Protection from
waterborne diseases from sewage is the main goal of municipal wastewater
treatment. In addition to raw sewage, wastewater treatment plants may receive stormwater
runoff, agricultural runoff, and industrial wastewater that may contain
chemical contaminants. According to the University of Michigan:
“Almost 15,000 POTWs {publicly owned treatment works} treat
and discharge over 34B gal/d of wastewater into U.S. waterways. 1.3M mi of
piping flow toward POTWs provide wastewater collection, treatment, and disposal
service to more than 238M people.”
Along with
protection from waterborne diseases, there is protection from industrial contaminants,
including contaminants of emerging concern (CECs). Mitigating these contaminants
may require new treatment processes.
The basic wastewater
treatment process is shown in the graphics below. Primary treatment involves screening,
sand and grit removal (these can damage pumps and equipment), and primary
clarification via sludge digesters. Secondary
treatment includes aeration, clarification via activated sludge, and
disinfection via chlorination and/or ultraviolet (UV) light. Tertiary treatment
includes nutrient removal and discharging the treated effluent back into the environment.
The graphic below shows modern wastewater treatment challenges.
Municipal Wastewater Contaminants and Their Impacts
Microbial
contaminants are the most common contaminants in municipal wastewater. These
include fecal coliform bacteria, viruses, and other pathogens of several types.
These contaminants are classified by the EPA into five types:
·
Oxygen demanding substances: These utilize
the dissolved oxygen in the wastewater and are measured as biochemical oxygen demand
(BOD). Organic contaminants and ammonia have high BODs. These substances use up
the available oxygen supply in the water over time.
·
Pathogens. These infectious microorganisms
can cause waterborne diseases such as typhoid fever, cholera, and dysentery. Those
diseases have largely been eliminated, at least in developed countries like the
U.S.
·
Nutrients. These are basically carbon,
phosphorous, and nitrogen. Secondary treatment only removes a tiny amount of
them so further treatment may be desirable. When discharged into the environment
these can lead to eutrophication and harmful algal blooms and if they get into
local water supplies they can cause undesirable odors and tastes. Therefore, nitrogen
and phosphorous recovery is often employed in tertiary treatment.
·
Inorganic and synthetic organic chemicals. These
can include many different chemicals including household chemicals, pharmaceuticals,
pesticides & herbicides, industrial chemicals, and heavy metals, These can
be harmful and can also cause taste and odor problems if present in local water
supplies.
·
Thermal pollution. Heat reduces the
capacity of water to retain oxygen. Hot weather can be a factor. Water used for
cooling in thermal power plants may be discharged at high temperatures, which
negatively affects some aquatic species, altering the ecology
Screening and Filtration
Primary treatment
involves screening and solids (mainly (grit and sand) removal. The grit and
sand, which mostly come from stormwater sewers, are collected in a sedimentation
tank and periodically removed and trucked away for disposal. The EPA notes some
details about screening strategies and dealing with large floating objects in
sewers by grinding and shredding.
“Screens are generally placed in a chamber or channel and
inclined towards the flow of the wastewater.
The inclined screen allows debris to be caught on the upstream surface
of the screen, and allows access for manual or mechanical cleaning. Some plants use devices known as comminutors
or barminutors which combine the functions of a screen and a grinder. These devices catch and then cut or shred the
heavy solid and floating material. In
the process, the pulverized matter remains in the wastewater flow to be removed
later in a primary settling tank.”
Primary Coagulation and Sedimentation
This process is
often part of primary treatment but is also used in nutrient control in tertiary
treatment. In primary treatment, the process may involve sedimentation or gravity
settling, chemical coagulation, or filtration. This primary sludge is removed
mechanically, either while the plant is running or after shutting down or
bypassing the tank.
Aerobic Treatment: Aeration and Activated Sludge
Secondary
treatment is basically biological treatment followed by disinfection. Aerobic
treatment of sewage-laden wastewater includes aeration in order to increase
oxygen availability and the use of aerobic bacteria in activated sludge to
decompose the waste. According to the EPA:
“Activated Sludge is a suspended growth process for
removing organic matter from sewage by saturating it with air and
microorganisms that can break down the organic matter.”
This process removes up to 90% of the organic matter. Thus,
one might refer to it as carbon removal. There are two main types of aerobic
treatment: attached growth processes and suspended growth processes.
In attached growth processes microbial growth occurs on the surface of stone or
plastic media. The wastewater passes over the media along with air to provide
oxygen. Attached growth process units
include trickling filters, biotowers, and rotating biological contactors. According
to the EPA suspended growth processes biodegrade
“…by converting ammonia nitrogen to nitrate unless
additional treatment is provided. In suspended growth processes, the microbial
growth is suspended in an aerated water mixture where the air is pumped in, or
the water is agitated sufficiently to allow oxygen transfer. Suspended growth
process units include variations of activated sludge, oxidation ditches and sequencing
batch reactors.”
This process speeds up biodegradation. In aeration, air is
added mechanically or pressure pumped into the aeration tank via small openings
as shown below to increase oxygen as the process proceeds.
The graph below
shows that over time wastewater treatment in the U.S. has gotten more
effective at reducing BOD, with removal efficiency doubling since 1960.
Sludge Removal
It is estimated
that one-third of the electricity used in a municipal WWTP is used for treating
and removing sludge. Sludge treatment is basically secondary treatment or aerobic
treatment. Aeration and clarification
tanks collect sludge that needs to be removed. In the past the plants had to be
taken offline, or sections bypassed in order to remove sludge but new methods
include removal of sludge during plant operation by robots. Company Sciphyn
offers robotic sludge removal:
“Our robots drive along the floor removing the sludge
which is then dewatered on-site prior to disposal. By avoiding the shutdown or
bypass of your normal operations, our method can result in significant cost
savings.”
Disinfection
Disinfection is a
part of secondary treatment that basically is used to kill pathogens. This step
is essential for protecting people. Chlorine is the most common method of
disinfection, but UV light is also common, and both may be utilized together.
Since any remaining uncombined chlorine after treatment would be dangerous for
aquatic life the wastewater is often dechlorinated before discharging into the
environment. Dechlorination typically involves the use of a reducing chemical
such as sodium bisulfite (NaHSO³) or sulfur dioxide (SO²). Ozone is sometimes
used for disinfection but is not economical. UV light, typically provided by
mercury arc lamps, is an effective means of disinfection but must be provided
at adequate levels to fully neutralize pathogens. UV treatment has the
advantage of not producing toxic byproducts.
Urine Diversion: Opportunities for Nutrient Recovery and
Urine-Derived Fertilizer Production
Urine diversion
is simply diverting and collecting the urine component of municipal wastewater
to be converted into fertilizer and/or mitigated through aerobic (usually) bioreaction.
Urine diversion has been proposed as an approach for producing renewable
fertilizers and reducing nutrient loads to wastewater treatment plants. A 2021
study in Environmental Science and Technology concluded that urine diversion
has great potential for helping WWTPs in several ways. In the study, two
methods were analyzed: a urine concentration alternative and a struvite
precipitation and ion exchange alternative.
“Both urine diversion technologies had better
environmental performance than the conventional system and led to reductions of
29-47% in greenhouse gas emissions, 26-41% in energy consumption, approximately
half the freshwater use, and 25-64% in eutrophication potential, while
acidification potential ranged between a 24% decrease to a 90% increase. In
some situations, wastewater treatment chemical requirements were eliminated.
The environmental performance improvement was usually dependent on offsetting the
production of synthetic fertilizers. This study suggests that urine diversion
could be applied broadly as a strategy for both improving wastewater management
and decarbonization.”
An August 2023
paper in Desalinization noted:
“Source separation of urine can be one of the most
effective solutions for nutrient recovery as a fertiliser, transforming the
conventional linear economy into a circular economy. The urine diversion from
wastewater can improve conventional wastewater treatment plants to be
energy-efficient and cost-effective, as a considerable quantity of nutrients in
wastewater is derived from urine.”
In August 2022
Australian researchers published a paper in analyzing the impacts of urine
diversion on treatment capacity, process design, and capex of a WWTP. The
highlights from that paper and a graphic that shows the nitrogen and phosphorus
that can be diverted are shown below.
These papers show
that urine diversion can be effective for increasing treatment capacity and
reducing capex for WWTPs. If I am reading this correctly, this is important because
it can help prevent the need to expand WWTP treatment capacity, where
applicable.
Nitrogen, Ammonia, and Phosphorus Control
As noted,
secondary treatment does not remove nitrogen and phosphorous. Thus, advanced or
tertiary treatment for nutrient removal requires physical and chemical methods including
adsorption, flocculation/precipitation, membranes for advanced filtration, ion
exchange, and reverse osmosis.
“…nitrifying bacteria present in wastewater treatment can
biologically convert ammonia to the non-toxic nitrate through a process known
as nitrification. The nitrification process
is normally sufficient to remove the toxicity associated with ammonia in the
effluent. Since nitrate is also a
nutrient, excess amounts can contribute to the uncontrolled growth of algae. In situations where nitrogen must be
completely removed from effluent, an additional biological process can be added
to the system to convert the nitrate to nitrogen gas.”
The conversion to nitrogen gas is accomplished by bacteria
in a process known as denitrification.
Phosphorous removal
involves a coagulation-sedimentation process along with chemical additives. A process
known as biological nutrient removal (BNR) can remove both nitrogen and
phosphorous. The EPA explains the process of chemical coagulation-sedimentation
for phosphorous removal:
“A process known as chemical coagulation-sedimentation is
used to increase the removal of solids from effluent after primary and
secondary treatment. Solids heavier than water settle out of wastewater by gravity.
With the addition of specific chemicals, solids can become heavier than water and
will settle.”
“Alum, lime, or iron salts are chemicals
added to the wastewater to remove phosphorus. With these chemicals, the smaller
particles ‘floc’ or clump together into large masses. The larger masses of particles
will settle faster when the effluent reaches the next step--the sedimentation tank. This process can reduce the concentration of phosphate
by more than 95 percent.”
The recovery of
ammonia from wastewater via biochemical processes is an emerging technology.
Since ammonia is a desirable chemical and can even be used as an energy source,
this may be practiced more in the future. Ammonia recovery is a form of nitrogen
recovery. According to MDPI and a 2022 paper in Environments, the following are
methods of ammonia and nitrogen removal from wastewater.
·
Bioelectrochemical system (BES)
·
Membrane electrosorption (MES)
·
Electrochemical stripping (ECS)
·
Electrodialysis (ED)
Other technologies for recovering nitrogen from
wastewater include air stripping, zeolite adsorption through ion exchange,
struvite precipitation, electrodialysis and reverse osmosis, and gas-permeable
membrane (GPM) technology.
New research from Sweden indicates that
phosphorous-rich sewage sludge can be converted into biochar. Biochar is made
via pyrolysis or burning in an oxygen-free chamber. The researchers combined
the sludge with agricultural residue at different amounts and temperatures. The
result is a phosphorous-rich carbon source that can improve soil fertility and
add phosphorous along with the known soil-building qualities of biochar. The
agricultural residue-biochar mix can also reduce the amount of heavy metals in the final
product. The lead researcher noted:
"By testing different compositions of materials and
different temperatures, I have been able to investigate the properties of
biochar to see how it can be improved to remove heavy metals, recover
phosphorus and ensure the long-term stability of biochar for applications in
the agricultural and environmental fields," explained Vali.
Odor and Corrosion Control
Odor control is an obvious need at WWTPs and
most of the odor derives from sulfides, primarily hydrogen sulfide (H2S). This
highly poisonous gas stinks. Odor control, or sulfide control is typically achieved
chemically with iron salts, calcium nitrate, and hydrogen peroxide (H2O2). H2S
is also highly corrosive so odor control is also corrosion control. The basic
oxidation reaction for H2S via H2O2 is:
H2O2 + H2S → S0 + 2H2O
Challenges to using H2O2 for odor control include providing adequate
reaction times. The process needs to be tweaked often.
Management of Contaminants of Emerging Concern (CECs)
According to the
2022 volume Wastewater Treatment:
“Emerging contaminants (ECs), termed contaminants of
emerging concern, emerging pollutants (EPs), micro-pollutants, or trace organic
compounds (TrOCs) are derived from different natural as well as anthropogenic
sources that extensively influence water quality. They are termed as emerging
not because they are new but due to enhancement in the level of concern. These
contaminants are generally in small concentrations, ranging from nano-gram per
liter (ng L−1) to micrograms per liter (μg L−1) in the atmosphere. United
States Environmental Protection Agency (USEPA) describes ECs as new chemical
compounds that have the potential to cause harmful effects on individual health
and the surroundings. It is essential to treat and recycle wastewater to an
acceptable standard to fulfill water demands.”
These compounds may include many different chemicals and
sources as shown below.
Some of the treatment methods along with their benefits and
challenges are shown in the table below.
A 2021 paper in
Science of the Total Environment concluded that ozonation and activated carbon
are the best-performing tertiary treatments available for treating emerging contaminants.
Biosolids Management: Anaerobic Treatment for Methane
Recovery and Fertilizer
According to the
EPA:
“Biosolids are processed wastewater solids (“sewage
sludge”) that meet rigorous standards allowing safe reuse for beneficial
purposes. Currently, more than half of
the biosolids produced by municipal wastewater treatment systems is applied to
land as a soil conditioner or fertilizer and the remaining solids are incinerated
or landfilled. Ocean dumping of these solids
is no longer allowed.”
Biosolids are dewatered and then stabilized by composting, heat
treatments, drying, or the addition of lime or other alkaline materials. Land
application of biosolids is currently being criticized and reevaluated due to
the presence of concentrated emerging contaminants such as microplastics and PFAS/PFOS.
Biosolids are
basically a peat-like product that can add carbon, nutrients, and desirable structure
to soils.
In addition to land
application and incineration, biosolids may be added to anaerobic digestors (ADs) to produce both usable methane and fertilizer. These ADs may occur at WWTPs with
the methane being used to power plant processes. The basic method is the two-stage
acid/gas phase system.
Industrial Wastewater Treatment
Industrial
wastewater has quite variable composition depending on the type of industry
producing it. The petrochemicals industry produces different wastewater than the
food & beverage industry, the metals processing industry, the solar
panel industry, or the pharmaceutical industry, for example. According to the
2023 book Anthropogenic Environmental Hazards:
“Contaminants can be grouped into different classes such
as endocrine disrupting compounds (EDCs), pharmaceuticals, pesticides, heavy
metals and metalloids, per- and polyfluoroalkyl substances (PFAS), and
microplastics. Each contaminant upon exposure possesses a specific health
impact on humans and animals as well as on marine life when mixed in the sewer.”
UK company Anguil
notes that wastewater can be challenging to treat due to high pollutant volume,
complex composition, and unpredictable variability. They also note that
automated treatment has driven innovation in recent years. Changes in
industrial operations due to new chemicals, increasing production volumes, or
changing processes are the most common reasons industrial effluent treatment
facilities fail compliance. Other factors include lack of maintenance, adapting
to regulatory changes, aging equipment, and upgrading issues. They note that
some companies opt to pay fines and fees for non-compliance rather than maintaining
equipment. Sometimes companies are not prepared to adapt to regulatory changes
such as updated contaminant limits. Aging equipment may become less effective
at removing contaminants. Upgrading equipment is costly and may be delayed,
triggering non-compliance.
Industrial
effluents vary in difficulty of treatment and each type and instance of wastewater
has its own challenges. They note that common industrial wastewater
contaminants include: total suspended solids (TSS), total dissolved solids
(TDS), dissolved metals, fats, oil, grease (FOG), biochemical oxygen demand
(BOD), chemical oxygen demand (COD), color, inorganic/organic compounds, pH, volatile
organic compounds (VOCs), and solids handling. They recommend water reuse where
applicable, for example, treating water to certain standards to be able to run
similar or other operations, such as boiler feedwater. This is a good way to
reduce total effluent discharge volumes. Anguil fits solutions to problems by
leveraging all existing wastewater treatment methods to find the best option for
each application according to client capabilities. They note:
“The industrial wastewater treatment solutions we offer
are developed from a collaborative process with our customer to understand
their needs, then validated through lab or pilot testing.”
The U.S. consumes
about 322 billion gallons per day. About half of this consumption is in industrial
applications. Anguil notes that industrial effluent contaminant management is
costly, whether that is through fines, which don’t address the issue, or through
added remediation and associated transportation costs, which do address the issue.
Typically industrial wastewater must be pretreated before it can be further
treated at municipal wastewater treatment plants. They also note that the
relationship between municipal and wastewater treatment plants and industrial wastewater
producers can change:
“Municipalities find it more cost-effective to tighten
standards for industrial clients rather than expand their own facilities. This
approach helps reduce the burden on the municipal treatment system. Industrial
companies then face the challenge of finding economical ways to meet these new
criteria to avoid penalties and surcharges.”
They also note that
in-house or on-site treatment options can save money on transportation costs. They
note that costs are important:
“The primary focus of most wastewater treatment solutions
is to discharge wastewater in compliance with national and local regulations.
The secondary goal is to be as cost-effective as possible when treating
wastewater.”
Treating
industrial wastewater involves contaminant-specific technologies. Anguil lists
the major ones below:
- Heavy
metals/dissolved metal materials can be removed through pH
adjustment and clarification, ion exchange, and carbon technologies.
- Dissolved
Air Flotation (DAF) and oil-water separators remove fats, oils, and
grease from wastewater.
- Filter
presses, belt presses, rotary vacuum drums, and rotary screw presses
squeeze water from sludge to achieve dewatering.
- Cartridge
filters, ballasting, parallel plate clarifiers, DAF, and bag filters
remove suspended solids.
- MBBR,
MBR, anaerobic, anoxic, bioreactor, and oxidation treatment eliminates
soluble biochemical oxygen demand (BOD) and chemical
oxygen demand (COD).
- Total
dissolved solids (TDS) are the measurement of the total
dissolved amount of organic and inorganic solid materials present in
wastewater. Reverse osmosis, ion exchange systems, and nanofiltration
facilitate the removal of TDS.
- Volatile
organic compounds (VOCs) are often present in wastewater,
requiring removal via air stripping, granular activated carbon (GAC)
adsorption, or oxidation.
- Ultra-pure
water requires the removal of minerals and other
contaminants from relatively clean water. Reverse osmosis (RO),
deionization (DI), ion exchange, ultrafiltration (UF), and microfiltration
are a few technologies that can be leveraged to create ultra-pure process
waters.
Their process
evolves from assessment to lab testing to pilot project and finally to final
project design and construction as shown below.
The table below
shows industrial wastewater treatment technologies and equipment in more
detail.
Industrial Wastewater Evaporation
Another way to
reduce industrial effluent volumes is through evaporation. Company ENCON Evaporators
offers several high-tech evaporators. Several types are shown below. Their
applications vary according to the composition and amount of wastewater. The
goal is to minimize the amount of wastewater to be treated. They explain
wastewater evaporation below:
“In its simplest form, the evaporator converts the water
portion of water-based wastes to water vapor, while leaving the higher boiling
contaminants behind. These wastewater evaporation solutions greatly minimize
the amount of waste that needs to be hauled off-site.”
“The evaporation process itself involves both a
thermodynamic and mass transfer phenomena.”
“The thermodynamic phenomenon of evaporation nvolves
providing enough heat energy (waste oil, off-spec gas, natural gas, propane,
oil, diesel, electricity, or steam) to convert water to water vapor.’
“The mass transfer phenomenon of evaporation can best be
described as the “carry off” of small droplets of water. These droplets are
created at the surface of vigorously boiling water and are “carried off” by
oversized blowers or unfiltered water vapor.”
“This “carry off” is problematic with wastewater
applications since the droplets of water may have contaminants such as soaps,
metals, or oils entrained in them, thus causing an environmental impact outside
the building.’
“This “carry off” of droplets is minimized on all ENCON
wastewater evaporators through use of a mist eliminator and other design
considerations.”
They note that if
the waste stream is over 70% water, then it is likely a good candidate for
evaporation. To determine if it is suitable requires some preliminary chemical laboratory
analysis.
References:
Challenges
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