Biosolids are the
separated solid end components of the wastewater treatment process that are
physically and chemically treated. The result is semi-solid nutrient-rich biosolids.
In most cases, biosolids are basically treated sewage sludge. Biosolids have
long been used as a land application treatment that increases soil fertility
but there are many potential problems with the chemical content of the biosolids such as
high levels of heavy metals, PFAS, dioxins, organic chemicals, and microplastics.
Human pathogens are also a concern since some thrive in sewage and can be difficult
to eliminate. They also contain phosphorus and carbon that are good for plants
and soil. That is one reason why land application of biosolids is the fate of
most biosolids as shown below. It should be remembered that it is not just
human bodily wastes that end up at sewage treatment plants but whatever is
dumped down a sink, including known illegal dumping. This may include toxic
chemicals.
Biosolids are
either land-applied or disposed of via incineration or landfilling. The share of each is shown below. The ash left over from incineration is also typically landfilled.
There are
different classes of biosolids based on how the wastewater is treated or
utilized. The EPA's classification scheme of Class B, Class A, and Class A-Exceptional Quality is shown below.
The different types are given below based on a Canadian study of
potential emerging contaminants from biosolids.
Anaerobic Digestion: Micro-organisms decompose the
sludge in the absence of oxygen either at mesophilic (at 35 °C) or thermophilic
(between 50° and 57 °C) temperatures.
Aerobic Digestion: Micro-organisms decompose the
sludge in the presence of oxygen either at ambient and mesophilic (10 °C to 40
°C) or auto-thermal (40 °C to 80 °C) temperatures.
Composting: A biological process where organic matter
decomposes to produce humus after the addition of some dry bulking material
such as sawdust, wood chips, or shredded yard waste under controlled aerobic
conditions.
Alkaline Treatment: The sludge is mixed with alkaline
materials such as lime or cement kiln dust, or incinerator fly ash and
maintained at pH above 12 for 24 hours (for Class B) or at temperature 70 °C
for 30 minutes (for Class A).
Heat Drying: Either convention or conduction dryers
are used to dry the biosolids
Dewatering: The separation of the water from biosolids
is done to obtain a semi-solid or solid product by using a dewatering
technologies (centrifuges, belt filter presses, plate and frame filter presses,
and drying beds and lagoons).
Some methods of biosolids composting are shown below.
Human
pathogens found in sewage wastewater include fecal coliform bacteria such as E.
Coli, Salmonella sp. bacteria, enteric viruses, and viable helminth
ova. The presence of these ‘indicator organisms’ suggests that the waste may be
unsafe. Some have been known to survive the wastewater treatment process. EPA
requires that there be no detectible level of such organisms in biosolids for
land application. Concentration limits and loading rates for metals are shown
below.
Biosolids are
used as a fertilizer in agriculture as well as in forests for timber land. They
are also used as an additive to condition soil. They are used on reclamation
sites to increase the rate of new vegetative growth. Certifiably the cleanest
biosolids, Class A, are approved for home
lawn and garden use.
The U.S. EPA
requires all publicly owned treatment works (POTWs) to produce annual reports summarizing
waste management practices and pollution monitoring data including contaminant
levels in their waste. Nine states (Arizona, Idaho, Michigan, Ohio, Oklahoma,
South Dakota, Texas, Utah, and Wisconsin) are authorized through the National
Pollutant Discharge Elimination System (NPDES) Program to be the permitting
authority for biosolids.
Land application
may be done in different ways and the table below compares their attributes for reclaimed land application. The
land application method often depends on the consistency of the biosolids,
whether they are mostly liquid or whether they are more solid granules or pellets.
EPA also explains biosolids odors:
“Biosolids may emit a distinctive odor depending on the
treatment process and methods used. The odorous compounds generated and
detected most often are ammonia, amines, and reduced sulfur-containing
compounds. Meteorological conditions such as wind speed and direction, relative
humidity, and temperature can impact nuisance odors. The presence of biosolids
odors does not mean that the biosolids pose harm to human health and the
environment.”
A 2016 study
published in Chemosphere evaluated the cadmium-phosphorus (Cd-P) ratios in
biosolids vs. biosolids ash, or combustion residuals. Cadmium is a toxic heavy
metal and it is desirable to keep its levels down. Some conclusions from the
abstract are given below:
“Combustion of biosolids improved the Cd/P ratio in
ashes by 2–5 times, compared with the initial biosolids. The low Cd content in
ashes (4–9 mg Cd (kg P)−1) makes this material a particularly attractive
alternative to mineral fertilizers. Significantly higher pore water P (as well
as total N) was measured in soils containing biosolids, but plants produced a
higher biomass in soil fertilized with ashes. The K and Ca amendments prior to
biosolids combustion generally decreased the total Cd in ash, but had little
effect on P and Cd uptake and biomass growth. Similarly, the combustion
temperature had negligible effect on these factors as well.”


Another study
published in the June 2023 issue of the Science of the Total Environment reviewed
the challenges and opportunities of biosolids-derived fertilizers. The
highlights given below indicate that there is considerable opportunity for
biosolids, particularly contaminant-free biosolids, to fertilize plants,
condition soil, reduce incineration ash, and increase landfill space.
•Land application of biosolids is a cost-effective way
to reuse nutrient in soils.
•Ever changing nature of biosolids contaminants
dictates regulatory guidelines.
•Nutrient content in biosolids provides an
understanding of baseline agronomic value.
•Extractive technologies can recover and purify
valuable constituents from biosolids.
•Prospects for novel granulated fertilisers derived
from biosolids are significant.
Emerging
technologies like chemical extraction of desired constituents of biosolids
before thermal processing are being considered more and more. This may be desirable
since nitrogen and carbon compounds are destroyed during combustion. Nitrogen,
phosphorous, and humic substances may be recovered in this way. The authors
think this will eventually become a future trend in wastewater treatment plants.
It would further the circular economy capabilities of biosolids. The graphic
below from the paper compares current practices to a low-value end-use and a
high-value end-use. The high-value end-use makes use of mineral and chemical
recovery.
EPA notes some important
advantages of biosolids-derived fertilizers over traditional synthetic
fertilizers:
“The nutrients in the biosolids offer several advantages over
those in inorganic fertilizers because they are organic and are released slowly
to growing plants. These organic forms of nutrients are less water soluble and,
therefore, less likely to leach into groundwater or run off into surface waters.”
EPA goes on to tout the overall the advantages of biosolids:
* Biosolids are a recycled product, use of which does not
deplete non-renewable resources such as phosphorous.
* The nutrients in biosolids are not as soluble as those
in chemical fertilizers and are therefore released more slowly.
* Biosolids appliers are required to maintain setbacks
from water resources and are often subject to more stringent soil conservation and
erosion control practices, nutrient management, and record keeping and reporting
requirements than farmers who use only chemical fertilizers or manures.
* Biosolids are closely monitored.
* The organic matter in biosolids improves soil
properties for optimum plant growth, including tilth, friability, fertility and
water holding capacity. They also decrease the need for pesticide use.
Incineration of Biosolids and Biosolids Ash-to-Soil
Incineration
of biosolids involves two steps: adequate evaporation of water content, and
combustion. 65-75% of the biosolids are combustible which means that biosolids
ash volumes are considerably less than non-combusted biosolids. The ash is more
inert than the original biosolids which may still be reactive. The combustible
content means that there is no need for additional fuel except for start-up of the
incinerator. The incinerated ash may have other uses such as a filler for
bricks and concrete, sub-base materials for road construction, daily landfill
cover (after pelletization), and as an “ingredient in footing at athletic
facilities, including baseball diamonds, and equestrian facilities, such as
race tracks and arenas.”
The two main
methods of incineration are multiple hearth furnace (MHF) technology and fluidized
bed furnace (FBF) technology. Both have advantages and disadvantages. Back in
1993 when a higher share of biosolids was incinerated EPA noted that in 1993, 343
biosolids incinerators were in operation in the U.S. and 80% of
them were MHFs and 20 percent were FBFs. Some comparisons are given in the
table below.
Northeast Ohio
Regional Sewer District Biosolids Ash Land Application Project
Six years ago, a
project was initiated in the Northeast Ohio Regional Sewer District to apply incinerated
biosolids ash to soil for fertilization. Previously, the biosolids ash was stored
in lagoons or ponds at the Southerly Wastewater Treatment plant. The sandy
slurry eventually becomes a solid that looks like red clay which would later be
dug out and shipped to a landfill. This project which began in 2018 was the
first of its kind. Has it worked? According to the District's Robin Halperin, it
has:
“It's worked fantastic; seven years later, we have reused
100% of our ash, and we have not landfilled anything. We've also saved an
estimated $6.5 million by not landfilling it, and we reduced our carbon
emissions by 96%.”
The solidified sludge is taken to Kurtz Brothers Landscape
Supply which has called the project a “win-win for them, their customers who
use the soil and, in a roundabout way, Lake Erie.” Since it is less likely
to runoff than regular synthetic fertilizer it can help protect the lake from
issues like harmful algae blooms. The District is also looking into a reuse
application for the grit that is removed at the early stages of wastewater
treatment. The grit is sand, rock, and gravel that finds its way to the
treatment plant. It needs to be cleaned but after that, it can be reused, they
say. They point out that while not all WWTPs have biosolids ash, they all have grit
that must be removed because it can damage pipes and pumps. Before the project
was initiated it took about a decade of testing and permitting before the Ohio
EPA approved the project. The decreased CO2 emissions are a result of being able to truck the biosolids to the nearby landscaping firm instead of taking them to the more distant landfill.

References:
Turning
solid waste ash into fertilized soil proves win-win for Northeast Ohio Regional
Sewer District. John Kosich. News 5 Cleveland. August 20, 2024. Turning
solid waste ash into fertilized soil proves win-win NEORSD (news5cleveland.com)
Biosolids-derived
fertilisers: A review of challenges and opportunities. Serhiy Marchuk, Stephan
Tait, Payel Sinha, Peter Harris, Diogenes L. Antille, and Bernadette K. McCabe.
Science of The Total Environment. Volume 875, 1 June 2023, 162555. Biosolids-derived
fertilisers: A review of challenges and opportunities - ScienceDirect
Using
Biosolids for Reclamation/Remediation of Disturbed Soils. Sally Brown and Chuck
Henry. University of Washington. (U.S. EPA.) May 2015. biosolidswhitepaper-uwash.pdf
Phosphorus
and cadmium availability in soil fertilized with biosolids and ashes. Jurate
Kumpiene, Evelina Brännvall, Martin Wolters, Nils Skoglund, Stasys Čirba, and Vladislovas
Česlovas Aksamitauskas. Chemosphere. Volume 151, May 2016, Pages 124-132. Phosphorus
and cadmium availability in soil fertilized with biosolids and ashes -
ScienceDirect
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