I have embraced “closing the circle” as a positive paradigm for biosolids resource recovery. Macy’s exhortation for a wholehearted commitment to humanity’s just and safe relationship to Earth reminded me of two issues that, with biosolids recycling to soil, niggle at me, just a little – microbial risks and persistent organic pollutants.
I am entirely confident that the scientific record
exonerates biosolids today from meaningful risk of harm to humans and
the environment and entirely supports my commitment to
recovering biosolids for the purpose of soil improvement. Yet,
I also read of the performance of innovative technologies that enable us,
tomorrow more so than yesterday, to eliminate microbial risks and organic
pollutants. Perhaps these targets are not mandated by regulation, in particular
not the 23-year-old Part 503 regulations. And, perhaps these new technologies
are more costly and risky than those our industry have used for 100 years.
But they are compelling in their high quality performance
and biosolids product.
The promise of a leap forward in technology was the big
message of Bill Barber’s presentation to the MABA Summer
Technical Symposium in Baltimore. He had me “rethinking” the
creative potential ahead of us to deploy high-performance processes as a
turning toward a wholehearted commitment to highly stable biosolids.
There is not just one way to do this. In fact, Barber suggests that our
fascination with thermal hydrolysis pretreatment for digesters is akin to
putting decorative decals on a Model T Ford. You can see Barber’s MABA’s
presentation on what may lie ahead for us in digester technology: “RETHINKING ANAEROBIC DIGESTION TO COMPLEMENT 21ST CENTURY
DRIVERS”.
In diving deeper into Barber’s concepts, I came across the
European-based “ROUTES” initiative, which has evolved as a tool to achieve
Europe"s “safe sludge matrix.” The global conversation around
ROUTES was sparked in October 2012 with a technical gathering in Rome,
Italy. NOVEL PROCESSING ROUTES FOR EFFECTIVE SEWAGE SLUDGE MANAGEMENT. I
learned in the paper ROUTES: innovative solutions for municipal sludge treatment and
management that the “project is addressed to discover new
routes in wastewater and sludge treatment which allow: (a) to prepare sludge
for agricultural utilization by transforming it in a very clean and stabilized
product with respect to hygienic aspects and phytotoxicity;….” To my ear, this
sounds all the world like the principal motivation for the WE&RF High
Quality Biosolids research project.
The European champions of ROUTES have put out some
extraordinary publications that take us toward “closed circle” goals in the
stabilization of biosolids.
The report by prolific female researcher from Italy, Camille Braguglia,
and her associates, Quality assessment of digested sludges produced by advanced
stabilization processes, found that: “Removals of conventional and emerging
organic pollutants were greatly enhanced by performing double-stage
digestion (UMT and AA treatment) compared to a single-stage process as TT; the
same trend was found as regards toxicity reduction.”
Double-stage digestion is neither new nor extremely risky.
Reaffirming Bill Barber’s assertion in his paper from Baltimore, the ROUTES
team concluded: “These results confirmed that temperature-phased anaerobic
digestion systems could show better performances and higher process stability
than single-stage mesophilic or thermophilic processes,
carried out under the same operative conditions.”
The ROUTES team looked at a wide variety of other digestion
approaches. One approach was to attempt higher organic loadings to the
digester, meaning smaller digesters and more room for co-digestion
of sludges with trucked-in wastes. In the article The impact of sludge pre-treatments
on mesophilic and thermophilic anaerobic digestion
efficiency: Role of the organic load the authors wrote that “at
higher organic loads, the TAD [thermophilic anaerobic digestion] yields
were significantly higher with respect to the MAD [mesophilic anaerobic
digestion] ones, assuring the sustainable economic benefit of operating smaller
anaerobic digesters to obtain higher methane production.
The ROUTE group looked at pre-treatment ahead of digesters,
noting the different functionality of different processes: “Thermal hydrolysis
enhanced the release of lipids and long chain fatty acids, while ultrasounds
application resulted in proteins being the main component of the released
matter.”
With the ROUTE group objective of meeting multiple goals for
product stability, energy balance and dewaterability, but also
importantly hygienization, they described in Enhanced Versus Conventional Sludge Anaerobic Processes: Performances and
Techno-Economic Assessment the following findings: “The TPAD
[two-phased anaerobic digestion] proved to improve the overall process by
enhancing the individual steps (Francioso et al., 2010), and had the advantage
to be operated at high loading rates (Azbar et al., 2001). At the same time the
short thermophilic step did not guarantee total hygienization (Huyard
et al., 2000). For this reason, in this work, an inverse TPAD (meso/thermo) is
proposed, where the mesophilic acidogenic step is followed by an
intense methanogenic step in thermophilic conditions aimed to achieve
higher methane yields, obtaining a final hygienized product suitable for land
application.”
In one experiment, WAS is treated with a physical
disintegration process, sonication, and then put through temperature-phased
anaerobic digestion (TPAD), but inversed, as described above, to have the
feedstock treated with a mesophilic acid phase followed by a high
temperature gas phase. In a second experiment involving dual digestion,
primary sludge is treated with wet oxidation, and the secondary sludge is
treated with thermal hydrolysis, then combined
for thermophilic digestion.
Wet oxidation? I needed to look that up (Wet oxidation of sewage sludge: full-scale experience and process
modeling).
One key driver for ROUTES is hygienization. Standards
of treatment go beyond indicator fecal coliform to include a higher test of
virus inactivation. Researchers concluded that viral inactivation requires
higher temperatures in the thermophilic digester than those
conventionally targetted: “…our study confirmed the higher resistance to
thermal treatments of viral particles with respect to bacteria indicating the
low reliability of bacteria as an indicator of virus fate at temperature
greater than 55 °C…. In contrast to what was observed with bacterial
indicators, the removal of viral indicators to below detection limit was
observed only at high temperature in the TH+TAD [thermal hydrolysis followed by
thermophilic anaerobic digestion] processes confirming, in agreement with other
studies, that temperatures above 80 °C are necessary for an efficient
inactivation of viruses.”
ROUTES also showed that biosolids quality made a
difference to the evaluation of technologies. The lowered cost of
disposal of the high-quality biosolids and the greater recovery of energy for
biogas released during digestion were two factors that justified the more
costly equipment. Measures of phytotoxicity and the soil-like quality of
the residuals sold the biosolids for agricultural users. Even though
new treatment practices required electricity input, the extra biogas production
yielded electricity production above that additional need.
Yet, the ROUTES researchers worked through some troublesome
areas. Thermophilic systems can be harder to operate, harder to keep
stable and difficult to avoid foaming and rapid rise. The ROUTES
paper Microbial diversity in
innovative mesophilic/thermophilic temperature-phased anaerobic
digestion of sludge explained that “thermophilic communities
may be therefore more susceptible to sudden changes and less prompt to adapting
to operative variations.” They also pointed to the release of
difficult-to-dewater COD. The impact of sludge pre-treatments on mesophilic and thermophilic anaerobic
digestion efficiency: Role of the organic load noted that
“Nevertheless, the colloidal charge increase
during thermophilic digestion impaired the sludge filterability much
more rapidly than in mesophilic conditions.”
The mind boggles at all of the combinations and complex
options for stabilization that have emerged recently for serious consideration
by public agencies. The most notable for its recent U.S. implementation
is Cambi’s Thermal Hydrolysis Process at DC
Water, but Trinity River Authority outside Dallas and Hampton Roads Sanitation Authority in Virginia Beach have
announced plans to move ahead with Cambi. At the MABA meeting,
GE Power described its Monsal biological hydrolysis system, and Ovivo provided
case studies of six high-tech aerobic digesters. At last
November’s MABA Annual Meeting, Veolia described European examples of advanced digestion, and we heard there
also of Suez’s TPAD (temperature phased digestion) at the Hermitage (PA) Municipal Authority, where it is deployed for a
very serious program of co-digestion.
This is just a start, I believe. I predict that within 20
years the common practices for biosolids stabilization will include a
number of sequential digester systems that we see today as experimental.
This is inevitable because the early results in the lab, at pilot plants,
at reference facilities, and in full scale in Europe, in terms of mass
reduction, pathogen control, pollutant reduction, and product stability are very
compelling, far above and beyond Part 503 standards requirements, but so much
closer to our vision as environmental stewards toward “closing the circle” in
our community. I feel underway the Great Turning to High
Quality Biosolids.
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