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IWOX®
systems engineered by DMT
The next standard in small scale wastewater treatment
Authors: Joost Edens
1
, Robert Lems
2
, Erwin H.M. Dirkse
3
1
Process eng. DMT B(a)Sc,
2
Manager R&D DMT MSc,
3
Managing Director DMT B(a)Sc.
Date: Monday, 04 November 2013
Companies: DMT Environmental Technology, The Netherlands. Viltra, partner of DMT, Northern Ireland.
ABSTRACT
Both technology and environmental awareness drive legislation for wastewater treatment. Now, the leap from 20/30
(BOD: Biological oxygen demand, mg/l / SS: suspended solids, mg/l) to 10/10 or even 5/5 is possible due to a
different design approach. For years, the sewage treatment plant market was dominated by systems from (septic)
tank suppliers, but now an engineering company from Holland (DMT Environmental Technology) has implemented its
experience from large wastewater treatment plants to design small scale sewage treatment plants (STPs). This
downscaling trajectory started in 2000 with concrete systems and developed to light weight modulated systems. The
current generation STPs engineered by DMT are two different systems, both extensively tested with a CE-certification
period of 40 weeks at the independent university “Van Hall Institute”, an accredited test house based in the
Netherlands. Analyzed discharge pollution concentrations showed that qualities lower then 10/10 (The IWOX
®
Premium-Standard) and even lower than 5/5 (mg/l BOD/SS) (The IWOX
®
Superior) were reached with complete
nitrification. The DMT IWOX
®
Superior also removes Nitrogen (N) by denitrification, which is in line with the scope of
the European Framework Directive. Future development of treatment technology will lead to further reduction of SS,
BOD, Nitrogen and Phosphate. It will also become possible to remove pathogens in the discharge. and DMT are
already anticipating these possibilities by developing special filters and Ultra Filtration membranes for their STPs.
With the continuous improving STP’s, easily capable to reach better discharge qualities then described by legislation,
the main question at this moment is : is the current legislation out of date?
KEY WORDS
Biochemical Oxygen Demand, denitrification, The
DMT IWOX
®
, eutrophication, nitrification, small
scale waste water treatment, STP, suspended
solids.
INTRODUCTION
Discharge of domestic wastewater without
treatment has different ecological consequences,
especially in small water courses. Pollution from
BOD, NH4 and SS causes depletion of oxygen,
which results in possible starvation of smaller and
larger organisms. Furthermore, the emission of
nitrogen (N), phosphate (P) in the ground- or
surface water may result in an overload of nutrients
(eutrophication). The overload enhances excessive
growth of various species in both soil (fast growing
vegetation) and water (algae). This can destroy
sensitive and valuable ecosystems or endanger
drinking water facilities. Emission of BOD, SS, N
and P is already restricted for surface water
according to the European Framework Directive,
and will become restricted for groundwater from
2013 as well.
Looking at the UK (Northern Ireland) and the
Republic of Ireland around 25 % of the waste water
is not treated and another 7 % only primarily.
(2004-2005, EPA, McCumsikey, 2007). The
investment in centralized WWTP’s is too expensive
due to the large distances between houses and
farms. To treat the waste water “on-site” is a better
solution for this problem, however the quality of the
treated water greatly depends on the treatment
technology.
HISTORICAL DEVELOPMENT
From the middle ages faeces were dumped
everywhere. Storage tanks were implemented to
prevent spreading of diseases. These septic tanks
mostly consist of only one chamber and remove 25
to 40 % of the pollutant due to settlement. Due to
rotting processes, these septic tanks are smelly
and dangerous (formation of toxic Hydrogen
Sulphide, H2S) as well as possibly explosive due to
the formation of methane gas (CH4). Therefore the
septic tank has been upgraded by adding an air
blower. The implemented oxygen is being brought
into the water limiting the formation of H2S and CH4.
This also enhances the biological degradation of
COD and NH4. However the air bubbles created
turbulence, which prevented particle settlement
and increased the SS-concentration in the
discharge. A large settlement tank was added to
reduce the SS to achieve a final quality of 20 mg/l
BOD and 30 mg/l SS. These systems (figure 1)
now set the standard both in legislation and
technology in Ireland. Reduction to 5/5 is only
possible by non CE-certified reed beds.
At present some STP tank manufacturers are
trying to increase effluent quality to BOD/SS of
15/30 mg/l. With the development of packed media,
rotating disks etc even a discharge of 10/13 has
been claimed. However this design greatly
complicates the system and increases the chance
of failures and still has minimal nitrification and no
nitrogen removal.
2
Figure 1; current storage systems.
Now DMT has entered the market with a STP
which has been engineered based on down scaling
WWTP technology. These systems easily achieve
10/10 effluent quality with complete NH4 removal
and can even reach better than 5/5 with nitrogen
removal. This makes it possible to meet current
and future legislation.
THEORY
Wastewater can contain various pollutants, in total
being determined as the Chemical Oxygen
Demand (COD, mgO2/l). The COD-value
represents the amount of oxygen required to
chemically degrade all pollutants. Part of the COD
is the “biological oxygen demand” (BOD, mg O2/l).
This represents the amount of pollutants which can
be degraded biologically. In domestic wastewater
this usually is 50 to 80 % of the COD. Main
degradation reaction is;
BiomassOHCOOBODCOD ++→+ 222)(
Other pollutants contain nitrogen (N). About 50 %
to 90 % of the nitrogen compound is ammonium
(NH4). Biological degradation goes in three steps;
first the nitrogen compounds are converted to NH4.
The ammonium is then degraded to nitrate (NO3)
with the addition of oxygen. When bacteria are not
aerated any more, the NO3 can be converted to
nitrogen gas (N2) with the addition of BOD. The
harmless N2 (nitrogen gas) is released into the
atmosphere. Degradation reactions are;
NH4 + O2 → NO3 + H + H2O
BOD + NO3 → N2 + CO2 +H2O
Degradation of NH4 to NO3 is called nitrification,
conversion from NO3 to N2 denitrification.
DESIGNING WWTP
Using years and years of experience in wastewater
engineering, DMT started in 2000 designing and
developing small scale treatment plants (STP’s).
Implementing its knowledge from large WWTP’s
resulted in a complete new design for the STP. The
pollutants are solely removed by flocks of micro
organisms (sludge) without interference of packed
media, discs or other carriers. To avoid any change
of clogging, DMT chose specifically using only
activated sludge for treatment, a proved technology.
The only one mechanical part used is a robust
blower. A sophisticated circulation system
equalizes influent flow fluctuations and prevents
sludge build up as well as SS wash out in a
compact two stage settlement tank. The circulation
system also makes it possible to implement both
nitrification as well as denitrification removing
nitrogen from the waste water.
To enable the sludge-water mixture to circulate,
good settlement is required. In normal WWTP this
is accomplished in large clarifiers. Here, sludge
settles and is circulated back. From existing
dimensioning parameters, a novel highly advanced
and compact clarifier has been developed by DMT.
In picture 1 samples of a well functioning activated
sludge system are shown.
Another new development in STP’s is the use of
the denitrification zone. In this zone, conversion of
NO3 to N2 takes place. The formed nitrogen gas
(N2) can escape to the surrounding air and is not
captured in the sludge. Because of this controlled
denitrification, no NO3 is left after treatment and no
flotation of sludge occur in the settlement tank,
further reducing SS concentrations in the effluent.
IWOX
®
engineered by DMT
Using previously explained theory while keeping
the typical domestic wastewater fluctuations (flow,
COD) in mind, DMT developed from waste water
engineering point of view two novel treatment
systems. Starting in 2000, a concrete system was
certified according to high Dutch standards (BRL
K10002). The current light weight modulated
systems are the next generation STP’s, which have
a reduced footprint and still are capable to reach
discharge values of <10/10 or even <5/5 (Van Hall
Institute, CE certification (NEN-EN 12566-3) and
been designed in conjunction with our partner
company . One existing out of 2 tank (3
compartments), named the DMT IWOX
®
Standard
or IWOX
®
Premium. The other one consists out of
3 tanks (5 compartments), the IWOX
®
Superior.
Picture 1; Picture with three samples (left to
right) influent, activated sludge mixture,
effluent.
3
Figure 2; Flow Schedule IWOX
®
Standard-
Premium.
Figure 2 illustrates a simplified flow schedule of the
IWOX
®
Standard-Premium. Raw wastewater enters
the pre-settlement tank, where large solids settle.
The large variations of influent flows are controlled,
and the water flows gradually to the 2
nd
tank. Here,
wastewater is optimally brought into contact with
micro organisms and air. The micro organisms
(present as sludge) settle in a highly advanced
shaped clarification tank and are returned to the
biological compartment. The purified water then
leaves the system.
Figure 3; Flow Schedule IWOX
®
Superior.
Differences between the Superior (Figure 3) and
the Standard-Premium system are the
implemented denitrification zone (NO3 to N2) and
the second clarifier. The denitrification zone makes
it possible to remove nitrogen, and BOD is further
reduced (both consumed by denitrifying bacteria).
Due to the denitrification, the SS in the effluent is
also lowered. The back-up clarification step is
implemented to minimize wash out of SS even at
peak flows or other disturbances. These
differences reduce the BOD and SS concentrations
to the strictest Irish demand of 5/5. Reduction up to
70 % of Nitrogen is caused due to the
denitrification as well.
Graph 1; BOD, SS concentrations and removal
efficiencies of the IWOX
®
Superior.
With these high removal efficiencies shown in
Graph 1, this system is an alternative to the
standard 20/30 systems with a reed bed. The DMT
system requires only 1/14
th
of the surface
compared to a standard system (shown in image 1).
Image 1; Indicative footprint difference between
footprint of an IWOX
®
Superior (0.8 m
2
) and a
classical 20-30 system (3.2m
2
) + reed bed (8 m
2
).
4
Graph 2; Overview development treatment technologies
1) Data from Balmoral Hydroclear, COD estimated
2) The DMT IWOX®
Superior + grid preliminary results
3) Estimated results IWOX®
Superior with membranes
At this moment, DMT is further developing the
systems by implementing a post-clarifying grid
and/or membranes. First tests with the grid indicate
an improvement for advanced reduction or
complete removal of SS. This system will be further
developed in the near future
CONCLUSION
Treatment of wastewater is required to avoid
environmental problems. Current STP systems set
the technology and legislation standard in Ireland,
and are only achieving 20/30 discharge without
nitrogen removal. Further removal to 5/5 is only
possible with addition of non-certified reed bed
systems. Designing from a waste water
engineering point of view rather than just tank
manufacturing led to the easily better performing /
the IWOX
®
systems. These differences in approach
resulted in far higher removal efficiencies of BOD
and SS and also total removal of ammonium, all
achieved in one compact system (Pictures 2 until 5,
below). Following the European Framework
Directive, nitrogen removal is also standard with
the IWOX
®
Superior, reducing
eutrophication in the environment. At this moment,
novel treatment technologies further reducing
nitrogen, phosphates as well as pathogens are in
development. These will become economically
feasible in the near future.
IS CURRENT LEGISLATION OUT OF DATE?
Current available systems reach easily higher
discharge qualities at economical costs then
described by legislation. An upcoming requirement
in Ireland will be nitrogen removal. Could it
therefore be the case that the current legislation is
out of date?
REFERENCES
Balmoral Hydroclear product sheet.
EPA, 2004-2005. Urban Waste Water Discharges
in Ireland for Population Equivalents greater
than 500 persons. Office of Environmental
Enforcement.
Independent University Van Hall Institute,
department of Agricultural University and
Reseach centre Wageningen.
L. M. McCumiskey, 2007. BE, MSc, FIEI, MICE*P.
F. TONER, PhD, Director and Section Head,
respectively, Environmental Research Unit,
Dublin, Water and Environment Journal,
Volume 6 Issue 1, Pages 89 - 100, Published
Online 26 Jul 2007
Graph 2 shows the development of
treatment technologies commencing
septic tanks. According to the ALARA
(As Low As Reasonably Achievable) the
law should be adjusted to the current
economical best technology.
5
Picture 2; Picture of a IWOX
®
Superior after
placement in Ireland
Picture 3; the IWOX
®
Superior being placed in
Ireland
Picture 4; Robust and light-weighted IWOX
®
Superior being placed in Greece
Picture 5; the IWOX
®
after placement in the
Netherlands

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WASTEWATER engineering.pptx
 

The IWOX®systems

  • 1. 1 IWOX® systems engineered by DMT The next standard in small scale wastewater treatment Authors: Joost Edens 1 , Robert Lems 2 , Erwin H.M. Dirkse 3 1 Process eng. DMT B(a)Sc, 2 Manager R&D DMT MSc, 3 Managing Director DMT B(a)Sc. Date: Monday, 04 November 2013 Companies: DMT Environmental Technology, The Netherlands. Viltra, partner of DMT, Northern Ireland. ABSTRACT Both technology and environmental awareness drive legislation for wastewater treatment. Now, the leap from 20/30 (BOD: Biological oxygen demand, mg/l / SS: suspended solids, mg/l) to 10/10 or even 5/5 is possible due to a different design approach. For years, the sewage treatment plant market was dominated by systems from (septic) tank suppliers, but now an engineering company from Holland (DMT Environmental Technology) has implemented its experience from large wastewater treatment plants to design small scale sewage treatment plants (STPs). This downscaling trajectory started in 2000 with concrete systems and developed to light weight modulated systems. The current generation STPs engineered by DMT are two different systems, both extensively tested with a CE-certification period of 40 weeks at the independent university “Van Hall Institute”, an accredited test house based in the Netherlands. Analyzed discharge pollution concentrations showed that qualities lower then 10/10 (The IWOX ® Premium-Standard) and even lower than 5/5 (mg/l BOD/SS) (The IWOX ® Superior) were reached with complete nitrification. The DMT IWOX ® Superior also removes Nitrogen (N) by denitrification, which is in line with the scope of the European Framework Directive. Future development of treatment technology will lead to further reduction of SS, BOD, Nitrogen and Phosphate. It will also become possible to remove pathogens in the discharge. and DMT are already anticipating these possibilities by developing special filters and Ultra Filtration membranes for their STPs. With the continuous improving STP’s, easily capable to reach better discharge qualities then described by legislation, the main question at this moment is : is the current legislation out of date? KEY WORDS Biochemical Oxygen Demand, denitrification, The DMT IWOX ® , eutrophication, nitrification, small scale waste water treatment, STP, suspended solids. INTRODUCTION Discharge of domestic wastewater without treatment has different ecological consequences, especially in small water courses. Pollution from BOD, NH4 and SS causes depletion of oxygen, which results in possible starvation of smaller and larger organisms. Furthermore, the emission of nitrogen (N), phosphate (P) in the ground- or surface water may result in an overload of nutrients (eutrophication). The overload enhances excessive growth of various species in both soil (fast growing vegetation) and water (algae). This can destroy sensitive and valuable ecosystems or endanger drinking water facilities. Emission of BOD, SS, N and P is already restricted for surface water according to the European Framework Directive, and will become restricted for groundwater from 2013 as well. Looking at the UK (Northern Ireland) and the Republic of Ireland around 25 % of the waste water is not treated and another 7 % only primarily. (2004-2005, EPA, McCumsikey, 2007). The investment in centralized WWTP’s is too expensive due to the large distances between houses and farms. To treat the waste water “on-site” is a better solution for this problem, however the quality of the treated water greatly depends on the treatment technology. HISTORICAL DEVELOPMENT From the middle ages faeces were dumped everywhere. Storage tanks were implemented to prevent spreading of diseases. These septic tanks mostly consist of only one chamber and remove 25 to 40 % of the pollutant due to settlement. Due to rotting processes, these septic tanks are smelly and dangerous (formation of toxic Hydrogen Sulphide, H2S) as well as possibly explosive due to the formation of methane gas (CH4). Therefore the septic tank has been upgraded by adding an air blower. The implemented oxygen is being brought into the water limiting the formation of H2S and CH4. This also enhances the biological degradation of COD and NH4. However the air bubbles created turbulence, which prevented particle settlement and increased the SS-concentration in the discharge. A large settlement tank was added to reduce the SS to achieve a final quality of 20 mg/l BOD and 30 mg/l SS. These systems (figure 1) now set the standard both in legislation and technology in Ireland. Reduction to 5/5 is only possible by non CE-certified reed beds. At present some STP tank manufacturers are trying to increase effluent quality to BOD/SS of 15/30 mg/l. With the development of packed media, rotating disks etc even a discharge of 10/13 has been claimed. However this design greatly complicates the system and increases the chance of failures and still has minimal nitrification and no nitrogen removal.
  • 2. 2 Figure 1; current storage systems. Now DMT has entered the market with a STP which has been engineered based on down scaling WWTP technology. These systems easily achieve 10/10 effluent quality with complete NH4 removal and can even reach better than 5/5 with nitrogen removal. This makes it possible to meet current and future legislation. THEORY Wastewater can contain various pollutants, in total being determined as the Chemical Oxygen Demand (COD, mgO2/l). The COD-value represents the amount of oxygen required to chemically degrade all pollutants. Part of the COD is the “biological oxygen demand” (BOD, mg O2/l). This represents the amount of pollutants which can be degraded biologically. In domestic wastewater this usually is 50 to 80 % of the COD. Main degradation reaction is; BiomassOHCOOBODCOD ++→+ 222)( Other pollutants contain nitrogen (N). About 50 % to 90 % of the nitrogen compound is ammonium (NH4). Biological degradation goes in three steps; first the nitrogen compounds are converted to NH4. The ammonium is then degraded to nitrate (NO3) with the addition of oxygen. When bacteria are not aerated any more, the NO3 can be converted to nitrogen gas (N2) with the addition of BOD. The harmless N2 (nitrogen gas) is released into the atmosphere. Degradation reactions are; NH4 + O2 → NO3 + H + H2O BOD + NO3 → N2 + CO2 +H2O Degradation of NH4 to NO3 is called nitrification, conversion from NO3 to N2 denitrification. DESIGNING WWTP Using years and years of experience in wastewater engineering, DMT started in 2000 designing and developing small scale treatment plants (STP’s). Implementing its knowledge from large WWTP’s resulted in a complete new design for the STP. The pollutants are solely removed by flocks of micro organisms (sludge) without interference of packed media, discs or other carriers. To avoid any change of clogging, DMT chose specifically using only activated sludge for treatment, a proved technology. The only one mechanical part used is a robust blower. A sophisticated circulation system equalizes influent flow fluctuations and prevents sludge build up as well as SS wash out in a compact two stage settlement tank. The circulation system also makes it possible to implement both nitrification as well as denitrification removing nitrogen from the waste water. To enable the sludge-water mixture to circulate, good settlement is required. In normal WWTP this is accomplished in large clarifiers. Here, sludge settles and is circulated back. From existing dimensioning parameters, a novel highly advanced and compact clarifier has been developed by DMT. In picture 1 samples of a well functioning activated sludge system are shown. Another new development in STP’s is the use of the denitrification zone. In this zone, conversion of NO3 to N2 takes place. The formed nitrogen gas (N2) can escape to the surrounding air and is not captured in the sludge. Because of this controlled denitrification, no NO3 is left after treatment and no flotation of sludge occur in the settlement tank, further reducing SS concentrations in the effluent. IWOX ® engineered by DMT Using previously explained theory while keeping the typical domestic wastewater fluctuations (flow, COD) in mind, DMT developed from waste water engineering point of view two novel treatment systems. Starting in 2000, a concrete system was certified according to high Dutch standards (BRL K10002). The current light weight modulated systems are the next generation STP’s, which have a reduced footprint and still are capable to reach discharge values of <10/10 or even <5/5 (Van Hall Institute, CE certification (NEN-EN 12566-3) and been designed in conjunction with our partner company . One existing out of 2 tank (3 compartments), named the DMT IWOX ® Standard or IWOX ® Premium. The other one consists out of 3 tanks (5 compartments), the IWOX ® Superior. Picture 1; Picture with three samples (left to right) influent, activated sludge mixture, effluent.
  • 3. 3 Figure 2; Flow Schedule IWOX ® Standard- Premium. Figure 2 illustrates a simplified flow schedule of the IWOX ® Standard-Premium. Raw wastewater enters the pre-settlement tank, where large solids settle. The large variations of influent flows are controlled, and the water flows gradually to the 2 nd tank. Here, wastewater is optimally brought into contact with micro organisms and air. The micro organisms (present as sludge) settle in a highly advanced shaped clarification tank and are returned to the biological compartment. The purified water then leaves the system. Figure 3; Flow Schedule IWOX ® Superior. Differences between the Superior (Figure 3) and the Standard-Premium system are the implemented denitrification zone (NO3 to N2) and the second clarifier. The denitrification zone makes it possible to remove nitrogen, and BOD is further reduced (both consumed by denitrifying bacteria). Due to the denitrification, the SS in the effluent is also lowered. The back-up clarification step is implemented to minimize wash out of SS even at peak flows or other disturbances. These differences reduce the BOD and SS concentrations to the strictest Irish demand of 5/5. Reduction up to 70 % of Nitrogen is caused due to the denitrification as well. Graph 1; BOD, SS concentrations and removal efficiencies of the IWOX ® Superior. With these high removal efficiencies shown in Graph 1, this system is an alternative to the standard 20/30 systems with a reed bed. The DMT system requires only 1/14 th of the surface compared to a standard system (shown in image 1). Image 1; Indicative footprint difference between footprint of an IWOX ® Superior (0.8 m 2 ) and a classical 20-30 system (3.2m 2 ) + reed bed (8 m 2 ).
  • 4. 4 Graph 2; Overview development treatment technologies 1) Data from Balmoral Hydroclear, COD estimated 2) The DMT IWOX® Superior + grid preliminary results 3) Estimated results IWOX® Superior with membranes At this moment, DMT is further developing the systems by implementing a post-clarifying grid and/or membranes. First tests with the grid indicate an improvement for advanced reduction or complete removal of SS. This system will be further developed in the near future CONCLUSION Treatment of wastewater is required to avoid environmental problems. Current STP systems set the technology and legislation standard in Ireland, and are only achieving 20/30 discharge without nitrogen removal. Further removal to 5/5 is only possible with addition of non-certified reed bed systems. Designing from a waste water engineering point of view rather than just tank manufacturing led to the easily better performing / the IWOX ® systems. These differences in approach resulted in far higher removal efficiencies of BOD and SS and also total removal of ammonium, all achieved in one compact system (Pictures 2 until 5, below). Following the European Framework Directive, nitrogen removal is also standard with the IWOX ® Superior, reducing eutrophication in the environment. At this moment, novel treatment technologies further reducing nitrogen, phosphates as well as pathogens are in development. These will become economically feasible in the near future. IS CURRENT LEGISLATION OUT OF DATE? Current available systems reach easily higher discharge qualities at economical costs then described by legislation. An upcoming requirement in Ireland will be nitrogen removal. Could it therefore be the case that the current legislation is out of date? REFERENCES Balmoral Hydroclear product sheet. EPA, 2004-2005. Urban Waste Water Discharges in Ireland for Population Equivalents greater than 500 persons. Office of Environmental Enforcement. Independent University Van Hall Institute, department of Agricultural University and Reseach centre Wageningen. L. M. McCumiskey, 2007. BE, MSc, FIEI, MICE*P. F. TONER, PhD, Director and Section Head, respectively, Environmental Research Unit, Dublin, Water and Environment Journal, Volume 6 Issue 1, Pages 89 - 100, Published Online 26 Jul 2007 Graph 2 shows the development of treatment technologies commencing septic tanks. According to the ALARA (As Low As Reasonably Achievable) the law should be adjusted to the current economical best technology.
  • 5. 5 Picture 2; Picture of a IWOX ® Superior after placement in Ireland Picture 3; the IWOX ® Superior being placed in Ireland Picture 4; Robust and light-weighted IWOX ® Superior being placed in Greece Picture 5; the IWOX ® after placement in the Netherlands