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1
Area 300 - Percolation & Digestion
Area Overview
June 2013
2
UR3R Plant Overview
 Waste is separated in area
200 using the two trommels.
 Any waste that drops through
both trommels is sent to area
300 as feed.
 This is the organic part of the
waste stream and is smaller
than 80mm.
 Typically 30-45% of waste is
fed into area 300
3
Area 300 Overview
4
300 - PERCOLATION
5
Percolation
 Percolators take a solid organic / mixed waste feed from area
200.
 Typically 150 – 250 tonnes / day.
 KPI is to accept 90% of available feed every day.
 The amount of feed to area 300 depends on the hourly
throughput in area 200 and the performance of the bag
splitters and the trommels.
 Waste is mixed with warm irrigation water and is mixed in the
percolator.
 The percolator further separates the organics from the waste
stream and converts these solids into a liquid feed for the
digesters.
K P IK P I
6
ISKA®
Percolation
Clean
Percolated
Waste
High Organic
Waste from
sorting
Sand, Glass &
Grit Removal
Percolator
Biogas
Recirculated Hydrolysis Solution
Air
Digestion
Water
7
KPI – Feed to Percolators
 Target is 90% of available feed.
 Percolators can be bypassed. This puts additional load onto
OGM and reduces the percolate production.
 To accept a full days feed, we need two of the three
percolators to be at a low level at the start of processing.
 If we don’t have this space, we need to discharge throughout
the day.
 If a percolator is fed too quickly, waste will build up at the feed
end and start to restrict the agitator movement.
 Maximum level is 60-70% - this is around the top of the
agitator.
8
Benefits of Percolation
 Creates a ‘clean’ homogenous
liquid feed from a solid mixture of
organics and other waste.
 Allows the digesters to be
operated with a liquid feed, to be
single stage and to have better
throughput for their size.
 Allows OGM to be smaller as
percs remove some organics and
give mass reduction.
 Perc discharge material is easy
to compost
9
Percolator Discharge / Sand Separation
 Waste from the percolators is discharged via screw feeder
into a SNAP press.
 This compresses the waste and squeezes out a thick, organic
rich ‘soup’ called percolate.
 The remaining solids (known as SNAP) are conveyed to
OGM.
 The snap press baskets wear rapidly because of glass/grit in
the waste and are inspected weekly and changed as often as
monthly.
10
Sand Separation / Screening
 Percolate is discharged from the snap presses into a sand
separator – this is a settlement tank, with a screw to remove
sand and grit.
 Percolate is then pumped over a vibrating screen to sieve out
any fibres and any other remaining grit or solids.
 Percolate contains sand and grit, plus fibres and small plastic
particles.
 Percolate is ‘cleaned’ in the sand separation process in area
300 basement.
 Many of the problems with percolator availability are caused
by failures on screens, which leads to blockages in pumps.
11
Percolation Performance
 We want to make as much percolate and have it as rich in
organics (measured as COD) as possible:
 Don’t bypass.
 Leave waste in percolators for as long as possible – utilise the
space available, but ensure there is space for feed.
 Add as much irrigation as possible (but not too much!). The
waste should always be wet, but not waterlogged. For every
tonne of waste feed, add 0.6 – 0.75 tonnes of water.
 Add hot irrigation water.
 Percolate production is between 500 – 800 tonnes / week.
For each tonne of feed, we should make 0.9 tonnes of
percolate
12
320 - DIGESTION
13
Area 320
 Percolate from area 300 is stored in the digester feed tanks.
 The digester is continuously mixed with a large recirculation pump – this
pumps the entire digester contents twice per day.
 Percolate is dosed into the digester circulation flow based on an hourly
feed rate. This is set based on a number of factors:
How much percolate is available
Digester health and performance
Required gas make
Strength of percolate
Percolate Feeds
Anaerobic Digester
Feed
Tank
14
What goes in, must come out..
 As percolate is added to the digester the level will rise. It is vital that we don’t exceed
the maximum liquid level in the digester.
 Digestate is removed using the biomass centrifuge. The centrifuge separates solids
from liquid.
 The solids are the biomass (the bacteria), that make the digester work. These are
returned to the digester.
 The liquid (or centrate) is then treated to remove ammonia and is then used to
irrigate the percolators. It can also be sent off-site, or can be returned directly to the
digesters
Percolate
Anaerobic Digester
Digestate
Biomass
Centrate
Ammonia
Removal
15
Anaerobic Digestion
 A digester uses
bacteria to digest
organics.
 This happens in the
absence of oxygen (Anaerobic).
 This is a living process, so behaves
more like a cow, than a tractor.
 The bacteria require a specific set of
conditions to survive and thrive.
 The process can not be turned on &
off, it must be run continuously.
 The useful product of the process is
methane, which is used as a fuel in
the gas engines
16
Digestion Overview
AmmoniaAmmonia
AcetogensAcetogens MethanogenMethanogen
MethaneMethaneCarbon
Dioxide
Carbon
Dioxide
H2SH2S
17
Stages of digestion
 Digestion happens in two main stages. Each stage is performed by a
separate class of bacteria.
 The acetogenic bacteria take feed and break this down into VFA’s (volatile
fatty acids) like acetic acid. They also produce carbon dioxide.
 The methanogens use the VFA’s and convert into methane.
 The first stage is very robust
and happens very easily.
 The second stage is more
delicate and requires more
specific conditions. The
bacteria also take longer to
grow.
 Both stages produce by-products
like ammonia and hydrogen
sulphide.
Ammo
nia
Ammo
nia
Aceto-
genesis
Aceto-
genesis
Methano-
genesis
Methano-
genesis
Methan
e
Methan
e
Carbon
Dioxide
Carbon
Dioxide H2SH2S
18
Digester Health
 The digesters need specific conditions to operate:
 Temperature 35.5 – 38.5 DegC – (ideally 37.0 DegC)
 If the temperature is too low, the bacteria will work very slowly
and will become dormant.
 If the temperature becomes too high, the bacteria will be
destroyed.
 The digesters lose heat to their surroundings. They are also
cooled by adding percolate. The gas producing reaction is
also endothermic, so takes heat energy from the digester.
 The digesters are heated continuously using a heat
exchanger, or by returning warm centrate from the
denitrification system.
K P IK P I
19
pH & VFA’s
 The digester pH should be between 7.0 – 8.0. (Ideally around
7.7)
 VFA’s are acidic and will change the pH. The VFA’s should
be used at the same rate they are produced so the levels
should stay constant.
 VFA levels should not exceed 3000 mg/l. (Ideally below
1500mg/l)
 High VFA’s are a sign that the methanogens (the delicate
bacteria) are not working properly. This can cause the pH to
change, which will damage these bacteria further. This can
lead to a spiral of increasing VFA’s and decreasing pH, which
if unchecked could kill the digester.
K P IK P I
K P IK P I
20
Ammonia
 Ammonia is produced as a waste product when the digester
breaks down proteins.
 Too much ammonia is toxic to the digester.
 Ammonia is alkaline and will increase the digester pH.
 Some ammonia is useful as it provides an alkalinity buffer
against pH changes, which can hold the pH more stable.
 Ammonia levels should not exceed 3500 mg/l.
 Ammonia is removed by treating centrate in denitrification.
 Ammonia levels also tend to plateau and self control due to
losses when controlling digester level.
K P IK P I
21
Solids content
 The digester liquid contains solids.
 Some of these are beneficial volatile solids – these are biomass
and the organic content of the percolate feed.
 Some of these are non-volatile solids. These are mainly sand, glass
& grit in the percolate feed (some are formed in the digester).
 These nv-solids are not beneficial and make it more difficult to mix
the digester and will cause damage to pumps, pipework and valves
as they are abrasive.
 The NV-Solids content should not exceed 6%.
 Solids are removed using the raking system. This draws the heavy
sludge from the bottom of the digester and processes it through a
centrifuge to separate the solids and liquid. The solids are sent to
OGM, whilst the liquid returns to the digester.
K P IK P I
22
Methane Content
 The methanogens make methane, whilst the acetogens make carbon
dioxide - biogas is therefore a mixture of both gases.
 The methane content is a good guide to the balance between the
separate parts of the digestion process and an early warning of
problems with the methanogens.
 The methane content should always
be above 55%.
 Methane content will fall as
feed rates are increased and
climb as feed rates fall.
 Different feed can reduce the
methane concentration, for
instance molasses.
Ammo
nia
Ammo
nia
Aceto-
genesis
Aceto-
genesis
Methano-
genesis
Methano-
genesis
Methan
e
Methan
e
Carbon
Dioxid
e
Carbon
Dioxid
e
H2
S
H2
S
K P IK P I
23
340 – GAS HANDLING
24
Area 340 Overview
 Biogas is continuously produced from the digesters.
 This gas is a mixture of methane and carbon dioxide and also
contains hydrogen sulphide (H2S).
 The gas must have the H2S removed using the
desulphurisation plant.
 The gas is then stored in the ‘bubble’.
 And then used as a fuel in a pair of gas powered engines,
which are used to generate power.
 This power is used on site and reduces our reliance on power
from the national grid, which is often generated using gas or
coal.
25
Biogas Safety
 Biogas is flammable.
 Biogas will asphyxiate.
 Biogas contains H2S which is
toxic.
 Biogas is often odourless.
 Biogas is a powerful
greenhouse gas
 We must not vent biogas
to the atmosphere. K P IK P I
26
Desulphurisation
 To remove the H2S from the biogas it is bubbled through an
iron rich liquid in the gas contactor vessel on Desulph.
 The H2S bonds with the iron and dissolves into solution,
leaving clean gas.
 This solution is then regenerated by reacting with oxygen.
This produces water and elemental sulphur as a fine powder.
 The sulphur is removed from the system by filtration. The filter
press will take 1 – 7 days to fill, depending on the H2S levels
and the gas flow rates.
 Clean gas should contain less than 500 ppm H2S.
 Desulph should be online >90% of the time.
K P IK P I
K P IK P I
27
Gas Storage
 Clean gas is sent via the drier (which removes moisture) into
the gas bubble.
 The bubble holds 330m3 of gas, which dependant on gas
make can be as little as 30 minutes storage.
 Gas can then be used:
1. In the gas engines to make power and earn ROCS.
2. In the water heater to make hot water.
3. In the flare – to burn off gas, if it can’t be used.
28
Gas Engines
 We have two 950KW generators.
 Each will run between 50 – 100% load. An engine at full load
for a day will make 22.8 MWhr.
 We are able to claim 2 ROCs (Renewable Obligation
Certificates) for each MWhr we generate. Together these are
worth twice as much as the actual power.
 Biogas must be >50% CH4 to be used in the gensets.
K P IK P I

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Area 300 Training - Rev B

  • 1. 1 Area 300 - Percolation & Digestion Area Overview June 2013
  • 2. 2 UR3R Plant Overview  Waste is separated in area 200 using the two trommels.  Any waste that drops through both trommels is sent to area 300 as feed.  This is the organic part of the waste stream and is smaller than 80mm.  Typically 30-45% of waste is fed into area 300
  • 5. 5 Percolation  Percolators take a solid organic / mixed waste feed from area 200.  Typically 150 – 250 tonnes / day.  KPI is to accept 90% of available feed every day.  The amount of feed to area 300 depends on the hourly throughput in area 200 and the performance of the bag splitters and the trommels.  Waste is mixed with warm irrigation water and is mixed in the percolator.  The percolator further separates the organics from the waste stream and converts these solids into a liquid feed for the digesters. K P IK P I
  • 6. 6 ISKA® Percolation Clean Percolated Waste High Organic Waste from sorting Sand, Glass & Grit Removal Percolator Biogas Recirculated Hydrolysis Solution Air Digestion Water
  • 7. 7 KPI – Feed to Percolators  Target is 90% of available feed.  Percolators can be bypassed. This puts additional load onto OGM and reduces the percolate production.  To accept a full days feed, we need two of the three percolators to be at a low level at the start of processing.  If we don’t have this space, we need to discharge throughout the day.  If a percolator is fed too quickly, waste will build up at the feed end and start to restrict the agitator movement.  Maximum level is 60-70% - this is around the top of the agitator.
  • 8. 8 Benefits of Percolation  Creates a ‘clean’ homogenous liquid feed from a solid mixture of organics and other waste.  Allows the digesters to be operated with a liquid feed, to be single stage and to have better throughput for their size.  Allows OGM to be smaller as percs remove some organics and give mass reduction.  Perc discharge material is easy to compost
  • 9. 9 Percolator Discharge / Sand Separation  Waste from the percolators is discharged via screw feeder into a SNAP press.  This compresses the waste and squeezes out a thick, organic rich ‘soup’ called percolate.  The remaining solids (known as SNAP) are conveyed to OGM.  The snap press baskets wear rapidly because of glass/grit in the waste and are inspected weekly and changed as often as monthly.
  • 10. 10 Sand Separation / Screening  Percolate is discharged from the snap presses into a sand separator – this is a settlement tank, with a screw to remove sand and grit.  Percolate is then pumped over a vibrating screen to sieve out any fibres and any other remaining grit or solids.  Percolate contains sand and grit, plus fibres and small plastic particles.  Percolate is ‘cleaned’ in the sand separation process in area 300 basement.  Many of the problems with percolator availability are caused by failures on screens, which leads to blockages in pumps.
  • 11. 11 Percolation Performance  We want to make as much percolate and have it as rich in organics (measured as COD) as possible:  Don’t bypass.  Leave waste in percolators for as long as possible – utilise the space available, but ensure there is space for feed.  Add as much irrigation as possible (but not too much!). The waste should always be wet, but not waterlogged. For every tonne of waste feed, add 0.6 – 0.75 tonnes of water.  Add hot irrigation water.  Percolate production is between 500 – 800 tonnes / week. For each tonne of feed, we should make 0.9 tonnes of percolate
  • 13. 13 Area 320  Percolate from area 300 is stored in the digester feed tanks.  The digester is continuously mixed with a large recirculation pump – this pumps the entire digester contents twice per day.  Percolate is dosed into the digester circulation flow based on an hourly feed rate. This is set based on a number of factors: How much percolate is available Digester health and performance Required gas make Strength of percolate Percolate Feeds Anaerobic Digester Feed Tank
  • 14. 14 What goes in, must come out..  As percolate is added to the digester the level will rise. It is vital that we don’t exceed the maximum liquid level in the digester.  Digestate is removed using the biomass centrifuge. The centrifuge separates solids from liquid.  The solids are the biomass (the bacteria), that make the digester work. These are returned to the digester.  The liquid (or centrate) is then treated to remove ammonia and is then used to irrigate the percolators. It can also be sent off-site, or can be returned directly to the digesters Percolate Anaerobic Digester Digestate Biomass Centrate Ammonia Removal
  • 15. 15 Anaerobic Digestion  A digester uses bacteria to digest organics.  This happens in the absence of oxygen (Anaerobic).  This is a living process, so behaves more like a cow, than a tractor.  The bacteria require a specific set of conditions to survive and thrive.  The process can not be turned on & off, it must be run continuously.  The useful product of the process is methane, which is used as a fuel in the gas engines
  • 17. 17 Stages of digestion  Digestion happens in two main stages. Each stage is performed by a separate class of bacteria.  The acetogenic bacteria take feed and break this down into VFA’s (volatile fatty acids) like acetic acid. They also produce carbon dioxide.  The methanogens use the VFA’s and convert into methane.  The first stage is very robust and happens very easily.  The second stage is more delicate and requires more specific conditions. The bacteria also take longer to grow.  Both stages produce by-products like ammonia and hydrogen sulphide. Ammo nia Ammo nia Aceto- genesis Aceto- genesis Methano- genesis Methano- genesis Methan e Methan e Carbon Dioxide Carbon Dioxide H2SH2S
  • 18. 18 Digester Health  The digesters need specific conditions to operate:  Temperature 35.5 – 38.5 DegC – (ideally 37.0 DegC)  If the temperature is too low, the bacteria will work very slowly and will become dormant.  If the temperature becomes too high, the bacteria will be destroyed.  The digesters lose heat to their surroundings. They are also cooled by adding percolate. The gas producing reaction is also endothermic, so takes heat energy from the digester.  The digesters are heated continuously using a heat exchanger, or by returning warm centrate from the denitrification system. K P IK P I
  • 19. 19 pH & VFA’s  The digester pH should be between 7.0 – 8.0. (Ideally around 7.7)  VFA’s are acidic and will change the pH. The VFA’s should be used at the same rate they are produced so the levels should stay constant.  VFA levels should not exceed 3000 mg/l. (Ideally below 1500mg/l)  High VFA’s are a sign that the methanogens (the delicate bacteria) are not working properly. This can cause the pH to change, which will damage these bacteria further. This can lead to a spiral of increasing VFA’s and decreasing pH, which if unchecked could kill the digester. K P IK P I K P IK P I
  • 20. 20 Ammonia  Ammonia is produced as a waste product when the digester breaks down proteins.  Too much ammonia is toxic to the digester.  Ammonia is alkaline and will increase the digester pH.  Some ammonia is useful as it provides an alkalinity buffer against pH changes, which can hold the pH more stable.  Ammonia levels should not exceed 3500 mg/l.  Ammonia is removed by treating centrate in denitrification.  Ammonia levels also tend to plateau and self control due to losses when controlling digester level. K P IK P I
  • 21. 21 Solids content  The digester liquid contains solids.  Some of these are beneficial volatile solids – these are biomass and the organic content of the percolate feed.  Some of these are non-volatile solids. These are mainly sand, glass & grit in the percolate feed (some are formed in the digester).  These nv-solids are not beneficial and make it more difficult to mix the digester and will cause damage to pumps, pipework and valves as they are abrasive.  The NV-Solids content should not exceed 6%.  Solids are removed using the raking system. This draws the heavy sludge from the bottom of the digester and processes it through a centrifuge to separate the solids and liquid. The solids are sent to OGM, whilst the liquid returns to the digester. K P IK P I
  • 22. 22 Methane Content  The methanogens make methane, whilst the acetogens make carbon dioxide - biogas is therefore a mixture of both gases.  The methane content is a good guide to the balance between the separate parts of the digestion process and an early warning of problems with the methanogens.  The methane content should always be above 55%.  Methane content will fall as feed rates are increased and climb as feed rates fall.  Different feed can reduce the methane concentration, for instance molasses. Ammo nia Ammo nia Aceto- genesis Aceto- genesis Methano- genesis Methano- genesis Methan e Methan e Carbon Dioxid e Carbon Dioxid e H2 S H2 S K P IK P I
  • 23. 23 340 – GAS HANDLING
  • 24. 24 Area 340 Overview  Biogas is continuously produced from the digesters.  This gas is a mixture of methane and carbon dioxide and also contains hydrogen sulphide (H2S).  The gas must have the H2S removed using the desulphurisation plant.  The gas is then stored in the ‘bubble’.  And then used as a fuel in a pair of gas powered engines, which are used to generate power.  This power is used on site and reduces our reliance on power from the national grid, which is often generated using gas or coal.
  • 25. 25 Biogas Safety  Biogas is flammable.  Biogas will asphyxiate.  Biogas contains H2S which is toxic.  Biogas is often odourless.  Biogas is a powerful greenhouse gas  We must not vent biogas to the atmosphere. K P IK P I
  • 26. 26 Desulphurisation  To remove the H2S from the biogas it is bubbled through an iron rich liquid in the gas contactor vessel on Desulph.  The H2S bonds with the iron and dissolves into solution, leaving clean gas.  This solution is then regenerated by reacting with oxygen. This produces water and elemental sulphur as a fine powder.  The sulphur is removed from the system by filtration. The filter press will take 1 – 7 days to fill, depending on the H2S levels and the gas flow rates.  Clean gas should contain less than 500 ppm H2S.  Desulph should be online >90% of the time. K P IK P I K P IK P I
  • 27. 27 Gas Storage  Clean gas is sent via the drier (which removes moisture) into the gas bubble.  The bubble holds 330m3 of gas, which dependant on gas make can be as little as 30 minutes storage.  Gas can then be used: 1. In the gas engines to make power and earn ROCS. 2. In the water heater to make hot water. 3. In the flare – to burn off gas, if it can’t be used.
  • 28. 28 Gas Engines  We have two 950KW generators.  Each will run between 50 – 100% load. An engine at full load for a day will make 22.8 MWhr.  We are able to claim 2 ROCs (Renewable Obligation Certificates) for each MWhr we generate. Together these are worth twice as much as the actual power.  Biogas must be >50% CH4 to be used in the gensets. K P IK P I