Keywords
life cycle assesment, food systems, agriculture, environmental impacts
This article is included in the Agriculture, Food and Nutrition gateway.
life cycle assesment, food systems, agriculture, environmental impacts
Greenhouse gas emissions from agriculture continue to rise on a global scale, although not as fast as emissions from other human activities. Having better information at a national level on emissions from agriculture1,2, live-stock, fisheries and forestry can help countries identify opportunities to reduce them, whilst pursuing objectives of food security, resilience and rural development and gaining access to global financing for implementation3. The agricultural sector is the sector that uses the most water, globally representing around 69% of all extraction, with household consumption at approximately 10% and industry at 21%4 The water footprint of a product is the total amount of water used to produce the goods or the service we use. In this study we calculated the green, blue and grey water footprint. The green water footprint is the amount of water in the root zone of the soil and evaporated, transpired or incorporated by plants. The blue water footprint is the amount of water that comes from surface or groundwater and is evaporated, incorporated into a product or taken from one body of water (for example irrigated agriculture have a blue water footprint). The grey water footprint "is the amount of fresh water required to assimilate pollutants to meet specific water quality standards" (see Water Footprint Network website). The agro-ecological agriculture is farming that “centers on food production that makes the best use of nature’s goods and services while not damaging these resources” (see More and Better report on a viable food future). It links ecology, culture, economics and society to create healthy environments, food production and communities in order to maintain the sustainable development (see Groundswell international page on agroecological farming). While the conventional agriculture also known as industrial agriculture, "refers to farming systems which include the use of synthetic chemical fertilizers, pesticides, herbicides and other continual inputs, genetically modified organisms, concentrated animal feeding operations, heavy irrigation, intensive tillage, or concentrated monoculture production. Thus conventional agriculture is typically highly resource and energy intensive, but also highly productive" see USDA factsheet on conventional farming In this study, emissions and water requirements for tomato cultivation in conventional production systems and agro-ecological production systems were calculated in the La Esperanza and Tabacundo parishes, Pedro Moncayo canton.
The present study examines the carbon and water footprint of product during the activities of the agricultural phase of tomato cultivation (between 2nd June and 5th of September 2017) in La Esperanza and Tabacundo, Pedro Moncayo canton, Ecuador. The average temperature was 20 °C, the humidity was 66% and the total precipitation was 320,8 mm in the examined period (https://en.climate-data.org/location/719640/). Three agro-ecologically managed plots (GPS decimal degrees: Plot 1: Latitude: -0.811193, Longitude: -78.6955; Plot 2: Latitude: -0.809214, Longitude: -78.6362; Plot 3: Latitude: -0.811429, Longitude: -78.6318) and three conventionally managed plots (GPS decimal degrees: Plot 4: Latitude: -0.809021, Longitude: -78.6273; Plot 5: Latitude: -0.805316, Longitude: -78.6114; Plot 6: Latitude: -0.805312, Longitude: -78.6114) were analyzed in this study. For information about the size of the experimental areas and the applied fertilizers please see Dataset 1. The water footprint was calculated as established by Hoekstra et al. (2011)5. For agro-ecological production systems, the green water footprint and blue water footprint were calculated. They lack a grey water footprint since they do not incorporate synthetic fertilisers, whereas for the conventional system the green water footprint, blue water footprint and the grey water footprint were calculated. Agro-ecological systems:
Water footprint = Green Water Footprint + Blue Water Footprint(m3/ton)
Conventional case:
Water Footprint = Green Water Footprint + Blue Water Footprint + Grey Water Footprint(m3/ton) (Hoekstraetal., 2011)
For the Carbon Footprint calculation, the equation given by greenhouse gases (GHG) Protocol, World Resources Institute and wbcsd (2011)6 was used:
kgCO2eq = Activity Data*Emission Factor x GWP
For the (GHG) calculation in the conventional plots, due to the use of fuels, the equation given by the IPCC7 belonging to the all-terrain category was used. This equation allows one to obtain CO2 emissions according to the type of fuel- be it diesel or petrol- as applicable for each case.
Source: IPCC (2006a)
where:
Emission: total emissions expressed in KgCO2eq
Fuel: fuel consumption TJ
EF: Emission factor (KgCO2eq TJ)
j: fuel type
For the greenhouse gas emissions calculation, due to the production of fertilisers, the activity data was multiplied by the emission factor. Phytosanitary emissions were calculated using the factor given by BioGrace8. Regarding greenhouse gases, due to direct emissions of N2O, the contributions of nitrogen in managed soils were taken into account and for the study the equation given by the IPCC9 was adapted so that for the case studies it was applied as follows.
For the conventional systems, the equation was reduced to:
N20 − NNcontributions = (FSN + FCR) * EF1
Source: IPCC (2006c)9
And for the agro-ecological systems:
N2O− NNcontributions = (FON + FCR) * EF1
Source: IPCC (2006c)9
The calculation of indirect emissions of N2O for managed soils was carried out by means of adapting equation 11.9 of the manual (IPCC, 2006c)7 to the case study, thus the applied equation was: Conventional systems:
N2O(ADT) − N = (FSN * FracGASF) * EF4
Source: IPCC (2006c)9
Agro-ecological systems:
N2O(ADT) − N = (FON * FracGASM) * EF4
Source: IPCC (2006c)9
For the calculation of greenhouse gas emissions due to the use of fertilisers, the results of direct and indirect emissions of N2O were taken into account. Regarding the emissions from applying phytosanitary products, this section was considered only in the conventional plots since they apply pesticides for the prevention of pests, such as fungicides and insecticides. To perform the calculation, the amount employed in kg/hectare (ha) and the emission factor given by BioGrace8 were taken into account.
Figure 1 shows the water requirements for each plot. Regarding the conventional system, the highest values of green and blue water footprints corresponded to plot 5 with 34.42 and 87.54 litres of water/kg of tomatoes, re-spectively. For the agro-ecological systems, the plot with the highest green and blue water footprint was plot number 1 with 16.46 and 42.54 litres of water/kg of tomatoes, respectively. In relation to the grey water footprint, the highest value was found for plot 5 with 2.59 litres of water/kg of tomato.
In relation to the green water footprint, on average an agro-ecological system requires 9.07 litres of water/kg of tomatoes. For the blue water footprint, it requires 32.04 litres of water/kg of tomatoes (Figure 2). For the conventional system the most representative footprint is that of blue water with 44.19 litres of water/kg of tomatoes, followed by the green water footprint with 14.42 litres of water/kg of tomato whilst the lowest value is 0.96 litres of water/kg of tomatoes for the grey water footprint.
These results show that conventional cultivation consumes 18.45 litres more water for every 1 kg of tomatoes in the La Esperanza and Tabacundo parishes of the Pedro Moncayo canton (Figure 3).
Table 1 shows that the highest generation of emissions was in plot 2 for the agro-ecological system and plot 4 for the conventional system The average emissions for the agro-ecological system in the study area was 757.83kg of CO2/ha whilst it was 830.96kg of CO2/ha for the conventional system. In the agro-ecological system, the greatest generation of emissions is due to the use of biofertilisers with an average of 426.68kg CO2/ha, whilst for the conventional system it is due to the use of fuel with a 552.32kg CO2/ha on average.
In the La Esperanza and Tabacundo parishes an agro-ecological system requires less water compared to a conventional system, since the latter consumes 18.45 litres more water to produce a kilogram of tomatoes. In terms of emissions, the agro-ecological system obviously generates less, since it does not include the use of fuels because all the activities are carried out manually.
In relation to the Water Footprint, we used the values provided by Villavicencio et al.10 as a referential Water Footprint for fresh tomatoes (grown in the Coquimbo Region in the Choapa basin in Chile). They found a total water footprint of 84.2l/kg for the central region whilst we found a total water footprint of 59.57l/kg of tomatoes in the conventional system and 41.11l/kg in the agro-ecological system. Our values reflect the characteristics of the study area.
As a whole, an agro-ecological system emits on average of 757.83kg CO2eq/ha whilst a conventional system emits on average 830.96kg CO2eq/ha. In the latter system, the greatest generation of emissions corresponded to the use of fuel, with an average of 552.32kg CO2eq/ha whilst for the agro-ecological system the greatest generation of emissions corresponded to the use of biofertilisers with 426.68kgCO2eq/ha.
The results obtained show that an agro-ecological system is the most efficient in terms of consumption of resources. Its produce also have an added value for promoting sustainability, responsible consumption and a healthier diet. The generation of eco-labels can encourage the consumption of these by expanding markets for this production system.
Dataset 1: Experimental setup. Area of the lands, total crop production (Kg), fertilizer application rate on total crop production, concentration of NPK in each solid fertilizer, mount of NPK (Kg), Liquid fertilizer application rate on the total crop production, Concentration of NPK in each liquid fertilizer, Amount of NPK in liquid fertilizer (Kg), GPS coordinates 10.5256/f1000research.14334.d20375011
Dataset 2: Calculated water footprint for each plot. Green, blue and grey water footprint in l (water)/kg(tomato). 10.5256/f1000research.14334.d20375112
Dataset 3: Calculated carbon footprint for each plots. Total GHG emission (kg CO2 eq): Fuel (CO2, N2O), fertiliser production (N, K2O, P2O) fertiliser use, photosanitary. 10.5256/f1000research.14334.d20375213
The present research was supported by Universidad Politécnica Salesiana and Secretaría de Educación Superior, Ciencia, Tecnología e Innovación (SENESCYT) [PIC-16-BENS-005].
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Is the work clearly and accurately presented and does it cite the current literature?
Yes
Is the study design appropriate and is the work technically sound?
Partly
Are sufficient details of methods and analysis provided to allow replication by others?
Partly
If applicable, is the statistical analysis and its interpretation appropriate?
Partly
Are all the source data underlying the results available to ensure full reproducibility?
Partly
Are the conclusions drawn adequately supported by the results?
Partly
Competing Interests: No competing interests were disclosed.
Is the work clearly and accurately presented and does it cite the current literature?
Partly
Is the study design appropriate and is the work technically sound?
Partly
Are sufficient details of methods and analysis provided to allow replication by others?
Partly
If applicable, is the statistical analysis and its interpretation appropriate?
Partly
Are all the source data underlying the results available to ensure full reproducibility?
Yes
Are the conclusions drawn adequately supported by the results?
Partly
Competing Interests: No competing interests were disclosed.
Alongside their report, reviewers assign a status to the article:
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Version 1 25 May 18 |
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