High waste-to-biomass conversion and efficient Salmonella spp. reduction using black soldier fly for waste recycling
Cecilia H. Lalander
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Jrgen Fidjeland
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Stefan Diener
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Sara Eriksson
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Bjrn Vinners
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S. Diener Eawag: Swiss Federal Institute of Aquatic Science and Technology
, Dbendorf,
Switzerland
The recycling of organic waste worldwide is not effective, which leads to water pollution and loss of potential crop fertilizers. Available resources have to be used more efficiently as the world population increases. An innovative solution is to use insects for the management of organic waste. Here, we used black soldier fly to convert organic waste into animal feed protein, as fly larvae, and plant fertilizer, as compost residue. A continuous fly reactor was monitored for 9 weeks. We analyzed physicochemical and microbial parameters, and we evaluated the sanitary risk. Results show 55.1 % of material degradation and 11.8 % of biomass conversion based upon total solids. We observed higher levels of N and P in the treatment residue than in the inflow material. Results also show a lower concentration of Salmonella spp. and viruses. Compost treatment with black soldier fly is therefore an efficient system for nutrient recycling.
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organic material, e.g., food waste, animal manure, and market
waste. If left untreated, the valuable energy and nutrients
contained in the waste can contribute to an increase in annual
greenhouse gas emissions (UNEP 2010) and a leaching of
nutrients into water bodies, causing eutrophication (Sharpley
et al. 1994). Over and above this, there is a risk of spreading
the pathogens contained in the organic waste.
The waste management coverage in high-income countries
is considerably higher, but at the same time the waste
generated per person is up to three times greater and still increasing
(Hoornweg and Bhada-Tata 2012). The proportion of organic
waste is around 30 % and only a small proportion of the
nutrients returns into the food cycle (Cordell et al. 2009). This
is a growing concern, since the nitrogen and phosphate cycle
has been identified as key factors that has to be maintained
within certain levels for the planet to be able to support human
existence in the future (Rockstrm et al. 2009). One way of
securing human well-being is, according to Griggs et al.
(2013), sustainable production systems. In a report by the
United Nations Food and Agricultural Organization, it was
stated that the consumption of insects in the food sector, as
animal feed and directly for human consumption, is one such
solution (van Huis et al. 2013).
The black soldier fly, encountered between 46N and 42S
(Martnez-Snchez et al. 2011), is of particular interest. Their
ability to consume prodigious amounts of organic waste has
long been known. Black soldier fly larvae have been reported
to consume and degrade a number of organic materials with
material degradation up to 70 % (Diener et al. 2011). The
larvae in the final larval stage, the prepupae, crawl out of the
feeding material to find a dry and dark place to pupate
(Sheppard et al. 2002) and are thus self-harvesting.
The prepupae contain around 40 % protein and 30 % fat
and have been demonstrated to be a good alternative feed in
fish (St-Hilaire et al. 2007) and pig (Newton et al. 1977)
production, with the potential to replace fish meal and fish
oil as source of animal feed protein. Replacing fish meal
would alleviate the pressure on the wild fish population
(Tacon and Metian 2008). With the increasing consumption
of fish and meat, the demand for animal feed protein has
increased greatly, while its availability is limited. As a
consequence, the price of fish meal has reached new heights valued
USD 1,820 per tons (World Bank, May 2014) making the
production of compatible alternative animal feed protein a
lucrative business. By producing an economically valuable
product, organic waste management could become a
financially sustainable system that would increase resource reuse
efficiency and reduce negative environmental impacts
(Fig. 1).
Hygiene aspects play an important role when dealing with
organic waste and animal feed (Sidhu and Toze 2009). In
several studies, black solider fly larvae waste treatment
systems have been shown to remove bacteria in the
Enterobacteriaceae family: the concentration of Salmonella
spp. was reduced by 7 log10 in 8 days in a small
batchoperated fly larvae system treating fecal sludge (Lalander
et al. 2013); Erickson et al. (2004) observed the reduction of
Salmonella enterica Serovar Enteritidis and Escherichia coli
O157:H7 in cattle manure, while Liu et al. (2008) have
reported on the reduction of E. coli in poultry manure. However,
a l t h o u g h a h i g h r e d u c t i o n i n b a c t e r i a o f t h e
Enterobacteriaceae family occur, reduction of other
organisms has not been observed. All these systems were operated
in batch mode. The question is whether the same results would
be obtained in a continuous flow reactor. In a large-scale fly
Fig. 1 A graphical representation
of the concept of fly larvae
composting: organic waste is
consumed by fly larvae, in the
sixths and final larval stage, the
prepupae migrate out of the
compost. The prepupae can be
used as animal feed and the
treatment residue used as organic
fertilizer. The loop is closed when
the animal manure and food waste
is diverted as substrate into the fly
larvae compost
larvae waste management system, it is likely that a continuous
flow reactor would be implemented, as it would be too
timeconsuming to operate in batch mode. One hypothesis is that
the operation over a long period would support the buildup of
a microbial community, helping to break down the waste
material and thus improve the hygienic quality of the
treatment residue.
The objective of this study was to establish a continuous
flow fly larvae reactor and to analyze important process and
hygiene parameters in order to evaluate material degradation,
waste-to-biomass conversion rate, nutrient flow, and average
weekly reduction of evaluated pathogens and indicator
organisms.
2 Materials and methods
2.1 Materials
Pig manure (21.11.7 % total solids) was collected on a pig
farm in Uppsala municipality, Sweden. Dog food (Puppy
Original, Pro Plan, Purina) mixed with water (21.9 0.2 %
total solids) was used as the model substrate for organic waste
(Vinners et al. 2003). Human feces were collected fresh in
plastic bags and stored at 20 C immediately upon collection.
A mixture of pig manure, dog food, and human feces was
prepared (4:4:2; 28.71.2 % total solids), divided into feeding
portions, and kept at 20 C until use.
Ascaris suum, which infects pigs, is often used as
model for Ascaris lumbricoides, which infects humans
(Johnson et al. 1998). A. suum extracted from the feces
of infected pigs were purchased from Excelsior Entinel,
Inc. and received in aqueous solution at a concentration
of 100,000 eggs mL1.
The bacterial inoculate solutions consisted of 108
colony forming units (CFU) mL1 Enterococcus faecalis
(ATCC 29212) and 109 CFU mL1 Salmonella enterica
subspecies ~ 1 s (...truncated)