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ChE 3113: Environmental
Science
Lecture- 7
Oxygen Sag Curve
The Oxygen Sag Curve
• The deoxygenation caused by microbial decomposition of wastes and
oxygenation by reaeration are competing processes that are
simultaneously removing and adding oxygen to a stream.
Equation (28) is
the classic
Streeter-Phelps
oxygen sag
equation first
described in
1925.
Factors that were not considered
• Photosynthesis also affects DO. Algae and other aquatic plants add DO during the
daytime hours while photosynthesis is occurring, but at night, their continued respiration
draws it down again. The net effect is a diurnal variation that can lead to elevated levels
of DO in the late afternoon and depressed concentrations at night. For a lake or a slow-
moving stream that is already overloaded with BOD and choked with algae, it is not
unusual for respiration to cause offensive, anaerobic conditions late at night, even
though the river seems fine during the day.
• There are other factors not included in our simple oxygen sag model. Accumulated
sludge along the bottom contributes to the oxygen demand; tributaries contribute their
own BOD and DO; multiple sources cause multiple dips in the sag curve; nonpoint-
sources contribute pulses of BOD and other contaminants when it rains; and this model
has not included the effects of nitrification. Nitrification causes a second dip in the
oxygen sag curve a little further downstream as ammonia and organic nitrogen convert
to nitrite and nitrate. If there is not enough DO downstream for nitrification to proceed,
nitrogen remains as ammonia, which is toxic
ChE 3113_L7.pdf

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ChE 3113_L7.pdf

  • 2. The Oxygen Sag Curve • The deoxygenation caused by microbial decomposition of wastes and oxygenation by reaeration are competing processes that are simultaneously removing and adding oxygen to a stream. Equation (28) is the classic Streeter-Phelps oxygen sag equation first described in 1925.
  • 3.
  • 4.
  • 5.
  • 6.
  • 7. Factors that were not considered • Photosynthesis also affects DO. Algae and other aquatic plants add DO during the daytime hours while photosynthesis is occurring, but at night, their continued respiration draws it down again. The net effect is a diurnal variation that can lead to elevated levels of DO in the late afternoon and depressed concentrations at night. For a lake or a slow- moving stream that is already overloaded with BOD and choked with algae, it is not unusual for respiration to cause offensive, anaerobic conditions late at night, even though the river seems fine during the day. • There are other factors not included in our simple oxygen sag model. Accumulated sludge along the bottom contributes to the oxygen demand; tributaries contribute their own BOD and DO; multiple sources cause multiple dips in the sag curve; nonpoint- sources contribute pulses of BOD and other contaminants when it rains; and this model has not included the effects of nitrification. Nitrification causes a second dip in the oxygen sag curve a little further downstream as ammonia and organic nitrogen convert to nitrite and nitrate. If there is not enough DO downstream for nitrification to proceed, nitrogen remains as ammonia, which is toxic