 8.62E‐05 4.31E‐06Fast	Rescue	Craft DR‐FR‐011.93E‐05 1.93E‐05 1.93E‐05 9.64E‐07 1.93E‐05 1.93E‐05 9.64E‐07 1.93E‐05 1.93E‐05 9.64E‐07 1.93E‐05 1.93E‐05 9.64E‐07 1.93E‐05 1.93E‐05 9.64E‐07 1.93E‐05 1.93E‐05 9.64E‐07Dust	Collectors	no.	1	to	3 DR‐DC‐01	to	DR‐DC‐030 00000000 0000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐180 00000000 0000000000Drillship	Fugitive	Emissions DR‐FE‐010 00000000 0000000000Mud	Degasser	Vent DR‐VG‐010 00000000 0000000000Painting	(paint	+	thinner)	Operations DR‐PO‐010 00000000 0000000000Welding	Operations DR‐WE‐010 00000000 0000000000EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐031.05E‐04 1.05E‐04 2.52E‐03 2.52E‐04 1.05E‐04 2.52E‐03 2.52E‐04 1.05E‐04 2.52E‐03 2.52E‐04 1.05E‐04 2.52E‐03 2.52E‐04 1.05E‐04 2.52E‐03 2.52E‐04 1.05E‐04 2.52E‐03 2.52E‐04EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐174.41E‐05 4.41E‐05 1.06E‐03 1.06E‐04 4.41E‐05 1.06E‐03 1.06E‐04 4.41E‐05 1.06E‐03 1.06E‐04 4.41E‐05 1.06E‐03 1.06E‐04 4.41E‐05 1.06E‐03 1.06E‐04 4.41E‐05 1.06E‐03 1.06E‐04Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐162.45E‐0400000000 00000002.45E‐04 5.89E‐03 1.53E‐05EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐052.10E‐0400000000 00000002.10E‐04 5.05E‐03 5.05E‐04EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐198.83E‐0500000000 00000008.83E‐05 2.12E‐03 2.12E‐04EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐072.10E‐0400000000 00000002.10E‐04 5.05E‐03 5.05E‐04EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐204.41E‐0500000000 04.41E‐05 1.06E‐03 1.06E‐04000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐214.41E‐050000004.41E‐05 1.06E‐03 1.06E‐04 4.41E‐05 1.06E‐03 1.06E‐04000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐092.10E‐0400000000 02.10E‐04 5.05E‐03 5.05E‐04000000Flowback	Boiler DR‐TP‐220 00000000 0000000000Boom	Flare DR‐TP‐230 00000000 0000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐013.01E‐0400000000 03.01E‐04 7.23E‐03 7.23E‐04000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐023.01E‐0400000000 03.01E‐04 7.23E‐03 7.23E‐04000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐112.10E‐0400000000 02.10E‐04 5.05E‐03 5.05E‐04000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐270.0000000000 0000000000Stimulation	Vessel	Engines Various4.26E‐040000004.00E‐03 9.60E‐02 1.01E‐03000000000Barges BG‐LP‐01	to	BG‐LP‐034.79E‐04 0 0 0 4.79E‐04 1.15E‐02 1.15E‐03 0 0 0000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐024.35E‐04 0 0 0 2.27E‐03 5.44E‐02 5.44E‐03 0 0 0000000000Well	Evaluation	Vessel Various3.36E‐0400000000 0 0002.02E‐03 4.84E‐02 4.84E‐03 0 0 0Supply	Boats Various2.88E‐04 1.20E‐03 2.88E‐02 2.88E‐03 1.20E‐03 2.88E‐02 2.88E‐03 1.20E‐03 2.88E‐02 2.88E‐03 2.40E‐03 5.75E‐02 5.75E‐03 1.20E‐03 2.88E‐02 2.88E‐03 2.40E‐03 5.75E‐02 5.75E‐039.89E‐03 2.37E‐01 2.32E‐02 1.15E‐02 2.75E‐01 2.98E‐02 1.31E‐02 3.14E‐01 2.42E‐02 1.37E‐02 3.28E‐01 2.61E‐02 1.27E‐02 3.05E‐01 2.80E‐02 1.39E‐02 3.34E‐01 2.61E‐02Anadarko Petroleum CorporationH2SO4Emissions MatrixEPNH2SO4AirEmissionSourcesDrillshipThirdPartyEnginesH2SO4Scenario2 Scenario3 Scenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselScenario1H2SO4 H2SO4 H2SO4 H2SO4 H2SO4SupportVesselsTotalAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet12	of	192H2SO4	Matrixlb/unit lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/year lb/hr lb/day ton/yearDrillship	Main	Propulsion	Electrical	GeneratorEngines	and	Emergency	GeneratorDR‐ME‐01	to	DR‐ME‐08	andDR‐GE‐010.0692 2.73E‐01 6.56E+00 6.38E‐01 2.36E‐01 5.67E+00 6.38E‐01 2.47E‐01 5.94E+00 6.38E‐01 3.55E‐01 8.51E+00 6.38E‐01 2.98E‐01 7.16E+00 6.38E‐013.55E‐01 8.51E+00 6.38E‐01Emergency	Air	Compressor	 DR‐AC‐015.29E‐04 2.64E‐04 2.64E‐04 2.64E‐05 2.64E‐04 2.64E‐04 2.64E‐05 2.64E‐04 2.64E‐04 2.64E‐05 2.64E‐04 2.64E‐04 2.64E‐05 2.64E‐04 2.64E‐04 2.64E‐05 2.64E‐04 2.64E‐04 2.64E‐05Life	Boat	Diesel	Engines	No.	1	to	6 DR‐LB‐01	to	DR‐LB‐066.67E‐03 6.67E‐03 6.67E‐03 3.34E‐04 6.67E‐03 6.67E‐03 3.34E‐04 6.67E‐03 6.67E‐03 3.34E‐04 6.67E‐03 6.67E‐03 3.34E‐04 6.67E‐03 6.67E‐03 3.34E‐04 6.67E‐03 6.67E‐03 3.34E‐04Fast	Rescue	Craft DR‐FR‐011.49E‐03 1.49E‐03 1.49E‐03 7.46E‐05 1.49E‐03 1.49E‐03 7.46E‐05 1.49E‐03 1.49E‐03 7.46E‐05 1.49E‐03 1.49E‐03 7.46E‐05 1.49E‐03 1.49E‐03 7.46E‐05 1.49E‐03 1.49E‐03 7.46E‐05Dust	Collectors	No.	1	to	3 DR‐DC‐01	to	DR‐DC‐03000000000 0000000000Drill	Ship	Diesel		and	Jet	Fuel	Storage	Tanks DR‐FT‐01	to	DR‐FT‐187.59E‐06 7.59E‐06 1.82E‐04 3.65E‐02 7.59E‐06 1.82E‐04 3.65E‐02 7.59E‐06 1.82E‐04 3.65E‐02 7.59E‐06 1.82E‐04 3.65E‐02 7.59E‐06 1.82E‐04 3.65E‐02 7.59E‐06 1.82E‐04 3.65E‐02Drillship	Fugitive	Emissions DR‐FE‐01000000000 0000000000Mud	Degasser	Vent DR‐VG‐01000000000 0000000000Painting	(paint	+	thinner)	Operations DR‐PO‐013 6.61E+00 1.59E+02 1.03E+01 6.61E+00 1.59E+02 1.03E+01 6.61E+00 1.59E+02 1.03E+01 6.61E+00 1.59E+02 1.03E+01 6.61E+00 1.59E+02 1.03E+01 6.61E+00 1.59E+02 1.03E+01Welding	Operations DR‐WE‐018.02E‐02 2.67E‐01 6.42E+00 6.42E‐01 2.67E‐01 6.42E+00 6.42E‐01 2.67E‐01 6.42E+00 6.42E‐01 2.67E‐01 6.42E+00 6.42E‐01 2.67E‐01 6.42E+00 6.42E‐01 2.67E‐01 6.42E+00 6.42E‐01EPA	Tier	II	Third	Party	Engines≤300	HP DR‐TP‐038.13E‐03 8.13E‐03 1.95E‐01 1.95E‐02 8.13E‐03 1.95E‐01 1.95E‐02 8.13E‐03 1.95E‐01 1.95E‐02 8.13E‐03 1.95E‐01 1.95E‐02 8.13E‐03 1.95E‐01 1.95E‐02 8.13E‐03 1.95E‐01 1.95E‐02EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐173.42E‐03 3.42E‐03 8.20E‐02 8.20E‐03 3.42E‐03 8.20E‐02 8.20E‐03 3.42E‐03 8.20E‐02 8.20E‐03 3.42E‐03 8.20E‐02 8.20E‐03 3.42E‐03 8.20E‐02 8.20E‐03 3.42E‐03 8.20E‐02 8.20E‐03Third	Party	Well	Evaluation	Engines	≤	140	HPDR‐TP‐12	to	DR‐TP‐161.90E‐02 00000000 00000001.90E‐02 4.56E‐01 1.19E‐03EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐04	and	DR‐TP‐051.63E‐02 00000000 00000001.63E‐02 3.90E‐01 3.90E‐02EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐18	and	DR‐TP‐196.83E‐03 00000000 00000006.83E‐03 1.64E‐01 1.64E‐02EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐06	and	DR‐TP‐071.63E‐02 00000000 00000001.63E‐02 3.90E‐01 3.90E‐02EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐203.42E‐03 00000000 03.42E‐03 8.20E‐02 8.20E‐03000000EPA	Tier	II	Third	Party	Engines	≤	126	HPDR‐TP‐213.42E‐03 0000003.42E‐03 8.20E‐02 8.20E‐03 3.42E‐03 8.20E‐02 8.20E‐03000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐08	and	DR‐TP‐091.63E‐02 00000000 01.63E‐02 3.90E‐01 3.90E‐02000000Flowback	Boiler DR‐TP‐222.36E‐05 1.89E‐04 4.53E‐03 1.36E‐05 1.89E‐04 4.53E‐03 1.36E‐05 0 0 0000000000Boom	Flare DR‐TP‐231.84 4.61E+00 1.11E+02 3.32E‐01 3.07E+00 7.37E+01 2.21E‐01 0 0 0000000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐011.03E‐02 00000000 01.03E‐02 2.46E‐01 2.46E‐02000000EPA	Tier	II	Third	Party	Engines	≤	860	HPDR‐TP‐021.03E‐02 00000000 01.03E‐02 2.46E‐01 2.46E‐02000000EPA	Tier	II	Third	Party	Engines	≤	300	HPDR‐TP‐10	and	DR‐TP‐111.63E‐02 00000000 01.63E‐02 3.90E‐01 3.90E‐02000000Condensate	Tanks DR‐TP‐25	to	DR‐TP‐271.05E‐04 7.59E‐06 1.82E‐04 5.02E‐01 7.59E‐06 1.82E‐04 5.02E‐01 7.59E‐06 1.82E‐04 1.82E‐05 7.59E‐06 1.82E‐04 1.82E‐05 7.59E‐06 1.82E‐04 1.82E‐05 7.59E‐06 1.82E‐04 1.82E‐05Stimulation	Vessel	Engines Various1.34E‐02 0000001.26E‐01 3.02E+00 3.17E‐02000000000Barges BG‐LP‐01	to	BG‐LP‐033.71E‐02 0 0 0 3.71E‐02 8.90E‐01 8.90E‐02 0 0 0000000000Tug	BoatsTG‐ME‐01	to	TG‐ME‐03	&	TG‐GE‐01	to	TG‐GE‐021.37E‐02 0 0 0 7.13E‐02 1.71E+00 1.71E‐01 0 0 0000000000Well	Evaluation	Vessel Various1.27E‐02 00000000 0 0007.61E‐02 1.83E+00 1.83E‐01 0 0 0Supply	Boats Various9.14E‐03 3.81E‐02 9.14E‐01 9.14E‐02 3.81E‐02 9.14E‐01 9.14E‐02 3.81E‐02 9.14E‐01 9.14E‐02 7.62E‐02 1.83E+00 1.83E‐01 3.81E‐02 9.14E‐01 9.14E‐02 7.62E‐02 1.83E+00 1.83E‐011.18E+01 2.83E+02 1.26E+01 1.03E+01 2.48E+02 1.27E+01 7.29E+00 1.75E+02 1.17E+01 7.31E+00 1.75E+02 1.18E+01 7.29E+00 1.75E+02 1.19E+01 7.33E+00 1.76E+02 1.18E+01Note:	Highest	single	HAP	emission: Xylene5.71E+00tpyAnadarko Petroleum CorporationHAP Emissions MatrixAirEmissionSources EPNDrillshipThirdPartyEnginesHAPScenario2 Scenario3 Scenario4 Scenario5DrillingScenarioGas	Flowback Oil	Flowback Stimulation	Vessel Completion Well	Evaluation	VesselScenario1HAP HAP HAP HAP HAPSupportVesselsTotalAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet13	of	192HAP	MatrixEngine Rating [1] = 94 kW 126 HP Operating Time [2] = 24 hrs/day [1] 4,800 hrs/yr Fuel Type [3] = ULSD No. of Engines [1] = 5

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

PM 40 CFR 89.112, AP-42 [4] 0.30 g/kW-hr 0.31 7.46 0.75

PM 10 40 CFR 89.112, AP-42 [5] 0.30 g/kW-hr 0.31 7.46 0.75

PM 2.5 40 CFR 89.112, AP-42 [5] 0.30 g/kW-hr 0.31 7.46 0.75 NO x 40 CFR 89.112 [4] 6.60 g/kW-hr 6.84 164.13 16.41 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 7.07E-03 0.17 0.02 CO 40 CFR 89.112 [4] 5.00 g/kW-hr 5.18 124.34 12.43 VOC AP-42 [6],[8] 2.51E-03 lb/HP-hr 1.58 37.97 3.80

Pb EPA [7] 2.03E-07 lb/HP-hr 1.28E-04 3.07E-03 3.07E-04 H 2 SO 4 Fuel S Conten t [3] 3.50E-07 lb/HP-hr 2.21E-04 5.30E-03 5.30E-04

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] Based on Engine Specification obtained provided by Mr. Aaron Wade (Anadarko) to Mr. Raghu Soule (Trinity) via email on August 8, 2012. Per provided information, this engine is EPA Tier II certified (Table 1 of Federal Register/Vol. 63, No. 205, October 23, 1998 and 40 CFR 89.112(a)). Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM2.5 = PM10 = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. 

## Anadarko Petroleum Corporation Emission Calculations 3rd Party Engines ≤ 126 HP, EPA Tier II DR-TP-17 To DR-TP-21 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Rating is based on the engine Specification Sheets. All engines with rating less than or equal to 126 HP are considered to have 126 HP for consistency. A total of five 3rd Party engines fall into this category. Assumptions: Max operating time of 24 hr/day .

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 14	of	192 3rd	Party	<	126HP	Crit.

### Engine Rating [1] = 94 kW 126 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Number of Engines [1] = 5

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4],[5] 7.67E-04 lb/MMBtu 3.38E-03 8.12E-02 8.12E-03

Acrolein AP-42 [4],[5] 9.25E-05 lb/MMBtu 4.08E-04 9.79E-03 9.79E-04 Benzene AP-42 [4],[5] 9.33E-04 lb/MMBtu 4.11E-03 9.87E-02 9.87E-03 Formaldehyde AP-42 [4],[5] 1.18E-03 lb/MMBtu 5.20E-03 1.25E-01 1.25E-02 Toluene AP-42 [4],[5] 4.09E-04 lb/MMBtu 1.80E-03 4.33E-02 4.33E-03 Xylenes AP-42 [4],[5] 2.85E-04 lb/MMBtu 1.26E-03 3.02E-02 3.02E-03 1,3-Butadiene AP-42 [4],[5] 3.91E-05 lb/MMBtu 1.72E-04 4.14E-03 4.14E-04

Total PAH AP-42 [4],[5] 1.68E-04 lb/MMBtu 7.41E-04 1.78E-02 1.78E-03 N aphthalene AP-42 [4],[5] 8.48E-05 lb/MMBtu 3.74E-04 8.98E-03 8.98E-04 0.02 0.41 0.04

[1]

[2] [3] [4]
[5] An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations 3rd Party Engines ≤ 126 HP, EPA Tier II DR-TP-17 To DR-TP-21 HAP

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Rating is based on the engine Specification Sheets. All engines with rating less than or equal to 126 HP are considered to have 126 HP for consistency. A total of five 3rd Party engines fall into this category. Operating time for this engine is conservatively assumed to be 24 hrs/day Per 40 CFR 80.510(b), Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 15	of	192 3rd	Party<126HP	HAPEngine Rating [1] = 94 kW 126 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Number of Engines [1] = 5

Maximum Hourly Emissions [7] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 719.07 17257.60 1725.76

CH 4 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 0.03 0.70 0.07

N 2 O 40 CFR 98 Subpart C [5] 6.00E-04 kg/MMBtu 5.83E-03 0.14 0.01

CO 2 e 40 CFR 98 Subpart C [6] -- -- 721.49 17,315.70 1,731.57

[1]

[2] [3]

[4]

[5]

[6]

[7] Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. Global warming potentials (GWP) for CH 4 , CO 2 and N 2 O are used to calculate CO 2 equivalent (CO 2 e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Pollutant Emission Factor Basis Emission Factor

Rating is based on the engine Specification Sheets. All engines with rating less than or equal to 126 HP are considered to have 126 HP for consistency. A total of five 3rd Party engines fall into this category. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. 

## Anadarko Petroleum Corporation Emission Calculations 3rd Party Engines ≤ 126 HP, EPA Tier II DR-TP-17 To DR-TP-21 GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 16	of	192 3rd	Party<126HP	GHG

### Engine Rating [1] = 104 kW 140 HP Operating Time [2] = 24 hrs/day 125 hrs/yr Fuel Type [3] = ULSD Number of Engines = 5

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [5],[4] 2.20E-03 lb/HP-hr 1.54 36.96 0.10 PM 10 

### AP-42 [5],[4] 2.20E-03 lb/HP-hr 1.54 36.96 0.10 PM 2.5 

### AP-42 [5],[4] 2.20E-03 lb/HP-hr 1.54 36.96 0.10 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 21.70 520.80 1.36 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 7.85E-03 0.19 0.00 CO AP-42 [5] 6.68E-03 lb/HP-hr 4.68 112.22 0.29 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 1.76 42.19 0.11

Pb EPA [6] 2.03E-07 lb/HP-hr 1.42E-04 3.41E-03 8.88E-06 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 2.45E-04 5.89E-03 1.53E-05

[1]

[2] [3]

[4]

[5]

[6]

[7] Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. 

## Anadarko Petroleum Corporation Emission Calculations

DR-TP-12 To DR-TP-16

Criteria Pollutants Third Party Well Evaluation Engines ≤ 140 HP, No EPA Tier Certification

SB-TP-05 to SB-TP-09

Pollutant Emission Factor Basis Emission Factor

Representative standard capacity engines to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 17	of	192 3rd	Party	<140	hp	Crit.

### Engine Rating [1] = 104 kW 140 HP Operating Time [2] = 24 hrs/day 125 hrs/yr Fuel Type [5] = ULSD Number of Engines = 5

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 3.76E-03 9.02E-02 2.35E-04

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 4.53E-04 1.09E-02 2.83E-05 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 4.57E-03 1.10E-01 2.86E-04 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 5.78E-03 1.39E-01 3.61E-04 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 2.00E-03 4.81E-02 1.25E-04 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 1.40E-03 3.35E-02 8.73E-05 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 8.23E-04 1.98E-02 5.15E-05 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 1.92E-04 4.60E-03 1.20E-05 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 4.16E-04 9.97E-03 2.60E-05 Total VOC HAPs 1.90E-02 4.56E-01 1.19E-03

[1]

[2] [3]
[4] An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## Third Party Engines ≤ 140 HP, No EPA Tier Certification

Pollutant Emission Factor Basis Emission Factor

Representative standard capacity engines to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

DR-TP-12 To DR-TP-16 HAP

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 18	of	192 3rd	Party<140	HP	HAP

### Engine Rating [1] = 104 kW 140 HP Operating Time [2] = 24 hrs/day [2] 125 hrs/yr Fuel Type [7] = ULSD Number of Engines = 5

Average Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 73.96 kg/MMBtu 799 19,175 49.94 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 0.03 0.78 2.03E-03 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 6.48E-03 0.16 4.05E-04 CO 2 

### e EPA [6] -- -- 801.65 19,239.67 50.10

[1]

[2] [3]

[4]

[5]
[6]

[7] Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion 

## Anadarko Petroleum Corporation Emission Calculations

DR-TP-12 To DR-TP-16 GHG Pollutants Third Party Engines ≤ 140 HP, No EPA Tier Certification

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Pollutant Emission Factor Basis Emission Factor

Representative standard capacity engines to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 19	of	192 3rd	Party	<140HP	GHG

### Engine Rating [1] = 224 kW 300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Number of Engines [1] = 9

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 40 CFR 89.112, AP-42 [4],[5] 0.20 g/kW-hr 0.89 21.33 2.13
PM 10 

### 40 CFR 89.112, AP-42 [4],[5] 0.20 g/kW-hr 0.89 21.33 2.13
PM 2.5 

### 40 CFR 89.112, AP-42 [4],[5] 0.20 g/kW-hr 0.89 21.33 2.13 NO x 

### 40 CFR 89.112 [5] 6.60 g/kW-hr 29.33 704.01 70.40 SO 2 

### Fuel S Content [3] 1.12E-05 lb/hp-hr 0.03 0.73 0.07 CO 40 CFR 89.112 [5] 3.50 g/kW-hr 15.56 373.34 37.33 VOC AP-42 [7] 2.51E-03 lb/hp-hr 6.79 162.91 16.29

Pb EPA [6] 2.03E-07 lb/hp-hr 5.48E-04 1.32E-02 1.32E-03 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/hp-hr 9.46E-04 2.27E-02 2.27E-03

[1]

[2] [3]

[4]

[5]

[6]

[7] Lead emission factor (2.9x10 -5 

### lb/MMBtu) is obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines is used as a surrogate for distillate oil-fired engines due to lack of specific emission factors for distillate oil-fired engines. Factor is based on AP-42, Table 3.3-1. All TOC is assumed to be VOC. TOC emission factor is calculated as the sum of exhaust and crankcase emission factors. Rating is based on the engine Specification Sheets. All engines with rating around 300 HP are considered to have 300 HP for consistency. A total of nine 3rd Party engines fall into this category. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 

### and 2 wt.% of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on AP-42 Appendix A, table 3.4.1 footnote e and Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, all PM is assumed to be < 1 μ m, therefore, assumed PM 2.5 

### = PM 10 

### = PM. According to Specification Sheet, this engine is EPA Tier 2 certified. The NOx+NMHC emission factor is 6.6 g/kW-hr. Factor for NOx+NMHC can also be found in 40 CFR, Part 89.112 Table 1. From the same reference, CO emission factor is 3.5 g/kW-hr, and PM emission factor is 0.2 g/kW-hr. Pollutant Emission Factor Basis Emission Factor 

## Anadarko Petroleum Corporation Emission Calculations Third Party Engines ≤ 300 HP, EPA Tier II DR-TP-03 To DR-TP-11 Criteria Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 20	of	192 3rd	Party	<300	HP	Crit.

## Third Party Engines ≤ 300 HP, EPA Tier II

Engine Rating [1] = 224 kW 300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Number of Engines [1] = 9

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4],[5] 7.67E-04 lb/MMBtu 0.01 0.35 0.03

Acrolein AP-42 [4],[5] 9.25E-05 lb/MMBtu 1.75E-03 0.04 4.20E-03 Benzene AP-42 [4],[5] 9.33E-04 lb/MMBtu 0.02 0.42 0.04 Formaldehyde AP-42 [4],[5] 1.18E-03 lb/MMBtu 0.02 0.54 0.05 Toluene AP-42 [4],[5] 4.09E-04 lb/MMBtu 7.73E-03 0.19 0.02 Xylenes AP-42 [4],[5] 2.85E-04 lb/MMBtu 5.39E-03 0.13 0.01 1,3-Butadiene AP-42 [4],[5] 3.91E-05 lb/MMBtu 7.39E-04 0.02 1.77E-03

Total PAH AP-42 [4],[5] 1.68E-04 lb/MMBtu 3.18E-03 0.08 7.62E-03 N aphthalene AP-42 [4],[5] 8.48E-05 lb/MMBtu 1.60E-03 0.04 3.85E-03 0.07 1.76 0.18

[1]

[2] [3] [4]
[5] An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr is used to convert from lb/MMBtu to lb/hphr to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations

DR-TP-03 To DR-TP-11 HAP

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Rating is based on the engine Specification Sheets. All engines with rating around 300 HP are considered to have 300 HP for consistency. A total of nine 3rd Party engines fall into this category. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Emission factors are based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 21	of	192 3rd	Party	<300	HP	HAP

### Engine Rating [1] = 224 kW 300 HP Operating Time [2] = 24 hrs/da y 4,800 hrs/yr CO 2 

### 1 Operating load [2] = 100% CH 4 

### 21 Fuel Type [3] = ULSD N 2 

### O 310 Number of Engines [1] = 9

Maximum Hourly Emissions [7] 

### Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 3081.71 73961.16 7396.12

CH 4 

### 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 0.13 3.00 0.30

N 2 

### O 40 C FR 98 Subpart C [5] 6.00E-04 kg/MMBtu 0.03 0.60 0.06

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 3128.22 74210.16 7421.02

[1]

[2] [3] [4]

[5]

[6]

[7] Emission factor is based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 is used to calculate emissions. Emission factor is based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) is used to calculate emissions. Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr is used to convert from lb/MMBtu to lb/hphr to calculate emissions. Pollutant Emission Factor Basis Emission Factor

Rating is based on the engine Specification Sheets. All engines with rating around 300 HP are considered to have 300 HP for consistency. A total of nine 3rd Party engines fall into this category. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Chemicals Global Warming Potential (100 yr.) 

## Anadarko Petroleum Corporation Emission Calculations Third Party Engines ≤ 300 HP, EPA Tier II DR-TP-03 To DR-TP-11 GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 22	of	192 3rd	Party<300HP	GHGEngine Rating [1] = 641 kW 860 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD No. of Engines [1] 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 40 CFR 89.112, AP-42 [6] 0.20 g/kW-hr 0.57 13.57 1.36 PM 10 40 CFR 89.112, AP-42 [5] 0.11 g/kW-hr 0.32 7.78 0.78 PM 2.5 40 CFR 89.112, AP-42 [5] 0.11 g/kW-hr 0.31 7.55 0.75 NO x 40 CFR 89.112 [6] 6.40 g/kW-hr 18.10 434.34 43.43 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.46 0.05 CO 40 CFR 89.112 [6] 3.50 g/kW-hr 9.90 237.53 23.75 VOC AP-42 [4],[8] 6.42E-04 lb/HP-hr 1.10 26.48 2.65

Pb EPA [7] 2.03E-07 lb/HP-hr 3.49E-04 8.38E-03 8.38E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 6.03E-04 1.45E-02 1.45E-03

[1]

[2]

[3]

[4]

[5]

[6]

[7]

[8] Based on Engine Specification obtained from Manufacturer's website for Caterpillar Engine which is certified for EPA Tier II (Table 1 of Federal Register/Vol. 63, No. 205, October 23, 1998 and 40 CFR 89.112(a)). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Rating is based on the engine Specification Sheets. All engines with rating around 860 HP are considered to have 860 HP for consistency. A total of two 3rd Party engines fall into this category. Assumptions: Max operating time of 24 hr/day. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012.

Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). PM 10 and PM 2.5 emission factors obatined by applying the ratio of PM/PM 10 and PM/PM 2.5 from AP-42 Chapter 3, Table 3.4

- 1 and Table 3.4-2 on EPA Tier II PM emission factor. Pollutant Emission Factor Basis Emission Factor 

## Anadarko Petroleum Corporation Emission Calculations Third Party, ≤ 860 HP, EPA Tier II Engines DR-TP-01 To DR-TP-02 Criteria Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 23	of	192 3rd	Party	<	860	HP	Crit.

### Engine Rating [1] = 641 kW 860 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [6] = ULSD No. of Engines [1] = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 3.03E-04 7.28E-03 7.28E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 9.49E-05 2.28E-03 2.28E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 9.34E-03 2.24E-01 2.24E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 9.50E-04 2.28E-02 2.28E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 3.38E-03 8.12E-02 8.12E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.32E-03 5.58E-02 5.58E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 2.55E-03 6.13E-02 6.13E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.57E-03 3.76E-02 3.76E-03 Total VOC HAPs 0.02 0.49 0.05

[1]

[2]

[3]

[4]

[5] 

## Anadarko Petroleum Corporation Emission Calculations Third Party, ≤ 860 HP, EPA Tier II DR-TP-01 To DR-TP-02 HAP

Pollutant Emission Factor Basis Emission Factor

Rating is based on the engine Specification Sheets. All engines with rating around 860 HP are considered to have 860 HP for consistency. A total of two 3rd Party engines fall into this category. Assumptions: Max operating time of 24 hr/day. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 24	of	192 3rd	Party<860HP	HAP

## Third Party, ≤ 860 HP, EPA Tier II Engines

Engine Rating [1] = 641 kW 860 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD No. of Engines [1] = 2

Average Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 73.96 kg/MMBtu 1,963.17 47,116.00 4,711.60

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.08 1.91 0.19

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.02 0.38 0.04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,969.78 47,274.62 4,727.46

[1]

[2]

[3]

[4]

[5] [6]

[7] Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Rating is based on the engine Specification Sheets. All engines with rating around 860 HP are considered to have 860 HP for consistency. A total of two 3rd Party engines fall into this category. Assumptions: Max operating time of 24 hr/day. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Pollutant Emission Factor Basis Emission Factor



## Anadarko Petroleum Corporation Emission Calculations

DR-TP-01 To DR-TP-02 GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 25	of	192 3rd	Party<860HP	GHG

### Rated Input [1] = 8 MMBtu/hr Conversion Factor [10] = 140 MMBtu/10 3 

### gal Operating Time [2] = 24 hrs/day [1] 1,152 MMBtu/yr Fuel Type [8] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4] 3.30 lb/10 3 

### gal 0.18 4.40 1.36E-02
PM 10 

### AP-42 [5] 3.30 lb/10 3 

### gal 0.18 4.40 1.36E-02
PM 2.5 

### AP-42 [5] 3.30 lb/10 3 

### gal 0.18 4.40 1.36E-02 NO x 

### AP-42 [3] 20.00 lb/10 3 

### gal 1.11 26.69 8.23E-02 SO 2 

### AP-42 [3] 0.21 lb/10 3 

### gal 0.01 0.28 8.76E-04 CO AP-42 [3] 5.00 lb/10 3 

### gal 0.28 6.67 2.06E-02 VOC AP-42 [6],[7] 0.20 lb/10 3 

### gal 0.01 0.27 8.23E-04

Pb AP-42 [9] 9.00 lb/10 12 

### Btu 7.01E-05 1.68E-03 5.18E-06

[1]

[2] [3]

[4]

[5] [6]

[7] [8] [9]

[10] 

## Anadarko Petroleum Corporation Emission Calculations

Flowback Boiler

Pollutant Emission Factor Basis Emission Factor 

## DR-TP-22

Criteria Pollutants

Based on AP-42 Section 1.3, Fuel Oil Combustion, Section 1.3.4.3, p. 1.3-8, 5/10. Representative Boiler to be used for well completion activities. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Assumptions: Max operating time of 24 hr/day. Based on AP-42 Section 1.3, Fuel Oil Combustion, Table 1.3-1 Emission Factors for No.2 fuel oil, p. 1.3-11,5/10. Weight % of sulfur in oil was estimated based on usage of ULSD as fuel containing 15 ppm of sulfur content.

Based on AP-42 Section 1.3, Fuel Oil Combustion, Table 1.3-1and Table 1.3-2, Emission Factors for No.2 fuel oil was used. Total particulate emissions is the sum of filterable and total condensable particulate emissions. All PM is assumed to be < 1 um, therefore, assumed PM2.5 = PM10 = PM. Based on AP-42 Section 1.3, Fuel Oil Combustion, Table 1.3-3, Industrial Boilers NMTOC Emission Factors for Distillate fuel oil was used, p. 1.3-14, 5/10. All NMTOC is assumed to be VOC. ULSD is proposed as fuel for the Well Completion Activity. Based on AP-42 Section 1.3, Fuel Oil Combustion, Table 1.3-10, Emission Factors for Distillate fuel oil was used, p. 1.3-22,5/10.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 26	of	192 DR‐TP‐22	‐	Criteria

### Rated Input [1] = 8 MMBtu/hr Conversion Factor [5] = 140 MMBtu/10 3 

### gal Operating Time [2] = 24 hrs/day [1] 1,152 MMBtu/yr Fuel Type [4] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Formaldehyde AP-42 [3] 0.061 lb/10 3 

### gal 3.39E-03 8.14E-02 2.51E-04 POM AP-42 [3] 3.30E-03 lb/10 3 

### gal 1.84E-04 4.40E-03 2.51E-04 Total VOC HAPs 1.84E-04 4.40E-03 2.51E-04

[1]

[2] [3]

[4] [5] 

## Anadarko Petroleum Corporation Emission Calculations

Flowback Boiler

Pollutant Emission Factor Basis Emission Factor 

## DR-TP-22

HAP

Representative Boiler to be used for well completion activities. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Assumptions: Max operating time of 24 hr/day. Based on AP-42 Section 1.3, Fuel Oil Combustion, Table 1.3-8, Emission Factors for Distillate fuel oil was used, p. 1.3-20,5/10. ULSD is proposed as fuel for the Well Completion Activity. Based on AP-42 Section 1.3, Fuel Oil Combustion, Section 1.3.4.3, p. 1.3-8, 5/10.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 27	of	192 DR‐TP‐22	‐	HAP

### Rated Input [1] = 8 MMBtu/hr Conversion Factor [5] = 140 MMBtu/10 3 

### gal Operating Time [2] = 24 hrs/day [1] 1,152 MMBtu/yr Fuel Type [7] = ULSD

Average Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 73.96 kg/MMBtu 1,269.54 30,468.87 93.89

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.05 1.24 3.81E-03

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.25 7.62E-04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,273.81 30,571.44 94.21

[1]

[2] [3]

[4]

[5] [6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations

Flowback Boiler

Pollutant Emission Factor Basis Emission Factor 

## DR-TP-22

GHG Pollutants

ULSD is proposed as fuel for the Well Completion Activity. Representative Boiler to be used for well completion activities. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. Based on AP-42 Section 1.3, Fuel Oil Combustion, Section 1.3.4.3, p. 1.3-8, 5/10. CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 28	of	192 DR‐TP‐22	‐	GHG

### Rated Firing [1] = 60 MMscf/day Heating Value [5] = 1,020 MMBtu/MMscf Operating Time [2] = 24 hrs/day [1] 360 MMscf/year Flare efficiency [4] = 98%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [6] 7.60 lb/MMscf 18.62 446.88 1.34 PM 10 

### AP-42 [3] 7.60 lb/MMscf 18.62 446.88 1.34 PM 2.5 

### AP-42 [3] 7.60 lb/MMscf 18.62 446.88 1.34 NO x 

### AP-42 [7] 0.07 lb/MMBtu 169.93 4078.37 12.24 SO 2 

### AP-42 [6] 0.60 lb/MMscf 1.47 35.28 0.11 CO AP-42 [7] 0.37 lb/MMBtu 924.63 22191.12 66.57 VOC AP-42 [7],[8] 0.14 lb/MMBtu 349.86 8396.64 25.19

[1]

[2] [3] [4] [5] [6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Boom Flare

Pollutant Emission Factor Basis Emission Factor 

## DR-TP-23

Criteria Pollutants

Based on AP-42 Section 13.5, Industrial Flares, Table 13.5-1, Emission Factors for Flare operation was used, p. 13.5-4, 09/91. Total hydrocarbon is assumed to be VOC. Representative Flare to be used for well completion activities. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Assumptions: Max operating time of 24 hr/day. All PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Flare destruction efficiency assumed to be 98%. Based on AP-42 Section 1.4, Natural Gas Combustion, footnote (a) of Table 1.4-2, p. 1.4-6, 07/98. Based on AP-42 Section 1.4, Natural Gas Combustion, Table 1.4-2, Emission Factors for NG combustion was used, p. 1.4-6, 07/98. Total particulate emissions is the sum of filterable and total condensable particulate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 29	of	192 DR‐TP‐23	‐	CriteriaFlare flow [1] = 60 MMscf/day Heating Value [5] = 1,020 MMBtu/MMscf Operating Time [2] = 24 hrs/day [1] 360 MMscf/year Total number of events [2] = 1 events/y r Flare efficiency [4] = 98%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Benzene AP-42 

### [3] 2.10E-03 lb/MMscf 5.15E-03 0.12 3.70E-04 Dichlorobenzene AP-42 

### [3] 1.20E-03 lb/MMscf 2.94E-03 0.07 2.12E-04

Formaldehyde AP-42 

### [3] 7.50E-02 lb/MMscf 0.18 4.41 1.32E-02 Hexane AP-42 

### [3] 1.80 lb/MMscf 4.41 105.84 3.18E-01 Naphthalene AP-42 

### [3] 6.10E-04 lb/MMscf 1.49E-03 0.04 1.08E-04

Toluene AP-42 

### [3] 3.40E-03 lb/MMscf 8.33E-03 0.20 6.00E-04 Arsenic AP-42 

### [7] 2.00E-04 lb/MMscf 4.90E-04 0.01 3.53E-05 Beryllium AP-42 

### [7] 1.20E-05 lb/MMscf 2.94E-05 7.06E-04 2.12E-06 Cadmium AP-42 

### [7] 1.10E-03 lb/MMscf 2.70E-03 0.06 1.94E-04 Chromium AP-42 

### [7] 1.40E-03 lb/MMscf 3.43E-03 0.08 2.47E-04

Cobalt AP-42 

### [7] 8.40E-05 lb/MMscf 2.06E-04 4.94E-03 1.48E-05 Manganese AP-42 

### [7] 3.80E-04 lb/MMscf 9.31E-04 0.02 6.70E-05

Mercury AP-42 

### [7] 2.60E-04 lb/MMscf 6.37E-04 0.02 4.59E-05 Nickel AP-42 

### [7] 2.10E-03 lb/MMscf 5.15E-03 0.12 3.70E-04 Selenium AP-42 

### [7] 2.40E-05 lb/MMscf 5.88E-05 1.41E-03 4.23E-06

POM AP-42 [3],[6] 8.82E-05 lb/MMscf 2.16E-04 5.19E-03 1.56E-05

Total VOC HAPs 4.61 110.58 0.33

[1]

[2] [3]

[4] [5] [6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations

Boom Flare

Pollutant Emission Factor Basis Emission Factor 

## DR-TP-23

HAP

Based on AP-42 Section 1.4 Natural Gas Combustion, Table 1.4-4 Emission Factors for Metals from Natural Gas Combustion, 7/98, p. 1.4-9. Representative Flare to be used for well completion activities. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Assumptions: Max operating time of 24 hr/day. Based on AP-42 Section 1.4 Natural Gas Combustion, Table 1.4-3 Emission Factors for Speciated Organics Compounds from Natural Gas Combustion, 7/98, p. 1.4-7. Flare destruction efficiency assumed to be 98%. Based on AP-42 Section 1.4, Natural Gas Combustion, footnote (a) of Table 1.4-2, p. 1.4-6, 07/98. Per footnote b and c of AP-42 Section 1.4 Natural Gas Combustion, Table 1.4-3 Emission Factors for Speciated Organics Compounds from Natural Gas Combustion, 7/98, p. 1.4-7. All individual species of POM have been conservatively added and represented as HAP. The emission factor for POM is calculated as the sum of the emission factors for all the individual species of POM.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 30	of	192 DR‐TP‐23	‐	HAP

### Flare flow [1] = 60 MMscf/day Heating Value [5] = 1,020 MMBtu/MMscf Operating Time [2] = 24 hrs/day [1] 360 MMscf/year Flare efficiency [7] = 98%

Average Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 53.02 kg/MMBtu 292,105 7,010,532 21,028

CH 4 

### 40 CFR 98 Subpart C [4] 1.00E-03 kg/MMBtu 5.51 132.22 0.40

N 2 

### O 40 C FR 98 Subpart C [4] 1.00E-04 kg/MMBtu 0.55 13.22 0.04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 292,392 7,017,407 21,048

[1]

[2] [3]

[4]

[5] [6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations

Boom Flare

Pollutant Emission Factor Basis Emission Factor 

## DR-TP-23

GHG Pollutants

Flare destruction efficiency assumed to be 98%. Representative Flare to be used for well completion activities. Information provided by Mr. Aaron Wade (Anadarko) on August 8, 2012. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Natural gas was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for Natural gas was used to calculate emissions. Based on AP-42 Section 1.4, Natural Gas Combustion, footnote (a) of Table 1.4-2, p. 1.4-6, 07/98. CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 31	of	192 DR‐TP‐23	‐	GHGEngine Rating [1] = 4,500 kW 6,035 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Number of Engines = 6

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

PM NSPS IIII [6] 2.47E-04 lb/HP-hr 8.93 214.29 21.43 PM 10 NSPS IIII [5],[6] 2.47E-04 lb/HP-hr 8.93 214.29 21.43 PM 2.5 NSPS IIII [5],[6] 2.47E-04 lb/HP-hr 8.93 214.29 21.43 NO x IMO Tier II [4] 9.7 g/kW-hr 577 13,841 1,384 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.41 9.75 0.97 CO AP-42 [6] 5.50E-03 lb/HP-hr 199.14 4,779 477.93 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 23.23 557.49 55.75

Pb EPA [7] 2.03E-07 lb/HP-hr 0.01 0.18 0.018 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 0.01 0.30 0.030

[1]

[2] [3]

[4]

[5] [6] [7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Main Propulsion Engines #1 through #6

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-ME-01 through DR-ME-06

Criteria Pollutants

Note: Potential to Emit is limited by proposed fuel consumption limit of 123 cubic meters/day. Refer to fuel based consumption factor sheet for details.

Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Operating time per engine has been conservatively assumed to be 24 hrs/day.

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the Engine Emission Report sent by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 3, 2012. The NO X emission comply with IMO Tier II limit and NSPS, Subpart IIII (40 CFR 60.4204(c)(2)(ii)).

Assumed PM=PM 10 =PM 2.5 The PM emission factor is obtained from NSPS Subpart IIII (40 CFR 60.4204(c)(4)). Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gasturbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 32	of	192 DR‐ME‐01	thr	DR‐ME‐06‐	CriteriaEngine Rating [1] = 4,500 kW 6,035 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [1] = ULSD Number of Engines = 6

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 6.39E-03 0.15 0.02

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 2.00E-03 0.05 4.79E-03 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 0.20 4.72 0.47 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 0.02 0.48 0.05 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 0.07 1.71 0.17 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 0.05 1.17 0.12 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 0.05 1.29 0.13 Naphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 0.03 0.79 0.08 Total VOC HAPs 0.40 9.57 0.96

[1]

[2] [3]

[4]

[5] 

## Anadarko Petroleum Corporation Emission Calculations

Main Propulsion Engines #1 through #6

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-ME-01 through DR-ME-06

HAP

Note: Potential to Emit is limited by proposed fuel consumption limit of 123 cubic meters/day. Refer to fuel based consumption factor sheet for details.

Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Operating time per engine has been conservatively assumed to be 24 hrs/day. Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 33	of	192 DR‐ME‐01	thr	DR‐ME‐06‐	HAPEngine Rating [1] = 4,500 kW 6,035 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD Number of Engines = 6

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 EPA [3] 73.96 kg/MMBtu 41,325.80 991,819.10 99,181.91 CH 4 EPA [4] 3.00E-03 kg/MMBtu 1.68 40.23 4.02 N 2 O EPA [4] 6.00E-04 kg/MMBtu 0.34 8.05 0.80 CO 2 e EPA [6] -- -- 41464.93 995158.25 99515.82

[1]

[2] [3]

[4]

[5] [6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations

Main Propulsion Engines #1 through #6

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-ME-01 through DR-ME-06

GHG Pollutants

Note: Potential to Emit is limited by proposed fuel consumption limit of 123 cubic meters/day. Refer to fuel based consumption factor sheet for details.

Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. CH 4 , CO 2 and N 2 O are included in the emissions of CO 2 equivalent (CO 2 e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Operating time per engine has been conservatively assumed to be 24 hrs/day. Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 34	of	192 DR‐ME‐01	thr	DR‐ME‐06‐	GHG

### Engine Rating [1] = 9,000 kW 12,069 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Number of Engines = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM NSPS IIII [6] 2.47E-04 lb/HP-hr 5.95 142.86 14.29 PM 10 

### NSPS IIII [5],[6] 2.47E-04 lb/HP-hr 5.95 142.86 14.29 PM 2.5 

### NSPS IIII [5],[6] 2.47E-04 lb/HP-hr 5.95 142.86 14.29 NO x 

### IMO Tier II [4] 9.69 g/kW-hr 384.53 9228.77 922.88 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.27 6.50 0.65 CO AP-42 [6] 5.50E-03 lb/HP-hr 132.76 3186.22 318.62 VOC AP-42 [6], [8] 6.42E-04 lb/HP-hr 15.49 371.66 37.17

Pb EPA [7] 2.03E-07 lb/HP-hr 0.005 0.12 0.012 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 0.008 0.20 0.020

[1]

[2] [3]

[4]

[5] [6] [7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Main Propulsion Engines #7 and #8

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-ME-07 and DR-ME-08

Criteria Pollutants

Note: Potential to Emit is limited by proposed fuel consumption limit of 123 cubic meters/day. Refer to fuel based consumption factor sheet for details.

Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Operating time per engine has been conservatively assumed to be 24 hrs/day.

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the Engine Emission Report sent by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 3, 2012. The NO X 

### emission comply with IMO Tier II limit and NSPS, Subpart IIII (40 CFR 60.4204(c)(2)(ii)).

Assumed PM=PM 10 

### =PM 2.5 

### The PM emission factor is obtained from NSPS Subpart IIII (40 CFR 60.4204(c)(4)). Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gasturbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 35	of	192 DR‐ME‐07	&	DR‐ME‐08‐	Criteria

### Engine Rating [1] = 9,000 kW 12,069 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [1] = ULSD Operating load [2] = 100% Number of Engines = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 4.26E-03 0.10 0.01

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.33E-03 0.03 3.20E-03 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 0.13 3.15 0.31 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 0.01 0.32 0.03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 0.05 1.14 0.11 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 0.03 0.78 0.08 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 0.04 0.86 0.09 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 0.02 0.53 0.05 Total VOC HAPs 0.27 6.38 0.64

[1]

[2] [3]

[4]

[5] Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Operating time per engine has been conservatively assumed to be 24 hrs/day. Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Main Propulsion Engines #7 and #8

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-ME-07 and DR-ME-08

HAP

Note: Potential to Emit is limited by proposed fuel consumption limit of 123 cubic meters/day. Refer to fuel based consumption factor sheet for details.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 36	of	192 DR‐ME‐07	&	DR‐ME‐08	‐	HAP

### Engine Rating [1] = 9,000 kW 12,069 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [1] = ULSD Operating load [2] = 100% Number of Engines = 2

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 73.96 kg/MMBtu 27550.53 661212.74 66121.27 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 1.12 26.82 2.68 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 0.22 5.36 0.54 CO 2 

### e EPA [6] -- -- 27643.28 663438.83 66343.88

[1]

[2] [3]

[4]

[5] [6] 

## Anadarko Petroleum Corporation Emission Calculations

Main Propulsion Engines #7 and #8

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-ME-07 and DR-ME-08

GHG Pollutants

Note: Potential to Emit is limited by proposed fuel consumption limit of 123 cubic meters/day. Refer to fuel based consumption factor sheet for details.

CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100- year Time Horizon). Operating time per engine has been conservatively assumed to be 24 hrs/day. Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 37	of	192 DR‐ME‐07	&	DR‐ME‐08	‐	GHGEngine Rating [1] = 28 kW 39 HP Operating Time [2] = 0.5 hr/day 100 hrs/yr Fuel Type [3] = ULSD Number of Engines = 1

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

PM 40 CFR 89.112, AP-42 [5],[8] 9.86E-04 lb/hp-hr 0.02 0.02 1.92E-03

PM 10 40 CFR 89.112, AP-42 [5],[8] 9.86E-04 lb/hp-hr 0.02 0.02 1.92E-03

PM 2.5 40 CFR 89.112, AP-42 [5],[8] 9.86E-04 lb/hp-hr 0.02 0.02 1.92E-03 NO x 40 CFR 89.112 [8] 0.012 lb/hp-hr 0.24 0.24 2.40E-02 SO 2 Fuel S Content [3] 1.12E-05 lb/hp-hr 2.19E-04 2.19E-04 2.19E-05 CO 40 CFR 89.112 [8] 9.04E-03 lb/hp-hr 0.18 0.18 1.76E-02 VOC AP-42 [4],[7] 2.51E-03 lb/hp-hr 0.05 0.05 4.90E-03

Pb EPA [6] 2.03E-07 lb/hp-hr 3.96E-06 3.96E-06 3.96E-07 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/hp-hr 6.83E-06 6.83E-06 6.83E-07

[1] [2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Emergency Air Compressor

Pollutant Emission Factor Basis Emission Factor

Emission factors are based on EPA Tier 2 Nonroad Compression-Ignition Engines -- Exhaust Emission Standards. All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. 

## DR-AC-01

Criteria Pollutants

Engine rating is obtained from the specification sheet for this equipment Operating time for this engine is conservatively assumed to be 0.5 hrs/day, 100.0 hr/year. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 and 2 wt.% of sulfur in the fuel is oxidized to H 2 SO 4 based on AP-42 Appendix A, table 3.4.1 footnote e and Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 = PM 10 = PM. Lead emission factor (2.9x10 -5 lb/MMBtu) is obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines is used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr is used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 38	of	192 DR‐AC‐01	‐	Criteria

### Engine Rating [1] 39 HP Operating Time [2] = 0.5 hr/day 100.0 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4],[5] 7.67E-04 lb/MMBtu 1.05E-04 1.05E-04 5.23E-06

Acrolein AP-42 [4],[5] 9.25E-05 lb/MMBtu 1.26E-05 1.26E-05 6.31E-07 Benzene AP-42 [4],[5] 9.33E-04 lb/MMBtu 1.27E-04 1.27E-04 6.37E-06 Formaldehyde AP-42 [4],[5] 1.18E-03 lb/MMBtu 1.61E-04 1.61E-04 8.05E-06 Toluene AP-42 [4],[5] 4.09E-04 lb/MMBtu 5.58E-05 5.58E-05 2.79E-06 Xylenes AP-42 [4],[5] 2.85E-04 lb/MMBtu 3.89E-05 3.89E-05 1.95E-06 1,3-Butadiene AP-42 [4],[5] 3.91E-05 lb/MMBtu 5.34E-06 5.34E-06 2.67E-07

Total PAH AP-42 [4],[5] 1.68E-04 lb/MMBtu 2.29E-05 2.29E-05 1.15E-06 N aphthalene AP-42 [4],[5] 8.48E-05 lb/MMBtu 1.16E-05 1.16E-05 5.79E-07 5.29E-04 5.29E-04 2.64E-05

[1] [2] [3] [4]

[5] 

## Anadarko Petroleum Corporation Emission Calculations

Emergency Air Compressor

Pollutant Emission Factor Basis Emission Factor

Engine rating is obtained from the specification sheet for this equipment Operating time for this engine is conservatively assumed to be 0.5 hrs/day, 100.0 hr/year. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Emission factors are based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr is used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## DR-AC-01

HAP

Total VOC HAPs

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 39	of	192 DR‐AC‐01	‐	HAP

### Engine Rating [1] 39 HP Operating Time [2] = 0.5 hrs/day 100 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions [7] 

### Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 22.26 22.26 1.11 CH 4 

### 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 9.03E-04 0.00 4.51E-05 N 2 

### O 40 CFR 98 Subpart C [5] 6.00E-04 kg/MMBtu 1.81E-04 0.00 9.03E-06
CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 22.33 22.33 1.12

[1] [2] [3] [4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations

Emergency Air Compressor

An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr is used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## DR-AC-01

GHG Pollutants

Engine rating is obtained from the specification sheet for this equipment Operating time for this engine is conservatively assumed to be 0.5 hrs/day, 100.0 hr/year. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Emission factor is based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 is used to calculate Emission factors are based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) is used to calculate emissions. Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 40	of	192 DR‐AC‐01	‐	GHGEngine Rating [1],[4] = 1,900 kW 2,547 HP Operating Time [2] = 2 hrs/day 100 hrs/yr Fuel Type [1] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [6],[7] 0.43 g/kW-hr 1.78 3.57 0.089 PM 10 AP-42 [6],[7] 0.24 g/kW-hr 1.02 2.05 0.051 PM 2.5 AP-42 [6],[7] 0.24 g/kW-hr 0.99 1.98 0.050 NO x IMO Tier 2 [4] 6.40 g/kW-hr 26.81 53.62 1.34 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 2.86E-02 5.71E-02 1.43E-03

CO Maufacturer Specification [8] 0.38 g/kW-hr 1.59 3.18 0.08 VOC AP-42 [7] 7.50 g/kW-hr 31.42 62.83 1.57

Pb EPA [5] 2.03E-07 lb/HP-hr 5.17E-04 1.03E-03 2.59E-05 H 2 SO 4 Fuel S Conten t [3] 3.50E-07 lb/HP-hr 8.92E-04 1.78E-03 4.46E-05

[1]

[2] [3]

[4] [5]

[6]

[7]
[8] As per manufacturer's specification sheet. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). PM 10 and PM 2.5 emission factors obtained by applying the ratio of PM/PM 10 and PM/PM 2.5 from AP-42 Chapter 3, Table 3.4-1 and Table 3.4-2 on EPA Tier II PM emission factor. Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gasturbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Engine specifications sheet provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on March 11, 2013.

Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory ImpactAnalysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Operating time for this engine has been assumed to be 1 hrs/day and 100 hrs/year.

As per the specification sheet, the engine is IMO Tier 2 compliant for NOx Emissions. 

## Anadarko Petroleum Corporation Emission Calculations

Emergency Generator

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-GE-01

Criteria Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 41	of	192 DR‐GE‐01	‐	CriteriaEngine Rating [1] = 1,900.0 kW 2,547.0 HP Operating Time [2] = 2 hrs/day 100 hrs/yr Fuel Type [1] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 4.49E-04 8.99E-04 2.25E-05

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.40E-04 2.81E-04 7.02E-06 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 1.38E-02 2.77E-02 6.92E-04 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 1.41E-03 2.81E-03 7.03E-05 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 5.01E-03 1.00E-02 2.50E-04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 3.44E-03 6.88E-03 1.72E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 3.78E-03 7.56E-03 1.89E-04 Naphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 2.32E-03 4.64E-03 1.16E-04 Total VOC HAPs 2.81E-02 5.61E-02 1.40E-03

[1]

[2] [3]

[4]

[5] 

## Anadarko Petroleum Corporation Emission Calculations

Emergency Generator

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-GE-01

HAP Pollutants

Engine specifications sheet provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on March 11, 2013.

Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Operating time for this engine has been assumed to be 2 hrs/day and 100 hrs/year.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 42	of	192 DR‐GE‐01	‐	HAPEngine Rating [1] = 1,900.0 kW 2,547.0 HP Operating Time [2] = 2 hrs/day 100 hrs/yr Fuel Type [1] = ULSD

Average Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 EPA [3] 73.96 kg/MMBtu 2907.08 5814.17 145.35 CH 4 EPA [4] 3.00E-03 kg/MMBtu 0.12 0.24 5.90E-03 N 2 O EPA [4] 6.00E-04 kg/MMBtu 0.02 0.05 1.18E-03 CO 2 e EPA [6] -- -- 2916.87 5833.74 145.84

[1]

[2] [3]

[4]

[5] [6] Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations

Emergency Generator

Emission Factor Pollutant 

### Emission Factor Basis

Engine specifications sheet provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on March 11, 2013.

Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 , CO 2 and N 2 Oare included in the emissions of CO 2 equivalent (CO 2 e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Operating time for this engine has been assumed to be 2 hrs/day and 100 hrs/year. 

## DR-GE-01

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 43	of	192 DR‐GE‐01		‐	GHG

### Engine Rating [1] = 31 kW 41 HP Operating Time [2] = 1.0 hrs/day 100 hrs/yr Fuel Type [1] = ULSD No of Engines [8] = 6

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.54 0.54 0.03 PM 10 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.54 0.54 0.03 PM 2.5 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.54 0.54 0.03 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 7.63 7.63 0.38 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 2.76E-03 2.76E-03 1.38E-04 CO AP-42 [5] 6.68E-03 lb/HP-hr 1.64 1.64 0.08 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.62 0.62 0.03

Pb EPA [6] 2.03E-07 lb/HP-hr 4.99E-05 4.99E-05 2.50E-06 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 8.62E-05 8.62E-05 4.31E-06

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Life Boat Engine #1 through #6

Emission Factor Pollutant 

### Emission Factor Basis

Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. 

## DR-LB-01 through DR-LB-06

Criteria Pollutants

Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on March 11, 2013. Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Operating time per engine has been assumed to be 1 hr/day and 100 hrs/year.

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM2.5 = PM10 = PM.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 44	of	192 DR‐LB‐01	thr	DR‐LB‐06‐	Criteria

### Engine Rating [1],[5] = 31 kW 41 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [1] = ULSD No of Engines [5] = 6

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 1.32E-03 1.32E-03 6.60E-05

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 1.59E-04 1.59E-04 7.96E-06 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 1.61E-03 1.61E-03 8.03E-05 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 2.03E-03 2.03E-03 1.02E-04 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 7.04E-04 7.04E-04 3.52E-05 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 4.91E-04 4.91E-04 2.45E-05 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 6.73E-05 6.73E-05 3.37E-06

Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 2.89E-04 2.89E-04 1.45E-05 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 1.46E-04 1.46E-04 7.30E-06 Total VOC HAPs 6.67E-03 6.67E-03 3.34E-04

[1]

[2] [3]

[4] [5] Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on March 11, 2013. Operating time per engine has been assumed to be 1 hr/day and 100 hrs/year. Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations

Life Boat Engine #1 through #6

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-LB-01 through DR-LB-06

HAP

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 45	of	192 DR‐LB‐01	thr	DR‐LB‐06‐	HAPEngine Rating [1],[7] = 31 kW 41 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [1] = ULSD No of Engines [7] = 6

Average Hourly Emissions Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 EPA [3] 7.40E+01 kg/MMBtu 280.78 280.78 14.04 CH 4 EPA [4] 3.00E-03 kg/MMBtu 1.14E-02 1.14E-02 5.69E-04 N 2 O EPA [4] 6.00E-04 kg/MMBtu 2.28E-03 2.28E-03 1.14E-04 CO 2 e EPA [6] -- -- 281.72 281.72 14.09

[1]

[2] [3]

[4]

[5] [6]

[7] Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on March 11, 2013. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations

Life Boat Engine #1 through #6

Emission Factor Pollutant 

### Emission Factor Basis

Engine specifications provided in a needs list spreadsheet by Ms. Kathryn Maness (Anadarko) to Mr. Raghu Soule (Trinity) via email on July 2, 2012.

Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 , CO 2 and N 2 Oare included in the emissions of CO 2 equivalent (CO 2 e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Operating time per engine has been assumed to be 1 hr/day and 100 hrs/year. 

## DR-LB-01 through DR-LB-06

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 46	of	192 DR‐LB‐01	thr	DR‐LB‐06‐	GHGEngine Rating [1],[4] = 41 kW 55 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [1] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

PM 40 CFR 94.8(a)(2)(i), AP42 [4],[5] 4.00E-01 g/kw-hr 0.04 0.04 1.81E-03

PM 10 40 CFR 94.8(a)(2)(i), AP42 [4],[5] 4.00E-01 g/kw-hr 0.04 0.04 1.81E-03

PM 2.5 40 CFR 94.8(a)(2)(i), AP42 [4],[5] 4.00E-01 g/kw-hr 0.04 0.04 1.81E-03

NO x 40 CFR 94.8(a)(2)(i), AP42 [5] 7.50E+00 g/kw-hr 0.68 0.68 0.03 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 6.17E-04 6.17E-04 3.08E-05 CO 40 CFR 94.8(a)(2)(i) [5] 5.00E+00 g/kw-hr 0.45 0.45 0.02 VOC AP-42 [7],[8] 2.51E-03 lb/HP-hr 0.14 0.14 0.01

Pb EPA [6] 2.03E-07 lb/HP-hr 1.12E-05 1.12E-05 5.58E-07 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 1.93E-05 1.93E-05 9.64E-07

[1]

[2] [3]

[4]

[5] [6]

[7]

[8] All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Engine specifications provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on August 7, 2013.

Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 and 2 wt.% of sulfur in the fuel is oxidized to H 2 SO 4 based on AP-42 Appendix A, table 3.4.1 footnote e and Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Operating time for this engine has been assumed to be 1 hr/day and 100 hrs/year.

Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM2.5 = PM10 = PM.
Emission factors are based on EPA Marine Tier 2 Compression Ignition Engines - Exhaust Emission Standards. Lead emission factor (2.9x10 -5 lb/MMBtu) is obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines is used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specifi c fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr is used to convert from lb/MMBtu to lb/hp-hr. 

## Anadarko Petroleum Corporation Emission Calculations

Fast Rescue Craft

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-FR-01

Criteria Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 47	of	192 DR‐FR‐01	‐	Criteria

### Engine Rating [1] = 41 kW 55 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [1] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 2.95E-04 2.95E-04 1.48E-05

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 3.56E-05 3.56E-05 1.78E-06 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 3.59E-04 3.59E-04 1.80E-05 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 4.54E-04 4.54E-04 2.27E-05 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 1.57E-04 1.57E-04 7.87E-06 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 1.10E-04 1.10E-04 5.49E-06 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 1.51E-05 1.51E-05 7.53E-07

Total PAH AP-43 [3],[4] 1.68E-04 lb/MMBtu 6.47E-05 6.47E-05 3.23E-06 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 3.26E-05 3.26E-05 1.63E-06 Total VOC HAPs 1.49E-03 1.49E-03 7.46E-05

[1]

[2] [3]

[4] An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Operating time for this engine has been assumed to be 1 hr/day and 100 hrs/year. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on August 7, 2013.

Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Fast Rescue Craft

Emission Factor Pollutant 

### Emission Factor Basis 

## DR-FR-01

HAP

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 48	of	192 DR‐FR‐01	‐	HAPEngine Rating [1] = 41 kW 55 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [1] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 EPA [3] 73.96 kg/MMBtu 62.78 62.78 3.14 CH 4 EPA [4] 3.00E-03 kg/MMBtu 2.55E-03 2.55E-03 1.27E-04 N 2 O EPA [4] 6.00E-04 kg/MMBtu 5.09E-04 5.09E-04 2.55E-05 CO 2 e EPA [6] -- -- 62.99 62.99 3.15

[1]

[2] [3]

[4]

[5] [6] Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations

Fast Rescue Craft

Emission Factor Pollutant 

### Emission Factor Basis

Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on August 7, 2013.

Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 , CO 2 and N 2 Oare included in the emissions of CO 2 equivalent (CO 2 e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Operating time for this engine has been assumed to be 1 hr/day and 100 hrs/year. 

## DR-FR-01

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 49	of	192 DR‐FR‐01	‐	GHG

### Dust Collector Emission Calculation - Cement and Mud Mixing Operations

Value Unit Value Unit lb/hr lb/day tpy DR-DC-01 4,800 0.15 3.56 0.36 DR-DC-02 4,800 0.15 3.56 0.36 DR-DC-03 4,800 0.15 3.56 0.36

0.45 10.69 1.07

[1] [2] [3] 

## Anadarko Petroleum Corporation

Dust Collector #1 through #3

TOTAL

AP-42 Table 11.12-2 (Controlled EF) for Cement Mixing Maximum material transfer rate provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on August 19, 20 13. lbs/ton of material loaded 0.00099 ton/hr 150

Dust collectors may be used only during periods of cement and/or mud mixing. However, emissions are calculated by conservative ly assuming continuous operations. 

### DR-DC-01 through DR-DC-03

Emission Unit PM/ PM10 / PM2.5 Emission Factor [1] Maximum Cement/Mud Loading Rate [1],[2] Operating Time (hr/year) [3] Estimated

Potential Emissions

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 50	of	192 DR‐DC‐01	thru	DR‐DC‐03Operating Data: [1]

Operating Hours = 4800 hrs/yr 200 days/year 24 hrs/day

Type of Welding Rod Amount (lbs/day) Amount (lbs/year) E308, E310, E316, E6010,

E6011, E7018, E7028, E11018 or equivalent 80 16,000

Total 80 16,000

Total PM/PM 10 /PM 2.5 AP-42 [2], [4] 57 lb/ 10 3 lb 0.38 4.56 912 0.46 Chromium AP-42 [3] 25.3 10 -1 lb/ 10 3 lb 1.69E-02 0.20 40.48 0.02 Chromium VI AP-42 [3] 18.8 10 -1 lb/ 10 3 lb 1.25E-02 0.15 30.08 0.02 Cobalt AP-42 [3] 0.01 10 -1 lb/ 10 3 lb 6.67E-06 0.00 0.02 0.00 Manganese AP-42 [3] 22.0 10 -1 lb/ 10 3 lb 1.47E-02 0.18 35.20 0.02 Pb AP-42 [3] 1.62 10 -1 lb/ 10 3 lb 1.08E-03 0.01 2.59 1.30E-03 Nickel AP-42 [3] 12.5 10 -1 lb/ 10 3 lb 8.33E-03 0.10 20.00 0.01

[1] Data provided by Sara Carlson (Anadarko) to Rahul Pendse (Trinity) via email on March 11, 2013. [2] Emission factors based on AP-42 Chapter 12 Section 12.19 Electric Arc Welding (1/95), Table 12.19-1 - PM-10 EMISSION FACTORS FOR WELDING OPERATIONS, for SMAW, page 12.19-4. [3] Emission factors based on AP-42 Chapter 12 Section 12.19 Electric Arc Welding (1/95), Table 12.19-2 - HAP EMISSION FACTORS FOR WELDING OPERATIONS, for SMAW, page 12.19-6. [4] PM10 emissions are conservatively assumed equal to PM2.5 and total PM emissions (i.e., PM = PM10 = PM2.5) 

### Welding Operations

Max. Daily Emissions (lb/day) 

### Anadarko Petroleum Corporation Emission Calculations

Pollutant Emission Factor Basis Unit Max. Hourly Emissions

(lb/hr) Annual Emissions

(lb/yr) Annual Emissions

(tpy) 

### DR-WO-01

Emission Factors

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 51	of	192 DR‐WO‐01Operating Data [1] Average Thinner Usage = 10 gallons/day Average Primer Usage = 40 gallons/day Spray Transfer Efficiency 4 = 30% Fall out Factor 5 = 98.56%
VOC PTE Calculations- Paint Coatings, and Thinners (or equivalent)

Product Code Name 1 Product Description Code 1 Density 1 (lb/gal) VOC Content 1 (wt %) Maximum Hourly Usage 2 (gal/hr) Maximum Daily Usage 2

(gal/day) Annual Usage 2 (gal/year) Maximum Hourly Emissions

(lb/hr) Maximum Daily Emissions (lb/day) Annual Emissions

(tpy)

Jotun Thinner No. 17 Paint Thinne r MM00000553 7.18 100.0% 0.4 10 1300 2.99 71.77 4.67
Jotun Thinner No. 23 Thinner MM00000555 7.26 100% 0.4 10 1300 3.03 72.60 4.72
Amercoat 10 - Thinner Thinner AT10/05 7.01 100.0% 0.4 10 1300 2.92 70.10 4.56

Amercoat 65 Thinner Paint Thinner AT765/05 7.26 100.0% 0.4 10 1300 3.03 72.60 4.72 Worst Case Thinner or Equivalent AT765/05 7.26 1 0.4 10 1300 3.03 72.6 4.72

Hardtop XP - Comp A Prime r 3140 11.68 27.7% 1.3 32 4160 4.32 103.57 6.73 Hardtop XP - Comp B Prime r 3240 9.43 96.3% 0.3 8 1040 3.03 72.65 4.72 Hardtop Flexi - Comp A 8 Primer MM00001531 9.76 30.8% 1.3 32 4160 4.01 96.32 6.26 Hardtop Flexi - Comp B Primer MM00001533 9.01 24.8% 0.3 8 1040 0.74 17.88 1.16 Resist 78 AV - Comp. A Primer MM00001151 9.18 100.0% 1.7 40 5200 15.30 367.20 23.87 Jotamastic 80 - Comp A Prime r 5580 13.35 48.0% 1.7 40 5200 10.68 256.38 16.66

Dimetcoat 9- Liquid Base D19-A/05 8.51 60.7% 1.7 40 5200 8.61 206.62 13.43 Dimetcoat 9- Powder Hardene r D19-P 59.50 0.0% 1.7 40 5200 0.00 0.00 0.00 Jotamastic 80 - Std Comp B Prime r 5660 8.68 49.0% 1.7 40 5200 7.09 170.12 11.06 Worst Case Paint or Equivalent Prime r MM00001151 9.18 1 1.7 40 5200 15.3 367.2 23.868 Worst Case VOC [6] 18.33 439.80 28.59

PM/PM 10 /PM 2.5 Emissions

Product Product Description Application Method Density Based on Mixing Ratio (lb/gal) Solids Content 3

(%) Maximum Hourly Usage 2 (gal/hr) Maximum Daily Usage 2

(gal/day) Annual Usage 2 (gal/year) Maximum Hourly Emissions

(lb/hr) Maximum Daily Emissions (lb/day) Annual Emissions

(tpy)

Any Paint Thinner Paint Thinne r spray gun 0.0% 0.4 10 1300 0.00 0.00 0.00 Hardtop XP - Comp A Prime r spray gun 11.68 72.3% 1.7 30 3900 0.14 2.55 0.17 Hardtop XP - Comp B Prime r spray gun 9.43 3.7% 1.7 10 1300 0.01 0.04 0.00 Jotamastic 80 - Comp A Prime r spray gun 13.35 52.0% 1.3 30 3900 0.09 2.10 0.14 Jotamastic 80 - Std Comp B Prime r spray gun 8.68 51.0% 1.7 30 3900 0.07 1.34 0.09 Barrier AV Prime r spray gun 18.36 85.3% 1.7 40 5200 0.26 6.31 0.41 Jotun Anti-skid [7] Coating spray gun 34.22 100.0% 0.4 10 1300 0.14 3.45 0.22 Worst Case PM/PM 10 /PM 2.5 [8] 0.26 6.31 0.41

[1]

[2] [3] Solids content is assumed to be 100% less VOC weight content.
[4] [5] Fax Transmittal Correspondence from Ms. Alyssa Aston (TCEQ) to Mr. Glen Muenchow (Aggregate Plant Production Company) regard ing Permit Number: 48092. [6] Total emissions based on the sum of the worst-case primer (Hardtop XP) and thinner (Jotun Thinner No.17) components. [7] Assuming all particles are alumina, and therefore specific weight equals to 4.1. Average usage assumed to be the same as thi nner, 5 gallons per hour. [8] Total emissions based on the worst-case primer (Jotamastic) and Jotun Anti Skid mixture. Spray transfer efficiency obtained from Phone converstaion between Mr. Dhesikan Venkatesan (Trinity) and manufacturer. As an al ternate scenario Air Assited spray gun with 50% control efficiency could be utilized. Anadarko Petroleum Corporation Emission Calculations

Painting Operations

Data provided in an email by Ms. Sara Carlson (Anadarko) on 3/11/2013 and 07/30/2013. The VOC content presented here represent the average content for each component on the MSDS. Any equivalent paint, thinner, primer will be utilized during painting operations Maximum daily usage determined based on email from Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) on 3/11/2013 and 0 7/30/2013. DR-PO-01

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 52	of	192 DR‐PO‐01	‐	CriteriaOperating Data [1] Maximum Thinner Usage = 10 gallons/day Maximum Primer Usage = 40 gallons/day
HAP PTE Calculations- Paint Coatings, and Thinners

Product Description Pollutant Weight % 3 Highest Emitting HAP by Product VOC Density
3 (lb/gal) Maximum Hourly Usage 2 (gal/hr) Maximum Daily Usage 2 (gal/day) Annual Usage 2 (gal/year) Maximum Hourly Emissions

(lb/hr) Maximum Daily Emissions (lb/day) Annual Emissions

(tpy) Xylenes 80.00% Amercoat 65 - Thinner 7.26 0.4 10 1300 2.34 56.08 3.78 Ethylbenzene 20.00% Amercoat 65 - Thinner 7.26 0.4 10 1300 0.58 14.02 0.94

Tolene 0.60% Amercoat 65 - Thinner 7.26 0.4 10 1300 0.02 0.42 0.03 Hexone 40.00% Amercoat 10 - Thinner 7.01 0.4 10 1300 1.21 29.04 1.82 Xylenes 25.00% Hardtop Flexi - Comp A 3.24 1.3 32 4160 1.08 25.89 1.68 Ethylbenzene 10.00% Hardtop Flexi - Comp A 9.76 1.3 32 4160 1.30 31.23 2.03 Naphtalene 1.00% Hardtop Flexi - Comp B 9.01 0.3 8 1040 0.03 0.72 0.05hexamethylenedi-isocyanate 1.00% Hardtop XP - Comp B 9.43 0.3 8.0 1040.0 0.03 0.75 0.05

Cumene 0.14% Amercoat 235-cure 8.01 1.7 40 5200 0.02 0.45 0.03 Maximum VOC HAP s [4] 6.61 158.61 10.41

[1] [2] [3] Data provided in emails by Ms. Sara Carlson (Anadarko) on 03/11/2013, and 07/30/2013. Primer usage is based on the mixing ratio provided in the technical data sheet. Based on MSDS provided in emails by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) on 6/24/2013. Average wt% have be en used for each VOC HAP. Anadarko Petroleum Corporation Emission Calculations

Painting Operations DR-PO-01

Thinner

Primer/Base/Cure

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 53	of	192 DR‐PO‐01	‐	HAP198 lb/day 200 Therefore, THC emissions (lb/yr) = 39,682 lb/yr

Component Volume % Composition [1] Molecular weight Vol % * M.W. Weight % Composition Hourly Emissions Annual Emissions (lb/lb-mol) (lb/hr) (tpy) Methane 83.85% 16.042 13.45 65% 5.38 12.92 Ethane 5.41% 30.07 1.63 8% 0.65 1.56 Propane 6.12% 44.1 2.70 13% 1.08 2.59 Butane 3.21% 58.12 1.87 9% 0.75 1.79 Pentane 1.40% 72.15 1.01 5% 0.40 0.97 20.65 Total VOC Emissions [3] = 2.23 5.36 Total CO2e Emissions [4] = 113.07 271.37

[1]

[2] Emissions have been calculated assuming a continuous operation. [3] VOC emissions include propane, butane, and pentane emissions. [4] Wilson, Darcy, Richard Billings, Regi Oommen, and Roger Chang; Eastern Research Group, Inc.; Year 2005 Gulfwide Emission Inventory Study; US Department of Interior, Minerals Management Service; Gulf of Mexico OCS Region, New Orleans, December 2007.

CO 2 e emissions have been calculated based on methane emissions and a methane global warming potential of 21. Number of drilling days [2] = 

## Anadarko Petroleum Corporation Emission Calculations

Mud Degasser Vent

Drilling mud is used in the drilling process to cool and lubricate the drill bit. When the drilling mud returns to the surface, it contains entrained hydrocarbons from the well. On reaching the surface, offgasing occurs, leading to VOC emissions.

THC emission factor for synthetic-based muds [1] = 

## DR-VG-01

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 54	of	192 DR‐VG‐01Maximum w/ Contingency (days per year) : 200 day s 24 hr/day Primary Diesel Engines: 8

Emission Calculations [1]
Emission Factor [3] Total Organic Compound Total Organic Compound Total Organic Compound (kg/hr/source) lbs/hr lbs/day tons/project Valves 152 8.40E-06 2.81E-03 0.07 0.01 Pump Seals (one per engine) 16 NA 0 0 0 Others 0 3.20E-05 0 0 0 Connectors 484 7.50E-06 8.00E-03 0.19 0.02 Flanges 0 3.90E-07 0 0 0 Open-ended lines 0 1.40E-04 0 0 0 0.01 0.26 0.03

Notes: Total TOC [4] - Heavy Oil Streams

[1] Component counts are conservatively estimated using engineering judgement. [2] Emission factors are obtained from the EPA-453/R-95-017, November 1995 "Protocol for Equipment Leak Emission Estimates" Tab le 2-4. [3] Emissions are represented by using "Heavy Oil" factors for diesel. Distillate fuel oil No. 2 (diesel)'s Vapor Pressure = 0.012 Pva (psi)@ 80 °F, Crude oil RVP 5 = 4.0 Pva (psi)@ 80 °F. [4] It is assumed that all total organic compounds (TOCs) are VOCs. 

### Anadarko Petroleum Corporation
Emission Calculations
Fugitive Emissions From Diesel Fuel Lines EPN: DR-FE-01

Component Type- Heavy Oil Streams [2] Number

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 55	of	192 DR‐FE‐01

### Engine Rating [1] = 1,656 kW 2,250 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD N umber of Engines = 2 Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 3.15 75.60 7.56 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 1.80 43.32 4.33 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 1.75 42.03 4.20 NO x 

### AP-42 [4] 2.40E-02 lb/HP-hr 108.00 2592.00 259.20 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.05 1.21 0.12 CO AP-42 [4] 5.50E-03 lb/HP-hr 24.75 594.00 59.40 VOC AP-42 [4],[7] 6.42E-04 lb/HP-hr 2.89 69.29 6.93

Pb EPA [6] 2.03E-07 lb/HP-hr 9.14E-04 2.19E-02 2.19E-03 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 1.58E-03 3.78E-02 3.78E-03

[1]

[2] [3]

[4]

[5]

[6]

[7] Pollutant 

### Emission Factor Basis Emission Factor

Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake

specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. Operating time for each engine has been conservatively assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). PM 10 

### and PM 2.5 

### emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 

### . Total particulate emissions is the sum of filterable and condensable particulate emissions. 

## Criteria Pollutants Anadarko Petroleum Corporation Emission Calculations

WE Vessel Main Engine #1 and #2 WE-ME-01 and WE-ME-02

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 56	of	192 WE‐ME‐01	and	WE‐ME‐02	‐Criteria

### Engine Rating [1] = 1,656 kW 2,250 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [1] = ULSD N umber of Engines = 2 Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 7.94E-04 1.91E-02 1.91E-03

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 2.48E-04 5.96E-03 5.96E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 2.44E-02 0.59 0.06 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 2.49E-03 0.06 0.01 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 8.85E-03 0.21 0.02 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 6.08E-03 0.15 0.01 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 6.68E-03 0.16 0.02 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 4.10E-03 0.10 0.01 Total VOC HAPs 0.05 1.29 0.13

[1]

[2] [3]

[4]

[5] 

## WE Vessel Main Engine #1 and #2

Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. Operating time for each engine has been conservatively assumed to be 24 hrs/day. Pollutant 

### Emission Factor Basis Emission Factor 

## Anadarko Petroleum Corporation Emission Calculations

Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## WE-ME-01 and WE-ME-02

HAP

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 57	of	192 WE‐ME‐01	and	WE‐ME‐02	‐	HAP

### Engine Rating [1] = 1,656 kW 2,250 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [1] = ULSD N umber of Engines = 2 Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 5,136.19 123,268.59 12,326.86 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 2.08E-01 5.00 0.50 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 0.04 1.00 0.10 CO 2 

### e EPA [6] -- -- 5153.48 123683.60 12368.36

[1]

[2] [3]

[4]

[5] [6] CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

WE Vessel Main Engine #1 and #2

Pollutant 

### Emission Factor Basis Emission Factor

Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. Operating time for each engine has been conservatively assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## WE-ME-01 and WE-ME-02

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 58	of	192 WE‐ME‐01	and	WE‐ME‐02	‐	GHG

### Engine Rating [1] = 1,055 kW 1,468 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD N umber of Engines = 2
Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 2.06 49.32 4.93 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 1.18 28.26 2.83 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 1.14 27.42 2.74 NO x 

### AP-42 [4] 2.40E-02 lb/HP-hr 70.46 1691.14 169.11 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.03 0.79 7.90E-02 CO AP-42 [4] 5.50E-03 lb/HP-hr 16.15 387.55 38.76 VOC AP-42 [4],[7] 6.42E-04 lb/HP-hr 1.88 45.21 4.52

Pb EPA [6] 2.03E-07 lb/HP-hr 5.96E-04 1.43E-02 1.43E-03 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 1.03E-03 2.47E-02 2.47E-03

[1]

[2] [3]

[4]

[5]

[6]

[7] Pollutant 

### Emission Factor Basis Emission Factor

Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-firedgas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. Operating time for each engine has been conservatively assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996).
PM 10 

### and PM 2.5 

### emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 

### . Total particulate emissions is the sum of filterable and condensable particulate emissions. 

## Criteria Pollutants Anadarko Petroleum Corporation Emission Calculations

WE Vessel Aux Engine #1 and #2 WE-AE-01 and WE-AE-02

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 59	of	192 WE‐AE‐01	and	WE‐AE‐02‐	Criteria

### Engine Rating [1] = 1,055 kW 1,468 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [1] = ULSD N umber of Engines = 2 Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 5.18E-04 1.24E-02 1.24E-03

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.62E-04 3.89E-03 3.89E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 1.59E-02 3.83E-01 3.83E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 1.62E-03 3.89E-02 3.89E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 5.78E-03 1.39E-01 1.39E-02 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 3.97E-03 9.52E-02 9.52E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 4.36E-03 1.05E-01 1.05E-02 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 2.67E-03 6.41E-02 6.41E-03 Total VOC HAPs 0.04 0.84 0.08

[1]

[2] [3]

[4]

[5] 

## WE Vessel Aux Engine #1 and #2

Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. Operating time for each engine has been conservatively assumed to be 24 hrs/day. Pollutant 

### Emission Factor Basis Emission Factor 

## Anadarko Petroleum Corporation Emission Calculations

Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## WE-AE-01 and WE-AE-02

HAP

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 60	of	192 WE‐AE‐01	and	WE‐AE‐02	‐	HAPEngine Rating [1] = 1,055 kW 1,468 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [1] = ULSD Number of Engines = 2

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 EPA [3] 73.96 kg/MMBtu 3351.08 80425.91 8042.59 CH 4 EPA [4] 3.00E-03 kg/MMBtu 0.14 3.26 0.33 N 2 O EPA [4] 6.00E-04 kg/MMBtu 0.03 0.65 0.07 CO 2 e EPA [6] -- -- 3362.36 80696.68 8069.67

[1]

[2] [3]

[4]

[5] [6] CH 4 , CO 2 and N 2 O are included in the emissions of CO 2 equivalent (CO 2 e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

WE Vessel Aux Engine #1 and #2

Pollutant 

### Emission Factor Basis Emission Factor

Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. Operating time for each engine has been conservatively assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## WE-AE-01 and WE-AE-02

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 61	of	192 WE‐AE‐01	and	WE‐AE‐02	‐	GHGEngine Rating [1] = 200 kW 272 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.60 14.36 1.44 PM 10 AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.60 14.36 1.44 PM 2.5 AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.60 14.36 1.44 NO x AP-42 [5] 3.10E-02 lb/HP-hr 8.43 202.37 20.24 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 3.05E-03 7.32E-02 7.32E-03 CO AP-42 [5] 6.68E-03 lb/HP-hr 1.82 43.61 4.36 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.68 16.40 1.64

Pb EPA [6] 2.03E-07 lb/HP-hr 5.52E-05 1.33E-03 1.33E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 9.53E-05 2.29E-03 2.29E-04

[1]

[2] [3]

[4]

[5]

[6]

[7] Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. Operating time for this engine has been conservatively assumed to be 24 hrs/day. Pollutant Emission Factor Basis Emission Factor 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-01 WE Vessel Emergency Generator Engine No. 1 Criteria Pollutants

Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 = PM 10 = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gasturbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 62	of	192 WE‐GE‐01	‐	Criteria

### Engine Rating [1] = 200 kW 272 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 1.46E-03 3.50E-02 3.50E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 1.76E-04 4.23E-03 4.23E-04 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 1.78E-03 0.04 4.26E-03 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 2.25E-03 0.05 5.39E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 7.79E-04 0.02 1.87E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 5.43E-04 0.01 1.30E-03 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 3.20E-04 7.68E-03 7.68E-04 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 7.44E-05 1.79E-03 1.79E-04 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 1.61E-04 3.88E-03 3.88E-04 Total VOC HAPs 7.38E-03 0.18 0.02

[1]

[2] [3]

[4]

[5] 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-01 WE Vessel Emergency Generator Engine No. 1 HAP Pollutants

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 63	of	192 WE‐GE‐01	‐	HAP

### Engine Rating [1] = 200 kW 272 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 73.96 kg/MMBtu 310 7,451 745 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 1.26E-02 0.30 3.02E-02 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 2.52E-03 0.06 6.04E-03 CO 2 

### e EPA [6] -- -- 311 7,476 748

[1]

[2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-01 WE Vessel Emergency Generator Engine No. 1 GHG Pollutants

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 64	of	192 WE‐GE‐01	‐	GHG

### Engine Rating [1] = 158 kW 212 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.47 11.19 1.12 PM 10 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.47 11.19 1.12 PM 2.5 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.47 11.19 1.12 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 6.57 157.64 15.76 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 2.38E-03 5.70E-02 5.70E-03 CO AP-42 [5] 6.68E-03 lb/HP-hr 1.42 33.97 3.40 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.53 12.77 1.28

Pb EPA [6] 2.03E-07 lb/HP-hr 4.30E-05 1.03E-03 1.03E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 7.42E-05 1.78E-03 1.78E-04

[1]

[2] [3]

[4]

[5]

[6]

[7] Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-02 WE Vessel Emergency Generator Engine No. 2 Criteria Pollutants

Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. Anaverage brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hphr. All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 65	of	192 WE‐GE‐02	‐	Criteria

### Engine Rating [1] = 158 kW 212 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 1.14E-03 2.73E-02 2.73E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 1.37E-04 3.29E-03 3.29E-04 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 1.38E-03 3.32E-02 3.32E-03 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 1.75E-03 4.20E-02 4.20E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 6.07E-04 1.46E-02 1.46E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 4.23E-04 1.01E-02 1.01E-03 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 2.49E-04 5.98E-03 5.98E-04 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 5.80E-05 1.39E-03 1.39E-04 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 1.26E-04 3.02E-03 3.02E-04 Total VOC HAPs 5.75E-03 0.14 0.01

[1]

[2] [3]

[4]

[5] 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-02 WE Vessel Emergency Generator Engine No. 2 HAP

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 66	of	192 WE‐GE‐02	‐	HAP

### Engine Rating [1] = 158 kW 212 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 242 5,804 580 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 9.81E-03 2.35E-01 2.35E-02 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 1.96E-03 4.71E-02 4.71E-03 CO 2 

### e EPA [6] -- -- 243 5,824 582

[1]

[2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-02 WE Vessel Emergency Generator Engine No. 2 GHG Pollutants

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 67	of	192 WE‐GE‐02	‐	GHG

### Engine Rating [1] = 147 kW 200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.44 10.56 1.06 PM 10 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.44 10.56 1.06 PM 2.5 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.44 10.56 1.06 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 6.20 148.80 14.88 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 2.24E-03 5.38E-02 5.38E-03 CO AP-42 [5] 6.68E-03 lb/HP-hr 1.34 32.06 3.21 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.50 12.06 1.21

Pb EPA [6] 2.03E-07 lb/HP-hr 4.06E-05 9.74E-04 9.74E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 7.01E-05 1.68E-03 1.68E-04

[1]

[2] [3]

[4]

[5]

[6]

[7] Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013. 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-03 WE Vessel Emergency Generator Engine No. 3 Criteria Pollutants

Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 68	of	192 WE‐GE‐03	‐	Criteria

### Engine Rating [1] = 147 kW 200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 1.07E-03 2.58E-02 2.58E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 1.30E-04 3.11E-03 3.11E-04 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 1.31E-03 3.13E-02 3.13E-03 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 1.65E-03 3.96E-02 3.96E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 5.73E-04 1.37E-02 1.37E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 3.99E-04 9.58E-03 9.58E-04 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 2.35E-04 5.64E-03 5.64E-04 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 5.47E-05 1.31E-03 1.31E-04 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 1.19E-04 2.85E-03 2.85E-04 Total VOC HAPs 5.42E-03 0.13 0.01

[1]

[2] [3]

[4] [5] 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-03 WE Vessel Emergency Generator Engine No. 3 HAP

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 69	of	192 WE‐GE‐03	‐	HAP

### Engine Rating [1] = 147 kW 200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 73.96 kg/MMBtu 228 5,479 548 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 9.26E-03 0.22 2.22E-02 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 1.85E-03 4.44E-02 4.44E-03 CO 2 

### e EPA [6] -- -- 229 5,497 550

[1]

[2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations WE-GE-03 WE Vessel Emergency Generator Engine No. 3 GHG Pollutants

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Pollutant Emission Factor Basis Emission Factor

Operating time for this engine has been conservatively assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Engine specifications provided in a needs list spreadsheet by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on May 1, 2013.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 70	of	192 WE‐GE‐03	‐	GHGMaximum w/ Contingency (days per year ) 200 days 24 hr/day Primary Diesel Engines : 8

Emission Calculations [1]

Emission Factor [3] Total Organic Compound Total Organic Compound Total Organic Compound
(kg/hr/source) lbs/hr lbs/day tons/project Valves 87 8.40E-06 1.61E-03 0.04 0.00 Pump Seals (one per engine) 8 NA 0 0 0 Others 0 3.20E-05 0 0 0 Connectors 277 7.50E-06 4.58E-03 0.11 0.01 Flanges 0 3.90E-07 0 0 0 Open-ended lines 0 1.40E-04 0 0 0 0.01 0.15 0.01

Notes: Total TOC [4] - Heavy Oil Streams

[1] Component counts are based on EPA Permit OCS-EPA-R4005. [2] Emission factors are obtained from the EPA-453/R-95-017, November 1995 "Protocol for Equipment Leak Emission Estimates" Tab le 2-4. [3] Emissions are represented by using "Heavy Oil" factors for diesel. Distillate fuel oil No. 2 (diesel)'s Vapor Pressure = 0.012 Pva (psi)@ 80 °F, Crude oil RVP 5 = 4.0 Pva (psi)@ 80 °F. [4] It is assumed that all TOCs are VOCs. 

### Anadarko Petroleum Corporation Emission Calculations

Work Boat Fugitive Emissions

Component Type- Heavy Oil Streams [2] Number 

### SB-FE-01

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 71	of	192 SB‐FE‐01Maximum w/ Contingency (days per year ) 200 days 24 hr/day Primary Diesel Engines : 13

Emission Calculations [1]

Emission Factor [3] Total Organic Compound Total Organic Compound Total Organic Compound
(kg/hr/source) lbs/hr lbs/day tons/project Valves 114 8.40E-06 2.11E-03 0.05 0.01 Pump Seals (one per engine) 13 NA 0 0 0 Others 0 3.20E-05 0 0 0 Connectors 449 7.50E-06 0.01 0.18 0.02 Flanges 0 3.90E-07 0 0 0 Open-ended lines 0 1.40E-04 0 0 0 0.01 0.23 0.02

Notes: Total TOC [4] - Heavy Oil Streams

[1] Component counts are based on EPA Permit OCS-EPA-R4005. [2] Emission factors are obtained from the EPA-453/R-95-017, November 1995 "Protocol for Equipment Leak Emission Estimates" Tab le 2-4. [3] Emissions are represented by using "Heavy Oil" factors for diesel. Distillate fuel oil No. 2 (diesel)'s Vapor Pressure = 0.012 Pva (psi)@ 80 °F, Crude oil RVP 5 = 4.0 Pva (psi)@ 80 °F. [4] It is assumed that all TOCs are VOCs. 

### Anadarko Petroleum Corporation Emission Calculations

Anchor Handling Boat Fugitive Emissions

Component Type- Heavy Oil Streams [2] Number 

### AB-FE-01

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 72	of	192 AB‐FE‐01Dimension

Length Diameter Shell Height

(ft) (ft) (ft) (Gallon ) (tpy) (tpy) (tpy) Drillship Tanks [1] DR-FT-01 No.1 Fuel Oil Storage Tank (Port) Vertical Fixed Roof Tank Diesel 22.96588 35.597114 20.997376 173,587 0.11 0.01 0.12
DR-FT-02 No. 1 Fuel Oil Storage Tank (Starboard) Vertical Fixed Roof Tank Diesel 22.96588 35.597114 20.997376 173,587 0.11 0.01 0.12 DR-FT-03 No.2 Fuel Oil Storage Tank (Port) Vertical Fixed Roof Tank Diesel 116.797904 56.758532 20.997376 392,428 0.19 0.01 0.20 DR-FT-04 No.2 Fuel Oil Storage Tank (Starboard) Vertical Fixed Roof Tank Diesel 116.797904 56.758532 20.997376 392,428 0.19 0.01 0.20 DR-FT-05 No. 3 Fuel Storage Tank (Port) Vertical Fixed Roof Tank Diesel 116.797904 56.758532 20.997376 397,247 0.19 0.01 0.20 DR-FT-06 No. 3 Fuel Oil Storage Tank (Starboard) Vertical Fixed Roof Tank Diesel 116.797904 56.758532 20.997376 397,247 0.19 0.01 0.20 DR-FT-07 No. 1 Fuel Oil Settling Tank (Starboard) Horizontal Tank Diesel 18.372704 15.419948 15.748032 22,723 0.04 0.01 0.05 DR-FT-08 No. 2 Fuel Oil Settling Tank (Port) Horizontal Tank Diesel 18.372704 15.419948 15.748032 22,723 0.04 0.01 0.05 DR-FT-09 No. 1 Fuel Oil Servicing Tank (#1 E/R) Vertical Fixed Roof Tank Diesel 9.186352 9.8097116 14.76378 8,321 0.03 0.01 0.05 DR-FT-10 No. 2 Fuel Oil Servicing Tank (#1 E/R) Vertical Fixed Roof Tank Diesel 9.186352 9.8097116 14.76378 8,321 0.03 0.01 0.05 DR-FT-11 No. 1 Fuel Oil Servicing Tank (#2 E/R) Vertical Fixed Roof Tank Diesel 9.186352 9.8097116 14.76378 8,321 0.03 0.01 0.05 DR-FT-12 No. 2 Fuel Oil Servicing Tank (#2 E/R) Vertical Fixed Roof Tank Diesel 9.186352 9.8097116 14.76378 8,321 0.03 0.01 0.05 DR-FT-13 No. 1 Fuel Oil Servicing Tank (#3 E/R) Vertical Fixed Roof Tank Diesel 11.48294 9.8097116 14.76378 10,402 0.04 0.01 0.05 DR-FT-14 No. 2 Fuel Oil Servicing Tank (#3 E/R) Vertical Fixed Roof Tank Diesel 11.48294 9.8097116 14.76378 10,402 0.04 0.01 0.05
DR-FT-15 Fuel Oil Over Tank Horizontal Tank Diesel 9.186352 19.192914 8.530184 18,463 0.19 0.01 0.20
DR-FT-16 Fuel Oil Leak Tank Horizontal Tank Diesel 4.593176 13.5826776 8.530184 9,231 0.19 0.01 0.20

0.19 0.01 0.20

DR-FT-17 Helifuel Tank 1 Horizontal Tank JP-4 6.5452758 6.5452758 7.3326774 766 0.17 0.08 0.25
DR-FT-18 Helifuel Tank 2 Horizontal Tank JP-4 6.5452758 6.5452758 7.3326774 766 0.17 0.08 0.25

0.52 0.17 0.69 Supply Boat Tanks [2]
SB-DT-01 Vessel's Diesel Fuel Storage Tank #1 Port Vertical Fixed Roof Tank Diesel 27.64 8.47 38,020 SB-DT-02 Vessel's Diesel Fuel Storage Tank #1 Starboard Vertical Fixed Roof Tank Diesel 27.64 8.47 38,020 SB-DT-03 Vessel's Diesel Fuel Storage Tank #2 Port Vertical Fixed Roof Tank Diesel 27.64 8.56 38,424 SB-DT-04 Vessel's Diesel Fuel Storage Tank #2 Starboard Vertical Fixed Roof Tank Diesel 27.64 8.56 38,424 SB-DT-05 Vessel's Diesel Fuel Storage Tank #3 Port Vertical Fixed Roof Tank Diesel 29.94 8.05 42,398 SB-DT-06 Vessel's Diesel Fuel Storage Tank #3 Starboard Vertical Fixed Roof Tank Diesel 29.94 8.05 42,398 SB-DT-07 Vessel's Diesel Fuel Storage Tank #4 Port Vertical Fixed Roof Tank Diesel 29.94 8.04 42,346 SB-DT-08 Vessel's Diesel Fuel Storage Tank #4 Starboard Vertical Fixed Roof Tank Diesel 29.94 8.04 42,346 SB-DT-09 Vessel's Diesel Fuel Storage Tank #5 Port Vertical Fixed Roof Tank Diesel 10.7 9.77 6,572 SB-DT-10 Vessel's Diesel Fuel Storage Tank #5 Starboard Vertical Fixed Roof Tank Diesel 12.21 8.38 7,340 SB-DT-11 Vessel's Diesel Fuel Storage Day Tank #1 Port Vertical Fixed Roof Tank Diesel 9.57 11.2 6,027 SB-DT-12 Vessel's Diesel Fuel Storage Day Tank #1 Starboard Vertical Fixed Roof Tank Diesel 10.7 13.6 9,149 SB-DT-13 Vessel's Diesel Fuel Stern Thruster Day Tank Vertical Fixed Roof Tank Diesel 4.79 11.1 1,496 SB-DT-14 Vessel's Diesel Fuel Overflow Port Storage Tank Vertical Fixed Roof Tank Diesel 8.29 10.9 4,401 SB-DT-15 Vessel's Diesel Fuel Overflow Standby Storage Tank Vertical Fixed Roof Tank Diesel 8.29 10.9 4,401

1.09E-02 1.09E-02 Anchor Handling Boat Tanks [3]
AB-DT-01 Port Side Double Bottom Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 20.908 5 12,842
AB-DT-02 Starboard Side Double Bottom Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 20.916 5 12,852
AB-DT-03 Center Double Bottom Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 26.436 3.825 15,706
AB-DT-04 Port Side Double Bottom Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 32.736 5 31,483
AB-DT-05 Starboard Side Double Bottom Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 32.736 5 31,483 AB-DT-06 Port Wing Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 15.909 10.975 16,321 AB-DT-07 Starboard Wing Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 15.909 10.975 16,321
AB-DT-08 Port Side Double Bottom Diesel Fuel Tank #3 Vertical Fixed Roof Tank Diesel 27.026 6.475 27,788
AB-DT-09 Starboard Side Double Bottom Diesel Fuel Tank #3 Vertical Fixed Roof Tank Diesel 27.026 6.475 27,788 AB-DT-10 Port Wing Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 17.548 29.475 53,328
AB-DT-11 Starboard Side Double Bottom Diesel Fuel Tank #4 Vertical Fixed Roof Tank Diesel 36.932 6.875 55,097 AB-DT-12 Starboard Wing Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 32.906 6.126 38,974
AB-DT-13 Port Side Double Bottom Diesel Fuel Tank #4 Vertical Fixed Roof Tank Diesel 22.482 9.475 28,138
AB-DT-14 Starboard Side Double Bottom Diesel Fuel Tank #5 Vertical Fixed Roof Tank Diesel 22.482 9.475 28,138
AB-DT-15 Port Service Diesel Tank Vertical Fixed Roof Tank Diesel 12.522 14.65 13,497
AB-DT-16 Starboard Service Diesel Tank Vertical Fixed Roof Tank Diesel 12.522 14.65 13,497 AB-DT-17 Port Diesel Settling Tank Vertical Fixed Roof Tank Diesel 12.627 14.65 13,724 AB-DT-18 Starboard Diesel Settling Tank Vertical Fixed Roof Tank Diesel 12.627 14.65 13,724 AB-DT-19 Diesel Fuel Overflow Tank Vertical Fixed Roof Tank Diesel 12.82 3.825 3,694

0 0.10 0.10 Well Completion Tanks [8] WC-CT-01 Well Completion Condensate Tank 1 Horizontal Tank Condensate 10 39.2 42000 0.26 2.96 3.22 WC-CT-02 Well Completion Condensate Tank 2 Horizontal Tank Condensate 10 39.2 42000 0.26 2.96 3.22 WC-CT-03 Well Completion Condensate Tank 3 Horizontal Tank Condensate 10 39.2 42000 0.26 2.96 3.22

0.78 8.87 9.65

Note: [1] For all diesel tanks on the drillship, the annual "capped" emissions of all the diesel tanks grouped together are calculate d based on a throughput of 123 cubic meter/day * 2 * 200 days/yr * 264.17 * 1.16 = 15,076,710 gal/yr (approximately with 16% sa fety factor)

[4] For all three jet fuel tanks, throughput is 450 GPD based on the email from Ms. Sara Carlson (Anadarko) to Rahul Pendse (Tr inity) on December 20, 2012. [5] Red/Primer was selected as the most appropriate shell color in Tanks 4.09d program, as yellow is not an option in TANKS 4.0 9d program. [6] Based on EPA-approved TANKS 4.09d program. 6604500 [7] The largest tanks DR-FT-05 and DR-FT-06 on the drillship are chosen to calculate the drillship tanks annual emissions. 6604500 [8] Tank volume 21,000 gal is provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on March 8, 2013. [2] Total Standing Losses = (maximum hourly standing losses for biggest tank on the supply boat) * (24 hrs/day) * 200 days/yr. Only the standing losses are calculated since diesel from all tanks on the supply boat will only be unloaded into the drillshi p tanks and no filling of tanks occurs on the supply boat. [3] Total Standing Losses = (maximum hourly standing losses for biggest tank on the anchor handling boat) * (24 hrs/day) * 200 days/yr. Only the standing losses are calculated since diesel from all tanks on the anchor handling boat will only be unloaded into the drillship tanks and no filling of tanks occurs on the anchor handling boat. Well Completion Total Emissions from Tanks Standing Loss Total Emissions

The average diesel fuel usage for the drillship is 774 bbl/day. For conservative assumption, a throughput equal to twice the a verage fuel usage restriction of 774 bbl/day is used and it is assumed that all fuel is loaded into the largest tank DR-FT-05 to calculate the maximum total tank VOC emissions (tpy) on the drillship.

Drillship Total Emissions from Tanks

Supply Boat Total Emissions from Tanks

Anchor Handling Boat Total Emissions from Tanks 1.09E-02 2.60E-02 Anadarko Petroleum Corporation Drillship and Support Vessel Tanks - Emissions Summary

Emission Unit ID Emission Unit Tank Type Tank Contents Tank Volume Emissions [6]
Working Loss

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 73	of	192 DR,SB	and	AB‐Tanks	tpyVOC VAPOR FRACTION[1]HAPE,GCondensateand HelifuelHelifuel TankEmissions (tpy)Condensate TankEmissions (tpy)Diesel FuelTanks Emissions (tpy)CASNumbersBenzene 0.90% 0.006 0.09 0.01% 3.40E-05 00071-43-2Ethylbenzene 0.10% 0.001 0.01 0.01% 3.40E-05 00100-41-4Hexane (-n) 1.60% 0.011 0.15 - -- 00110-54-3Isooctane 0.80% 0.006 0.08 - -- 00540-84-1Toluene 1.30% 0.009 0.13 0.06% 1.82E-04 00108-88-3Xylene (-m) 0.50% 0.003 0.05 0.05% 1.45E-04 00108-38-3Cresol (-o) -- -- -- 0.00% 0.00E+00 00095-48-7Isopropyl benzene -- -- -- 0.01% 1.86E-05 00098-82-8Naphthalene -- -- -- 0.00% 3.09E-06 00091-20-3Phenol -- -- -- 0.00% 0.00E+00 00108-95-2Note:[1] VOC Vapor fraction is based on Gasoline RVP 13 speciation profile.[2] VOC Vapor fraction is based on Distillate Oil #2 speciation profile.VOC VAPOR FRACTION[2]Anadarko Petroleum CorporationEmission CalculationsDrillship and Support Vessel Tanks -HAP Emissions Speciation SummaryAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet74	of	192HAP	Speciation	DataPumping rateMax HourlyThroughputMax HourlyThroughput(gals) (gals) (gal/hr) (gal/hr) (bbl/hr) (lbs/hr) (lbs/hr) (lbs/hr)DR-FT-01 No.1 Fuel Oil Storage Tank (Port)Vertical Fixed Roof Tank Diesel 173,587173,5877,560 7,560 180 0.298 0.19 0.490DR-FT-02 No. 1 Fuel Oil Storage Tank (Starboard)Vertical Fixed Roof Tank Diesel 173,587 173,587 7,560 7,560 180 0.298 0.19 0.490DR-FT-03 No.2 Fuel Oil Storage Tank (Port)Horizontal Tank Diesel 392,428 392,428 7,560 7,560 180 0.298 6.33E-03 0.305DR-FT-04 No.2 Fuel Oil Storage Tank (Starboard)Horizontal Tank Diesel 392,428 392,428 7,560 7,560 180 0.298 0.006 0.305DR-FT-05 No. 3 Fuel Storage Tank (Port)Horizontal Tank Diesel 380,038 380,038 7,560 7,560 180 0.298 3.33E-04 0.299DR-FT-06 No. 3 Fuel Oil Storage Tank (Starboard)Horizontal Tank Diesel 380,038 380,038 7,560 7,560 180 0.298 3.33E-04 0.299DR-FT-07 No. 1 Fuel Oil Settling Tank (Starboard)Horizontal Tank Diesel 18,756 18,756 7,560 7,560 180 0.298 0.02 0.319DR-FT-08 No. 2 Fuel Oil Settling Tank (Port)Horizontal Tank Diesel 18,756 18,756 7,560 7,560 180 0.298 0.02 0.319DR-FT-09 No. 1 Fuel Oil Servicing Tank (#1 E/R)Vertical Fixed Roof Tank Diesel 8,136 8,136 7,560 7,560 180 0.298 1.03E-02 0.309DR-FT-10 No. 2 Fuel Oil Servicing Tank (#1 E/R)Vertical Fixed Roof Tank Diesel 8,136 8,136 7,560 7,560 180 0.298 1.03E-02 0.309DR-FT-11 No. 1 Fuel Oil Servicing Tank (#2 E/R)Vertical Fixed Roof Tank Diesel 8,136 8,136 7,560 7,560 180 0.298 1.03E-02 0.309DR-FT-12 No. 2 Fuel Oil Servicing Tank (#2 E/R)Vertical Fixed Roof Tank Diesel 8,136 8,136 7,560 7,560 180 0.298 1.03E-02 0.309DR-FT-13 No. 1 Fuel Oil Servicing Tank (#3 E/R)Vertical Fixed Roof Tank Diesel 9,193 9,193 7,560 7,560 180 0.298 1.03E-02 0.309DR-FT-14 No. 2 Fuel Oil Servicing Tank (#3 E/R)Vertical Fixed Roof Tank Diesel 9,114 9,114 7,560 7,560 180 0.298 1.03E-02 0.309DR-FT-15 Fuel Oil Over TankHorizontal Tank Diesel 12,178 12,178 7,560 7,560 180 0.184 1.57E-02 0.199DR-FT-16 Fuel Oil Leak TankHorizontal Tank Diesel6,102 6,102 7,560 6,102 145 0.148 4.33E-03 0.153DR-FT-17 Helifuel Tank 1Horizontal Tank JP-4 766 766 7,560 766 18 3.939 0.60 4.537DR-FT-18 Helifuel Tank 2Horizontal Tank JP-4 766 766 7,560 766 18 3.939 0.60 4.5374.28Note:[2] Maximum hourly standing losses and breathing losses were calculated using EPA TANKS 4.09d program for the month of June, since June results in the highest emissions.[1] Maximum hourly working loss was calculated using AP-42 chapter 7 equation 29.Working Loss = 0.0010 * Vapor molecular weight * vapor pressure * throughput * working loss turnover factor * working loss product factorMaximum vapor pressure from June is used in the calculation.Maximum HourlyWorking Loss [1]Maximum HourlyStanding Loss [2]MaximumHourly EmissionsAnadarko Petroleum CorporationDrillship Tanks - Maximum Hourly EmissionsEmission Unit ID Emission Unit Tank Type Tank ContentsTank VolumeDesignCapacityParameters for Calculate the Working LossAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet75	of	192Drill	Ship	Tanks	Max	HourlyDesignCapacityDiameter Shell Height(gals)(ft) (ft) (gals) (lbs/day) (lbs/hr)SB-DT-01 Vessel's Diesel Fuel Storage Tank #1 Port Vertical Fixed Roof Tank Diesel 27.64 8.4738,020 38,052 7,560 7,5600.0803.33E-03SB-DT-02 Vessel's Diesel Fuel Storage Tank #1 Starboard Vertical Fixed Roof Tank Diesel 27.64 8.4738,020 38,052 7,560 7,5600.0803.33E-03SB-DT-03 Vessel's Diesel Fuel Storage Tank #2 Port Vertical Fixed Roof Tank Diesel 27.64 8.5638,424 38,430 7,560 7,5600.0803.33E-03SB-DT-04 Vessel's Diesel Fuel Storage Tank #2 Starboard Vertical Fixed Roof Tank Diesel 27.64 8.5638,424 38,430 7,560 7,5600.0813.39E-03SB-DT-05 Vessel's Diesel Fuel Storage Tank #3 Port Vertical Fixed Roof Tank Diesel 29.94 8.0542,398 42,420 7,560 7,5600.0863.57E-03SB-DT-06 Vessel's Diesel Fuel Storage Tank #3 Starboard Vertical Fixed Roof Tank Diesel 29.94 8.0542,398 42,420 7,560 7,5600.0863.57E-03SB-DT-07 Vessel's Diesel Fuel Storage Tank #4 Port Vertical Fixed Roof Tank Diesel 29.94 8.0442,346 42,378 7,560 7,5600.0863.57E-03SB-DT-08 Vessel's Diesel Fuel Storage Tank #4 Starboard Vertical Fixed Roof Tank Diesel 29.94 8.0442,346 42,378 7,560 7,5600.0863.57E-03SB-DT-09 Vessel's Diesel Fuel Storage Tank #5 Port Vertical Fixed Roof Tank Diesel 10.7 9.776,572 6,594 7,560 6,5940.0145.69E-04SB-DT-10 Vessel's Diesel Fuel Storage Tank #5 Starboard Vertical Fixed Roof Tank Diesel 12.21 8.387,340 7,350 7,560 7,3500.0156.11E-04SB-DT-11 Vessel's Diesel Fuel Storage Day Tank #1 Port Vertical Fixed Roof Tank Diesel 9.57 11.26,027 6,048 7,560 6,0480.0124.86E-04SB-DT-12 Vessel's Diesel Fuel Storage Day Tank #1 Starboard Vertical Fixed Roof Tank Diesel 10.7 13.69,149 9,156 7,560 7,5600.0187.50E-04SB-DT-13 Vessel's Diesel Fuel Stern Thruster Day Tank Vertical Fixed Roof Tank Diesel 4.79 11.11,496 1,512 7,560 1,5120.0031.25E-04SB-DT-14 Vessel's Diesel Fuel Overflow Port Storage Tank Vertical Fixed Roof Tank Diesel 8.29 10.94,401 4,410 7,560 4,4100.0083.47E-04SB-DT-15 Vessel's Diesel Fuel Overflow Standby Storage Tank Vertical Fixed Roof Tank Diesel 8.29 10.94,401 4,410 7,560 4,4100.0083.47E-040.08Note:[1] Maximum hourly standing loss was calculated using EPA TANKS 4.09d program for the month of June.[2] Only standing loss is calculated for the maximum hourly emission since all tanks on the supply boat will only be unloadedinto the drillship tanks and no filling of tanks occurs on the supply boat.Max hourlyThroughputMaximum DailyStanding LossMaximum HourlyStanding Loss[1],[2]DimensionsAnadarko Petroleum CorporationSupply Boat Tanks - Maximum Hourly EmissionsEmission Unit ID Emission Unit Tank Type Tank ContentsTankTank VolumePumping rategal/hrAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet76	of	192Supply	Boat	Tanks	Max	HourlyDiameter Shell Height(ft) (ft) (gals) (lbs/day) (lbs/hr)AB-DT-01 Port Side Double Bottom Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel20.908 5 12,842 0.028 1.18E-03AB-DT-02 Starboard Side Double Bottom Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 20.916 512,852 0.028 1.18E-03AB-DT-03 Center Double Bottom Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 26.436 3.82515,706 0.043 1.78E-03AB-DT-04 Port Side Double Bottom Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 32.736 531,483 0.075 3.13E-03AB-DT-05 Starboard Side Double Bottom Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 32.736 531,483 0.075 3.13E-03AB-DT-06 Port Wing Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 15.909 10.97516,321 0.031 1.31E-03AB-DT-07 Starboard Wing Diesel Fuel Tank #1 Vertical Fixed Roof Tank Diesel 15.909 10.97516,321 0.031 1.31E-03AB-DT-08 Port Side Double Bottom Diesel Fuel Tank #3 Vertical Fixed Roof Tank Diesel 27.026 6.47527,788 0.057 2.36E-03AB-DT-09 Starboard Side Double Bottom Diesel Fuel Tank #3 Vertical Fixed Roof Tank Diesel 27.026 6.47527,788 0.057 2.36E-03AB-DT-10 Port Wing Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 17.548 29.47553,328 0.100 4.17E-03AB-DT-11 Starboard Side Double Bottom Diesel Fuel Tank #4 Vertical Fixed Roof Tank Diesel 36.932 6.87555,097 0.115 4.78E-03AB-DT-12 Starboard Wing Diesel Fuel Tank #2 Vertical Fixed Roof Tank Diesel 32.906 6.12638,974 0.088 3.68E-03AB-DT-13 Port Side Double Bottom Diesel Fuel Tank #4 Vertical Fixed Roof Tank Diesel 22.482 9.47528,138 0.069 2.89E-03AB-DT-14 Starboard Side Double Bottom Diesel Fuel Tank #5 Vertical Fixed Roof Tank Diesel 22.482 9.47528,138 0.055 2.29E-03AB-DT-15 Port Service Diesel Tank Vertical Fixed Roof Tank Diesel 12.522 14.6513,497 0.026 1.07E-03AB-DT-16 Starboard Service Diesel Tank Vertical Fixed Roof Tank Diesel 12.522 14.6513,497 0.026 1.07E-03AB-DT-17 Port Diesel Settling Tank Vertical Fixed Roof Tank Diesel 12.627 14.6513,724 0.026 1.08E-03AB-DT-18 Starboard Diesel Settling Tank Vertical Fixed Roof Tank Diesel 12.627 14.6513,724 0.026 1.08E-03AB-DT-19 Diesel Fuel Overflow Tank Vertical Fixed Roof Tank Diesel 12.82 3.8253,694 0.010 4.17E-041.00E-01Note:[1] Maximum hourly standing loss was calculated using EPA TANKS 4.09d program for the month of June.[2] Only standing loss is calculated for the maximum hourly emission since diesel from all tanks on the anchor handling boat will only be unloaded into the drillship tanks and no filling of tanks occurs on the anchor handling boat.MaximumDaily StandingLossMaximumHourlyStanding Loss[1],[2]Anadarko Petroleum CorporationAnchor Handling Boat Tanks - Maximum Hourly EmissionsEmission UnitIDEmission Unit Tank Type Tank ContentsTank DimensionsTank VolumeAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet77	of	192Anchor	Boat	Tanks	Max	HourlyDiameter Shell Height(ft) (ft) (gals) (lbs/day) (lbs/day) (lbs/day) (lbs/hr)DR-TP-24 Well Completion Condensate Tank 1 Horizontal Tank Condensate10 39.221,000 20.78 0.78 21.56 0.90DR-TP-25 Well Completion Condensate Tank 2 Horizontal Tank Condensate10 39.221,000 20.14 0.78 21.56 0.90DR-TP-26 Well Completion Condensate Tank 3 Horizontal Tank Condensate10 39.221,000 20.14 0.78 21.56 0.90Note:[1] Maximum hourly standing loss and working loss were calculated using EPA TANKS 4.09d program for the month of June which generates the highest daily emissions.Anadarko Petroleum CorporationWell Completion Condensate Tanks - Maximum Hourly EmissionsEmission Unit ID Emission Unit Tank Type Tank ContentsTank DimensionsTank VolumeMaximumDaily StandingLossMaximumDaily WorkingLossMaximumDailyEmissionsMaximumHourlyEmissions [1]Anadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet78	of	192WC	Condensate	Tank	Max	HourlyEngine Rating [1] = 2,240 kW 3,004 HP Operating Time [2] = 24 hrs/day (combination of supply boats ) 4,800 hrs/yr Fuel Type [3] = ULSD No. of Engines = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 40 CFR 94.8(a)(2)(i) [4] 0.2 g/kW-hr 1.98 47.41 4.74 PM 10 40 CFR 94.8(a)(2)(i), AP-42 [4],[5] 0.164 g/kW-hr 1.62 38.98 3.90 PM 2.5 40 CFR 94.8(a)(2)(i), AP-42 [4],[5] 0.160 g/kW-hr 1.58 37.82 3.78 NO x 40 CFR 94.8(a)(2)(i) [4] 7.2 g/kW-hr 71.12 1706.79 170.68 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.07 1.62 0.16 CO 40 CFR 94.8(a)(2)(i) [4] 5.0 g/kW-hr 49.39 1185.27 118.53 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 3.85 92.51 9.25

Pb EPA [7] 2.03E-07 lb/HP-hr 1.22E-03 2.93E-02 2.93E-03 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 2.11E-03 5.05E-02 5.05E-03

[1] [2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar 3516C DITA (Diesel Marine Propulsion Engines #1 and 2) EPN: SB-ME-01 and SB-ME-02

Pollutant Emission Factor Basis Emission Factor 

### Criteria Pollutants and Sulfuric Acid

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

VOC emission factor is based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor (2.9x10 -5 lb/MMBtu) is obtained from EPA guidance document: Locating and Estimating Air Emissionsfrom Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oilfired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor is 91% of TOC emission factor. Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 and 2 wt.% of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Per Caterpillar Marine Engine Guidance, for Caterpillar 3516C, displacement of each cylinder is 78.08 L/16 cylinders =4.88 L/cylinder which is less than 5L/cylinder. Therefore, according to 40 CFR 94.8(a)(2)(i), the emission factors of NOx, CO and PM are 7.2, 5 and 0.2 g/kW-hr respectively. Emission factor of PM 2.5 and PM 10 are calculated based on ratio of PM/PM 2.5 and PM/PM 10 which are obtained from AP-42 Chapter 3, Table 3.4-2.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 79	of	192 SB‐ME‐01	and	02	‐	Crit

### Engine Rating [1] = 2,240 kW 3,004 HP Operating Time [2] = 24 hrs/day (combination of supply boats) 4,800 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [6] = 148.3 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 19.16 MMBtu/hr No. of Engines = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4] 2.52E-05 lb/MMBtu 9.66E-04 2.32E-02 2.32E-03

Acrolein AP-42 [4] 7.88E-06 lb/MMBtu 3.02E-04 7.25E-03 7.25E-04 Benzene AP-42 [4] 7.76E-04 lb/MMBtu 2.97E-02 7.14E-01 7.14E-02 Formaldehyde AP-42 [4] 7.89E-05 lb/MMBtu 3.02E-03 7.26E-02 7.26E-03 Toluene AP-42 [4] 2.81E-04 lb/MMBtu 1.08E-02 2.58E-01 2.58E-02 Xylenes AP-42 [4] 1.93E-04 lb/MMBtu 7.40E-03 1.78E-01 1.78E-02 Total PAH AP-42 [5] 2.12E-04 lb/MMBtu 8.13E-03 1.95E-01 1.95E-02 N aphthalene AP-42 [5] 1.30E-04 lb/MMBtu 4.98E-03 1.20E-01 1.20E-02 0.06 1.45 0.14

[1] [2] [3]

[4]

[5]
[6] Fuel consumption rate obtained from Caterpillar 3516C DITA Specification Sheet. Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel En g ines ( October 1996 )

. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar 3516C DITA (Diesel Marine Propulsion Engines #1 and 2) EPN: SB-ME-01 and SB-ME-02

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day (for all supply boats combined). Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). 

### HAP

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 80	of	192 SB‐ME‐01	and	02	‐	HAPEngine Rating [1] = 2,240 kW 3,004 HP Operating Time [2] = 24 hrs/day (combination of supply boats) 4,800 hrs/yr Fuel Type [3] = ULSD Operating load [2] = 100% Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [7] = 148.3 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 19.16 MMBtu/hr No. of Engines = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 6249.63 149991.10 14999.11

CH 4 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 0.25 6.08 0.61

N 2 O 40 CFR 98 Subpart C [5] 6.00E-04 kg/MMBtu 0.05 1.22 0.12

CO 2 e 40 CFR 98 Subpart C [6] -- -- 6270.67 150496.07 15049.61

[1] [2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar 3516C DITA (Diesel Marine Propulsion Engines #1 and 2) EPN: SB-ME-01 and SB-ME-02 Greenhouse Gases

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Emission factor is based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 is used to calculate emissions. Emission factors are based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. Global warming potentials (GWP) for CH 4 , CO 2 and N 2 O are used to calculate CO 2 equivalent (CO 2 e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). Fuel consumption rate obtained from Caterpillar 3516C DITA Specification Sheet. Pollutant Emission Factor Basis Emission Factor

Engine rate is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day (for all supply boats combined). Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 81	of	192 SB‐ME‐01	and	02	‐	GHGEngine Rating [1] = 820 kW 1,100 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD No. of Engines = 3

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 94.8(a)(2)(i) [4] 0.2 g/kW-hr 1.09 26.04 2.60 PM 10 94.8(a)(2)(i) [4],[5] 0.164 g/kW-hr 0.89 21.41 2.14 PM 2.5 94.8(a)(2)(i) [4],[5] 0.160 g/kW-hr 0.87 20.77 2.08 NO x 94.8(a)(2)(i) [4] 7.2 g/kW-hr 39.06 937.48 93.75 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.04 0.89 0.09 CO 94.8(a)(2)(i) [4] 5.0 g/kW-hr 27.13 651.03 65.10 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 2.12 50.81 5.08

Pb EPA [7] 2.03E-07 lb/HP-hr 6.70E-04 1.61E-02 1.61E-03 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 1.16E-03 2.77E-02 2.77E-03

[1] [2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar 3508C DITA (Diesel Marine Forward Bow Thruster Engines #1-2-3) EPN: SB-TE-01, SB-TE-02, SB-TE-03

Pollutant Emission Factor Basis Emission Factor 

### Criteria Pollutants and Sulfuric Acid

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day (for all supply boats combined). Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 and 2 wt.% of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Per Caterpillar Marine Engine Guidance, for Caterpillar 3516C, displacement of each cylinder is 78.08 L/16 cylinders =4.88 L/cylinder which is less than 5L/cylinder. Therefore, according to 40 CFR 94.8(a)(2)(i), the emission factors of NOx, CO and PM are 7.2, 5 and 0.2 g/kW-hr respectively. Emission factor of PM 2.5 and PM 10 are calculated based on ratio of PM/PM 2.5 and PM/PM 10 which are obtained from AP-42 Chapter 3, Table 3.4-2. VOC emission factor is based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor (2.9x10 -5 lb/MMBtu) is obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor is 91% of TOC emission factor.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 82	of	192 SB‐TE‐01‐02‐03	‐	CriteriaEngine Rating [1] = 820 kW 1,100 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [6] = 54.2 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 7.00 MMBtu/hr No. of Engines = 3

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4] 2.52E-05 lb/MMBtu 5.30E-04 1.27E-02 1.27E-03

Acrolein AP-42 [4] 7.88E-06 lb/MMBtu 1.66E-04 3.97E-03 3.97E-04 Benzene AP-42 [4] 7.76E-04 lb/MMBtu 1.63E-02 3.91E-01 3.91E-02 Formaldehyde AP-42 [4] 7.89E-05 lb/MMBtu 1.66E-03 3.98E-02 3.98E-03 Toluene AP-42 [4] 2.81E-04 lb/MMBtu 5.90E-03 1.42E-01 1.42E-02 Xylenes AP-42 [4] 1.93E-04 lb/MMBtu 4.06E-03 9.73E-02 9.73E-03 Total PAH AP-42 [5] 2.12E-04 lb/MMBtu 4.45E-03 1.07E-01 1.07E-02 Naphthalene AP-42 [5] 1.30E-04 lb/MMBtu 2.73E-03 6.56E-02 6.56E-03 0.03 0.79 0.08

[1] [2] [3]

[4]
[5]
[6] Fuel consumption rate obtained from Caterpillar 3508C DITA Specification Sheet. Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel En g ines ( October 1996 )

. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar 3508C DITA (Diesel Marine Forward Bow Thruster Engines #1-2-3) EPN: SB-TE-01, SB-TE-02, SB-TE-03

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day (for all supply boats combined). Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationar y Diesel En g ines ( October 1996 )

. 

### HAP

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 83	of	192 SB‐TE‐01‐02‐03	‐	HAPEngine Rating [1] = 820 kW 1,100 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [7] = 54.2 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 7.00 MMBtu/hr No. of Engines = 3

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 3,426.13 82,227.08 8,222.71

CH 4 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 0.14 3.34 0.33

N 2 O 40 CFR 98 Subpart C [5] 6.00E-04 kg/MMBtu 0.03 0.67 0.07

CO 2 e 40 CFR 98 Subpart C [6] -- -- 3,437.66 82,503.92 8,250.39

[1] [2] [3]

[4]

[5]

[6]

[7] Fuel consumption rate obtained from Caterpillar 3508C DITA Specification Sheet. Pollutant Emission Factor Basis Emission Factor

Engine rate is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Global warming potentials (GWP) for CH 4 , CO 2 and N 2 O are used to calculate CO 2 equivalent (CO 2 e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar 3508C DITA (Diesel Marine Forward Bow Thruster Engines #1-2-3) EPN: SB-TE-01, SB-TE-02, SB-TE-03

Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factor is based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 is used to calculate emissions. Emission factors are based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. 

### Greenhouse Gases

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 84	of	192 SB‐TE‐01‐02‐03	‐	GHGEngine Rating [1] = 781 kW 1,047 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 94.8(a)(2)(i) [4] 0.2 g/kW-hr 0.34 8.26 0.83 PM 10 94.8(a)(2)(i) [4],[5] 0.164 g/kW-hr 0.28 6.79 0.68 PM 2.5 94.8(a)(2)(i) [4],[5] 0.160 g/kW-hr 0.27 6.59 0.66 NO x 94.8(a)(2)(i) [4] 7.2 g/kW-hr 12.39 297.44 29.74 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.28 0.028 CO 94.8(a)(2)(i) [4] 5.0 g/kW-hr 8.61 206.55 20.66 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 0.67 16.12 1.61

Pb EPA [7] 2.03E-07 lb/HP-hr 2.13E-04 5.10E-03 5.10E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 3.67E-04 8.80E-03 8.80E-04

[1] [2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar C32 DITA (Port Electrical Generator Diesel Engine #1) EPN: SB-GE-01 Criteria Pollutants and Sulfuric Acid

Pollutant Emission Factor Basis Emission Factor

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor is 91% of TOC emission factor. Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 and 2 wt.% of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, Per Caterpillar C32 DITA Specifications, displacement of each cylinder is 2.5-5 L/cylinder which is less than or equal to 5L/cylinder. Therefore, according to 40 CFR 94.8(a)(2)(i), the emission factors of NOx, CO and PM are 7.2, 5 and 0.2 g/kW-hr respectively. Emission factor of PM 2.5 and PM 10 are calculated based on ratio of PM/PM 2.5 and PM/PM 10 which are obtained from AP-42 Chapter 3, Table 3.4-2. VOC emission factor is based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor (2.9x10 -5 lb/MMBtu) is obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 85	of	192 SB‐GE‐01	‐	Criteria

### Engine Rating [1] = 781 kW 1,047 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [6] = 50.8 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 6.56 MMBtu/hr

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4] 2.52E-05 lb/MMBtu 1.65E-04 3.97E-03 3.97E-04

Acrolein AP-42 [4] 7.88E-06 lb/MMBtu 5.17E-05 1.24E-03 1.24E-04 Benzene AP-42 [4] 7.76E-04 lb/MMBtu 5.09E-03 1.22E-01 1.22E-02 Formaldehyde AP-42 [4] 7.89E-05 lb/MMBtu 5.18E-04 1.24E-02 1.24E-03 Toluene AP-42 [4] 2.81E-04 lb/MMBtu 1.84E-03 4.43E-02 4.43E-03 Xylenes AP-42 [4] 1.93E-04 lb/MMBtu 1.27E-03 3.04E-02 3.04E-03 Total PAH AP-42 [5] 2.12E-04 lb/MMBtu 1.39E-03 3.34E-02 3.34E-03 N aphthalene AP-42 [5] 1.30E-04 lb/MMBtu 8.53E-04 2.05E-02 2.05E-03 0.01 0.25 0.02

[1] [2] [3]

[4]

[5]
[6] Fuel consumption rate obtained from Caterpillar C32 DITA Specification Sheet. Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationar y Diesel En g ines ( October 1996 )

. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar C32 DITA (Port Electrical Generator Diesel Engine #1) EPN: SB-GE-01 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 86	of	192 SB‐GE‐01	‐	HAPEngine Rating [1] = 781 kW 1,047 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [7] = 50.8 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 6.56 MMBtu/hr

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 1,070.40 25,689.64 2,568.96

CH 4 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 0.04 1.04 0.10

N 2 O 40 CFR 98 Subpart C [5] 6.00E-04 kg/MMBtu 0.01 0.21 0.02

CO 2 e 40 CFR 98 Subpart C [6] -- -- 1,074.01 25,776.13 2,577.61

[1] [2] [3]

[4]

[5]

[6]

[7] Fuel consumption rate obtained from Caterpillar C32 DITA Specification Sheet. Pollutant Emission Factor Basis Emission Factor

Engine rate is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1.

Global warming potentials (GWP) for CH 4 , CO 2 and N 2 O are used to calculate CO 2 equivalent (CO 2 e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar C32 DITA (Port Electrical Generator Diesel Engine #1) EPN: SB-GE-01 Greenhouse Gases

Operating time for this engine is conservatively assumed to be 24 hrs/day Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factor is based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 is used to calculate emissions. Emission factors are based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 87	of	192 SB‐GE‐01	‐	GHGEngine Rating [1] = 781 kW 1,047 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 94.8(a)(2)(i) [4] 0.2 g/kW-hr 0.34 8.26 0.83 PM 10 94.8(a)(2)(i), AP-42 [4],[5] 0.164 g/kW-hr 0.28 6.79 0.68 PM 2.5 94.8(a)(2)(i), AP-42 [4],[5] 0.160 g/kW-hr 0.27 6.59 0.66 NO x 94.8(a)(2)(i) [4] 7.2 g/kW-hr 12.39 297.44 29.74 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.012 0.28 0.028 CO 94.8(a)(2)(i) [4] 5.0 g/kW-hr 8.61 206.55 20.66 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 0.67 16.12 1.61

Pb EPA [7] 2.03E-07 lb/HP-hr 2.13E-04 5.10E-03 5.10E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 3.67E-04 8.80E-03 8.80E-04

[1] [2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar C32 DITA (Starboard Electrical Generator Diesel Engine #2) EPN: SB-GE-02 Criteria Pollutants and Sulfuric Acid

Pollutant Emission Factor Basis Emission Factor

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor is 91% of TOC emission factor. Based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day, 200 days/year. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 and 2 wt.% of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Per Caterpillar C9 DITA Specifications, displacement of each cylinder is 2.5-5 L/cylinder which is less than or equal to5L/cylinder. Therefore, according to 40 CFR 94.8(a)(2)(i), the emission factors of NOx, PM and CO are 7.2, 5 and 0.2 g/kWhr respectively.
Emission factor of PM 2.5 and PM 10 are calculated based on ratio of PM/PM 2.5 and PM/PM 10 which are obtained from AP-42 Chapter 3, Table 3.4-2. VOC emission factor is based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor (2.9x10 -5 lb/MMBtu) is obtained from EPA guidance document: Locating and Estimating Air Emissionsfrom Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oilfired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 88	of	192 SB‐GE‐02	‐	Criteria

### Engine Rating [1] = 781 kW 1,047 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [6] = 50.8 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 6.56 MMBtu/hr

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4] 2.52E-05 lb/MMBtu 1.65E-04 3.97E-03 3.97E-04

Acrolein AP-42 [4] 7.88E-06 lb/MMBtu 5.17E-05 1.24E-03 1.24E-04 Benzene AP-42 [4] 7.76E-04 lb/MMBtu 5.09E-03 1.22E-01 1.22E-02 Formaldehyde AP-42 [4] 7.89E-05 lb/MMBtu 5.18E-04 1.24E-02 1.24E-03 Toluene AP-42 [4] 2.81E-04 lb/MMBtu 1.84E-03 4.43E-02 4.43E-03 Xylenes AP-42 [4] 1.93E-04 lb/MMBtu 1.27E-03 3.04E-02 3.04E-03 Total PAH AP-42 [5] 2.12E-04 lb/MMBtu 1.39E-03 3.34E-02 3.34E-03 N aphthalene AP-42 [5] 1.30E-04 lb/MMBtu 8.53E-04 2.05E-02 2.05E-03 0.01 0.25 0.02

[1] [2] [3]

[4]

[5]

[6] Fuel consumption rate obtained from Caterpillar C32 DITA Specification Sheet. Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar C32 DITA (Port Electrical Generator Diesel Engine #2) EPN: SB-GE-02 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 24 hrs/day. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 89	of	192 SB‐GE‐02	‐	HAP

### Engine Rating [1] = 781 kW 1,047 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [7] = 50.8 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 6.56 MMBtu/hr

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 1,070.40 25,689.64 2,568.96

CH 4 

### 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 0.04 1.04 0.10

N 2 

### O 40 CFR 98 Subpart C [5] 6.00E-04 kg/MMBtu 8.68E-03 2.08E-01 2.08E-02

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,074.01 25,776.13 2,577.61

[1] [2] [3]
[4]

[5]

[6]

[7] Fuel consumption rate obtained from Caterpillar C32 DITA Specification Sheet. Pollutant Emission Factor Basis Emission Factor

Engine rate is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1.

Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar C32 DITA (Starboard Electrical Generator Diesel Engine #2) EPN: SB-GE-02 Greenhouse Gases

Operating time for this engine is conservatively assumed to be 24 hrs/day. . Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Heatin g value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factor is based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 is used to calculate emissions. Emission factors are based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 90	of	192 SB‐GE‐02	‐	GHG

### Engine Rating [1] = 189 kW 253 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 94.8(a)(2)(i) [4] 0.2 g/kW-hr 8.32E-02 8.32E-02 4.16E-03 PM 10 

### 94.8(a)(2)(i) [4],[5] 0.2 g/kW-hr 8.32E-02 8.32E-02 4.16E-03 PM 2.5 

### 94.8(a)(2)(i) [4],[5] 0.2 g/kW-hr 8.32E-02 8.32E-02 4.16E-03 NO x 

### 94.8(a)(2)(i) [4] 7.2 g/kW-hr 2.99 2.99 0.15 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 2.84E-03 2.84E-03 1.42E-04 CO 94.8(a)(2)(i) [4] 5.0 g/kW-hr 2.08 2.08 0.10 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.16 0.16 0.01

Pb EPA [6] 2.03E-07 lb/HP-hr 5.14E-05 5.14E-05 2.57E-06 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 8.86E-05 8.86E-05 4.43E-06

[1] [2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar C9 DITA ( Emergency Electrical Generator Diesel Engine #3) EPN: SB-GE-03 Criteria Pollutants and Sulfuric Acid

Pollutant Emission Factor Basis Emission Factor

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 1 hrs/day, 100.0 hrs/year. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppmw in diesel fuel assuming that 98 wt.% of sulfur in the fuel is oxidized to SO 2 

### and 2 wt.% of sulfur in the fuel is oxidized to H2SO4 b ased on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Per Caterpillar C9 DITA Specifications, displacement of each cylinder is 2.5-5 L/cylinder which is less than or equal to 5L/cylinder. Therefore, according to 40 CFR 94.8(a)(2)(i), the emission factors of NOx, CO and PM are 7.2, 5 and 0.2 g/kW-hr respectively. VOC emission factors is based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 91	of	192 SB‐GE‐03	‐	Criteria

### Engine Rating [1] = 189 kW 253 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [5] = 13.63 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 1.76 MMBtu/hr

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4] 7.67E-04 lb/MMBtu 1.35E-03 1.35E-03 6.75E-05

Acrolein AP-42 [4] 9.25E-05 lb/MMBtu 1.63E-04 1.63E-04 8.15E-06 Benzene AP-42 [4] 9.33E-04 lb/MMBtu 1.64E-03 1.64E-03 8.22E-05 Formaldehyde AP-42 [4] 1.18E-03 lb/MMBtu 2.08E-03 2.08E-03 1.04E-04 Toluene AP-42 [4] 4.09E-04 lb/MMBtu 7.20E-04 7.20E-04 3.60E-05 Xylenes AP-42 [4] 2.85E-04 lb/MMBtu 5.02E-04 5.02E-04 2.51E-05 Total PAH AP-42 [4] 1.68E-04 lb/MMBtu 2.96E-04 2.96E-04 1.48E-05 1,3-Butadiene AP-42 [4] 3.91E-05 lb/MMBtu 6.89E-05 6.89E-05 3.44E-06 N aphthalene AP-42 [4] 8.48E-05 lb/MMBtu 1.50E-04 1.50E-04 7.51E-06 6.82E-03 6.82E-03 3.41E-04

[1] [2] [3]

[4]

[5] Fuel consumption rate obtained from Caterpillar C9 DITA Specification Sheet. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar C9 DITA ( Emergency Electrical Generator Diesel Engine #3) EPN: SB-GE-03 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Engine rating is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1. Operating time for this engine is conservatively assumed to be 1.0 hrs/day, 100.0 hrs/year. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Heating value is obtained from Chevron Diesel Fuels Technical Review Table 4.3. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 92	of	192 SB‐GE‐03	‐	HAP

### Engine Rating [1] = 189 kW 253 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [3] = ULSD Diesel Fuel Heat Value [3] = 18,330 btu/lb Fuel Consumption [7] = 13.63 gal/hr ULSD density = 7.05 lb/gal Calculated Heat Rate = 1.76 MMBtu/hr

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [4] 73.96 kg/MMBtu 287.20 287.20 14.36

CH 4 

### 40 CFR 98 Subpart C [5] 3.00E-03 kg/MMBtu 1.16E-02 1.16E-02 5.82E-04

N 2 

### O 40 CFR 98 Subpart C [5] 6.00E-04 kg/MMBtu 2.33E-03 2.33E-03 1.16E-04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 288.16 288.16 14.41

[1] [2]

[3]
[4]

[5]

[6]

[7] Fuel consumption rate obtained from Caterpillar C9 DITA Specification Sheet. Pollutant Emission Factor Basis Emission Factor

Engine rate is based on EPA Region 4 Permit No. OCS-EPA-R4005-M1.

Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon )

. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar C9 DITA ( Emergency Electrical Generator Diesel Engine #3) EPN: SB-GE-03 Greenhouse Gases

Operating time for this engine is conservatively assumed to be 1.0 hrs/day, 100.0 hrs/year. Operating Load is assumed to be 100% based on expected operating condition. Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion

sources. Emission factor is based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 is used to calculate emissions. Emission factors are based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate

e mi ss i o n s.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 93	of	192 SB‐GE‐03	‐	GHGEngine Rating [1],[4] = 354 kW 475 HP Operating Time [2] = 24 hrs/day 4,800 hrs/year Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM EPA Tier II [4] 0.20 g/kW-hr 0.16 3.75 0.37 PM 10 EPA Tier II, AP -42 [4],[5] 0.20 g/kW-hr 0.16 3.75 0.37 PM 2.5 EPA Tier II, AP -42 [4],[5] 0.20 g/kW-hr 0.16 3.75 0.37 NO x EPA Tier II [4] 6.40 g/kW-hr 5.00 119.95 11.99 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 8.76E-06 2.10E-04 2.10E-05 CO EPA Tier II [4] 3.50 g/kW-hr 2.73 65.60 6.56 VOC AP-42 [6],[7] 2.51E-03 g/kW-hr 1.96E-03 4.71E-02 4.71E-03

Pb EPA [8] 2.03E-07 lb/HP-hr 1.59E-07 3.80E-06 3.80E-07 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 2.74E-07 6.57E-06 6.57E-07

[1]

[2]

[3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Emission Calculations

Cummins QSX15-G9 NR2 ( ROV Electric Generator Diesel Engine #4) EPN: SB-GE-04 Criteria Pollutants and Sulfuric Acid

Pollutant Emission Factor Basis Emission Factor

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors.

Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumpti on (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Data obtained from engine specification sheet provided by Ms. Katie Maness (Anadarko) via email to Mr. Bill Bruscino (Trinity) on 11/13/2012. ROV electric generator engine will be used up to 24 hour per day. Information provided by Ms. Katie Maness (Anadarko) on 11/12/12. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on Engine Specification for Cummins QSX15-G9 NR 2, this engine is a non-road Tier 2 engine. 40 CFR 89.112(a) Table 1 Emission Standards. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, all PM is assumed to be < 1 μ m. Therefore, it is assumed PM 2.5 = PM 10 = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 94	of	192 SB‐GE‐04	‐	CriteriaEngine Rating [1] = 354 kW 475 HP Operating Time [2] = 24 hrs/day 4,800 hrs/year Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 2.55E-03 6.12E-02 6.12E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 3.08E-04 7.38E-03 7.38E-04 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 3.10E-03 7.45E-02 7.45E-03 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 3.92E-03 9.42E-02 9.42E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 1.36E-03 3.26E-02 3.26E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 9.48E-04 2.27E-02 2.27E-03 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 5.59E-04 1.34E-02 1.34E-03 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 1.30E-04 3.12E-03 3.12E-04 Naphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 2.82E-04 6.77E-03 6.77E-04 0.01 0.31 0.03

[1]

[2]

[3]

[4] [5] Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. 

## Anadarko Petroleum Corporation Emission Calculations

Cummins QSX15-G9 NR2 ( ROV Electric Generator Diesel Engine #4) EPN: SB-GE-04 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Data obtained from engine specification sheet provided by Ms. Katie Maness (Anadarko) via email to Mr. Bill Bruscino (Trinity) on 11/13/2012. ROV electric generator engine will be used up to 24 hour per day. Information provided by Ms. Katie Maness (Anadarko) on 11/12/12. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 95	of	192 SB‐GE‐04	‐	HAP

### Engine Rating [1],[4] = 354 kW 475 HP Operating Time [2] = 24 hrs/day 4,800 hrs/year Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 542.15 13011.68 1301.17

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 2.20E-02 0.53 5.28E-02

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 4.40E-03 0.11 1.06E-02

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 543.98 13055.49 1305.55

[1]

[2]

[3]

[4]

[5] [6]

[7] Pollutant Emission Factor Basis Emission Factor 

## Anadarko Petroleum Corporation Emission Calculations

Cummins QSX15-G9 NR2 ( ROV Electric Generator Diesel Engine #4) EPN: SB-GE-04 Greenhouse Gases

Per 40 CFR 80.510(b), Anadarko proposes the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Data obtained from engine specification sheet provided by Ms. Katie Maness (Anadarko) via email to Mr. Bill Bruscino (Trinity) on 11/13/2012. ROV electric generator engine will be used up to 24 hour per day. Information provided by Ms. Katie Maness (Anadarko) on 11/12/12. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 96	of	192 SB‐GE‐04	‐	GHGEngine Rating [1],[4] = 268 kW 360 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD Number of Engines = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 1.58 38.02 3.80 PM 10 AP-42 [4],[5] 2.20E-03 lb/HP-hr 1.58 38.02 3.80 PM 2.5 AP-42 [4],[5] 2.20E-03 lb/HP-hr 1.58 38.02 3.80 NO x AP-42 [5] 3.10E-02 lb/HP-hr 22.32 535.68 53.57 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 8.08E-03 1.94E-01 1.94E-02 CO AP-42 [5] 6.68E-03 lb/HP-hr 4.81 115.43 11.54 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 1.81 43.40 4.34

Pb EPA [6] 2.03E-07 lb/HP-hr 1.46E-04 3.51E-03 3.51E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 2.52E-04 6.05E-03 6.05E-04

[1]

[2] [3]

[4]

[5]

[6]

[7] Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Representative high capacity compressor to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 = PM 10 = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Third Party Engine #6 and #7

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-01 and SB-TP-02

Criteria Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 97	of	192 SB‐TP‐01	and	SB‐TP‐02	Criteria

### Engine Rating [1] = 268 kW 360 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD Number of Engines = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 3.87E-03 9.28E-02 9.28E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 4.66E-04 1.12E-02 1.12E-03 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 4.70E-03 0.11 0.01 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 5.95E-03 0.14 0.01 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 2.06E-03 0.05 4.95E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 1.44E-03 0.03 3.45E-03 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 8.47E-04 0.02 2.03E-03 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 1.97E-04 4.73E-03 4.73E-04 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 4.27E-04 1.03E-02 1.03E-03 Total VOC HAPs 0.02 0.47 0.05

[1]

[2] [3]

[4] [5] Representative high capacity compressor to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day . Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Third Party Engine #6 and #7

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-01 and SB-TP-02

HAP

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 98	of	192 SB‐TP‐01	and	SB‐TP‐02	HAP

### Engine Rating [1] = 268 kW 360 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD Number of Engines = 2

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 73.96 kg/MMBtu 822 19,723 1,972.30 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 3.33E-02 0.80 8.00E-02 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 6.67E-03 0.16 1.60E-02 CO 2 

### e EPA [6] -- -- 825 19,789 1,978.94

[1]

[2] [3]

[4]

[5]

[6]

[7] Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Representative high capacity compressor to be used for Well evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Third Party Engine #6 and #7

Note: Potential to Emit is limited by proposed supply boat wide fuel consumption limit of 200 bbl/day. Refer to fuel based consumption factor sheet for details.

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-01 and SB-TP-02

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 99	of	192 SB‐TP‐01	and	SB‐TP‐02	GHG

### Engine Rating [1],[4] = 46 kW 62 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.14 3.27 0.33 PM 10 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.14 3.27 0.33 PM 2.5 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.14 3.27 0.33 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 1.92 46.13 4.61 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 6.95E-04 1.67E-02 1.67E-03 CO AP-42 [5] 6.68E-03 lb/HP-hr 0.41 9.94 0.99 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.16 3.74 0.37

Pb EPA [6] 2.03E-07 lb/HP-hr 1.26E-05 3.02E-04 3.02E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 2.17E-05 5.21E-04 5.21E-05

[1]

[2] [3]

[4]

[5]

[6]

[7] Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions fromSources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oilfired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Representative engine crane to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Crane Motor Engine #1

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-03

Criteria Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 100	of	192 SB‐TP‐03	‐	Criteria

### Engine Rating [1] = 46 kW 62 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 3.33E-04 7.99E-03 7.99E-04

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 4.01E-05 9.63E-04 9.63E-05 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 4.05E-04 9.72E-03 9.72E-04 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 5.12E-04 1.23E-02 1.23E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 1.78E-04 4.26E-03 4.26E-04 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 1.24E-04 2.97E-03 2.97E-04 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 7.29E-05 1.75E-03 1.75E-04 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 1.70E-05 4.07E-04 4.07E-05 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 3.68E-05 8.83E-04 8.83E-05 Total VOC HAPs 1.68E-03 4.03E-02 4.03E-03

[1]

[2] [3]

[4]

[5] Representative engine crane to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day . Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Crane Motor Engine #1

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-03

HAP

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 101	of	192 SB‐TP‐03	‐	HAP

### Engine Rating [1] = 46 kW 62 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 71 1,698 170 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 2.87E-03 6.89E-02 6.89E-03 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 5.74E-04 1.38E-02 1.38E-03 CO 2 

### e EPA [6] -- -- 71 1,704 170

[1]

[2] [3]

[4]

[5]

[6]

[7] Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Representative engine crane to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Crane Motor Engine #1

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-03

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 102	of	192 SB‐TP‐03	‐	GHG

### Engine Rating [1],[4] = 97 kW 130 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.29 6.86 0.69 PM 10 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.29 6.86 0.69 PM 2.5 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.29 6.86 0.69 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 4.03 96.72 9.67 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 1.46E-03 3.50E-02 3.50E-03 CO AP-42 [5] 6.68E-03 lb/HP-hr 0.87 20.84 2.08 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.33 7.84 0.78

Pb EPA [6] 2.03E-07 lb/HP-hr 2.64E-05 6.33E-04 6.33E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 4.55E-05 1.09E-03 1.09E-04

[1]

[2] [3]

[4]

[5]

[6]

[7] All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Representative engine crane to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day at 100% Operating Load. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. Anaverage brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hphr. 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Crane Motor Engine #2

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-04

Criteria Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 103	of	192 SB‐TP‐04	‐	Criteria

### Engine Rating [1] = 97 kW 130 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 6.98E-04 1.68E-02 1.68E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 8.42E-05 2.02E-03 2.02E-04 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 8.49E-04 2.04E-02 2.04E-03 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 1.07E-03 2.58E-02 2.58E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 3.72E-04 8.93E-03 8.93E-04 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 2.59E-04 6.22E-03 6.22E-04 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 1.53E-04 3.67E-03 3.67E-04 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 3.56E-05 8.54E-04 8.54E-05 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 7.72E-05 1.85E-03 1.85E-04 Total VOC HAPs 3.52E-03 8.46E-02 8.46E-03

[1]

[2] [3]

[4]

[5] Representative engine crane to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Crane Motor Engine #2

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-04

HAP Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 104	of	192 SB‐TP‐04	‐	HAP

### Engine Rating [1] = 97 kW 130 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 148 3,561 356 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 6.02E-03 1.44E-01 1.44E-02 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 1.20E-03 2.89E-02 2.89E-03 CO 2 

### e EPA [6] -- -- 149 3,573 357

[1]

[2] [3]

[4]

[5] [6]

[7] Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Representative engine crane to be used for Well Evaluation activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on April 18, 2013. Assumptions: Max operating time of 24 hr/day . Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.
CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Well Evaluation Crane Motor Engine #2

Pollutant Emission Factor Basis Emission Factor 

## SB-TP-04

GHG Pollutants

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 105	of	192 SB‐TP‐04	‐	GHG

### Engine Rating [1] = 5,650 kW 7,570 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 5.30 127.18 12.72 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 3.04 72.87 7.29 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 2.95 70.71 7.07 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 181.68 4,360.32 436.03 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.08 2.04 0.20 CO AP-42 [5] 5.50E-03 lb/HP-hr 41.64 999.24 99.92 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 4.86 116.56 11.66

Pb EPA [6] 2.03E-07 lb/HP-hr 1.54E-03 3.69E-02 3.69E-03 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 2.65E-03 6.37E-02 6.37E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-firedgas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.
Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.
PM 10 

### and PM 2.5 

### emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 

### . Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3616, (Main Engine 1) AB-ME-01 Criteria Pollutants and Sulfuric Acid

Pollutant Emission Factor Basis Emission Factor Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 106	of	192 Anchor	Boat	(Engine	1)	‐	Criter

### Engine Rating [1] = 5,650 kW 7,570 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 1.34E-03 3.20E-02 3.20E-03

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 4.18E-04 1.00E-02 1.00E-03 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 4.11E-02 0.99 0.10 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 4.18E-03 0.10 0.01 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 1.49E-02 0.36 0.04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.02E-02 0.25 0.02 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.12E-02 0.27 0.03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 6.89E-03 0.17 0.02 0.08 2.00 0.20

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Anchor Handling boats. Total VOC HAPs

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3616, (Main Engine 1) AB-ME-01 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 107	of	192 Anchor	Boat	(Engine	1)	‐	HAP

### Engine Rating [1] = 5,650 kW 7,570 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 73.96 kg/MMBtu 8,640 207,365 20,737

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.35 8.41 0.84

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.07 1.68 0.17

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 8,669 208,063 20,806

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3616, (Main Engine 1) AB-ME-01 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 108	of	192 Anchor	Boat	(Engine	1)	‐	GHG

### Engine Rating [1] = 5,650 kW 7,570 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [4] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 5.30 127.18 12.72 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 3.04 72.87 7.29 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 2.95 70.71 7.07 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 181.68 4,360.32 436.03 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.08 2.04 0.20 CO AP-42 [5] 5.50E-03 lb/HP-hr 41.64 999.24 99.92 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 4.86 116.56 11.66

Pb EPA [6] 2.03E-07 lb/HP-hr 1.54E-03 3.69E-02 3.69E-03 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 2.65E-03 6.37E-02 6.37E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizingEmission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3616, (Main Engine 2) AB-ME-02 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 109	of	192 Anchor	Boat	(Engine	2)	‐	Criter

### Engine Rating [1] = 5,650 kW 7,570 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 1.34E-03 3.20E-02 3.20E-03

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 4.18E-04 0.01 0.00 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 4.11E-02 0.99 0.10 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 4.18E-03 0.10 0.01 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 1.49E-02 0.36 0.04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.02E-02 0.25 0.02 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.12E-02 0.27 0.03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 6.89E-03 0.17 0.02 Total VOC HAPs 0.08 2.00 0.20

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3616, (Main Engine 2) AB-ME-02 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 110	of	192 Anchor	Boat	(Engine	2)	‐	HAP

### Engine Rating [1] = 5,650 kW 7,570 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 8,640 207,365 20,737

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.35 8.41 0.84

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.07 1.68 0.17

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 8,669 208,063 20,806

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3616, (Main Engine 2) AB-ME-02 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 111	of	192 Anchor	Boat	(Engine	2)	‐	GHG

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 1.17 28.12 2.81 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.67 16.11 1.61 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.65 15.64 1.56 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 40.18 964.22 96.42 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.45 0.05 CO AP-42 [5] 5.50E-03 lb/HP-hr 9.21 220.97 22.10 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 1.07 25.77 2.58

Pb EPA [6] 2.03E-07 lb/HP-hr 3.40E-04 8.16E-03 8.16E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 5.87E-04 1.41E-02 1.41E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizingEmission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Bow Tunnel Thruster) AB-TE-01 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 112	of	192 Anchor	Boat	(Bow	Tunn)	‐	Crite

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.95E-04 7.09E-03 7.09E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 9.23E-05 2.22E-03 2.22E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 9.09E-03 2.18E-01 2.18E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 9.25E-04 2.22E-02 2.22E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 3.29E-03 7.90E-02 7.90E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.26E-03 5.43E-02 5.43E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 2.48E-03 5.96E-02 5.96E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.52E-03 3.66E-02 3.66E-03 Total VOC HAPs 0.02 0.44 0.04

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Bow Tunnel Thruster) AB-TE-01 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 113	of	192 Anchor	Boat	(Bow	Tunn)	‐	HAP

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,911 45,856 4,586

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.08 1.86 0.19

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.02 0.37 0.04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,917 46,010 4,601

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. Global warming potentials (GWP) for CH 4 

### , CO 2 

### and N 2 

### O are used to calculate CO 2 

### equivalent (CO 2 

### e). The GWPs are obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3512D-HD, (Bow Tunnel Thruster) AB-TE-01 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 114	of	192 Anchor	Boat	(Bow	Tunn)	‐	GHG

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [4] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 1.17 28.12 2.81 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.67 16.11 1.61 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.65 15.64 1.56 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 40.18 964.22 96.42 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.45 0.045 CO AP-42 [5] 5.50E-03 lb/HP-hr 9.21 220.97 22.10 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 1.07 25.77 2.58

Pb EPA [6] 2.03E-07 lb/HP-hr 3.40E-04 8.16E-03 8.16E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 5.87E-04 1.41E-02 1.41E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-firedgas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.
PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Aft Tunnel Thruster) AB-TE-02 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 115	of	192 Anchor	Boat	(Aft	Tunn)	‐	Criter

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.95E-04 7.09E-03 7.09E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 9.23E-05 2.22E-03 2.22E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 9.09E-03 2.18E-01 2.18E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 9.25E-04 2.22E-02 2.22E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 3.29E-03 7.90E-02 7.90E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.26E-03 5.43E-02 5.43E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 2.48E-03 5.96E-02 5.96E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.52E-03 3.66E-02 3.66E-03 Total VOC HAPs 0.02 0.44 0.04

[1] [2] [3]

[4]

[5]

[6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Aft Tunnel Thruster) AB-TE-02 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 116	of	192 Anchor	Boat	(Aft	Tunn)	‐	HAP

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,910.66 45,855.92 4,585.59

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.08 1.86 0.19

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.02 0.37 0.04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,917.10 46,010.30 4,601.03

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Aft Tunnel Thruster) AB-TE-02 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 117	of	192 Anchor	Boat	(Aft	Tunn)	‐	GHG

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 1.17 28.12 2.81 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.67 16.11 1.61 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.65 15.64 1.56 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 40.18 964.22 96.42 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.45 0.045 CO AP-42 [5] 5.50E-03 lb/HP-hr 9.21 220.97 22.10 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 1.07 25.77 2.58

Pb EPA [6] 2.03E-07 lb/HP-hr 3.40E-04 8.16E-03 8.16E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 5.87E-04 1.41E-02 1.41E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-firedgas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Bow Drop Down Thruster) AB-TE-03 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 118	of	192 Anchor	Boat	(Bow	Drop)	‐	Criter

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.95E-04 7.09E-03 7.09E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 9.23E-05 2.22E-03 2.22E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 9.09E-03 2.18E-01 2.18E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 9.25E-04 2.22E-02 2.22E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 3.29E-03 7.90E-02 7.90E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.26E-03 5.43E-02 5.43E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 2.48E-03 5.96E-02 5.96E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.52E-03 3.66E-02 3.66E-03 Total VOC HAPs 0.02 0.44 0.04

[1] [2] [3]

[4]

[5]

[6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Bow Drop Down Thruster) AB-TE-03 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 119	of	192 Anchor	Boat	(Bow	Drop)	‐	HAP

### Engine Rating [1] = 1,248 kW 1,674 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,910.66 45,855.92 4,585.59

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.08 1.86 0.19

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.02 0.37 0.04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,917.10 46,010.30 4,601.03

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3512B-HD, (Bow Drop Down Thruster) AB-TE-03 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 120	of	192 Anchor	Boat	(Bow	Drop)	‐	GHG

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 0.50 12.03 1.20 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.29 6.89 0.69 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.28 6.69 0.67 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 17.18 412.42 41.24 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.19 0.019 CO AP-42 [5] 5.50E-03 lb/HP-hr 3.94 94.51 9.45 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.46 11.02 1.10

Pb EPA [6] 2.03E-07 lb/HP-hr 1.45E-04 3.49E-03 3.49E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 2.51E-04 6.02E-03 6.02E-04

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emissionfactors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hphr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable p articulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3412C, (Service Generator Engine 1) AB-GE-01 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 121	of	192 Anchor	Boat	(S.	Gen	1)	‐	Criter

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 1.26E-04 3.03E-03 3.03E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 3.95E-05 9.48E-04 9.48E-05 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 3.89E-03 9.33E-02 9.33E-03 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 3.95E-04 9.49E-03 9.49E-04 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 1.41E-03 3.38E-02 3.38E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 9.67E-04 2.32E-02 2.32E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.06E-03 2.55E-02 2.55E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 6.52E-04 1.56E-02 1.56E-03 Total VOC HAPs 7.89E-03 1.89E-01 1.89E-02

[1] [2] [3]

[4]

[5]
[6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3412C, (Service Generator Engine 1) AB-GE-01 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 122	of	192 Anchor	Boat	(S.	Gen	1)	‐	HAP

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 817.23 19,613.40 1,961.34

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.03 0.80 0.08

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.16 0.02

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 819.98 19,679.44 1,967.94

[1] [2] [3]

[4]

[5] [6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3412C, (Service Generator Engine 1) AB-GE-01 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 123	of	192 Anchor	Boat	(S.	Gen	1)	‐	GHG

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 0.50 12.03 1.20 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.29 6.89 0.69 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.28 6.69 0.67 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 17.18 412.42 41.24 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.19 0.019 CO AP-42 [5] 5.50E-03 lb/HP-hr 3.94 94.51 9.45 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.46 11.02 1.10

Pb EPA [6] 2.03E-07 lb/HP-hr 1.45E-04 3.49E-03 3.49E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 2.51E-04 6.02E-03 6.02E-04

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizingEmission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable p articulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3412C, (Service Generator Engine 2) AB-GE-02 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 124	of	192 Anchor	Boat	(S.	Gen	2)	‐	Criter

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 1.26E-04 3.03E-03 3.03E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 3.95E-05 9.48E-04 9.48E-05 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 3.89E-03 9.33E-02 9.33E-03 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 3.95E-04 9.49E-03 9.49E-04 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 1.41E-03 3.38E-02 3.38E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 9.67E-04 2.32E-02 2.32E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.06E-03 2.55E-02 2.55E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 6.52E-04 1.56E-02 1.56E-03 Total VOC HAPs 7.89E-03 1.89E-01 1.89E-02

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3412C, (Service Generator Engine 2) AB-GE-02 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 125	of	192 Anchor	Boat	(S.	Gen	2)	‐	HAP

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 817.23 19,613.40 1,961.34

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.03 0.80 0.08

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.16 0.02

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 819.98 19,679.44 1,967.94

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.
CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3412C, (Service Generator Engine 2) AB-GE-02 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 126	of	192 Anchor	Boat	(S.	Gen	2)	‐	GHG

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 0.50 12.03 1.20 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.29 6.89 0.69 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.28 6.69 0.67 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 17.18 412.42 41.24 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.19 0.019 CO AP-42 [5] 5.50E-03 lb/HP-hr 3.94 94.51 9.45 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.46 11.02 1.10

Pb EPA [6] 2.03E-07 lb/HP-hr 1.45E-04 3.49E-03 3.49E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 2.51E-04 6.02E-03 6.02E-04

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizingEmission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3412C, (Service Generator Engine 3) AB-GE-03 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 127	of	192 Anchor	Boat	(S.	Gen	3)	‐	Criter

### Engine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 1.26E-04 3.03E-03 3.03E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 3.95E-05 9.48E-04 9.48E-05 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 3.89E-03 9.33E-02 9.33E-03 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 3.95E-04 9.49E-03 9.49E-04 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 1.41E-03 3.38E-02 3.38E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 9.67E-04 2.32E-02 2.32E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.06E-03 2.55E-02 2.55E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 6.52E-04 1.56E-02 1.56E-03 Total VOC HAPs 7.89E-03 1.89E-01 1.89E-02

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3412C, (Service Generator Engine 3) AB-GE-03 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 128	of	192 Anchor	Boat	(S.	Gen	3)	‐	HAPEngine Rating [1] = 534 kW 716 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 817.23 19,613.40 1,961.34

CH 4 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.03 0.80 0.08

N 2 O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.16 0.02

CO 2 e 40 CFR 98 Subpart C [6] -- -- 819.98 19,679.44 1,967.94

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 and N 2 O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 , CO 2 and N 2 Oare included in the emissions of CO 2 equivalent (CO 2 e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3412C, (Service Generator Engine 3) AB-GE-03 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restr icted to proposed supply boat fuel limitations for all scenarios.

Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 129	of	192 Anchor	Boat	(S.	Gen	3)	‐	GHG

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 0.91 21.84 2.18 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.52 12.51 1.25 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.51 12.14 1.21 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 31.20 748.80 74.88 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.35 0.035 CO AP-42 [5] 5.50E-03 lb/HP-hr 7.15 171.60 17.16 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.83 20.02 2.00

Pb EPA [6] 2.03E-07 lb/HP-hr 2.64E-04 6.33E-03 6.33E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 4.55E-04 1.09E-02 1.09E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable p articulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3508B, (Service Generator Engine 4) AB-GE-04 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 130	of	192 Anchor	Boat	(S.	Gen	4)	‐	Criter

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.29E-04 5.50E-03 5.50E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 7.17E-05 1.72E-03 1.72E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 7.06E-03 1.69E-01 1.69E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 7.18E-04 1.72E-02 1.72E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 2.56E-03 6.14E-02 6.14E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.76E-03 4.22E-02 4.22E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.93E-03 4.63E-02 4.63E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.18E-03 2.84E-02 2.84E-03 Total VOC HAPs 0.01 0.34 0.03

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3508B, (Service Generator Engine 4) AB-GE-04 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 131	of	192 Anchor	Boat	(S.	Gen	4)	‐	HAP

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,483.79 35,610.93 3,561.09

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.06 1.44 0.14

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.29 0.03

CO 2 

### e 40 C FR 98 Subpart C [6] -- -- 1,488.78 35,730.82 3,573.08

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3508B, (Service Generator Engine 4) AB-GE-04 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 132	of	192 Anchor	Boat	(S.	Gen	4)	‐	GHG

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 0.91 21.84 2.18 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.52 12.51 1.25 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.51 12.14 1.21 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 31.20 748.80 74.88 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.35 0.035 CO AP-42 [5] 5.50E-03 lb/HP-hr 7.15 171.60 17.16 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.83 20.02 2.00

Pb EPA [6] 2.03E-07 lb/HP-hr 2.64E-04 6.33E-03 6.33E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 4.55E-04 1.09E-02 1.09E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gasturbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3508B, (Service Generator Engine 5) AB-GE-05 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 133	of	192 Anchor	Boat	(S.	Gen	5)	‐	Criter

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.29E-04 5.50E-03 5.50E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 7.17E-05 1.72E-03 1.72E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 7.06E-03 1.69E-01 1.69E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 7.18E-04 1.72E-02 1.72E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 2.56E-03 6.14E-02 6.14E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.76E-03 4.22E-02 4.22E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.93E-03 4.63E-02 4.63E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.18E-03 2.84E-02 2.84E-03 0.01 0.34 0.03

[1] [2] [3]

[4]

[5]

[6] ULSD is proposed as fuel for the Anchor Handling boats. Total VOC HAPs

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996).An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hphr to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3508B, (Service Generator Engine 5) AB-GE-05 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 134	of	192 Anchor	Boat	(S.	Gen	5)	‐	HAP

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,483.79 35,610.93 3,561.09

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.06 1.44 0.14

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.29 0.03

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,488.78 35,730.82 3,573.08

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3508B, (Service Generator Engine 5) AB-GE-05 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis 

### Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 135	of	192 Anchor	Boat	(S.	Gen	5)	‐	GHG

### Engine Rating [1] = 229 kW 307 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.68 0.68 0.03 PM 10 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.68 0.68 0.03 PM 2.5 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.68 0.68 0.03 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 9.52 9.52 0.48 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 3.44E-03 3.44E-03 1.72E-04 CO AP-42 [5] 6.68E-03 lb/HP-hr 2.05 2.05 0.10 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.77 0.77 0.04

Pb EPA [6] 2.03E-07 lb/HP-hr 6.23E-05 6.23E-05 3.12E-06 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 1.08E-04 1.08E-04 5.38E-06

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-firedgas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 100 hrs/year. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM2.5 = PM10 = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used. 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model 3406C, (Emergency Generator) AB-GE-06 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 136	of	192 Anchor	Boat	(Emer	Gen)	‐	Criter

### Engine Rating [1] = 229 kW 307 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [4],[5] 7.67E-04 lb/MMBtu 1.65E-03 1.65E-03 8.24E-05

Acrolein AP-42 [4],[5] 9.25E-05 lb/MMBtu 1.99E-04 1.99E-04 9.94E-06 Benzene AP-42 [4],[5] 9.33E-04 lb/MMBtu 2.01E-03 2.01E-03 1.00E-04 Formaldehyde AP-42 [4],[5] 1.18E-03 lb/MMBtu 2.54E-03 2.54E-03 1.27E-04 Toluene AP-42 [4],[5] 4.09E-04 lb/MMBtu 8.79E-04 8.79E-04 4.39E-05 Xylenes AP-42 [4],[5] 2.85E-04 lb/MMBtu 6.12E-04 6.12E-04 3.06E-05 Total PAH AP-42 [4],[5] 1.68E-04 lb/MMBtu 3.61E-04 3.61E-04 1.81E-05 1,3-Butadiene AP-42 [4],[5] 3.91E-05 lb/MMBtu 8.40E-05 8.40E-05 4.20E-06 N aphthalene AP-42 [4],[5] 8.48E-05 lb/MMBtu 1.82E-04 1.82E-04 9.11E-06 8.32E-03 8.32E-03 4.16E-04

[1] [2] [3]

[4]

[5] ULSD is proposed as fuel for the Anchor Handling boats. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3406C, (Emergency Generator) AB-GE-06 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Total VOC HAPs

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 100 hrs/year. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 137	of	192 Anchor	Boat	(Emer	Gen)	‐	HAP

### Engine Rating [1] = 229 kW 307 HP Operating Time [2] = 1 hrs/day 100 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 350.40 350.40 17.52

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 1.42E-02 1.42E-02 7.11E-04

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 2.84E-03 2.84E-03 1.42E-04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 351.58 351.58 17.58

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 100 hrs/year. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model 3406C, (Emergency Generator) AB-GE-06 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 138	of	192 Anchor	Boat	(Emer	Gen)	‐	GHG

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 0.91 21.84 2.18 PM 10 

### AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.52 12.51 1.25 PM 2.5 

### AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.51 12.14 1.21 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 31.20 748.80 74.88 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.35 0.035 CO AP-42 [5] 5.50E-03 lb/HP-hr 7.15 171.60 17.16 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.83 20.02 2.00

Pb EPA [6] 2.03E-07 lb/HP-hr 2.64E-04 6.33E-03 6.33E-04 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 4.55E-04 1.09E-02 1.09E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emissionfactors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hphr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.
PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model C32, (Port Winch Hydraulic Engine) AB-GE-07 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 139	of	192 Anchor	Boat	(Port	Winch)	‐	Crit

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.29E-04 5.50E-03 5.50E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 7.17E-05 1.72E-03 1.72E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 7.06E-03 1.69E-01 1.69E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 7.18E-04 1.72E-02 1.72E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 2.56E-03 6.14E-02 6.14E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.76E-03 4.22E-02 4.22E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.93E-03 4.63E-02 4.63E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.18E-03 2.84E-02 2.84E-03 0.01 0.34 0.03

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Anchor Handling boats. Total VOC HAPs

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model C32, (Port Winch Hydraulic Engine) AB-GE-07 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 140	of	192 Anchor	Boat	(Port	Winch)	‐	HAP

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,483.79 35,610.93 3,561.09

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.06 1.44 0.14

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.29 0.03

CO 2 

### e 40 C FR 98 Subpart C [6] -- -- 1,488.78 35,730.82 3,573.08

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hphr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100- year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model C32, (Port Winch Hydraulic Engine) AB-GE-07 Greenhouse Gases

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 141	of	192 Anchor	Boat	(Port	Winch)	‐	GHGEngine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 7.00E-04 lb/HP-hr 0.91 21.84 2.18 PM 10 AP-42 [4],[5] 4.01E-04 lb/HP-hr 0.52 12.51 1.25 PM 2.5 AP-42 [4],[5] 3.89E-04 lb/HP-hr 0.51 12.14 1.21 NO x AP-42 [5] 2.40E-02 lb/HP-hr 31.20 748.80 74.88 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.01 0.35 0.035 CO AP-42 [5] 5.50E-03 lb/HP-hr 7.15 171.60 17.16 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.83 20.02 2.00

Pb EPA [6] 2.03E-07 lb/HP-hr 2.64E-04 6.33E-03 6.33E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 4.55E-04 1.09E-02 1.09E-03

[1] [2] [3]

[4]

[5]

[6]

[7] Lead emission factor obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM10 and PM2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (Brake Specific Fuel Consumption (BFSC)) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM2.5. Total particulate emissions is the sum of filterable and condensable particulate emissions.

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model C32, (Starboard Winch Hydraulic Engine) AB-GE-08 Criteria Pollutants and Sulfuric Acid

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restr icted to proposed supply boat fuel limitations for all scenarios.

Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 142	of	192 Anchor	Boat	(Star	Winch)	‐	Cri t

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.29E-04 5.50E-03 5.50E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 7.17E-05 1.72E-03 1.72E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 7.06E-03 1.69E-01 1.69E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 7.18E-04 1.72E-02 1.72E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 2.56E-03 6.14E-02 6.14E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.76E-03 4.22E-02 4.22E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.93E-03 4.63E-02 4.63E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.18E-03 2.84E-02 2.84E-03 0.01 0.34 0.03

[1] [2] [3]

[4]

[5]

[6] ULSD is proposed as fuel for the Anchor Handling boats. Total VOC HAPs

Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. 

## Anadarko Petroleum Corporation Emission Calculations
Caterpillar Model C32, (Starboard Winch Hydraulic Engine) AB-GE-08 Hazardous Air Pollutants

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 143	of	192 Anchor	Boat	(Star	Winch)	‐	HAP

### Engine Rating [1] = 968 kW 1,300 HP Operating Time [2] = 24 hrs/day 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,483.79 35,610.93 3,561.09

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.06 1.44 0.14

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.29 0.03

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,488.78 35,730.82 3,573.08

[1] [2] [3]

[4]

[5]

[6]

[7] ULSD is proposed as fuel for the Anchor Handling boats. Based on the engine specification sheet provided in Appendix G-3. Operating time for this engine has been assumed to be 24 hrs/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average Brake Specific Fuel Consumption (BFSC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### Oare included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon). 

## Anadarko Petroleum Corporation Emission Calculations

Caterpillar Model C32, (Starboard Winch Hydraulic Engine)

Note: The table below represents the potential to emit from this source. However, emissions from the anchor handling boats are restricted to proposed supply boat fuel limitations for all scenarios.



### Pollutant Emission Factor Basis Emission Factor 

### AB-GE-08

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 144	of	192 Anchor	Boat	(Star	Winch)	‐	GHGEngine Rating [1], [4] = 2,710 kW 3,634 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 40 CFR 94.8(a)(2)(i)) [4], [5] 0.50 g/kW-hr 0.75 17.92 0.19 PM 10 40 CFR 94.8(a)(2)(i)) [4], [5] 0.29 g/kW-hr 0.43 10.27 0.11 PM 2.5 40 CFR 94.8(a)(2)(i)) [4], [5] 0.28 g/kW-hr 0.42 9.97 0.10 NO x 40 CFR 94.8(a)(2)(i)) [4] 8.70 g/kW-hr 12.99 311.87 3.27 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 1.02E-02 2.45E-01 2.57E-03 CO 40 CFR 94.8(a)(2)(i)) [4] 5.00 g/kW-hr 7.47 179.24 1.88 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 0.58 13.99 0.15

Pb EPA [7] 2.03E-07 lb/HP-hr 1.84E-04 4.43E-03 4.65E-05 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 3.18E-04 7.64E-03 8.02E-05

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C280-8 (Main Engine) SV-ME-01 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Engine Specification Obtained from Caterpillar website for C280-8 Engine as a representative stimulation vessel main engine.

Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on Engine Specification obtained from Manufacturer's website for C280-8 Engine which is certified to IMO Tier II/EPA Marine Tier II (Table A-1 of 40 CFR 94.8(a)(2)(i)). Engine displacement is 148L as per engine specification. http://catoilandgas.cat.com/cda/files/2180159/7/C280-8%2050%20Hz%20LEHW0086-02%20P2.pdf PM 10 and PM 2.5 emission factors obtained by applying the ratio of PM/PM 10 and PM/PM 2.5 from AP-42 Chapter 3, Table 3.4-1 and Table 3.4-2 on EPA Tier II PM emission factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 145	of	192 Stimu	Vessel	(ME‐01)	‐	Crit

### Engine Rating [1] = 2,710 kW 3,634 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [6] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 1.60E-04 3.85E-03 4.04E-05

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 5.01E-05 1.20E-03 1.26E-05 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 4.93E-03 1.18E-01 1.24E-03 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 5.02E-04 1.20E-02 1.26E-04 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 1.79E-03 4.29E-02 4.50E-04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.23E-03 2.95E-02 3.09E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.35E-03 3.24E-02 3.40E-04 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 8.27E-04 1.98E-02 2.08E-04 Total VOC HAPs 0.01 0.24 2.52E-03

[1]

[2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Well Completion Activity. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C280 -08 (Main Engine) SV-ME-01 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Engine Specification Obtained from Caterpillar website for C280-8 Engine as a representative stimulation vessel main engine. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 146	of	192 Stimu	Vessel	(ME‐01)	‐	HAP

### Engine Rating [1] = 2,710 kW 3,634 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [7] = ULSD Operating load [2] = 25%

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,036.94 24,886.56 261.31

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 4.21E-02 1.01 0.01

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 8.41E-03 0.20 2.12E-03

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,040.43 24,970.34 262.19

[1]

[2]

[3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C280-8 (Main Engine) SV-ME-01 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Engine Specification Obtained from Caterpillar website for C280-8 Engine as a representative stimulation vessel main engine. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012.

Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 147	of	192 Stimu	Vessel	(ME‐01)	‐	GHGEngine Rating [1], [4] = 2,710 kW 3,634 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 40 CFR 94.8(a)(2)(i)) [4], [5] 0.50 g/kW-hr 0.75 17.92 0.19 PM 10 40 CFR 94.8(a)(2)(i)) [4], [5] 0.29 g/kW-hr 0.43 10.27 0.11 PM 2.5 40 CFR 94.8(a)(2)(i)) [4], [5] 0.28 g/kW-hr 0.42 9.97 0.10 NO x 40 CFR 94.8(a)(2)(i)) [4] 8.70 g/kW-hr 12.99 311.87 3.27 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 1.02E-02 0.24 2.57E-03 CO 40 CFR 94.8(a)(2)(i)) [4] 5.00 g/kW-hr 7.47 179.24 1.88 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 0.58 13.99 0.15

Pb EPA [7] 2.03E-07 lb/HP-hr 1.84E-04 4.43E-03 4.65E-05 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 3.18E-04 7.64E-03 8.02E-05

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C280-8 (Main Engine) SV-ME-02 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Engine Specification Obtained from Caterpillar website for C280-8 Engine as a representative stimulation vessel main engine.

Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012. Anadarko is proposing the use of ULSD (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO2 and 2 percent of sulfur in the fuel is oxidized to H2SO4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on Engine Specification obtained from Manufacturer's website for C280-8 Engine which is certified to IMO Tier II/EPA Marine Tier II (Table A-1 of 40 CFR 94.8(a)(2)(i)). Engine displacement is 148L as per engine specification. http://catoilandgas.cat.com/cda/files/2180159/7/C280-8%2050%20Hz%20LEHW0086-02%20P2.pdf PM 10 and PM 2.5 emission factors obtained by applying the ratio of PM/PM 10 and PM/PM 2.5 from AP-42 Chapter 3, Table 3.4-1 and Table 3.4-2 on EPA Tier II PM emission factor

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 148	of	192 Stimu	Vessel	(ME‐02)	‐	Crit

### Engine Rating [1] = 2,710 kW 3,634 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [6] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 1.60E-04 3.85E-03 4.04E-05

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 5.01E-05 1.20E-03 1.26E-05 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 4.93E-03 1.18E-01 1.24E-03 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 5.02E-04 1.20E-02 1.26E-04 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 1.79E-03 4.29E-02 4.50E-04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 1.23E-03 2.95E-02 3.09E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 1.35E-03 3.24E-02 3.40E-04 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 8.27E-04 1.98E-02 2.08E-04 Total VOC HAPs 0.01 0.24 2.52E-03

[1]

[2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Well Completion Activity. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C280-8 (Main Engine) SV-ME-02 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Engine Specification Obtained from Caterpillar website for C280-8 Engine as a representative stimulation vessel main engine. Operating information provided by Ms. Sara Carlson (Anadarko) on October 22, 2012. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 149	of	192 Stimu	Vessel	(ME‐02)	‐	HAP

### Engine Rating [1] = 2,710 kW 3,634 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [7] = ULSD Operating load [2] = 25%

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,036.94 24,886.56 261.31

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.04 1.01 1.06E-02

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.01 0.20 2.12E-03

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 1,040.43 24,970.34 262.19

[1]

[2] [3]

[4]

[5] [6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Caterpillar C280-8 (Main Engine) SV-ME-02 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Engine Specification Obtained from Caterpillar website for C280-8 Engine as a representative stimulation vessel main engine. Operating information provided by Ms. Sara Carlson (Anadarko) on October 22, 2012. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 150	of	192 Stimu	Vessel	(ME‐02)	‐	GHG

### Engine Rating [1] = 1249 kW 1675 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4], [5] 7.00E-04 lb/HP-hr 0.29 7.04 0.07 PM 10 

### AP-42 [4], [5] 4.01E-04 lb/HP-hr 0.17 4.03 0.04 PM 2.5 

### AP-42 [4], [5] 3.89E-04 lb/HP-hr 0.16 3.91 0.04 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 10.05 241.20 2.53 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 4.70E-03 1.13E-01 1.18E-03 CO AP-42 [5] 5.50E-03 lb/HP-hr 2.30 55.28 0.58 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.27 6.45 0.07

Pb EPA [6] 2.03E-07 lb/HP-hr 8.50E-05 2.04E-03 2.14E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 1.47E-04 3.52E-03 3.70E-05

[1] [2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Bow Thruster SV-BT-01 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.

PM 10 

### and PM 2.5 

### emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 

### . Total particulate emissions is the sum of filterable and condensable particulate emissions. Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 151	of	192 Stimu	Vessel	(Bow	Thrus)	‐	Crit

### Engine Rating [1] = 1,249 kW 1,675 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [6] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 7.39E-05 1.77E-03 1.86E-05

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 2.31E-05 5.54E-04 5.82E-06 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 2.27E-03 5.46E-02 5.73E-04 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 2.31E-04 5.55E-03 5.83E-05 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 8.24E-04 1.98E-02 2.08E-04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 5.66E-04 1.36E-02 1.43E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 6.21E-04 1.49E-02 1.57E-04 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 3.81E-04 9.15E-03 9.60E-05 Total VOC HAPs 4.61E-03 1.11E-01 1.16E-03

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Well Completion Activity. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Bow Thruster SV-BT-01 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 152	of	192 Stimu	Vessel	(Bow	Thrus)	‐	HAP

### Engine Rating [1] = 1,249 kW 1,675 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [7] = ULSD Operating load [2] = 25%

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 477.95 11,470.83 120.44

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 1.94E-02 4.65E-01 4.89E-03

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 3.88E-03 9.31E-02 9.77E-04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 479.56 11,509.45 120.85

[1] [2]
[3]

[4]

[5] [6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Bow Thruster SV-BT-01 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012.
Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 153	of	192 Stimu	Vessel	(Bow	Thrus)	‐	GHG

### Engine Rating [1] = 895 kW 1,200 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4], [5] 7.00E-04 lb/HP-hr 0.21 5.04 0.05 PM 10 

### AP-42 [4], [5] 4.01E-04 lb/HP-hr 0.12 2.89 0.03 PM 2.5 

### AP-42 [4], [5] 3.89E-04 lb/HP-hr 0.12 2.80 0.03 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 7.20 172.80 1.81 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 3.36E-03 8.08E-02 8.48E-04 CO AP-42 [5] 5.50E-03 lb/HP-hr 1.65 39.60 0.42 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.19 4.62 0.05

Pb EPA [6] 2.03E-07 lb/HP-hr 6.09E-05 1.46E-03 1.53E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 1.05E-04 2.52E-03 2.65E-05

[1] [2]

[3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Bow Drop-Down SV-DD-01 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012.
Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM 10 

### and PM 2.5 

### emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 

### . Total particulate emissions is the sum of filterable and condensable particulate emissions.
Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 154	of	192 Stimu	Vessel	(Bow	Drop)	‐	Crit

### Engine Rating [1] = 895 kW 1,200 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [6] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 5.29E-05 1.27E-03 1.33E-05

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.65E-05 3.97E-04 4.17E-06 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 1.63E-03 3.91E-02 4.11E-04 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 1.66E-04 3.98E-03 4.18E-05 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 5.90E-04 1.42E-02 1.49E-04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 4.05E-04 9.73E-03 1.02E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 4.45E-04 1.07E-02 1.12E-04 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 2.73E-04 6.55E-03 6.88E-05 Total VOC HAPs 3.31E-03 7.93E-02 8.33E-04

[1] [2]

[3]

[4]

[5] [6] ULSD is proposed as fuel for the Well Completion Activity. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Bow Drop-Down SV-DD-01 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012.

Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 155	of	192 Stimu	Vessel	(Bow	Drop)	‐	HAP

### Engine Rating [1] = 895 kW 1,200 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [7] = ULSD Operating load [2] = 25%

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 342.41 8,217.91 86.29

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 1.39E-02 3.33E-01 3.50E-03

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 2.78E-03 6.67E-02 7.00E-04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 343.57 8,245.57 86.58

[1] [2] [3]

[4]

[5]
[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Bow Drop-Down SV-DD-01 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 156	of	192 Stimu	Vessel	(Bow	Drop)	‐	GHG

### Engine Rating [1] = 1,249 kW 1,675 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4], [5] 7.00E-04 lb/HP-hr 0.29 7.04 0.07 PM 10 

### AP-42 [4], [5] 4.01E-04 lb/HP-hr 0.17 4.03 0.04 PM 2.5 

### AP-42 [4], [5] 3.89E-04 lb/HP-hr 0.16 3.91 0.04 NO x 

### AP-42 [5] 2.40E-02 lb/HP-hr 10.05 241.20 2.53 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 4.70E-03 1.13E-01 1.18E-03 CO AP-42 [5] 5.50E-03 lb/HP-hr 2.30 55.28 0.58 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 0.27 6.45 0.07

Pb EPA [6] 2.03E-07 lb/HP-hr 8.50E-05 2.04E-03 2.14E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 1.47E-04 3.52E-03 3.70E-05

[1] [2]
[3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Stern Thruster SV-ST-01 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012.
Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008 , A p ril 2003. PM 10 

### and PM 2.5 

### emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 

### . Total particulate emissions is the sum of filterable and condensable particulate emissions.

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 157	of	192 Stimu	Vessel	(Stern	Thr)	‐	Crit

### Engine Rating [1] = 1,249 kW 1,675 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [6] = ULSD Operating load [2] = 25%

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 7.39E-05 1.77E-03 1.86E-05

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 2.31E-05 5.54E-04 5.82E-06 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 2.27E-03 5.46E-02 5.73E-04 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 2.31E-04 5.55E-03 5.83E-05 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 8.24E-04 1.98E-02 2.08E-04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 5.66E-04 1.36E-02 1.43E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 6.21E-04 1.49E-02 1.57E-04 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 3.81E-04 9.15E-03 9.60E-05 Total VOC HAPs 4.61E-03 1.11E-01 1.16E-03

[1] [2] [3]

[4]

[5] [6] ULSD is proposed as fuel for the Well Completion Activity. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Stern Thruster SV-ST-01 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Representative thrusters for the stimulation vessel. Operating information provided by Ms. Sara Carlson (Anadarko) on October 22, 2012. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 158	of	192 Stimu	Vessel	(Stern	Thr)	‐	HAP

### Engine Rating [1] = 1,249 kW 1,675 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [7] = ULSD Operating load [2] = 25%
Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 477.95 11,470.83 120.44

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 1.94E-02 4.65E-01 4.89E-03

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 3.88E-03 9.31E-02 9.77E-04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 479.56 11,509.45 120.85

[1] [2]

[3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Stern Thruster SV-ST-01 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Representative thrusters for the stimulation vessel. Operating information provided by Mr. Aaron Wade and Ms. Sara Carlson (Anadarko) on October 22, 2012.
Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 159	of	192 Stimu	Vessel	(Stern	Thr)	‐	GHGEngine Rating [1] = 1,678 kW 2,250 HP Operating Time [2] = 10 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Operating load [2] = 100% No of representative engines [2] = 8

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4], [5] 7.00E-04 lb/HP-hr 12.60 126.00 3.18 PM 10 AP-42 [4], [5] 4.01E-04 lb/HP-hr 7.22 72.20 1.82 PM 2.5 AP-42 [4], [5] 3.89E-04 lb/HP-hr 7.01 70.06 1.77 NO x AP-42 [5] 2.40E-02 lb/HP-hr 432.00 4320.00 108.86 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.20 2.02 0.05 CO AP-42 [5] 5.50E-03 lb/HP-hr 99.00 990.00 24.95 VOC AP-42 [5],[7] 6.42E-04 lb/HP-hr 11.55 115.48 2.91

Pb EPA [6] 2.03E-07 lb/HP-hr 3.65E-03 3.65E-02 9.21E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 6.31E-03 6.31E-02 1.59E-03

[1]

[2]

[3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CAT 3512 DITA Engine Representative Pump SV-PE-01 through SV-PE-08 Criteria Pollutants

Note: The following calculation is the Potential To Emit at 100% load for all 8 engines. The stimulation vessel pumps emissions are restricted to the proposed stimulation vessel daily and annual operating hour limitations. It is expected that all 8 engine s are not required to be used simultaneously.

Pollutant Emission Factor Basis Emission Factor

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Representative pump to be used on simulation vessel. Representative Specification sheet provided by Ms. Sara Carlson (Anadarko) on November 19, 2012. A total of 8 engines represent the combined hydraulic pumping capacity. Anadarko proposes to utilize same or equivalent pumps or any equivalent combination of number and capacity of pumps. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. PM 10 and PM 2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 . Total particulate emissions is the sum of filterable and condensable particulate emissions.

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. Anaverage brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hphr.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 160	of	192 Stimu	Vessel	(Rep	Pump)	‐	Cri t

### Engine Rating [1] = 1,678 kW 2,250 HP Operating Time [2] = 10 hrs/day 504 hrs/yr Fuel Type [6] = ULSD No of representative engines [2] = 8

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 3.18E-03 3.18E-02 8.00E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 9.93E-04 9.93E-03 2.50E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 0.10 0.98 2.46E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 0.01 0.10 2.51E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 0.04 0.35 8.92E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 0.02 0.24 6.13E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 0.03 0.27 6.73E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 0.02 0.16 4.13E-03 Total VOC HAPs 0.20 1.98 5.00E-02

[1]

[2]

[3]

[4]

[5]

[6] ULSD is proposed as fuel for the Well Completion Activity. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CAT 3512 DITA Engine Representative Pump SV-PE-01 through SV-PE-08

Hazardous Air Pollutants

Note: The following calculation is the Potential To Emit at 100% load for all 8 engines. The stimulation vessel pumps emissions are restricted to the proposed stimulation vessel daily and annual operating hour limitations. It is expected that all 8 engine s are not required to be used simultaneously.



### Pollutant Emission Factor Basis Emission Factor

Representative pump to be used on simulation vessel. Representative Specification sheet provided by Ms. Sara Carlson (Anadarko) on November 19, 2012. A total of 8 engines represent the combined hydraulic pumping capacity. Anadarko proposes to utilize same or equivalent pumps or any equivalent combination of number and capacity of pumps. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 161	of	192 Stimu	Vessel	(Rep	Pump)	‐	HAP

### Engine Rating [1] = 1,678 kW 2,250 HP Operating Time [2] = 10 hrs/day 504 hrs/yr Fuel Type [7] = ULSD No of representative engines [2] = 8

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 20,544.77 205,447.66 5,177.28

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.83 8.33 0.21

N 2 

### O 40 CFR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.17 1.67 0.04

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 20,613.93 206,139.33 5,194.71

[1]

[2]

[3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CAT 3512 DITA Engine Representative Pump SV-PE-01 through SV-PE-08 Greenhouse Gases

Note: The following calculation is the Potential To Emit at 100% load for all 8 engines. The stimulation vessel pumps emissions are restricted to the proposed stimulation vessel daily and annual operating hour limitations. It is expected that all 8 engine s are not required to be used simultaneously.



### Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Representative pump to be used on simulation vessel. Representative Specification sheet provided by Ms. Sara Carlson (Anadarko) on November 19, 2012. A total of 8 engines represent the combined hydraulic pumping capacity. Anadarko proposes to utilize same or equivalent pumps or any equivalent combination of number and capacity of pumps. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 162	of	192 Stimu	Vessel	(Rep	Pump)	‐	GHGEngine Rating [1],[4] = 910 kW 1,220 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Number of Generators [1] = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM 40 CFR 89.112, AP-42 [4] 0.20 g/kW-hr 0.80 19.26 0.20 PM 10 40 CFR 89.112, AP-42 [4], [5] 0.11 g/kW-hr 0.46 11.04 0.12 PM 2.5 40 CFR 89.112, AP-42 [4], [5] 0.11 g/kW-hr 0.45 10.71 0.11 NO x 40 CFR 89.112 [4] 6.40 g/kW-hr 25.68 616.31 6.47 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.03 0.66 0.01 CO 40 CFR 89.112 [4] 3.50 g/kW-hr 14.04 337.04 3.54 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 1.57 37.58 0.39

Pb EPA [7] 2.03E-07 lb/HP-hr 4.95E-04 0.012 1.25E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 8.55E-04 0.02 2.15E-04

[1]

[2]

[3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C32 ATAAC Engine (SV-GE-01 and SV-GE-02 Generators) - Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dua l-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Representative Generator Chouest to be used on simulation vessel as provided by Mr. Aaron Wade (Anadarko) on August 29, 2012.

Operating information provided in an email from Ms. Sara Carlson (Anadarko) to Mr. Raghu Soule (Trinity) on October 22, 2012.
Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have b een calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidize d to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on Engine Specification obtained from Manufacturer's website for Caterpillar C-32 Engine which is certified for EPA Tier II (Table 1 of Federal Register/Vol. 63, No. 205, October 23, 1998 and 40 CFR 89.112(a)). http://www.cat.com/cda/files/1563866/7/C32%20910%20ekW%20Prime%20LowBSFC_EMCP4.pdf http://www.miltoncat.com/products/NewGenerators/Documents/C32/C32%20Spec%20Sheet%20rated%20900%20kW.pdf PM 10 and PM 2.5 emission factors obtained by applying the ratio of PM/PM 10 and PM/PM 2.5 from AP-42 Chapter 3, Table 3.4-1 and Table 3.4-2 on EPA Tier II PM emission factor.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 163	of	192 Generators	Chouest	‐	Criteria

### Engine Rating [1],[7] = 910 kW 1,220 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [6] = ULSD Number of Generators [1] = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 4.31E-04 1.03E-02 1.08E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.35E-04 3.23E-03 3.39E-05 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 1.33E-02 3.18E-01 3.34E-03 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 1.35E-03 3.24E-02 3.40E-04 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 4.80E-03 1.15E-01 1.21E-03 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 3.30E-03 7.91E-02 8.31E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 3.62E-03 8.69E-02 9.13E-04 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 2.22E-03 5.33E-02 5.60E-04 Total VOC HAPs 0.03 0.65 0.01

[1]

[2]

[3]

[4]

[5] [6] [7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C32 ATAAC Engine (SV-GE-01 and SV-GE-02 Generators) - Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Based on Engine Specification obtained from Manufacturer's website for Caterpillar C-32 Engine. http://www.cat.com/cda/files/1563866/7/C32%20910%20ekW%20Prime%20LowBSFC_EMCP4.pdf http://www.miltoncat.com/products/NewGenerators/Documents/C32/C32%20Spec%20Sheet%20rated%20900%20kW .pdf Representative Generator Chouest to be used on simulation vessel as provided by Mr. Aaron Wade (Anadarko) on August 29, 2012. Operating information provided in an email from Ms. Sara Carlson (Anadarko) to Mr. Raghu Soule (Trinity) on October 22, 2012. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. ULSD is proposed as fuel for the Well Completion Activity.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 164	of	192 Generators	Chouest	‐	HAP

### Engine Rating [1],[8] = 910 kW 1,220 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [7] = ULSD Number of Generators [1] = 2

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 2,785.66 66,855.95 701.99

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.11 2.71 0.03

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 0.02 0.54 0.01

CO 2 

### e 40 CFR 98 Subpart C [6] -- -- 2,795.04 67,081.04 704.35

[1]

[2]

[3]

[4]

[5]

[6]

[7] [8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Caterpillar C32 ATAAC Engine (SV-GE-01 and SV-GE-02 Generators) - Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Based on Engine Specification obtained from Manufacturer's website for Caterpillar C-32 Engine. http://www.cat.com/cda/files/1563866/7/C32%20910%20ekW%20Prime%20LowBSFC_EMCP4.pdf http://www.miltoncat.com/products/NewGenerators/Documents/C32/C32%20Spec%20Sheet%20rated%20900% 20kW.pdf Representative Generator Chouest to be used on simulation vessel as provided by Mr. Aaron Wade (Anadarko) on August 29, 2012. Operating information provided in an email from Ms. Sara Carlson (Anadarko) to Mr. Raghu Soule (Trinity) on October 22, 2012. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 165	of	192 Generators	Chouest	‐	GHGEngine Rating [1],[4] = 600 kW 805 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [3] = ULSD Number of Generators [2] = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

PM 40 CFR 89.112, AP42 [4] 0.20 g/kW-hr 0.53 12.70 0.13

PM 10 40 CFR 89.112, AP42 [4], [5] 0.11 g/kW-hr 0.30 7.28 0.08

PM 2.5 40 CFR 89.112, AP42 [4], [5] 0.11 g/kW-hr 0.29 7.06 0.07 NO x 40 CFR 89.112 [4] 6.40 g/kW-hr 16.93 406.36 4.27 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.43 0.00 CO 40 CFR 89.112 [4] 3.50 g/kW-h r 9.26 222.23 2.33 VOC AP-42 [6],[8] 6.42E-04 lb/HP-h r 1.03 24.78 0.26

Pb EPA [7] 2.03E-07 lb/HP-h r 3.27E-04 7.84E-03 8.23E-05 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 5.64E-04 1.35E-02 1.42E-04

[1]

[2]

[3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Caterpillar C18 ATAAC Engine (SV-GE-03 and SV-GE-04 Generators) - Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gasturbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.
Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor. Representative Generator Hughes to be used on simulation vessel as provided by Mr. Aaron Wade (Anadarko) on August 29, 2012. Operating information provided in an email from Ms. Sara Carlson (Anadarko) to Mr. Raghu Soule (Trinity) on October 22, 2012. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.
Based on Engine Specification obtained from Manufacturer's website for Caterpillar C-18 Engine which is certified for EPA Tier II (Table 1 of Federal Register/Vol. 63, No. 205, October 23, 1998 and 40 CFR 89.112(a)). http://www.cat.com/cda/files/301199/7/C18%20600%20ekw%20Standby%20Tier2_EMCP4.pdf
PM 10 and PM 2.5 emission factors obtained by applying the ratio of PM/PM 10 and PM/PM 2.5 from AP-42 Chapter 3, Table 3.4-1 and Table 3.4-2 on EPA Tier II PM emission factor.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 166	of	192 Generators	B.	Hughes	‐	Crit

### Engine Rating [1],[7] = 600 kW 805 HP Operating Time [2] = 24 hrs/day 504 hrs/yr Fuel Type [6] = ULSD Number of Generators [2] = 2

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 2.84E-04 6.81E-03 7.15E-05

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 8.88E-05 2.13E-03 2.24E-05 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 8.74E-03 0.21 2.20E-03 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 8.89E-04 0.02 2.24E-04 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 3.17E-03 0.08 7.98E-04 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.17E-03 0.05 5.48E-04 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 2.39E-03 0.06 6.02E-04 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 1.46E-03 0.04 3.69E-04 Total VOC HAPs 0.02 0.43 4.47E-03

[1]

[2]

[3]

[4]

[5]

[6] [7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Caterpillar C18 ATAAC Engine (SV-GE-03 and SV-GE-04 Generators) - Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Based on Engine Specification obtained from Manufacturer's website for Caterpillar C-18 Engine. http://www.cat.com/cda/files/301199/7/C18%20600%20ekw%20Standby%20Tier2_EMCP4.pdf Representative Generator Hughes to be used on simulation vessel as provided by Mr. Aaron Wade (Anadarko) on August 29, 2012. Operating information provided in an email from Ms. Sara Carlson (Anadarko) to Mr. Raghu Soule (Trinity) on October 22, 2012. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

ULSD is proposed as fuel for the Well Completion Activity.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 167	of	192 Generators	B.	Hughes	‐	HAP

### Engine Rating [1],[8] = 600 kW 805 HP Operating Time [2] = 24 hrs/day [1] 504 hrs/yr Fuel Type [7] = ULSD N umber of Generators [2] = 2 Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr)

CO 2 

### 40 CFR 98 Subpart C [3] 7.40E+01 kg/MMBtu 1,836.70 44,080.85 462.85

CH 4 

### 40 CFR 98 Subpart C [4] 3.00E-03 kg/MMBtu 0.07 1.79 0.02

N 2 

### O 40 C FR 98 Subpart C [4] 6.00E-04 kg/MMBtu 1.49E-02 3.58E-01 3.75E-03

CO 2 

### e 40 C FR 98 Subpart C [6] -- -- 1,842.89 44,229.26 464.41

[1]

[2]

[3]

[4]

[5]

[6]

[7] [8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Caterpillar C18 ATAAC Engine (SV-GE-03 and SV-GE-04 Generators) - Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Based on Engine Specification obtained from Manufacturer's website for Caterpillar C-18 Engine. http://www.cat.com/cda/files/301199/7/C18%20600%20ekw%20Standby%20Tier2_EMCP4.pdf Representative Generator Hughes to be used on simulation vessel as provided by Mr. Aaron Wade (Anadarko) on August 29, 2012. Operating information provided in an email from Ms. Sara Carlson (Anadarko) to Mr. Raghu Soule (Trinity) on October 22, 2012. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 168	of	192 Generators	B.	Hughes	‐	GHGEngine Rating [1], [4] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [6] 7.00E-04 lb/HP-hr 1.54 36.96 3.70 PM 10 AP-42 [5] 4.01E-04 lb/HP-hr 0.88 21.18 2.12 PM 2.5 AP-42 [5] 3.89E-04 lb/HP-hr 0.86 20.55 2.05 NO x IMO Tier II [4] 7.85 g/kW-hr 28.39 681.39 68.14 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.59 0.06 CO AP-42 [6] 5.50E-03 lb/HP-hr 12.10 290.40 29.04 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 1.41 33.87 3.39

Pb EPA [7] 2.03E-07 lb/HP-hr 4.47E-04 0.01 1.07E-03 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 7.71E-04 0.02 1.85E-03

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Cummins QSK 60 MCRS Engine (Main Engine 1) TB-ME-01 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day.

Based on Engine Specification obtained from Manufacturer's website for Cummins QSK 60 MCRS Engine which is certified to IMO Tier II. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Comm ercial_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf PM 10 and PM 2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 . Total particulate emissions is the sum of filterable and condensable particulate emissions.
Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. Anaverage brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hphr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 169	of	192 Tug	ME1	‐	Criteria

### Engine Rating [1], [7] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 3.88E-04 9.31E-03 9.31E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.21E-04 2.91E-03 2.91E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 1.20E-02 2.87E-01 2.87E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 1.22E-03 2.92E-02 2.92E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 4.33E-03 1.04E-01 1.04E-02 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.97E-03 7.13E-02 7.13E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 3.26E-03 7.84E-02 7.84E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 2.00E-03 4.80E-02 4.80E-03 Total VOC HAPs 0.02 0.58 0.06

[1]

[2] [3]

[4]

[5] [6] [7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Cummins QSK 60 MCRS Engine (Main Engine 1) TB-ME-01 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Based on Engine Specification obtained from Manufacturer's website for Cummins QSK 60 MCRS Engine. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Commer cial_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. ULSD is proposed as fuel for the Well Completion Activity.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 170	of	192 Tug	ME1	‐	HAP

### Engine Rating [1], [8] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 2,511.03 60,264.65 6,026.46 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 0.10 2.44 0.24 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 0.02 0.49 0.05 CO 2 

### e EPA [6] -- -- 2,519.48 60,467.54 6,046.75

[1]

[2] [3]

[4]

[5] [6]

[7] [8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Cummins QSK 60 MCRS Engine (Main Engine 1) TB-ME-01 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Based on Engine Specification obtained from Manufacturer's wesbite for Cummins QSK 60 MCRS Engine. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Com mercial_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.

Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.
CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 171	of	192 Tug	ME1	‐	GHGEngine Rating [1], [4] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [6] 7.00E-04 lb/HP-hr 1.54 36.96 3.70 PM 10 AP-42 [5] 4.01E-04 lb/HP-hr 0.88 21.18 2.12 PM 2.5 AP-42 [5] 3.89E-04 lb/HP-hr 0.86 20.55 2.05 NO x IMO Tier II [4] 7.85E+00 g/kW-hr 28.39 681.39 68.14 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.59 0.06 CO AP-42 [6] 5.50E-03 lb/HP-hr 12.10 290.40 29.04 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 1.41 33.87 3.39

Pb EPA [7] 2.03E-07 lb/HP-hr 4.47E-04 1.07E-02 1.07E-03 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 7.71E-04 1.85E-02 1.85E-03

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Cummins QSK 60 MCRS Engine (Main Engine 2) TB-ME-02 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day.

Based on Engine Specification obtained from Manufacturer's website for Cummins QSK 60 MCRS Engine which is certified to IMO Tier II. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Commerci al_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf
PM 10 and PM 2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 . Total particulate emissions is the sum of filterable and condensable particulate emissions.

Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 172	of	192 Tug	ME2	‐	Criteria

### Engine Rating [1], [7] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 3.88E-04 9.31E-03 9.31E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.21E-04 2.91E-03 2.91E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 1.20E-02 0.29 2.87E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 1.22E-03 0.03 2.92E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 4.33E-03 0.10 1.04E-02 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.97E-03 0.07 7.13E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 3.26E-03 0.08 7.84E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 2.00E-03 0.05 4.80E-03 Total VOC HAPs 0.02 0.58 0.06

[1]

[2] [3]

[4]

[5] [6] [7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Cummins QSK 60 MCRS En g ine (Main En g ine 2) TB-ME-02 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Based on Engine Specification obtained from Manufacturer's website for Cummins QSK 60 MCRS Engine. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Commercial _Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. ULSD is proposed as fuel for the Well Completion Activity.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 173	of	192 Tug	ME2	‐	HAP

### Engine Rating [1], [8] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 2,511.03 60,264.65 6,026.46 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 0.10 2.44 0.24 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 0.02 0.49 0.05 CO 2 

### e EPA [6] -- -- 2,519.48 60,467.54 6,046.75

[1]

[2] [3]

[4]

[5]

[6]

[7] [8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Cummins QSK 60 MCRS Engine (Main Engine 2) TB-ME-02 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Based on Engine Specification obtained from Manufacturer's wesbite for Cummins QSK 60 MCRS Engine. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Co mmercial_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day,. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 174	of	192 Tug	ME2	‐	GHGEngine Rating [1], [4] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [6] 7.00E-04 lb/HP-hr 1.54 36.96 3.70 PM 10 AP-42 [5] 4.01E-04 lb/HP-hr 0.88 21.18 2.12 PM 2.5 AP-42 [5] 3.89E-04 lb/HP-hr 0.86 20.55 2.05 NO x IMO Tier II [4] 7.85E+00 g/kW-hr 28.39 681.39 68.14 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 0.02 0.59 0.06 CO AP-42 [6] 5.50E-03 lb/HP-hr 12.10 290.40 29.04 VOC AP-42 [6],[8] 6.42E-04 lb/HP-hr 1.41 33.87 3.39

Pb EPA [7] 2.03E-07 lb/HP-hr 4.47E-04 1.07E-02 1.07E-03 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 7.71E-04 1.85E-02 1.85E-03

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Cummins QSK 60 MCRS Engine (Main Engine 3) TB-ME-03 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day.

Based on Engine Specification obtained from Manufacturer's website for Cummins QSK 60 MCRS Engine which is certified to IMO Tier II. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Com mercial_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf

PM 10 and PM 2.5 emission factors based on AP-42 Chapter 3, Table 3.4-2, Particulate and Particle-sizing Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. PM < 3um taken as PM 2.5 . Total particulate emissions is the sum of filterable and condensable particulate emissions.
Emission factors are based on AP-42 Chapter 3, Table 3.4-1, Emission Factors for Large Stationary Diesel and all Stationary Dual-fuel Engines (October 1996). Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. Anaverage brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hphr. Per footnote f of AP-42 Chapter 3, Table 3.4-1, non methane VOC emission factor has been taken as 91% of TOC emission factor.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 175	of	192 Tug	ME3	‐	Criteria

### Engine Rating [1], [7] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [6] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[5] 2.52E-05 lb/MMBtu 3.88E-04 9.31E-03 9.31E-04

Acrolein AP-42 [3],[5] 7.88E-06 lb/MMBtu 1.21E-04 2.91E-03 2.91E-04 Benzene AP-42 [3],[5] 7.76E-04 lb/MMBtu 1.20E-02 0.29 2.87E-02 Formaldehyde AP-42 [3],[5] 7.89E-05 lb/MMBtu 1.22E-03 0.03 2.92E-03 Toluene AP-42 [3],[5] 2.81E-04 lb/MMBtu 4.33E-03 0.10 1.04E-02 Xylenes AP-42 [3],[5] 1.93E-04 lb/MMBtu 2.97E-03 0.07 7.13E-03 Total PAH AP-42 [4],[5] 2.12E-04 lb/MMBtu 3.26E-03 0.08 7.84E-03 N aphthalene AP-42 [4],[5] 1.30E-04 lb/MMBtu 2.00E-03 0.05 4.80E-03 Total VOC HAPs 0.02 0.58 0.06

[1]

[2] [3]

[4]

[5]

[6] [7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
Cummins QSK 60 MCRS Engine (Main Engine 3) TB-ME-03 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Based on Engine Specification obtained from Manufacturer's website for Cummins QSK 60 MCRS Engine. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Com mercial_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.4-3, Speciated Organic Compound Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). Emission factors based on AP-42, Chapter 3, Table 3.4-4, PAH Emission Factors for Large Uncontrolled Stationary Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

ULSD is proposed as fuel for the Well Completion Activity.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 176	of	192 Tug	ME3	‐	HAP

### Engine Rating [1], [8] = 1,641 kW 2,200 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 2,511.03 60,264.65 6,026.46 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 0.10 2.44 0.24 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 0.02 0.49 0.05 CO 2 

### e EPA [6] -- -- 2,519.48 60,467.54 6,046.75

[1]

[2] [3]

[4]

[5] [6]

[7] [8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Cummins QSK 60 MCRS Engine (Main Engine 3) TB-ME-03 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Based on Engine Specification obtained from Manufacturer's wesbite for Cummins QSK 60 MCRS Engine. https://marine.cummins.com/MarineECM/MarineContent/SiteContent/en/Binary_Asset/attachments/Products/Com mercial_Propulsion/QSK60_MCRS/QSK60_IMO_Tier_II_and_EPA_Tier_3_Certified_Ratings_SS.pdf Representative Tug Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.

An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 177	of	192 Tug	ME3	‐	GHG

### Engine Rating [1] = 130 kW 174 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.38 9.20 0.920 PM 10 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.38 9.20 0.920 PM 2.5 

### AP-42 [4],[5] 2.20E-03 lb/HP-hr 0.38 9.20 0.920 NO x 

### AP-42 [5] 3.10E-02 lb/HP-hr 5.40 129.70 12.970 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 1.96E-03 4.69E-02 4.69E-03 CO AP-42 [5] 6.68E-03 lb/HP-hr 1.16 27.95 2.795 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 0.44 10.51 1.051

Pb EPA [6] 2.03E-07 lb/HP-hr 3.54E-05 8.49E-04 8.49E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 6.11E-05 1.47E-03 1.47E-04

[1]

[2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CUMMINS 6C8.3T (Generator Engine 1) TB-GE-01 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gasturbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brakespecific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.

All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Representative Tug Generator Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003.
Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 

### = PM 10 

### = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 178	of	192 Tug	Generator	1	‐	Criteria

### Engine Rating [1] = 130 kW 174 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 9.36E-04 2.25E-02 2.25E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 1.13E-04 2.71E-03 2.71E-04 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 1.14E-03 2.73E-02 2.73E-03 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 1.44E-03 3.46E-02 3.46E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 4.99E-04 1.20E-02 1.20E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 3.48E-04 8.35E-03 8.35E-04 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 2.05E-04 4.92E-03 4.92E-04 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 4.77E-05 1.15E-03 1.15E-04 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 1.03E-04 2.48E-03 2.48E-04 Total VOC HAPs 4.73E-03 1.13E-01 1.13E-02

[1]

[2] [3]

[4] [5] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CUMMINS 6C8.3T (Generator Engine 1) TB-GE-01 Hazardous Air Pollutants

Pollutant Emission Factor Basis Emission Factor

Representative Tug Generator Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. ULSD is proposed as fuel for the Well Completion Activity.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 179	of	192 Tug	Generator	1	‐	HAP

### Engine Rating [1] = 130 kW 174 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 198.98 4,775.43 477.54 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 8.07E-03 1.94E-01 1.94E-02 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 1.61E-03 3.87E-02 3.87E-03 CO 2 

### e EPA [6] -- -- 199.65 4,791.50 479.15

[1]

[2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CUMMINS 6C8.3T (Generator Engine 1) TB-GE-01 Greenhouse Gases

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Representative Tug Generator Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 180	of	192 Tug	Generator	1	‐	GHG

### Engine Rating [1],[4] = 130 kW 174 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [6],[5] 2.20E-03 lb/HP-hr 0.38 9.20 0.92 PM 10 

### AP-42 [6],[5] 2.20E-03 lb/HP-hr 0.38 9.20 0.92 PM 2.5 

### AP-42 [6],[5] 2.20E-03 lb/HP-hr 0.38 9.20 0.92 NO x 

### AP-42 [6] 3.10E-02 lb/HP-hr 5.40 129.70 12.97 SO 2 

### Fuel S Content [3] 1.12E-05 lb/HP-hr 1.96E-03 4.69E-02 4.69E-03 CO AP-42 [6] 6.68E-03 lb/HP-hr 1.16 27.95 2.79 VOC AP-42 [6],[8] 2.51E-03 lb/HP-hr 0.44 10.51 1.05

Pb EPA [7] 2.03E-07 lb/HP-hr 3.54E-05 8.49E-04 8.49E-05 H 2 

### SO 4 

### Fuel S Content [3] 3.50E-07 lb/HP-hr 6.11E-05 1.47E-03 1.47E-04

[1]

[2] [3], [4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

CUMMINS 6C8.3T (Generator Engine 2) TB-GE-02 Criteria Pollutants

Pollutant Emission Factor Basis Emission Factor

Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions fromSources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oilfired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr.
All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. Representative Tug Generator Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 

### and 2 percent of sulfur in the fuel is oxidized to H 2 

### SO 4 

### based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM2.5 = PM10 = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 181	of	192 Tug	Generator	2	‐	Criteria

### Engine Rating [1] = 130 kW 174 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Daily Emissions Maximum Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 9.36E-04 2.25E-02 2.25E-03

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 1.13E-04 2.71E-03 2.71E-04 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 1.14E-03 2.73E-02 2.73E-03 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 1.44E-03 3.46E-02 3.46E-03 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 4.99E-04 1.20E-02 1.20E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 3.48E-04 8.35E-03 8.35E-04 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 2.05E-04 4.92E-03 4.92E-04 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 4.77E-05 1.15E-03 1.15E-04 N aphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 1.03E-04 2.48E-03 2.48E-04 Total VOC HAPs 4.73E-03 1.13E-01 1.13E-02

[1]

[2] [3]

[4] [5] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CUMMINS 6C8.3T (Generator Engine 2)

Pollutant Emission Factor Basis Emission Factor

Representative Tug Generator Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. ULSD is proposed as fuel for the Well Completion Activity.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 182	of	192 Tug	Generator	2	‐	HAP

### Engine Rating [1] = 130 kW 174 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD

Average Hourly Emissions [5] Average Daily Emissions Annual Emissions Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 199 4,775 478 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 8.07E-03 1.94E-01 1.94E-02 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 1.61E-03 3.87E-02 3.87E-03 CO 2 

### e EPA [6] -- -- 200 4,792 479

[1]

[2] [3]

[4]

[5]

[6]

[7] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations
CUMMINS 6C8.3T (Generator Engine 2)

Pollutant Emission Factor Basis Emission Factor

ULSD is proposed as fuel for the Well Completion Activity. Representative Tug Generator Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions. Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions. An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.

CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 183	of	192 Tug	Generator	2	‐	GHGCombined Engine Rating [1] = 1,020 kW 1,368 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [3] = ULSD

Maximum Hourly Emissions 9 Maximum Daily Emissions 9 Annual Emissions 9 Value Units (lb/hr) (lb/day) (tons/yr) PM AP-42 [4],[5] 2.20E-03 lb/HP-hr 3.01 72.23 7.22 PM 10 AP-42 [4],[5] 2.20E-03 lb/HP-hr 3.01 72.23 7.22 PM 2.5 AP-42 [4],[5] 2.20E-03 lb/HP-hr 3.01 72.23 7.22 NO x AP-42 [5] 3.10E-02 lb/HP-hr 42.41 1017.79 101.78 SO 2 Fuel S Content [3] 1.12E-05 lb/HP-hr 1.53E-02 3.68E-01 3.68E-02 CO AP-42 [5] 6.68E-03 lb/HP-hr 9.14 219.32 21.93 VOC AP-42 [5],[7] 2.51E-03 lb/HP-hr 3.44 82.46 8.25

Pb EPA [6] 2.03E-07 lb/HP-hr 2.78E-04 6.66E-03 6.66E-04 H 2 SO 4 Fuel S Content [3] 3.50E-07 lb/HP-hr 4.79E-04 1.15E-02 1.15E-03

[1]

[2] [3]

[4]

[5]

[6]

[7]

[8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Barge Electrical Generators 1, 2 and 3 (identical)

Pollutant Emission Factor Basis Emission Factor 

# BG-LP-01 to -03

Lead emission factor was obtained from EPA guidance document: Locating and Estimating Air Emissions from Sources of Lead and Lead Compounds, EPA 454/R-98-006, May 1998, Section 5.2.2. Emission factor for distillate oil-fired gas turbines was used as a surrogate for distillate oil-fired engines due to lack of emission factors. An average brake-specific fuel consumption (BSFC) of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr. All TOC is assumed to be VOC. TOC emission factor has been calculated as the sum of exhaust and crankcase emission factors. The emissions have been conservatively doubled to represent worst-case barge emissions. Representative Barge Pump Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Anadarko is proposing the use of Ultra Low Sulfur Diesel (ULSD) for all diesel combustion sources. Therefore, emissions have been calculated based on a maximum sulfur content of 15 ppm in diesel fuel assuming that 98 percent of sulfur in the fuel is oxidized to SO 2 and 2 percent of sulfur in the fuel is oxidized to H 2 SO 4 based on Draft Regulatory Impact Analysis: Control of Emissions from Nonroad Diesel Engines, EPA420-R-03-008, April 2003. Based on footnote b of AP-42 Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Per footnote b of Table 3.3-1, all PM is assumed to be < 1 um, therefore, assumed PM 2.5 = PM 10 = PM. Emission factors are based on AP-42, Chapter 3, Table 3.3-1, Emission Factors for Uncontrolled Gasoline and Diesel Industrial Engines (October 1996). Emission factors for diesel fuel are used.

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 184	of	192 BG‐LP‐01	‐	CriteriaEngine Rating [1] = 1,020 kW 1,368 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [5] = ULSD

Maximum Hourly Emissions 6 Maximum Daily Emissions 6 Annual Emissions 6 Value Units (lb/hr) (lb/day) (tons/yr) Acetaldehyde AP-42 [3],[4] 7.67E-04 lb/MMBtu 7.34E-03 1.76E-01 1.76E-02

Acrolein AP-42 [3],[4] 9.25E-05 lb/MMBtu 8.86E-04 2.13E-02 2.13E-03 Benzene AP-42 [3],[4] 9.33E-04 lb/MMBtu 8.93E-03 2.14E-01 2.14E-02 Formaldehyde AP-42 [3],[4] 1.18E-03 lb/MMBtu 1.13E-02 2.71E-01 2.71E-02 Toluene AP-42 [3],[4] 4.09E-04 lb/MMBtu 3.92E-03 9.40E-02 9.40E-03 Xylenes AP-42 [3],[4] 2.85E-04 lb/MMBtu 2.73E-03 6.55E-02 6.55E-03 Total PAH AP-42 [3],[4] 1.68E-04 lb/MMBtu 1.61E-03 3.86E-02 3.86E-03 1,3-Butadiene AP-42 [3],[4] 3.91E-05 lb/MMBtu 3.74E-04 8.99E-03 8.99E-04 Naphthalene AP-42 [3],[4] 8.48E-05 lb/MMBtu 8.12E-04 1.95E-02 1.95E-03 Total VOC HAPs 0.04 0.89 0.09

[1]

[2] [3]

[4] [5] [6] The emissions have been conservatively doubled to represent worst-case barge emissions. 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Barge Electrical Generators 1, 2 and 3 (identical)

Pollutant Emission Factor Basis Emission Factor

Representative Barge Pump Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) to Mr. Rahul Pendse (Trinity) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factors based on AP-42, Chapter 3, Table 3.3-2 Speciated Organic Compound Emission Factors for Uncontrolled Diesel Engines (October 1996). An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions. ULSD is proposed as fuel for the Well Completion Activity. 

# BG-LP-01 to -03

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 185	of	192 BG‐LP‐01	‐	HAP

### Engine Rating [1] = 1,020 kW 1,368 HP Operating Time [2] = 24 hrs/day [2] 4,800 hrs/yr Fuel Type [7] = ULSD
Average Hourly Emissions 5,8 

### Average Daily Emissions 8 

### Annual Emissions 8 

### Value Units (lb/hr) (lb/day) (tons/yr) CO 2 

### EPA [3] 7.40E+01 kg/MMBtu 1,561 37,474 3,747 CH 4 

### EPA [4] 3.00E-03 kg/MMBtu 6.33E-02 1.52E+00 1.52E-01 N 2 

### O EPA [4] 6.00E-04 kg/MMBtu 1.27E-02 3.04E-01 3.04E-02 CO 2 

### e EPA [6] -- -- 1,567 37,600 3,760

[1]

[2] [3]

[4]

[5] [6]

[7] [8] 

## Anadarko Petroleum Corporation Well Completion Emission Calculations

Barge Electrical Generators 1, 2 and 3 (identical)

Pollutant Emission Factor Basis Emission Factor 

# BG-LP-01 to -03

ULSD is proposed as fuel for the Well Completion Activity. The emissions have been conservatively doubled to represent worst-case barge emissions. Representative Barge Pump Engine to be used for well completion activities. Information provided by Ms. Sara Carlson (Anadarko) via email on October 1, 2012. Assumptions: Max operating time of 24 hr/day. Emission factor based on 40 CFR 98 Subpart C, Table C-1 Default CO 2 

### Emission Factors and High Heat Values for Various Types of Fuel. The emission factor for Distillate Fuel Oil No. 2 was used to calculate emissions.
Emission factors based on 40 CFR 98 Subpart C, Table C-2 Default CH 4 

### and N 2 

### O Emission Factors for Various Types of Fuel. The emission factor for petroleum (All types in table C-1) was used to calculate emissions.
An average BSFC of 7,000 Btu/hp-hr was used to convert from lb/MMBtu to lb/hp-hr to calculate emissions.
CH 4 

### , CO 2 

### and N 2 

### O are included in the emissions of CO 2 

### equivalent (CO 2 

### e), weighted according to their global warming potential (GWP). The GWP was obtained from 40 CFR 98, Subpart A, Table A-1 Global Warming Potentials (100-year Time Horizon).

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 186	of	192 BG‐LP‐01	‐	GHG

### EPN Engine Description Max Power (KW

‐ hr) Fuel use (g/kw

‐ hr) Max Fuel Usage (bbl/day)

WE-ME-01 VSP Vessel Main Engine #1 1,656 196 58

WE-ME-02 VSP Vessel Main Engine #2 1,656 196 58

WE-AE-01 Auxillary Engine Generator No. 1 1,055 194 37

WE-AE-02 Auxillary Engine Generator No. 2 1,055 194 37

WE-GE-01 Emergency Generator Engine 1 200 214 8

WE-GE-03 Emergency Generator Engine 3 147 6 Total 203

** Maximum fuel usage for emergency electrical generator (WE-GE-02) is not utilized for emission factor calculation. * The fuel usage for each engine was obtained from the respective engine specification sheet. Refer to Appendix G for specification sheets. 

## Well Evaluation Vessel Fuel Based Emission Factor Calculations Anadarko Petroleum Corporation

Anadarko	Petroleum	Corporation EGOM	Exploratory	Project	‐	Blackhornet 187	of	192 Dedicated	WE	Fuel	Based	EFEPN DescriptionMaxPower(KW‐hr)OperatingLoad(%)Operatinghours/dayMaxFueluse(gal/hr)MaxFueluse(lbs/hp‐hr)MaxFueluse(g/kw‐hr)MaxFueluse(bbl/day)SV‐ME‐01StimulationVesselMainEngine#12,71025% 24200 24SV‐ME‐02StimulationVesselMainEngine#22,71025% 24200 24SV‐BT‐01StimulationVesselBowthruster1,24925% 2412SV‐DD‐01StimulationVesselBowDrop‐Down89525% 248SV‐ST‐01StimulationVesselSternThruster1,24925% 2412SV‐PE‐01thruSV‐PE‐08StimulationVesselRepresentativePumps13423 100% 10 0.34207 207286** Maximum fuel usage for electrical generators (SV-GE-01 through SV-GE-04) are not utilized for emission factor calculation.Total* The fuel usage for each engine was obtained from the respective engine specification sheet. Refer to Appendix G for specification sheets.Stimulation Vessel Fuel Based Emission Factor CalculationsAnadarko Petroleum CorporationAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet188	of	192Stim	Vessel	EFEPN DescriptionMaxPower(KW‐hr)**MaxFueluse(gal/hr)***MaxFueluse(bbl/day)TB‐ME‐1 TugBoatMainEngines(Max8Engines)13,128594.40340** The fuel requirement for Tug Boats is calculated based on power requirement of 8 main engines.* The fuel usage for each engine was obtained from the respective engine specification sheet. Refer to Appendix G for specificationsheets.*** Maximum fuel usage per main engine is 74.30 gal/hr as specified in the engine specification sheet. Hence, the maximum fuelusage for 8 engines is calculated accordingly.TugBoat Fuel Based Emission Factor CalculationsAnadarko Petroleum CorporationAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet189	of	192Tug	Boat	‐	EFEPN DescriptionMaxPower(KW‐hr)Fueluse(gal/hr)Fueluse(bbl/day)SB‐ME‐01DieselMarinePropulsionEngine#12240 148.31 85SB‐ME‐02DieselMarinePropulsionEngine#22240 148.31 85SB‐TE‐01DieselMarineForwardBowthroughsterEngine#1820 54.26 31SB‐TE‐02DieselMarineAftBowthroughsterEngine#2820 54.26 31SB‐TE‐03DieselMarineSternthroughsterEngine#3820 54.26 31SB‐GE‐01PortElectricalGeneratorDieselEngine#1781 50.77 29SB‐GE‐02PortElectricalGeneratorDieselEngine#2781 50.77 29SB‐GE‐04ROVEletricalGeneratorDieselEngine#4354 22.50 13333** Maximum fuel usage for emergency electrical generator (SB-GE-03) is not available in specificationsheet. Hence, it is not utilized for emission factor calculation.* The fuel usage for each engine was obtained from the respective engine specification sheet. Refer toAppendix G for specification sheets.SupplyBoat Fuel Based Emission Factor CalculationsAnadarko Petroleum CorporationTotalAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet190	of	192Supply	Boat	EFValue Unitslb/lb of fuellb pollutant perbbl fuel**lb pollutant percubic meterfuel***PM 2.47E-04 lb/HP-hr 8.38E-04 0.25 1.55PM102.47E-04 lb/HP-hr 8.38E-04 0.25 1.55PM2.52.47E-04 lb/HP-hr 8.38E-04 0.25 1.55NOx9.69 g/kW-hr 5.41E-02 15.92 100.10SO21.12E-05 lb/HP-hr 3.81E-05 0.01 7.05E-02CO 5.50E-03 lb/HP-hr 1.87E-02 5.49 34.56VOC 6.42E-04 lb/HP-hr 2.18E-03 0.64 4.03Pb 2.03E-07 lb/HP-hr 6.90E-07 0.00 1.28E-03H2SO43.50E-07 lb/HP-hr 1.19E-06 0.00 2.20E-03GHGs 1.15E+00 lb/HP-hr 3.89E+00 1144 7196Total HAP 1.10E-05 lb/HP-hr3.74E-05 0.01 6.92E-02** Average density of diesel fuel of 7 lb/gal is used to convert lb of fuel to cubic meter of fuel.*** A conversion factor of 0.159 cubic meter of diesel per barrel of diesel is used.* The fuel usage for each engine was obtained from the respective engine specification sheet. Refer to Appendix G for specificationsheets.Emission FactorAnadarko Petroleum CorporationDrillship Main Engines Fuel Based Emission Factors Development179Emission FactorPollutantFuelRequirement(g/kw-hr)Anadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet191	of	192Drillship	Fuel	EF	SummaryPM PM10 PM2.5 NOx SO2 H2SO4 CO VOC Pb GHG TotalHAPMax.FuelConsumedformPermanentEngines(bbl/day) 203Max.EmissionsFromFixedEnginesontheVessel(lb/day)*161 108 106 4792 2 6.83E-02 1091 156 3.96E-02 223177 2.57E+00FuelBasedEmissionFactorlb/bbl0.79 0.53 0.52 23.61 0.01 3.36E-04 5.38 0.77 1.95E-04 1099.39 1.27E-02Max.FuelConsumedformPermanentEngines(bbl/day) 333Max.EmissionsFromFixedEnginesontheVessel(lb/day)*94 78 76 3359 3 0.10 2315 176 0.06 297608 3.05FuelBasedEmissionFactorlb/bbl0.28 0.23 0.22 10.1 0.01 2.88E-04 6.99 0.54 1.67E-04 889.76 9.14E-03Max.FuelConsumedformPermanentEngines(bbl/day) 340Max.EmissionsFromEightMainEnginesontheVessel(lb/day)*296 169 164 5451 5 1.48E‐01 2323 271 8.57E‐02 483740 7.45E‐02FuelBasedEmissionFactorlb/bbl0.87 0.50 0.48 16.05 0.01 4.36E‐04 6.84 0.80 2.52E‐04 1424 2.19E‐04Max.FuelConsumedformPermanentEngines(bbl/day)286Max.EmissionsFromFixedEnginesontheVessel(lb/day)*213 122 118 6622 4 1.22E‐01 2058 223 7.07E‐02 398655 3.84E+00FuelBasedEmissionFactorlb/bbl0.74 0.43 0.41 23.13 0.01 4.26E‐04 7.19 0.78 2.47E‐04 1392 1.34E‐02*Refertotherespectivefuelbasedemissionfactordevelopmenttabforidentifyingincludedemissionsources.StimulationVesselAnadarko Petroleum CorporationSupport Vessel Fuel Based Emission Factors DevelopmentWellEvaluationVesselSupplyBoatTugBoatAnadarko	Petroleum	CorporationEGOM	Exploratory	Project	‐	Blackhornet192	of	192Support	Vessels	Fuel	EF	Summary