Mar 27, 2023
Life Cycle Assessment for Black Soldier Fly Larvae Dried Production
- Rudy Agung Nugroho1
- 1Department of Biology, Faculty of Mathematics and Natural Sciences, Mulawarman University
Protocol Citation: Rudy Agung Nugroho 2023. Life Cycle Assessment for Black Soldier Fly Larvae Dried Production. protocols.io https://dx.doi.org/10.17504/protocols.io.8epv5j54dl1b/v1
License: This is an open access protocol distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Protocol status: Working
We use this protocol and it's working
Created: March 24, 2023
Last Modified: March 27, 2023
Protocol Integer ID: 79429
Keywords: black soldier fly larvae dried production background, biowaste bioconversion process of bsfl, dried larva production system, biowaste production, larva production system, organic waste bioconversion, issue of organic waste bioconversion, biowaste bioconversion process, biowaste bioconversion, life cycle assessment, larvae, dried production, substrate for bsfl, production of prepupa, terrestrial eutrophication, environmental load, environmental impact analysis, bsfl frass production, environmental consequence, dried bsfl, cycle of bsfl, environmental impact, prepupa production, environmental impact category, potential future food, using bsfl, methods for bsfl
Abstract
Background: Hermetia illucens L. has gained popularity in recent years as a potential ecologically friendly response to both the present and potential future food/feed crisis. The larvae of H. illucensL., also known as black soldier fly larvae (BSFL), is an alternative solution to tackle the issue of organic waste bioconversion. However, understanding the environmental loads associated with biowaste bioconversion using BSFL to produce dried BSFL is a pivotal point to keep the environment sustainable. This study reported a life cycle assessment (LCA) of the biowaste bioconversion process of BSFL and determined the environmental impact analysis to make recommendations for modifications to lessen environmental consequences.
Methods: The data used was starting from biowaste production, biowaste bioconversion, prepupa production; and BSFL frass production. All these system productions were evaluated using the OpenLCA 1.11 withTRACI 2.1 methods based on a gate-to-gate approach.The system boundary of the dried larva production system is designed for both the processing and production of one cycle of BSFL. Further, five environmental impact categories, namely global warming potential (GWP), acidification (AC), terrestrial eutrophication (TE), fossil fuel depletion (FFE), and eco-toxicity (ET) were determined. The study was conducted at the PT Biomagg Sinergi Internasional, Depok, West Java, Indonesia.
Results: Based on the results of the study, the impact values of GWP, AC, TE, FFE, and ET, per 100 kg of BSFL dried production werewas6.687 kg CO2eq; 0.029 kg SO2-eq; 0.092 kg N-eq; 16.732 MJ surplus; 121.231 CTUe, respectively. Production of prepupa had the highest hotspots in these emissions, followed by the production of dried BSFL.
Conclusions. Efforts to reduce environmental impacts that can be done are by implementing an integrated rearing system for the utilization of substrate from a single type of known substrate for BSFL and using alternative drying methods for BSFL dried production.
Troubleshooting
Life cycle assessment goal and scope definition
The goal and scope definition step ensures that the LCA is performed consistently.
The present goal is to identify and analyze input-output based on inventory data from BSFL-dried products and determine potential environmental impacts in the form of global warming potential (GWP), acidification (AC), terrestrial eutrophication (TE), fossil fuel depletion (FFE), and ecotoxicity (ET).
The scope: The system boundaries used gate to gate.
Inventory analysis of extractions and emissions
The following processes were evaluated: biowaste preparation for BSFL substrate, bioconversion of biowaste, production of prepupa, and production of the dried larva. The CH4and N2O gases emmision were calculated based on the previous study performed by Martenat et al. (2019)
Mertenat, A., Diener, S., and Zurbrügg, C. (2019). Black Soldier Fly biowaste treatment–Assessment of global warming potential. Waste management. 84: p. 173-181.
At biowaste preparation for BSFL substrate, the volume of biowaste (1000 kg), the total need of diesel for crushing biowaste, and the operation time of the chopper machine were recorded.
The number of egg that was hatched (100 g) and the energy of electricity consumed (0.264 kWh) during the hatching process were noted.
In the bioconversion of biowaste, the volume of biowaste (1000 kg), themass of baby larvae of BSFL (100 kg), and the energy of electricity consumed (0.264 kWh) were also recorded
The volume of crushed biowaste (1000 kg), baby larva (100 g), and electricity (0.264 kWh) during the production of prepupa were obtained and noted
The wet prepupa (1000 kg), electricity energy consumed, and hour of microwave used in production of dried prepupa per 100 kg, were kept
Life cycle impact assessment (LCIA)
The data used was starting from biowaste production, biowaste bioconversion, prepupa and frass production, and BSFL-dried production. This data was primary data that directly was taken from the PT Biomagg Sinergi Internasionalwere evaluated using the OpenLCA 1.11.0 (GreenDelta, Berlin), Ecoinvent database version 3.8 (Secondary data) and TRACI 2.1 method based on a gate-to-gate approach.Secondary data such as data biowaste, electricity, diesel, and chopper were obtained from the dataset of Ecoinvent 3.8 database.
The LCI involved input waste (biowaste), emissions, and energy consumption of each subprocess were based on the principle of mass balance. Meanwhile, the Impact environment that includes GWP, AC, TE, FFE, and, ET, were evaluated. Additionally, all inventory data was obtained and calculated from this facility (PT Biomagg Sinergi Internasional, Depok West Java, Indonesia), except for CH4 and N2O emissions. The published values for CH4and N2O emissions during BSFL bioconversion were used (Martenat et al. 2019)
Mertenat, A., Diener, S., and Zurbrügg, C. (2019). Black Soldier Fly biowaste treatment–Assessment of global warming potential. Waste management. 84: p. 173-181.
Interpretation
The global warming potential (GWP), acidification (AC), terrestrial eutrophication (TE), fossil fuel depletion (FFE), and ecotoxicity (ET). were determined and interpreted based on the results of the TRACI 2.1 method based on a gate-to-gate approach. The following link is the raw data calculation of the measurement of the impact assessment interpretation
Protocol references