Att ta hand om överskottsmat från butiker och livsmedelsindustrin och donera överskottet till behövande är inte något nytt fenomen globalt, men att göra detta för att minska matsvinnet är tämligen nytt. Som ett resultat av detta så har det på senare tid kommit en rad aktörer som på olika sätt försöker hitta vägar för att ta hand om överskottsmaten till olika kundgrupper via olika distributionssätt. Frågan som kan ställas är vilken nytta som den levererade överskottsmaten ger och för vem? I den nya artikeln “Sustainability Assessment of Food Redistribution Initiatives in Sweden” undersöker vi en rad olika distributionssätt för överskottsmat och vilka sociala, miljömässiga och ekonomiska nyttor dessa skapar. Resultaten visar att använda sig av matkassar till socialt utsatta grupper genererar den största vinsten i termer av att minimera växthusgasutsläpp. Att använda sig av överskottsmat för att producera nya produkter visade sig skapa högst social nytta då det undersökta konceptet skapade flest arbetstillfällen (arbetade timmar per kg distribuerad mat). Problemet som samtliga iniativ har är att få ekonomin att gå ihop, då endast två av de undersökta fallen gick med vinst och inte var direkt beroende av extern finansiering.
Food banks that redistribute surplus food from retailers and the food industry to people in need are not a new concept globally, but their connection to food waste prevention is new. As a result, new types of food redistribution units are emerging and diversifying to find new target groups and distribution methods. The aim of a new study “Sustainability Assessment of Food Redistribution Initiatives in Sweden” was to identify and study surplus food redistribution units in Sweden, and then to assess the impact on several sustainability indicators for selected redistribution units, in order to increase knowledge on the types of values these redistribution concepts generate. The methods used for analyzing the scenarios were Environmental Life Cycle Assessment, Life Cycle Costing and Social Life Cycle Assessment. The results showed that providing food bags to socially exposed people generated the largest reduction of greenhouse gas emissions per kg of redistributed food. Reprocessing surplus food to a high-quality end-product was attributed to a high social value, due to job creation effects in the high number of working hours required per kg of redistributed food. With regard to economic impacts, all but two scenarios studied had monthly financial losses and therefore needed other sources of financial support.
The article has been published open access in MDPI resources:
Bergström, P.; Malefors, C.; Strid, I.; Hanssen, O.J.; Eriksson, M. Sustainability Assessment of Food Redistribution Initiatives in Sweden. Resources2020, 9, 27. doi.org/10.3390/resources9030027
Albedo change can make an important contribution to the climate impact of cropping systems. Albedo is the share of solar radiation reflected back from the ground. It ranges between 5 and 30% for bare and vegetated agricultural land, and can reach up to 90% due to snow cover. The more reflective a surface, the higher its albedo and the greater the potential for radiative cooling and eventually temperature change.
Albedo has increased globally due to agricultural expansion, converting forests to more reflective grass- and croplands. However, deforestation is associated with losses of crucial ecosystem functions including carbon storage and local surface cooling by evapotranspiration. Managing agricultural land to achieve higher reflectivity has the potential to mitigate local heat waves and global warming. Strategies to increase the albedo of croplands include selection of reflective species or varieties, introduction of cover crops, intercropping, residue retention, and delayed or no ploughing.
In a recently published article, we studied how cultivating abandoned land with short-rotation willow affects albedo and evaluated its potential as a climate change mitigation measure. We found that albedo increased from 16.5 to 21.5% on average when fallow land was cultivated with willow, based on three years of field-measured data. These data were subsequently combined with a time-dependent life cycle assessment (LCA) model of bioenergy produced from willow. Here, we included emissions from the production of inputs, field operations, soil, transport and energy conversion.
Simulating processes and emission along the life cycle and impacts on climate over time allowed us to compare the effect of albedo change (cooling) to that of greenhouse gas emissions (warming) and carbon sequestration in biomass and soil (cooling). In sum, the bioenergy system had a net cooling effect because albedo change and carbon sequestration outweighed emissions from the supply chain and soil. Our results over time showcase the different nature of albedo and long-lived greenhouse gases as climate forcers. Albedo change needs to be sustained for years in order to offset the temperature response to a one-off greenhouse gas emission.
The article has been published open access in GCB Bioenergy: Sieber, P., Ericsson, N., Hammar, T., & Hansson, P.-A. Including albedo in time-dependent LCA of bioenergy. GCB Bioenergy, n/a(n/a). doi:10.1111/gcbb.12682
In a new study by researchers from the Food System Group together with the Stockholm Resilience Centre, the environmental impacts of the Swedish diet were benchmarked relative to global environmental boundaries suggested by the EAT-Lancet Commission. To identify local environmental concerns not captured by the global boundaries, relationships between the global EAT-Lancet variables and the national Swedish Environmental Objectives were analysed and additional indicators for missing aspects were identified.
The results showed that the environmental impacts caused by the average Swedish diet exceeded the global boundaries for greenhouse gas emissions, cropland use and application of nutrients by two- to more than four-fold when the boundaries were scaled to per capita level. With regard to biodiversity, the impacts caused by the Swedish diet transgressed the boundary by six-fold. For freshwater use, the diet performed well within the boundary.
Comparison of global and local indicators revealed that the EAT-Lancet variables covered many aspects included in the SEOs, but that these global indicators are not always of sufficiently fine resolution to capture local aspects of environmental sustainability, such as eutrophication impacts. To consider aspects and impact categories included in the SEO but not currently covered by the EAT-Lancet variables, such as chemical pollution and acidification, additional indicators and boundaries are needed. This requires better inventory data on e.g., pesticide use and improved traceability for imported foods.