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1
ST Classification: UNMARKED
Circular solutions for
Relevant data
Lead partners
Relevant sectors
#5.
Spernal (UK)
Waste Water Treatment Plant
Water Materials Energy
Spernal WWTP serves as Severn Trent Water’s “Resource
Recovery and Innovation Centre” where emerging
technologies compatible with a low energy, circular
economy approach will be evaluated.
A multi-stream test bed facility was constructed in 2019 and
this will incorporate an anaerobic membrane bioreactor
(AnMBR) to be commissioned in January 2020.
AnMBR combines several benefits such as:
• no aeration energy for removal of Chemical and Biological
Oxygen Demand (COD/BOD)
• low sludge production and hence reduced downstream
sludge treatment costs
• biogas production (production of electricity/heat
• pathogen and solids free effluent which can be re-used in a
number of applications (e.g.: farming and industrial use).
Waste water plant serving the town of Redditch
(Birmingham, UK): 92.000 PE
Agriculture Domestic sector Energy sector
2
ST Classification: UNMARKED
1. Objectives of the NextGen solutions
 Nutrient removal and recovery through adsorption or
ion exchange technologies
 AnMBR demonstration in cold climate northern
European countries with a membrane degassing unit to
recover dissolved methane for water and energy reuse
3
ST Classification: UNMARKED
Technology Evidence Base (TEB).
Initial draft – to be finalised in D1.6
Spernal
Positioning of demo case within the CE
1. Objectives of the NextGen solutions
4
ST Classification: UNMARKED
2. New NextGen solutions
Scheme of the new Nextgen solution
5
ST Classification: UNMARKED
2. New NextGen solutions
The anaerobic membrane bioreactor (AnMBR) pilot plant comprises 3 main process units
1. Upflow anaerobic sludge blanket reactor (UASB)
• Technology provider - Waterleau
• This will be housed in three 20’ shipping containers mounted one on top of the other
• The UASB will contain granular sludge and have a 3 phase separator at the top of the reactor
• Most of the solids will be retained in the UASB, the effluent will be directed to the UF membrane and the biogas will
be sent to the on-site gas bag
• Currently delivered to R2IC and undergoing installation and system testing
2. Ultra-filtration (UF) membrane
• Technology provider – SFC / Trant Engineering
• This will be housed in two 20’ shipping containers
• The UF membrane will remove any remaining solids from the effluent returning the sludge to the UASB and the
effluent to the membrane contactor for degassing
• Currently delivered to R2IC and undergoing wet testing
3. Membrane contactor for degassing
• Technology provider – 3M (Membrane)
• The membrane contactor will remove the dissolved methane from the effluent
• The methane will be sent to the gas bag and the effluent to the ion exchange nutrient recovery plant
• Membrane modules on site and system build underway
Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
6
ST Classification: UNMARKED
2. New NextGen solutions
Ion Exchange (IEX) nutrient recovery pilot plant - 10 m3/day, 4 main process units
1. N removal column
• Contains 70L of Zeolite, operated at an empty bed contact time of 10-30 min
• Zeolite needs regeneration when ammonia in the effluent is > 5 mg/L
• Zeolite is regenerated with NaCl or KCl
2. P removal column
• Contains 35L of hybrid anion exchange (HAIX), LayneRT (Layne, USA), Operated at an empty bed contact time of
5-15 min
• HAIX needs regeneration when phosphorus in the effluent is > 2-3 mg/L
• HAIX is regenerated with NaOH
3. N recovery
• Ammonia stripping or membrane processes can be used to produced ammonia solution at 3-5% or ammonium
sulphate, respectively. The regenerant is re-used.
4. P recovery
• Addition of CaOH to the spent regenerant, results in the immediate precipitation of CaP that is filtered from the
regenerant. The regenerant is re-used.
Task 1.4.5 Nutrient removal and recovery from AnMBR effluent for local reuse
7
ST Classification: UNMARKED
 AnMBR under construction at R2IC and plant in use
forecast for Jan 2021.
 Current status (November 2020)
• UASB interface pipe work under construction
• UF membrane installed and wet tested
• De-gas system civils works complete.
2. New NextGen solutions
Waterleau UASB
SCF UF
3M De-gas
R2IC Gas handling
R2IC Chemical
dosing rig
R2IC
wastewater
tank
Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
8
ST Classification: UNMARKED
2. New NextGen solutions
Granular sludge supplied by Waterleau Pilot scale UASB reactors
Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
9
ST Classification: UNMARKED
2. New NextGen solutions
Pilot scale membrane module
Membrane
cartridge is
kept
suspended
inside the
membrane
tank
Cover
Cartridge
Several hundreds of parallel fibres (1-3 m long with an outside
diameter of 0.3-0.5 mm) are wound up around a carrier cartridge
The cartridge has a permeate connection on the top and an
air/biogas connection for gas sparging on the bottom
Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
10
ST Classification: UNMARKED
2. New NextGen solutions
Pilot scale nutrient recovery Ion Exchange (IEX) reactors
mesolite for N recovery nano-particle imbedded IEX
beads for P recovery
Adsorption media used in the columns
Task 1.4.5 Nutrient removal and recovery from AnMBR effluent for local reuse
11
ST Classification: UNMARKED
3. Specific KPIs (actual vs expected)
Case
study
Topic Objectives
Specific Key Performance
Indicator (KPI)
Current value Expected value
#5
Speranl
(UK)
Wastewater treatment and reuse
To increase reuse application for
external uses
Volume of water recovered and its
use (m3/day)
Not specified 500
Water yield of the system (produc
ed/collected, %)
Not yet measured
Not specified
To enhance water quality:
Influent and effluent quality –
Rejection rate [%]
Salinity Not yet measured Not specified
BOD Not yet measured 95% removal
COD Not yet measured 90% removal
SS Not yet measured 100% removal
Turbidity Not yet measured 100% removal
TN Not yet measured 60-80% removal
TP Not yet measured 70-90% removal
To reduce the pathogens content of
the effluent
E.Coli [CFU/100 ml] Not yet measured 0
Legionella spp. [CFU/100 ml] Not yet measured 0
Organics removal Pesticides and pharmaceuticals Not yet measured Not specified
Energy
Energy recovery – create energy
neutral WWTP and export to
community (biogas)
Methane yield [m3 CH4/(kg COD)] Not yet measured 0.19-0.28
Quantity of re-used heat (seasonal,
m3/d)
Not yet measured 11-33
Energy consumption [kWh/m3] Not yet measured Not specified
Energy generation [kWh/m3] Not yet measured Not specified
Materials
To recover nutrients from
wastewater effluent
Calcium phosphate (as P, kg/day) Not yet measured 0.03
Ammonium sulphate (as N, kg/day) Not yet measured 0.22
12
ST Classification: UNMARKED
4. Results
The wastewater has very low
strength, making the UASB
operation very challenging, as
anaerobic processes are favoured
by high organic loading rates
The pilot UASB reactor, which
mimics the reactor in Spernal, is
producing the expected effluent
quality
The link to the MBR tank is delayed
due to the closing of the pilot site for
4 months and supply chain issues
Data on methane production are
sparce and more data points are
required
OCT 2020 – ongoing (T=13°C)
Biogas production L d-1 0.6
Dissolved CH4/total CH4 % 93.6
Methane yield L CH4/g COD 0.13
JUL-SEPT 2020 (T=18°C)
Characterisation
Removal rates (%)
Influent UASB effluent
COD mg L-1
153 56 63
sCOD mg L-1
36 29 19
BOD5 mg L-1
65 38 42
TSS mg L-1
117 37 68
VSS mg L-1
108 31 71
SO4 mg L-1
62 40 35
OCT 2020 – ongoing
(T=13°C)
Characterisation
Removal rates (%)
Influent UASB effluent
COD mg L-1
195 103 47
sCOD mg L-1
44 39 11
BOD5 mg L-1
73 44 40
TSS mg L-1
120 40 67
VSS mg L-1
103 36 65
SO4 mg L-1
69 43 38
13
ST Classification: UNMARKED
5. Lessons learned
 Pilot Operation (at Cranfield)
• fast start up of the UASB with commercial granular sludge from pulp and
paper industry
• no significant difference in the UASB effluent between the commercial
granular sludge and acclimatised sludge
 Construction of demonstration facility at Spernal
 The HAZOP / explosive atmosphere zoning assessment has highlighted that
managing partially de-gassed effluent requires further investigation on the
release of dissolved methane in drainage systems.
 Process design development highlighted the opportunity to recycle water
feed for vacuum pumps to significantly reduce potable water demand
 Pilot work and initial supplier guidance is suggesting a 3 week process
stabilisation period which has been built into the commissioning
programme
14
ST Classification: UNMARKED
Thank you!
xtGen - Community of Practice

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NextGen Spernal United Kingdom

  • 1. 1 ST Classification: UNMARKED Circular solutions for Relevant data Lead partners Relevant sectors #5. Spernal (UK) Waste Water Treatment Plant Water Materials Energy Spernal WWTP serves as Severn Trent Water’s “Resource Recovery and Innovation Centre” where emerging technologies compatible with a low energy, circular economy approach will be evaluated. A multi-stream test bed facility was constructed in 2019 and this will incorporate an anaerobic membrane bioreactor (AnMBR) to be commissioned in January 2020. AnMBR combines several benefits such as: • no aeration energy for removal of Chemical and Biological Oxygen Demand (COD/BOD) • low sludge production and hence reduced downstream sludge treatment costs • biogas production (production of electricity/heat • pathogen and solids free effluent which can be re-used in a number of applications (e.g.: farming and industrial use). Waste water plant serving the town of Redditch (Birmingham, UK): 92.000 PE Agriculture Domestic sector Energy sector
  • 2. 2 ST Classification: UNMARKED 1. Objectives of the NextGen solutions  Nutrient removal and recovery through adsorption or ion exchange technologies  AnMBR demonstration in cold climate northern European countries with a membrane degassing unit to recover dissolved methane for water and energy reuse
  • 3. 3 ST Classification: UNMARKED Technology Evidence Base (TEB). Initial draft – to be finalised in D1.6 Spernal Positioning of demo case within the CE 1. Objectives of the NextGen solutions
  • 4. 4 ST Classification: UNMARKED 2. New NextGen solutions Scheme of the new Nextgen solution
  • 5. 5 ST Classification: UNMARKED 2. New NextGen solutions The anaerobic membrane bioreactor (AnMBR) pilot plant comprises 3 main process units 1. Upflow anaerobic sludge blanket reactor (UASB) • Technology provider - Waterleau • This will be housed in three 20’ shipping containers mounted one on top of the other • The UASB will contain granular sludge and have a 3 phase separator at the top of the reactor • Most of the solids will be retained in the UASB, the effluent will be directed to the UF membrane and the biogas will be sent to the on-site gas bag • Currently delivered to R2IC and undergoing installation and system testing 2. Ultra-filtration (UF) membrane • Technology provider – SFC / Trant Engineering • This will be housed in two 20’ shipping containers • The UF membrane will remove any remaining solids from the effluent returning the sludge to the UASB and the effluent to the membrane contactor for degassing • Currently delivered to R2IC and undergoing wet testing 3. Membrane contactor for degassing • Technology provider – 3M (Membrane) • The membrane contactor will remove the dissolved methane from the effluent • The methane will be sent to the gas bag and the effluent to the ion exchange nutrient recovery plant • Membrane modules on site and system build underway Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
  • 6. 6 ST Classification: UNMARKED 2. New NextGen solutions Ion Exchange (IEX) nutrient recovery pilot plant - 10 m3/day, 4 main process units 1. N removal column • Contains 70L of Zeolite, operated at an empty bed contact time of 10-30 min • Zeolite needs regeneration when ammonia in the effluent is > 5 mg/L • Zeolite is regenerated with NaCl or KCl 2. P removal column • Contains 35L of hybrid anion exchange (HAIX), LayneRT (Layne, USA), Operated at an empty bed contact time of 5-15 min • HAIX needs regeneration when phosphorus in the effluent is > 2-3 mg/L • HAIX is regenerated with NaOH 3. N recovery • Ammonia stripping or membrane processes can be used to produced ammonia solution at 3-5% or ammonium sulphate, respectively. The regenerant is re-used. 4. P recovery • Addition of CaOH to the spent regenerant, results in the immediate precipitation of CaP that is filtered from the regenerant. The regenerant is re-used. Task 1.4.5 Nutrient removal and recovery from AnMBR effluent for local reuse
  • 7. 7 ST Classification: UNMARKED  AnMBR under construction at R2IC and plant in use forecast for Jan 2021.  Current status (November 2020) • UASB interface pipe work under construction • UF membrane installed and wet tested • De-gas system civils works complete. 2. New NextGen solutions Waterleau UASB SCF UF 3M De-gas R2IC Gas handling R2IC Chemical dosing rig R2IC wastewater tank Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
  • 8. 8 ST Classification: UNMARKED 2. New NextGen solutions Granular sludge supplied by Waterleau Pilot scale UASB reactors Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
  • 9. 9 ST Classification: UNMARKED 2. New NextGen solutions Pilot scale membrane module Membrane cartridge is kept suspended inside the membrane tank Cover Cartridge Several hundreds of parallel fibres (1-3 m long with an outside diameter of 0.3-0.5 mm) are wound up around a carrier cartridge The cartridge has a permeate connection on the top and an air/biogas connection for gas sparging on the bottom Task 1.2.3 Multi-stream anaerobic MBR for district-scale reuse applications
  • 10. 10 ST Classification: UNMARKED 2. New NextGen solutions Pilot scale nutrient recovery Ion Exchange (IEX) reactors mesolite for N recovery nano-particle imbedded IEX beads for P recovery Adsorption media used in the columns Task 1.4.5 Nutrient removal and recovery from AnMBR effluent for local reuse
  • 11. 11 ST Classification: UNMARKED 3. Specific KPIs (actual vs expected) Case study Topic Objectives Specific Key Performance Indicator (KPI) Current value Expected value #5 Speranl (UK) Wastewater treatment and reuse To increase reuse application for external uses Volume of water recovered and its use (m3/day) Not specified 500 Water yield of the system (produc ed/collected, %) Not yet measured Not specified To enhance water quality: Influent and effluent quality – Rejection rate [%] Salinity Not yet measured Not specified BOD Not yet measured 95% removal COD Not yet measured 90% removal SS Not yet measured 100% removal Turbidity Not yet measured 100% removal TN Not yet measured 60-80% removal TP Not yet measured 70-90% removal To reduce the pathogens content of the effluent E.Coli [CFU/100 ml] Not yet measured 0 Legionella spp. [CFU/100 ml] Not yet measured 0 Organics removal Pesticides and pharmaceuticals Not yet measured Not specified Energy Energy recovery – create energy neutral WWTP and export to community (biogas) Methane yield [m3 CH4/(kg COD)] Not yet measured 0.19-0.28 Quantity of re-used heat (seasonal, m3/d) Not yet measured 11-33 Energy consumption [kWh/m3] Not yet measured Not specified Energy generation [kWh/m3] Not yet measured Not specified Materials To recover nutrients from wastewater effluent Calcium phosphate (as P, kg/day) Not yet measured 0.03 Ammonium sulphate (as N, kg/day) Not yet measured 0.22
  • 12. 12 ST Classification: UNMARKED 4. Results The wastewater has very low strength, making the UASB operation very challenging, as anaerobic processes are favoured by high organic loading rates The pilot UASB reactor, which mimics the reactor in Spernal, is producing the expected effluent quality The link to the MBR tank is delayed due to the closing of the pilot site for 4 months and supply chain issues Data on methane production are sparce and more data points are required OCT 2020 – ongoing (T=13°C) Biogas production L d-1 0.6 Dissolved CH4/total CH4 % 93.6 Methane yield L CH4/g COD 0.13 JUL-SEPT 2020 (T=18°C) Characterisation Removal rates (%) Influent UASB effluent COD mg L-1 153 56 63 sCOD mg L-1 36 29 19 BOD5 mg L-1 65 38 42 TSS mg L-1 117 37 68 VSS mg L-1 108 31 71 SO4 mg L-1 62 40 35 OCT 2020 – ongoing (T=13°C) Characterisation Removal rates (%) Influent UASB effluent COD mg L-1 195 103 47 sCOD mg L-1 44 39 11 BOD5 mg L-1 73 44 40 TSS mg L-1 120 40 67 VSS mg L-1 103 36 65 SO4 mg L-1 69 43 38
  • 13. 13 ST Classification: UNMARKED 5. Lessons learned  Pilot Operation (at Cranfield) • fast start up of the UASB with commercial granular sludge from pulp and paper industry • no significant difference in the UASB effluent between the commercial granular sludge and acclimatised sludge  Construction of demonstration facility at Spernal  The HAZOP / explosive atmosphere zoning assessment has highlighted that managing partially de-gassed effluent requires further investigation on the release of dissolved methane in drainage systems.  Process design development highlighted the opportunity to recycle water feed for vacuum pumps to significantly reduce potable water demand  Pilot work and initial supplier guidance is suggesting a 3 week process stabilisation period which has been built into the commissioning programme
  • 14. 14 ST Classification: UNMARKED Thank you! xtGen - Community of Practice