Influence of different substrates on black solider fly larval biomass
The fresh and dry weight of black solider fly larvae biomass showed highly significant differences between four substrates (CM, 3CM:1BW, 1CM:1BW, and BW). The lowest weight was recorded when larvae were treated with CM substrate. The fresh larval weight was increased by 7.2%, 46.1%, and 49.9% when treated with BW, 3CM:1BW, and 1CM:1BW substrates, respectively. The dry larval weight was increased by 68.2%, 70.69%, and 99.5% when treated with BW, 3CM:1BW, and 1CM:1BW substrates, respectively (Table 2).
Influence of different substrates on BSF pupal weight
Statistical analysis showed highly significant differences between pupal dry weights of BSF when treated with four substrates (CM, 3CM:1BW, 1CM:1BW, and BW). The lowest weight was observed when treated with CM substrate. The dry pupal weight was increased by 41.7%, 51.3%, and 105.9% at 3CM:1BW, BW, and 1CM:1BW substrates, respectively (Table 2).
The co-conversion efficiency of BSFL
As shown in Table 2, the conversion rate of the different substrates recorded was highly significant. The lowest was achieved at CM and BW substrates. The conversion rate was increased for 3CM:1BW and 1CM:1BW substrates, by 46.3% and 50.5%, respectively. But, as with waste conversion, CM treatment lowered BSFL weight gain as compared with BW treatment.
Table 2
Larval, pupal weight and percentage conversion rate of black solider fly on four substrates.
Substrates | FW/50 Larvae ± se1 | DW/50 Larvae ± se1 | DW/50Pupae ± se1 | Conversion rate |
CM | 8.67 ± 0.33b | 2.17 ± 0.05c | 1.87 ± 0.05c | 10.8b |
BW | 9.3 ± 0.33b | 3.65 ± 0.16b | 2.83 ± 0.01b | 11.62b |
3CM :1BW | 12.67 ± 0.33a | 3.71 ± 0.01b | 2.65 ± 0.09b | 15.8a |
1CM:1BW | 13 ± 0.58a | 4.33 ± 0.05a | 3.85 ± .18a | 16.25a |
F value2 | 29.944*** | 83.422*** | 60.511*** | 29.944*** |
H.S.D.3 | 1.33g | 0.32g | 0.34g | 1.66% |
1se = standard error. 2F values determined after ANOVA (SPSS date), *** signifies p < 0.001. 3Means followed by different letters are significantly different at P < 0.05 level; Tukey’s HSD test. CM: Chicken manure, BW: Bread waste, FW: Fresh weight, DW: Dry weight |
Essential chemical composition of larval biomass
Chemical compositions of larval biomass were analyzed to investigate the effect of larval feeding on the previous substrates. Table 3 shows the variation in contents of protein, fat, carbohydrate, crude fiber, and ash depending on treatments. Crude protein recorded the lowest value (25.2%) at CM treatment. CP content was increased by 3%, 3.4%, and 26.5% at 3CM:1BW, 1CM:1BW, and BW substrates, respectively, compared to CM treatment.
Fat content recorded the lowest value at CM treatment, where it recorded 12.77%. The percentage of fat increased to be 115.2%, 128.7%, and 282.8% compared to CM treatment when treated with 3CM:1BW, 1CM:1BW, and BW substrates, respectively.
Carbohydrates recorded the highest value at CM treatment (13%). Carbohydrate content decreased by 32%, 46.2%, and 48.6% in 3CM:1BW, BW, and 1CM:1BW substrates, respectively, compared to CM treatment.
Crude fiber (CF) contents recorded the lowest value at CM treatment (5.7%). CF content decreased by 10.3%, 11.2%, and 42.4% at 3CM:1BW, 1CM:1BW, and BW substrates, respectively, compared to CM treatment.
When ash contents were analyzed, they achieved the highest value at CM treatment (43.33%). Ash content decreased by 7.4%, 26.8%, 27.5%, and 90.53% at 1CM:1BW, 3CM:1BW, and BW substrates, respectively, compared to CM treatment.
Table 3
Chemical composition of BSFL reared on different substrates.
| Chemical component ± se1 |
| %CP2 | %Fat2 | %Carbohydrate2 | %CF2 | %Ash2 |
Substrates | | | | | |
CM | 25.2 ± 1.4b | 12.77 ± 0.69c | 13 ± 0.92a | 5.7 ± 0.17b | 43.33 ± 2.37a |
BW | 31.89 ± 1.8a | 48.89 ± 2.3a | 6.99 ± 0.54b | 8.12 ± 0.57a | 4.1 ± 0.23c |
3CM :1BW | 25.97 ± 1.39ab | 27.48 ± 1.73b | 8.83 ± 0.64b | 6.29 ± 0.49ab | 31.42 ± 1.04b |
1CM:1BW | 26.06 ± 1.25ab | 29.2 ± 1.65b | 6.68 ± 0.83b | 6.34 ± 0.38ab | 31.72 ± .98b |
F. value3 | 4.430** | 76.384*** | 15.118*** | 5.876** | 144.689*** |
H.S.D.4 | 4.79% | 5.53% | 2.4% | 1.4% | 4.5% |
1se = standard error. 2The chemical composition of larvae. See Material and methods. 3F values determined after ANOVA (SPSS date), *** signifies p < 0.001. 4Means followed by different letters are significantly different at P < 0.05 level; Tukey’s HSD test. CM: Chicken manure, BW: Bread waste, CP: Crude protein, CF: Crude fiber. |
The obtained data investigated the effect of different treatments on larval, pupal weight, conversion efficiency, and nutritional accumulation of BSFL. Data analysis proved that chicken manure treatment (CM) recorded the lowest values of weight and nutritional accumulation of BSF, while bread waste (BW) recorded higher weight and protein values when compared with CM treatment, but it recorded the opposite result with fat and cost. In addition, it is notable that the 3CM:1BW and 1CM:1BW demonstrated the highest values in weight and nutritional accumulation of BSFL. 1CM:1BW treatment is 14% larger in weight than 3CM:1BW treatment, and at the same time, it is 14% more expensive.
Among these results, the 1CM:1BW treatment may be the best one. It was greater in weight and conversion efficiency compared to other treatments. The nutritional accumulation of BSFL was balanced. Adding 50% of the bread waste enhances the properties of the chicken manure and promotes its benefits in terms of aeration and the accumulation of harmful bacteria.
The best chemical composition substrates of BSFL were recorded when adding of 1CM:1BW substrate. This remarkable result in BSFL weight could be attributed to the change of chemical composition ingredient that achieved after mixing chicken manure (CM) with bread waste (BW). Regarding to Table 1 CM show high percentage of protein (18.65%), fat (22.28%), and ash (27.18%) compared to BW which represents percentages 9.49%, 5.93%, and 1.03%, respectively. However, after mixing CM with BW, we recorded different values of all chemical composition. in this respect, the mixing 1CM:1BW show more efficiency larval weight (4.33 g/50 larvae) compared to 3CM:1BW (3.71 g/50 larvae) and individual substrate either CM (2.17 g/50 larvae) or BW (3.65 g/50 larvae). The 1CM:1BW substrate percentage was modified as follow: protein (14.07%), Carbs (50.25%), fats (14.1%), crude fiber (7.47%), and ash (14.1%). Regarding to previous percentage, on one side could be revealed that this adding of CM with BW led to elevate protein value from 9.49 to14.07%, fats from 5.93 to14.1%, and ash from 1.03 to 14.1%, on the other side, decreasing carbs from 75.30 to 50.25%.
This modulation in substrate composition percentage revealed that mixing substrates resulted in best balanced ingredient substrate for BSFL to produce the best weight of BSFL (4.33 g/50 larvae). This result could be interpreted that CM contains high percent of protein and fat along with lower percent in carbs which either palatable or efficient for neediness for larvae to gain best weight, not only that but also the BW gives the same result (3.65 g/50 larvae).
This increase in BW compared to CM could be attributed to high percentage of carbs and lower fat in this substrate which more digestible to larvae, and supply larvae with fast energy where, in contrary lower weight of larvae in CM could be form lower carbs of CM 25% which reflect the neediness of larvae in this age phase to more bioenergetics power
BSFL organic waste treatment varied in reliability and efficiency30. Recent studies recorded various types of organic waste in BSF treatment as a substrate, including kitchen waste31, poultry waste32, chicken manure12, dairy manure33, and cereals, fruits, and vegetables34. In contrast, Msang, et al.35 demonstrated the effects of three organic waste substrates: Irish potato peels, kale remains, and bovine ruminal content, on larval weight gain, prepupal yield, and bioconversion rate of BSFL. Kale remains recorded outperformed Irish potato peels and bovine ruminal contents, suggesting that they can be enriched to provide an alternative feed for BSFL instead of chick mash. Nguyen, et al.31 investigated the consumption and reduction of five different organic waste types by black solider fly: rendered fish, pig liver, pig manure, kitchen waste, fruits and vegetables, and control poultry feed. BSFL reduced all types of waste that were examined. They recorded the heaviest black soldier flies that fed on kitchen waste, which also had the highest mean rate of reduction per day. Although some waste generated larvae with a higher nutritional content, larvae grown on liver, manure, fruits and vegetables, and fish were almost the same length and weight as larvae fed the control feed.
When analyzing the CP, EE, NFE, CF, and ash for different treatments, the nutrient accumulation of BSFL raised on various organic waste substrates has been the subject of some recent studies31,36,12.
The performance of the process is significantly impacted by the macronutrients found in organic waste, including protein, carbohydrates, fats, and fibers37. Protein has such a good impact on larval development; it is a necessary nutrient in larval feeding substrates38. BSFL raised on organic wastes with greater protein contents has larger larval weights, higher protein levels, higher feed conversion rates, shorter growth times, and lower lipid contents, according to research by Nguyen, et al. 31 and Oonincx, et al.39.
Jalil, et al.40 proved that larvae reared in protein food sources are larger than those feeding on a carbohydrate food source. Jucker, et al.41 found that larvae feeding on substrates with low protein contents have a longer development time, are smaller, and have higher lipid contents if the carbohydrate content is high. The performance of the BSFL is determined by the nutritional contents of the organic wastes. For example, animal manure and municipal organic solid waste have higher protein contents than fruits and vegetables, which have higher carbohydrate contents; city municipal organic solid wastes have the largest lipid contents. The median fiber and ash content is higher in animal manures and fruit and vegetable wastes30. Consequently, BSFL biomass values could be enhanced by mixing nutrient-rich substrates during the pre-treatment step of the BSFL feeding.
In comparison to traditional composting, black soldier fly larvae (BSFL) lower the original weight of organic waste by approximately 50% in a shorter period of time. They do this by feeding voraciously on a variety of organic waste, including food wastes, agro-industrial by-products, and poultry and dairy manure. The nutrients in the wastes are converted by BSFL into proteins and lipids that are valuable animal feed. The residue left over from this process can be applied as organic fertilizer42.
Identification of the bacterial isolates
Bacteria were isolated from the BSF egg-associated and gut-companion bacteria and reared on BW substrate to obtain isolates with properties potentially relevant for host nutrition. Upon the appearance of colonies on the plates, the isolates were selected according to their morphology and then purified, establishing a collection of pure cultures (Fig. 1(A-E)).
The isolated selected bacteria were identified based on their microscopic shape and Gram staining (Fig. 1(F-I)). Bacteria were identified based on molecular characterization (16S rRNA sequencing). The bacterial isolate was grown on sterile Petri plates containing autoclaved LB agar medium and incubated for two days at 30 ºC. For DNA extraction, the cultures were sent to the Molecular Biology Research Unit at Assiut University. Intron Biotechnology Company, Korea, supplied the Patho-gene-spin DNA/RNA extraction kit. After that, the fungal DNA product was shipped to SolGent Company in Daejeon, South Korea, for rRNA gene sequencing and polymerase chain reaction (PCR). Two universal primers, 27F (5'-AGAGTTTGATCC TGGCTCAG-3') and 1492R (5'-GGTTACCTTGTTA CGACTT-3'), were used in the PCR process. By electrophoresis on 1% agarose gel, the purified PCR products (amplicons) were verified using a size nucleotide marker (100 base pairs). Dodeoxynucleotides (dd NTPs) were added to the reaction mixture and 27F and 1492R primers were used to sequence the purified amplicons in both the sense and antisense directions27. Sequences were further analyzed using Basic Local Alignment Search Tool (BLAST) from the National Center of Biotechnology Information (NCBI) website. Phylogenetic analysis of sequences was done using MegAlign (DNA Star) software version 5.05.
The five bacterial isolates were classified into three phylums; Proteobacteria (1 isolate), Firmicutes (3 isolates), and Actinobacteria (1 isolate) by 16S rRNA gene partial sequencing. The phylum Proteobacteria, with one isolate belonging to the Morganellaceae family, was assigned to the genus Morganella. Within the phylum Firmicutes, there are three isolates belonging to the Bacillaceae family (all assigned to the genus Bacillus). Within the phylum Actinobacteria, one isolate belonging to the Microbacteriaceae family was assigned to the genus Microbacterium43 (Fig. 2).
Proteases and ureases enzyme activity
At the end of the incubation period, urea degradation ability was present among the isolates: three out of a total of five isolates were able to degrade urea (Fig. 3 (A–E)). All five isolates were screened to characterize the potential bacteria for nitrogen uptake. At the end of the incubation period of skimmed milk agar medium, we found that three out of a total of five isolates were able to degrade protein (Fig. 3 (F–I)).
Effect of bacterial isolates supplementation on larval development
Four bacterial isolates were isolated from BSF-associated eggs, namely: Microbacterium paraoxidans (EN2), Bacillus proteolyticus (EO3), Bacillus megaterium (EO4), and Bacillus subtilis (EO6). One bacterial strain, Morganella morganii (GL), was isolated from the larval gut. These bacterial isolates were individually inoculated to a sterile medium. After the end of the incubation period, supplement the substrate individually.
The bacterial isolates achieved positive effect on the development and growth parameters of BSFL. In CM treatment, M. morganii (GL) isolated from the larval gut, was significantly higher than that of the control by 12.44% in dry larval weight. M. paraoxidans (EN2), isolated from the egg, recorded 5.1% higher than control. In 3CM:1BW treatment, M. morganii was significantly higher than control by 9.7%, followed by M. paraoxidans and B. subtilis, which recorded 5.7 and 5.4%, respectively. In 1CM:1BW treatment, there were non- significant differences between treated with bacteria isolated and control (Fig. 4-A).
The conversion rate of CM treated with bacteria into BSFL biomass was significantly greater in the M. morganii treatment by 11.11% compared to control. In 3CM:1BW treated, the conversion rate was non-significantly greater by 3.16% in both M. morganii and M. paraoxidans compared to control. The conversion rate of 1CM:1BW treated with bacteria into BSFL biomass was significantly greater in both M. morganii and B. subtilis treatments by 4.9% compared to control (Fig. 4-B).
The influence of companion bacteria on chemical components of BSFL biomass:
Chemical components of BSFL after co-conversion were analyzed, such as the CP, EE, NFE, CF, and ash for the isolates (Bacillus subtilis, Microbacterium paraoxidans, Morganella morganii, and control) at the treatments (CM, 3CM:1BW, and 1CM:1BW substrates). Biochemical components varied depending on treatments. In the CM treatment, M. morganii was significantly higher than the control in all contents but carbohydrates. The carbohydrate content of BSFL resulting from M. morganii was significantly lower than control (Fig. 5).
In the 3CM:1BW treatment, there were non-significant differences between the four treatments in CP and ash contents. M. morganii was significantly higher than the control in carbohydrate content and lower in fat and CF contents. (Fig. 5)
In the 1CM:1BW treatment, there were non-significant differences between the four treatments in chemical components except carbohydrate. M. morganii was significantly higher than the control in carbohydrate contents (Fig. 5).
Feed production contributes to 25.5% of the CO2 emissions produced in the chicken meat and egg supply chains, amounting to 606 million tons of CO2 per year. The transportation of soy products across the Atlantic increases the carbon footprint. Recent research has revealed that 5% of the European carbon footprint associated with imported Brazilian soybean is a result of maritime transport, further diminishing the sustainability of egg production. The deforestation and land use change in the soybean supply chain contribute to over 50% of the EU's carbon footprint, which highlights a significant opportunity to decrease greenhouse gas emissions in poultry production by utilizing locally produced larvae fed with organic waste as a protein alternative44.
The present study investigated the effects of BSF egg-associated and gut-companion bacteria on dry larval weight gain, conversion efficiency, and nutritional accumulation of BSFL reared on chicken manure and bread waste with different ratios. Callegari, et al.45; Zhang, et al.46; Mannaa, et al.47 found that the administration of BSF-associated bacteria contributed to enhanced insect growth, development, and involvement in organic waste bioconversion processes. Isolated companion bacteria from BSFL and inoculated with chicken manure could promote larval growth and development, according to Mazza, et al.12. Our results proved that the companion bacteria from BSF eggs and gut could improve weight, conversion efficiency, and nutrient accumulation of BSFL, especially BSF-CL (Morganella morganii), which contributed positively in increasing BSFL biomass, with a significant increase of 12.44% compared to the control in the CM treatments and a 9.7% increase in the 3CM:1BW treatment. In the 1CM:BW treatment, BSFL biomass increased significantly by 4.6%. The conversion rate of 1CM:1BW treated with bacteria into BSFL biomass was significantly greater in both M. morganii and B. subtilis treatments by 4.9% compared to control. This finding is similar to Rehman, et al.48; Lalander, et al.49;Vandeweyer, et al.50 who studied how gut microbiota composition varies depending on rearing substrates, via a mechanism that might support the recruitment of microorganisms to facilitate digestion of a specific substrate. Our results were also in agreement with Meneguz, et al.36 as they indicated that the evaluation of an appropriate feeding system and the initial pH value of the substrate are important parameters to reduce the time and increase the weight in the production of larvae. BSFL weight was increased by increasing the pH value of the substrates.
Makkar, et al.1 discussed that if an increased demand for cattle and poultry to alternate foods may arise if there is a scarcity of soymeal, fishmeal, and other protein sources; H. illucens larvae are comparable to high-protein feedstuffs according to their protein content and amino acid profiles. Also, egg mass was positively affected by the insect meal diets, as was the lay percentage, although only at the lowest inclusion level. Overall, a protein replacement of 25% with an insect meal from Hermetia illucens larvae in the diet of laying hens seems to be more suitable and closer to the optimal level44. Bovera, et al.51 studied how egg weight, feed intake, and feed conversion rate were not affected by the soybean meal substitution at both inclusion levels of insect meal (25% and 50%). Based on the current findings indicating a 25% decrease in concentrate consumption among the 20% hens, it can be inferred that for this diet to be more cost-effective than the conventional one, 1 kg of live BSF larvae would need to be priced at less than 40% of the cost of 1 kg of concentrate if the 20% concentrate is retailed at the same price as the conventional concentrate44.