A
Presentation
on
Oxidation Ponds & Lagoons
Oxidation Ponds
What are Oxidation Ponds ?
Oxidation Pond is an open, flow through earthen basin of
controlled shape specially design and constructed to treat
sewage and bio-degradable industrial waste by natural
processes involving bacteria and in many instances algae.
Types Of Oxidation ponds
Aerobic Ponds
Anaerobic Ponds
Facultative Ponds
Maturation or Tertiary Ponds
Applications
Type of Ponds Applications
Aerobic Nutrient removal, treatment of soluble
organic waste & effluents from waste water
treatment plants.
Anaerobic Treatment of domestic and industrial wastes.
Facultative Treatment of untreated screened waste water
and industrial wastes.
New
Algae
Algae
O2
Bacteria
CO2, NH3, H2O
New
Bacteria
Organic
Bacteria
Solar
Energy
Symbiosis
Aerobic Ponds
The aerobic pond is shallow pond in which light penetrates
to the bottom there by maintaining active algal
photosynthesis through out the entire system.
Aerobic Ponds contain dissolved oxygen (DO) throughout
the entire depth of the pond all the time.
Treatment is accomplished through the stabilization of
organic wastes by aerobic bacteria and algae.
Dissolved oxygen can be introduced into a pond through several means:
 Algae, like other plants, emit dissolved oxygen as a by-product of photosynthesis.
 Wind, blowing across the surface of a pond, will cause oxygen to be absorbed into
the water.
 Mechanical aeration devices agitate the water surface to cause spray and waves so
that oxygen can be absorbed from the air. Some mechanical devices include paddle
wheels, mixers, and rotating brushes.
 Diffused aeration utilizes a blower system to discharge air into the water. The air
stream is broken into fine bubbles; the smaller the bubbles, the greater the oxygen
transfer.
ALGAE
AEROBIC BACTERIA
Light Energy from Sun
New Algal
Biomass
New
Bacterial
Biomass
Organics
from
Waste
Water
Variations in Aerobic Ponds
Diurnal(daily) variation in DO concentration
Diurnal variation in pH
Extreme values of these, in either direction may be
detrimental to microbial activity.
Design Considerations
Parameter Value
Depth in mts. 0.15-.5
Retention time (day) 2-6
BODu loading( lb/acre-day) 100-200
BODu removal(%) 80-90
Algae concentration(mg/l) 100-200
Re-circulation ratio 0.2-2.0
Effluent suspended solids
concentration(mg/l)
150-350
Problems
Nuisance vegetation
Inhibitory temperatures
Shock loads
Anaerobic Ponds
These ponds requires no D.O. for microbial activity
as the organisms use O2 from compounds such as
NO3, SO4 as their hydrogen acceptors and give end
product such as methane, carbon dioxide etc.
 Anaerobic Ponds function without dissolved oxygen (DO)
throughout any of its depth. Treatment is accomplished by anaerobic
bacteria at the bottom of the pond, which ferment the sludge.
 Anaerobic ponds have a depth of eight (8) to twenty (20) feet, and a
typical detention time of 20 to 50 days. A deep sludge blanket covers the
bottom of these ponds, while a scum layer covers the surface. The scum
layer is important to the pond because:
 It helps to minimize offensive odors
 It blocks transfer of DO through surface contact
 It helps insulate the pond or lagoon to ensure ideal conditions for sludge
fermentation.
Anaerobic decomposition
 It take place in two separate but inter related steps :-
1. Decomposition of dissolved organic waste by acid
producing bacteria to organic acids (such as acetic
propionic acid) and,
2. Further decomposition of these acids to the end
products of methane, carbon dioxide and water by
methane producing bacteria.
Acid producing Bacteria
Methane producing
bacteria
H2O, CO2, CH4
Organic Wastes
H2O, CO2
Bacterial
Cells
Bacterial Cells
Facultative Ponds
Facultative Ponds contain a supernatant (upper) layer that is
aerobic, and lower layers that are anaerobic.
These are neither fully aerobic nor fully anaerobic. They are
often about 1 to 2 m in depth and favor algal growth along with
the growth of aerobic, anaerobic and facultative
microorganisms. Such ponds are predominantly aerobic during
day light as well as for some hours of the light. In the few
remaining hours the pond bottom may turn anaerobic.
Zones of facultative pond
1) Aerobic zone
2) Anaerobic zone
3) Facultative zone
The decomposition of incoming organic waste and
products of anaerobic decomposition is done by
facultative bacteria.
Wind
CO2
Anaerobi
c
Zone
Aerobic
Zone
Anaerobi
c
Zone
Facultative
Zone
O2
alga
e
(CO2, NO2, PO4, SO4)
Aerobic
Bacteria
Biomass
Biomass
Anaerobic
Bacteria
Sludge Blanket
Organic acids &
Compounds of C, N, P, S
Impermeable lining
Sunligh
t
Maturation / Tertiary Ponds
These are similar to aerobic ponds but are very lightly
loaded with organic wastes. Generally used for upgrading
effluents from conventional secondary treatment
processes.
Reasons For Poor Performance of
Oxidation Pond
 DO level in the pond during night & early morning hours
was almost zero.
 BOD removal efficiency was only 60-70%
LAGOONS
LAGOONS
 Lagoons are deep waste stabilization ponds -like
bodies of water or basins designed to receive, hold,
and treat wastewater for a predetermined period of
time by artificial means of aeration.
 In the lagoon, wastewater is treated through a
combination of physical, biological, and chemical
processes.
TYPES OF LAGOONS
TYPES OF LAGOONS
According to the microbial activity in the aerated
lagoons-
Aerobic aerated lagoons.
Facultative aerated lagoons.
AEROBIC AERATED LAGOONS
AEROBIC AERATED LAGOONS
 Dissolved oxygen is present throughout much of the
depth of aerobic lagoons.
 They tend to be much shallower than other lagoons.
 They are better suited for warm, sunny climates, where
they are less likely to freeze.
 HRT = 2 to 10 days
 SS concentration between 60 to 300mg/l
 The BOD removal is of order of 75 to 85%
 Oxygenation requirement is of order of .7 to 1.3 kg per
kg of BOD removed.
Units of aerobic lagoon
1) The mechanical surface aerators so that solids do not
settle to bottom of tank.
2) The other unit is settling tank for removal of
suspended solids .
FACULTATIVE AERATED LAGOONS
FACULTATIVE AERATED LAGOONS
 Three types of zones are present
Aerobic Zone.
Anaerobic Zone.
Facultative Zone.
 HRT is higher than aerobic lagoons because time
requires for the solids to settle and for many pathogens
viruses to either die off or settle out.
Facultative lagoons
 Detentions time ranges from 3 to 5 days .
 BOD removal are of order 75 to 90%
ponds and lagoons
Two, Three, or Four Lagoons Are Better
Than One
Two, Three, or Four Lagoons Are Better
Than One
 Each lagoon cell has a different function to perform,
and a different kind of lagoon design may be used for
each cell.
In Series
When lagoons operate in
series, more of the solid
material in the wastewater,
such as algae, has an
opportunity to settle out
before the effluent is
disposed of.
In Parallel
This system design is
particularly useful in
cold climates or where
lagoons are covered
with ice for parts of the
year
ponds and lagoons
Operation And Maintenance
Operation And Maintenance
For Aerobic Lagoons
Any earthen structures used as impoundments must be periodically
inspected. If left unchecked, rodent damage can cause severe
weakening of lagoon embankments.
In submerged diffused aeration, the routine application of HCl gas
in the system is used to dissolve accumulated material on the
diffuser units
The use of submerged perforated tubing for diffused aeration
requires maintenance and cleaning on a routine basis to maintain
design aeration rates
Operation And Maintenance
For Facultative Lagoons
Most facultative lagoons are designed to operate by gravity flow.
The system is not maintenance intensive and power costs are
minimal because pumps and other electrically operated devices
may not be required.
Earthen structures used as impoundments must be inspected
for rodent damage.
Applicability
Applicability
Type of Lagoon Application
Aerobic Lagoon Municipal and industrial wastewaters of
low to medium strength.
Facultative Lagoon Treated raw, screened, or primary settled
municipal wastewater and biodegradable
industrial wastewaters.
Limitations
For Aerated Lagoons
Aerated lagoons may experience ice formation on the water
surface during cold weather periods
Reduced rates of biological activity also occur during cold
weather
Formation of ice on Floating Aerators.
For facultative Lagoons
The inability of the process to meet a 30 mg/L limit for TSS
due to the presence of algae in the effluent.
Odors may be a problem in the spring and fall during periods of
excessive algal blooms and unfavorable weather conditions
Thanks

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ponds and lagoons

  • 2. Oxidation Ponds What are Oxidation Ponds ? Oxidation Pond is an open, flow through earthen basin of controlled shape specially design and constructed to treat sewage and bio-degradable industrial waste by natural processes involving bacteria and in many instances algae.
  • 3. Types Of Oxidation ponds Aerobic Ponds Anaerobic Ponds Facultative Ponds Maturation or Tertiary Ponds
  • 4. Applications Type of Ponds Applications Aerobic Nutrient removal, treatment of soluble organic waste & effluents from waste water treatment plants. Anaerobic Treatment of domestic and industrial wastes. Facultative Treatment of untreated screened waste water and industrial wastes.
  • 6. Aerobic Ponds The aerobic pond is shallow pond in which light penetrates to the bottom there by maintaining active algal photosynthesis through out the entire system. Aerobic Ponds contain dissolved oxygen (DO) throughout the entire depth of the pond all the time. Treatment is accomplished through the stabilization of organic wastes by aerobic bacteria and algae.
  • 7. Dissolved oxygen can be introduced into a pond through several means:  Algae, like other plants, emit dissolved oxygen as a by-product of photosynthesis.  Wind, blowing across the surface of a pond, will cause oxygen to be absorbed into the water.  Mechanical aeration devices agitate the water surface to cause spray and waves so that oxygen can be absorbed from the air. Some mechanical devices include paddle wheels, mixers, and rotating brushes.  Diffused aeration utilizes a blower system to discharge air into the water. The air stream is broken into fine bubbles; the smaller the bubbles, the greater the oxygen transfer.
  • 8. ALGAE AEROBIC BACTERIA Light Energy from Sun New Algal Biomass New Bacterial Biomass Organics from Waste Water
  • 9. Variations in Aerobic Ponds Diurnal(daily) variation in DO concentration Diurnal variation in pH Extreme values of these, in either direction may be detrimental to microbial activity.
  • 10. Design Considerations Parameter Value Depth in mts. 0.15-.5 Retention time (day) 2-6 BODu loading( lb/acre-day) 100-200 BODu removal(%) 80-90 Algae concentration(mg/l) 100-200 Re-circulation ratio 0.2-2.0 Effluent suspended solids concentration(mg/l) 150-350
  • 12. Anaerobic Ponds These ponds requires no D.O. for microbial activity as the organisms use O2 from compounds such as NO3, SO4 as their hydrogen acceptors and give end product such as methane, carbon dioxide etc.
  • 13.  Anaerobic Ponds function without dissolved oxygen (DO) throughout any of its depth. Treatment is accomplished by anaerobic bacteria at the bottom of the pond, which ferment the sludge.  Anaerobic ponds have a depth of eight (8) to twenty (20) feet, and a typical detention time of 20 to 50 days. A deep sludge blanket covers the bottom of these ponds, while a scum layer covers the surface. The scum layer is important to the pond because:  It helps to minimize offensive odors  It blocks transfer of DO through surface contact  It helps insulate the pond or lagoon to ensure ideal conditions for sludge fermentation.
  • 14. Anaerobic decomposition  It take place in two separate but inter related steps :- 1. Decomposition of dissolved organic waste by acid producing bacteria to organic acids (such as acetic propionic acid) and, 2. Further decomposition of these acids to the end products of methane, carbon dioxide and water by methane producing bacteria.
  • 15. Acid producing Bacteria Methane producing bacteria H2O, CO2, CH4 Organic Wastes H2O, CO2 Bacterial Cells Bacterial Cells
  • 16. Facultative Ponds Facultative Ponds contain a supernatant (upper) layer that is aerobic, and lower layers that are anaerobic. These are neither fully aerobic nor fully anaerobic. They are often about 1 to 2 m in depth and favor algal growth along with the growth of aerobic, anaerobic and facultative microorganisms. Such ponds are predominantly aerobic during day light as well as for some hours of the light. In the few remaining hours the pond bottom may turn anaerobic.
  • 17. Zones of facultative pond 1) Aerobic zone 2) Anaerobic zone 3) Facultative zone The decomposition of incoming organic waste and products of anaerobic decomposition is done by facultative bacteria.
  • 18. Wind CO2 Anaerobi c Zone Aerobic Zone Anaerobi c Zone Facultative Zone O2 alga e (CO2, NO2, PO4, SO4) Aerobic Bacteria Biomass Biomass Anaerobic Bacteria Sludge Blanket Organic acids & Compounds of C, N, P, S Impermeable lining Sunligh t
  • 19. Maturation / Tertiary Ponds These are similar to aerobic ponds but are very lightly loaded with organic wastes. Generally used for upgrading effluents from conventional secondary treatment processes.
  • 20. Reasons For Poor Performance of Oxidation Pond  DO level in the pond during night & early morning hours was almost zero.  BOD removal efficiency was only 60-70%
  • 21. LAGOONS LAGOONS  Lagoons are deep waste stabilization ponds -like bodies of water or basins designed to receive, hold, and treat wastewater for a predetermined period of time by artificial means of aeration.  In the lagoon, wastewater is treated through a combination of physical, biological, and chemical processes.
  • 22. TYPES OF LAGOONS TYPES OF LAGOONS According to the microbial activity in the aerated lagoons- Aerobic aerated lagoons. Facultative aerated lagoons.
  • 23. AEROBIC AERATED LAGOONS AEROBIC AERATED LAGOONS  Dissolved oxygen is present throughout much of the depth of aerobic lagoons.  They tend to be much shallower than other lagoons.  They are better suited for warm, sunny climates, where they are less likely to freeze.  HRT = 2 to 10 days  SS concentration between 60 to 300mg/l  The BOD removal is of order of 75 to 85%  Oxygenation requirement is of order of .7 to 1.3 kg per kg of BOD removed.
  • 24. Units of aerobic lagoon 1) The mechanical surface aerators so that solids do not settle to bottom of tank. 2) The other unit is settling tank for removal of suspended solids .
  • 25. FACULTATIVE AERATED LAGOONS FACULTATIVE AERATED LAGOONS  Three types of zones are present Aerobic Zone. Anaerobic Zone. Facultative Zone.  HRT is higher than aerobic lagoons because time requires for the solids to settle and for many pathogens viruses to either die off or settle out.
  • 26. Facultative lagoons  Detentions time ranges from 3 to 5 days .  BOD removal are of order 75 to 90%
  • 28. Two, Three, or Four Lagoons Are Better Than One Two, Three, or Four Lagoons Are Better Than One  Each lagoon cell has a different function to perform, and a different kind of lagoon design may be used for each cell. In Series When lagoons operate in series, more of the solid material in the wastewater, such as algae, has an opportunity to settle out before the effluent is disposed of. In Parallel This system design is particularly useful in cold climates or where lagoons are covered with ice for parts of the year
  • 30. Operation And Maintenance Operation And Maintenance For Aerobic Lagoons Any earthen structures used as impoundments must be periodically inspected. If left unchecked, rodent damage can cause severe weakening of lagoon embankments. In submerged diffused aeration, the routine application of HCl gas in the system is used to dissolve accumulated material on the diffuser units The use of submerged perforated tubing for diffused aeration requires maintenance and cleaning on a routine basis to maintain design aeration rates
  • 31. Operation And Maintenance For Facultative Lagoons Most facultative lagoons are designed to operate by gravity flow. The system is not maintenance intensive and power costs are minimal because pumps and other electrically operated devices may not be required. Earthen structures used as impoundments must be inspected for rodent damage.
  • 32. Applicability Applicability Type of Lagoon Application Aerobic Lagoon Municipal and industrial wastewaters of low to medium strength. Facultative Lagoon Treated raw, screened, or primary settled municipal wastewater and biodegradable industrial wastewaters.
  • 33. Limitations For Aerated Lagoons Aerated lagoons may experience ice formation on the water surface during cold weather periods Reduced rates of biological activity also occur during cold weather Formation of ice on Floating Aerators. For facultative Lagoons The inability of the process to meet a 30 mg/L limit for TSS due to the presence of algae in the effluent. Odors may be a problem in the spring and fall during periods of excessive algal blooms and unfavorable weather conditions