Abstract
Nopal (Opuntia ficus-indica) is widely cultivated in Mexico as a food raw material. However, the environmental impact caused by the growth and harvesting life cycle of this feedstock has been poorly studied. In this study, the environmental consequences of the growing, harvesting and transportation processes of nopal were evaluated with the aid of a life cycle assessment (LCA) method using SimaPro software version 8.5.2. The results showed that global warming (83.13%) and ozone depletion (99.25%) were significantly affected by the cultivation process due to current fertilization methods. The number of estimated gasses and chemicals emitted like ammonium (18.88 kgNH3/ha/year), nitrogen oxides (35.32 kgNOX–NO2/ha/year) and nitrous oxide (28.57 kgN2O/ha/year) were believed to be the result of the chemical fertilizers employed. The current cultivation process additionally reported emissions of nitrate (886.48 kgNO3/ha/year) and phosphorus (0.041 kg P/ha/year) caused by soil water erosion. The transportation process reported low levels of environmental impact; however, a significant amount of acidification (88.54%), mineral depletion (80.95%) and water consumption (84.06%) resulted from the process utilized to produce nopal in brine. In summary, the entire process resulted in a Global Warming Potential (GWP) of 0.562 kg/CO2 eq.
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Guillermo Alexis Vergel-Rangel was involved in methodology, investigation and validation. Pablo Emilio Escamilla-García was involved in conceptualization, writing—original draft and project administration. Raúl Horacio Camarillo-López was involved in writing—review and editing and formal analysis. Jair Azael Esquivel-Guzmán was involved in resources, writing—review and editing. Francisco Pérez-Soto was involved in investigation.
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Appendix A: Main characteristics of Regosol soil in Milpa Alta, Mexico City
Appendix A: Main characteristics of Regosol soil in Milpa Alta, Mexico City
General data of the soil in Milpa Alta | ||||||||
---|---|---|---|---|---|---|---|---|
General soil | Dominant soil | Associated soils and inclusions | ||||||
Sequence | 1 | 2 | 3 | 4 | ||||
Share in Soil Mapping Unit (%) | 55 | 30 | 10 | 5 | ||||
Database ID | 19,616 | 19,617 | 19,618 | 19,619 | ||||
Soil unit symbol (FAO 74) | – | – | – | – | ||||
Soil unit name (FAO74) | – | – | – | – | ||||
Soil unit symbol (FAO 85) | – | – | – | – | ||||
Soil unit name (FAO 85) | – | – | – | – | ||||
Soil unit symbol (FAO 90) | RGe | PHh | RGe | ANu | ||||
Soil unit name (FAO 90) | Eutric Regosols | Haplic Phaeozems | Eutric Regosols | Umbric Andosols | ||||
Soil texture | Coarse | Fine | Coarse | Medium | ||||
Ref. floor depth (cm) | 100 | 100 | 100 | 100 | ||||
AWC (mm) | 100 | 150 | 100 | 150 |
General data of surface soil (0–30 cm) in Milpa Alta | ||||||||
---|---|---|---|---|---|---|---|---|
Surface soil (0–30 cm) | Dominant soil | Associated soils and inclusions | ||||||
Sand fraction in soil (%) | 73 | 25 | 73 | 50 | ||||
Silt fraction in soil (%) | 23 | 35 | 23 | 42 | ||||
Clay fraction in soil (%) | 4 | 40 | 4 | 8 | ||||
USDA classification of soil texture | Sandy loam | Clay (light) | Sandy loam | Loam | ||||
Apparent density of the reference soil (kg/dm3) | 1,7 | 1,27 | 1,7 | 1,56 | ||||
Soil apparent density (kg/dm3) | 1,52 | 1,18 | 1,52 | 1,41 | ||||
Gravel content in soil (%) | 19 | 4 | 19 | 10 | ||||
Soil organic carbon (% weight) | 0,41 | 2,74 | 0,41 | 4,19 | ||||
Soil pH (H2O) | 6 | 6,4 | 6 | 6,4 | ||||
Topsoil CEC (clay) (cmol/kg) | 140 | 21 | 140 | 140 | ||||
Topsoil CEC (soil) (cmol/kg) | 14 | 18 | 14 | 38 | ||||
Soil base saturation (%) | 80 | 90 | 80 | 80 | ||||
Topsoil TEB (cmol/kg) | 11,2 | 16,2 | 11,2 | 30,4 | ||||
Soil calcium carbonate (% weight) | 0 | 0,2 | 0 | 0 | ||||
Soil gypsum (% weight) | 0 | 0,1 | 0 | 0 | ||||
Soil sodium (ESP) (%) | 2 | 1 | 2 | 1 | ||||
Soil salinity (ECe) (dS/m) | 0 | 0,1 | 0 | 0 |
General data of surface soil (30–100 cm) in Milpa Alta | ||||||||
---|---|---|---|---|---|---|---|---|
Surface soil (30–100 cm) | Dominant soil | Associated soils and inclusions | ||||||
Sand fraction in soil (%) | 73 | 21 | 73 | 51 | ||||
Silt fraction in soil (%) | 23 | 29 | 23 | 46 | ||||
Clay fraction in soil (%) | 4 | 50 | 4 | 3 | ||||
USDA classification of soil texture | Sandy loam | Clay (light) | Sandy loam | Sandy loam | ||||
Apparent density of the reference soil (kg/dm3) | 1,7 | 1,23 | 1,7 | 1,7 | ||||
Soil apparent density (kg/dm3) | 1,53 | 1,12 | 1,53 | 1,47 | ||||
Gravel content in soil (%) | 19 | 4 | 19 | 10 | ||||
Soil organic carbon (% weight) | 0,15 | 1,42 | 0,15 | 2,3 | ||||
Soil pH (H2O) | 6,4 | 6,2 | 6,4 | 6,3 | ||||
Subsoil CEC (clay) (cmol/kg) | 140 | 20 | 140 | 140 | ||||
Subsoil CEC (soil) (cmol/kg) | 13 | 15 | 13 | 30 | ||||
Soil base saturation (%) | 85 | 94 | 85 | 80 | ||||
Subsoil TEB (cmol/kg) | 11,1 | 14,1 | 11,1 | 24 | ||||
Soil calcium carbonate (% weight) | 0,2 | 0,1 | 0,2 | 0,1 |
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Vergel-Rangel, G.A., Escamilla-García, P.E., Camarillo-López, R.H. et al. The environmental impact of nopal (Opuntia ficus-indica) production in Mexico City, Mexico through a life cycle assessment (LCA). Environ Dev Sustain 23, 18068–18095 (2021). https://doi.org/10.1007/s10668-021-01428-7
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DOI: https://doi.org/10.1007/s10668-021-01428-7