Next Article in Journal
Decision-Making under Uncertainty for Water Sustainability and Urban Climate Change Adaptation
Previous Article in Journal
The Response of Grain Potential Productivity to Land Use Change: A Case Study in Western Jilin, China
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Food Waste in School Catering: An Italian Case Study

Department of Agricultural and Food Sciences, University of Bologna, Via Fanin 50, Bologna 40127, Italy
*
Author to whom correspondence should be addressed.
Sustainability 2015, 7(11), 14745-14760; https://doi.org/10.3390/su71114745
Submission received: 12 August 2015 / Revised: 23 October 2015 / Accepted: 28 October 2015 / Published: 4 November 2015
(This article belongs to the Section Sustainable Agriculture)

Abstract

:
Food losses and waste are currently at the heart of academic debates, civil society initiatives, and political agendas. This paper investigates food waste in school catering services focusing on six schools located in the municipality of Verona (Italy). It aims to quantify food waste, as a measure of food catering inefficiency, to identify the main causes, and to suggest a set of prevention and reduction interventions. For these purposes food waste is defined as all the products discarded from the food chain while still preserving their nutritional value and complying with safety standards. The work shows a significant level of inefficiency in the school catering services, measured by the amount of food processed and still perfectly edible, but not served during the meals. On average more than 15% of the overall processed food is wasted. Among the causes identified in this study, four of them were more relevant than others because of their implications and impact on prevention: the lack of attention to dietary habits, the rigid food procurement specifications, the menu composition, and the meal presentation.

1. Introduction

Food waste is a significant phenomenon that is currently at the heart of academic debates, civil society initiatives, and political agendas. The issue is addressed through different approaches and disciplines [1]. These factors and the lack of research attention so far have not allowed the development of shared terminology to clearly define food waste. This, in turn, affects the general debate, the definition of the concept, and the identification of possible remedies [2,3,4,5,6,7]. In this respect this work identifies as food waste all the products discarded from the food chain while still preserving their nutritional value and complying with safety standards. The literature related to the production and retailing stages is rather significant [5,8,9,10,11,12,13], suggesting some consensus over the major issues related to this segment of the food chain. On the other hand, what is missing is information at the consumption level (catering, domestic consumption, etc.), which is where a number of scientists and reports locate the higher share of food waste—but there is no consensus about its quantitative dimension [3,11,12,14,15].
Engström and Carlsson-Kanyama [16] analyzed waste in the catering industry, providing insight and data about this issue with a case study on Sweden. WRAP [17] conducted an investigation in a number of schools in England in order to understand the nature and causes of waste in this sector and the potential impact of corrective actions. Sonnino and McWilliam [18] argued how scientific studies have been dealing with the topic mainly from a climate change perspective and focused their attention on food services with a case study on Welsh hospital catering services. An additional work aimed at assessing the amount of food waste by meal components was carried out by Byker et al. [19], who identified the highest rate of food waste in vegetables (51.4%), followed by the main entrée (51%). When converted to cups, the amount of waste seems to be extremely significant: 38.2 out of 130.5 cups of fruit and 92.6 cups of veggies out of 139.8 were wasted. Particular attention has to be given to the “Portuguese school” that presents several works addressing food waste in food catering services. Ferreira et al. [20] evaluated food waste in a Portuguese university to assess the efficiency of the service. They identified an index of waste/consumption (%) obtained as the ratio between plate waste and the quantity of distributed food, subtracting the weight of leftovers. Results suggest an index of waste/consumption at approximately 24%. Liz Martins et al. [21] compared the visual estimation method with the weighing method, finding that the visual estimation method is not as accurate as the weighing method in assessing nonselective aggregated plate waste. Dânia et al. [22] investigated plate waste as a potential indicator of portion inadequacy at school lunch. Within this study plate waste (%) was calculated as the ratio of food discarded to food served to the children.
In the past decade private companies and public service providers made significant efforts to increase the sustainability of their operations. Within this framework, to improve the efficiency and quality of school catering services, the Italian public administration essentially focused on two elements: the preparation of meals with organic and locally-sourced produce, and the design of healthy diets following the guidelines of the Italian National Research Institute for Food and Nutrition and the Ministry of Education, University and Research [23]. The guidelines do not address food waste directly but include a set of recommendations on purchase decisions and consumption behaviors [24] directly related to a number of food waste drivers [25].
At the European level, the aforementioned WRAP study suggests that “in England, over a school year (40 weeks), a total of 55,408 tons of food waste is generated by primary schools and 24,974 tons by secondary schools, giving a total food waste weight of 80,382 tons” [17]. A significant amount of food waste in catering services was also identified by Sonnino and McWilliam [18] who––in the case study carried out in the Welsh hospital catering services––suggested food waste ranging between 19% and 66% per meal. This phenomenon should be regarded as an indicator of the (in)efficiency of the catering industry. If the highest system efficiency implies the complete transformation of the supplied food into consumed food, waste could then be considered a shortfall in the system’s output, leading to an efficiency decrease. In other words, a system is efficient when the resources are utilized in an economic manner whereas, according to Pareto’s concept, efficiency means reaching an allocation of resources that does not allow further improvements [26]. Consequently, the more meals unconsumed and thus wasted, the higher the inefficiency.
In July 2003, the intensification of the food waste debate led to the approval of Italian law 155, “Regulation on the distribution of foodstuffs for social purposes”, the so-called “Good Samaritan Law.” This legislative measure simplifies the rules on the recovery of foodstuffs for non-profit organizations or an equivalent. This law boosted the number of recovery activities and the amounts of recovered food, for charitable purposes, from school and company canteens all over the country [27].
This paper investigated food waste in school catering in order to assess the operational efficiency of the food services and to contribute to the understanding of food waste dynamics. By analyzing the school catering system’s features and collecting quantitative evidence and information, this paper attempted to analyze the amount of food waste (i.e., food processed and still perfectly edible, but not served during the meals) and to investigate the main causes that lead to the identified amount of unserved food and so to assess the operational efficiency of the food services to suggest a recovery intervention model in order to reduce waste amounts and improve a rational (economic) use of resources.

2. Material and Methods

A research protocol was designed to combine a systematic data collection from six school canteens with a number of non-structured interviews carried out with caterers and teachers during three focus groups [28,29,30].

2.1. Case Study Identification

In 2005, the municipality of Verona and Last Minute Market (LMM), a subsidiary of the University of Bologna, signed an agreement to identify a joint solution for food waste reduction in public school canteens (see Figure 1).
The approach included the recovery and distribution of unserved meals, perfectly fit for consumption, to low-income brackets of the population, following the LMM model based not only on the prevention of food waste, but also on the recovery of discarded edible food.
The food recovery model designed and implemented by LMM is based upon the principle of proximity [31,32]. This means that a donor (the school canteen) and a beneficiary (a body or association helping vulnerable people) need to be located in the same neighborhood or in the near vicinity. The aim is to reduce the distance and the duration of transport. This principle is relevant to increase the safety of an operation carrying a high contamination risk owing to the health and hygiene aspects. In this respect, the municipality of Verona and LMM, with the support of the local health authorities, implemented a set of appropriate measures to ensure the safety of the products.
Schools were chosen according to their location, in order to establish a restricted area of operation and thus facilitate recovery activities. Six schools, consisting of three primary (Primary 1, Primary 2, and Primary 3) and three first grade secondary schools (Secondary 1, Secondary 2, and Secondary 3) were identified.
Meals were produced in a centralized cooking facility and then distributed to each school. The products, transported in isothermal steel food containers (Gastronorm), were then portioned and served at tables to the children. Once the service was completed, unserved meals were made available for collection by the charitable organizations’ volunteers.
The actors involved in the study included 480 students from six primary and first grade secondary schools; 18 caterers, three per school; 12 teachers, two per school; four municipal managers; four beneficiary charitable organizations, their volunteers, and aid recipients; the LMM working group, consisting of three people who regularly monitored the correct implementation of the given protocols and the health and hygiene standards of the recovered food; and the research team, consisting of three people responsible for the accuracy of the data collection.
Figure 1. Research rationale.
Figure 1. Research rationale.
Sustainability 07 14745 g001

2.2. Data Collection

This paper analyzed data for three scholastic years, from 2008 to 2011. During the first year (2008–2009), as a pilot project in two schools, a preliminary analysis of the efficiency of the canteen management system was conducted. Data were collected to categorize the quantity and the nutritional characteristics of the food processed (prepared) but not served, and disposed of as waste. For five days a week (from Monday to Friday), each portion of unserved food was weighed. Its temperature was then measured and recorded. In order to gather additional qualitative information on consumption and distribution modalities, data collection was integrated by a number of non-structured interviews carried out within three focus groups (focus group participants: two researchers from the University of Bologna (one as facilitator); 12 teachers (two per each school); four municipal managers; two representatives for each of the charitable organizations) [28,29,30].
During the second year (2009–2010), corrective actions to reduce inefficiencies were identified on the basis of the results obtained in the preliminary analysis. Remedial actions can be divided in two categories: a theoretical/didactical one aimed at reducing the causes of food waste, and an applied one aimed at identifying alternative uses of the food that is still edible. In particular, a procedure for product recovery, in compliance with hygienic and sanitary regulations, and for its distribution to charitable organizations that deliver food to disadvantaged people, was defined.
In order to apply corrective actions comprehensively, a protocol for food recovery was set, aiming at ensuring the nutritional value, physical integrity, and hygienic standard of the food distributed to the final beneficiaries.
During the third year (2010–2011), data and information were collected along with food recovery. School catering generally lasts from the beginning of October to the end of May. During October 2010, all the stakeholders were informed about the results of the preliminary analysis (of year one) and the identified remedial actions (of year two). Particular attention was given to the canteen staff and the charitable organizations involved in the collection of the unserved food, and the entire month was devoted to training them and testing the corrective actions. Food recovery and data collection began in November 2010 and concluded at the end of May 2011. The overall duration of the survey is particularly significant, considering that the studies listed in the existing literature have often been limited to a few weeks [16,18].
Collected data focused on food recovery, treatment, and transport. Related operations and processes were repeated each day, from Monday to Friday, in all the pilot schools. The only exception was Secondary School 3, where the catering service was functioning only three days a week (Tuesday, Wednesday, and Friday). Moreover, an inefficiency index of the catering system was calculated as a percentage of wasted food compared to the amount of processed food.
Canteen staff followed the guidelines to keep the unserved food, received from the kitchen in steel Gastronorm containers, in good condition. Association members involved in the recovery operation were asked to observe the typology, the weight, the temperature, and other relevant parameters of each food portion. Collected data was then discussed in a weekly briefing between canteen and association staff and the research group.
At the end of each day, unserved food was transferred to other insulated containers in order to maintain its physical characteristics. In the case of warm food, the proper conservation temperature was set to at least 65 °C, while for cold food it was not to exceed 4 °C. When the indicated limits were not observed, food was not recovered.
All the portions (pasta and soups, meat and fish, fruit, and bread) were kept separately during the entire process and placed in different stations (school and association canteens). In the canteens of the charitable organizations, food was immediately consumed by the final beneficiaries or, after cooling down, stored for later consumption. The process allowed for the identification of the amount of recovered portions and the inefficiencies of the catering management system.
Lunch menus were divided into two main typologies: summer and winter. The winter menu was served from October to March for a total of 92 days. The summer menu was served from April to May for a total of 33 days. The main difference between the two menus was the variation in fruit and vegetables depending on their seasonality. Menus consisted of the same food categories: a warm (pasta, rice, or soup) or cold (pasta or rice) entrée; a main warm course (meat, cheese, fish, or eggs) with the exception of certain cheeses such as mozzarella or Monte Veronese (a local cheese); a warm or cold seasonal side dish; seasonal fruit; and bread. One day every two weeks, pizza, along with charcuterie, was served instead of the usual entrée.
Among the recovered products, there were no beverages, since during the meals only water was served from dispensers.
Furthermore, in accordance with the guidelines on balanced meals [23], portions were composed as follows: 0.2 kg for an entrée, 0.12 kg for a main course, 0.12 kg for a side dish, 0.15 kg for fruit, and 0.08 kg for bread.
Partially consumed portions of food were not taken into account since they do not respect the minimum sanitary and hygienic standards to be considered as edible food, hence they do not fit the definition of ‘food waste’ utilized within the present work.

3. Results

The analysis suggested that during the period of investigation the catering service management had a high level of inefficiency, measured as the amount of food processed but not served. This amount represented an average of 15.31% (6523.35 kg) of the overall processed food.
Side dishes had the highest percentage of food waste: 24.67% (1883.06 kg) of the total vegetables delivered to the cafeterias, with a prevalence of cooked vegetables (1202.10 kg) over raw vegetables (680.96 kg), as the former were served more frequently than the latter. In absolute terms, the entrée had the highest number of unconsumed portions, with the total of 2533.60 kg representing 19.92% of the processed entrées. Risotto had the highest degree of inefficiency with waste amounting to 629.15 kg, followed by pasta with tomato ragout (462.71 kg), and soups or pasta in broth (440.73 kg). Bread was also characterized by a high percentage of waste for a total of 900.58 kg, corresponding to 17.7% (see Table 1).
Main courses and fruit presented results below the average. In the case of main courses, unconsumed portions amounted to 12.59%, corresponding to 960.84 kg. In this category, the dish with the highest number of unconsumed portions was beef (241.62 kg), followed by eggs (138.53 kg). Fruit was characterized by a limited number of unconsumed portions, representing 1.51% (114.26 kg) of the total. The limited amount of remaining portions can be explained by action taken by the catering management: while leaving the canteen students were encouraged to take remaining fruit that could be consumed during the afternoon.
In a comparison between the summer and the winter menu, it appears that the percentage of unconsumed portions is not significantly different (15.00% and 16.08%, respectively), whereas the absolute values diverged considerably (4579.07 kg against 1944.28 kg, respectively). The difference in absolute values is related to the duration of the period under investigation: 92 days during winter and 33 days during the summer period. On an average basis, the quantity of unserved food was 49.77 kg per day during winter and 58.92 kg per day during summer.
Waste increase was strongly linked to wastage of side dishes, which rose from 16.97% to 44.12% (see Table 2). This indicated that raw vegetables, mostly present in the summer menu, often remained unserved. By contrast, the survey indicated a reduction of the amount of waste for entrées (about from 21.75 to 15.29) and main courses (from 13.43 to 10.46). Thus, excluding vegetables, cold courses were characterized by a lower amount of waste than warm courses.
Table 1. Processed food (kg) and unserved food (kg and %)––from November 2010 to May 2011.
Table 1. Processed food (kg) and unserved food (kg and %)––from November 2010 to May 2011.
CategoryProcessed FoodUnserved Food Inefficiency Index
Total kgAverage kg Per DayAverage Portions Per DayTotal kgAverage kg Per DayAverage Portions Per Day(%)
Entrée12720101.76 509 2533.6020.2710119.92
Pasta meat ragout1774.88104.40522307.4718.099017.32
Pasta fish ragout295.8198.60493135.2745.0922545.73
Pasta tomato ragout2070.7090.03450462.7120.1210122.35
Pasta vegetables ragout1479.0792.44462289.2718.089019.56
Soup2366.51102.89514440.7319.169618.62
Risotto2662.33110.93555629.1526.2113123.63
Pasta with oil2070.70108.98545268.9914.167112.99
Main course7632.0061.06509960.847,696412.59
Beef1347.858.60488241.6210.518817.94
Turkey748.2462.35520116.129.688115.52
Chicken1346.8264.13534160.147.636411.89
Pork299.2959.8649939.777.956613.29
Pizza748.2462.3552047.473.96336.34
Cold cut598.5966.5155439.584.40376.61
Fish897.8856.1246891.725.734810.21
Eggs748.2462.35520138.5311.549618.51
Cheese897.8859.8649985.895.73489.57
Side dish7632.0061.065091883.0615.0612624.67
Raw vegetables2598.1355.28461680.9614.4912126,21
Cooked vegetables5033.8764.545381202.1015.4112823,88
Fruit/Yogurt9540.0076.32509144.261.1581.51
Bread5088.0040.70509900.587.209017.70
Other * 101.01
Total42612.00340.905096523.3551.3738915.31
Note: *: Unutilized ingredients such as sauces, garnishes, etc.
The quantity of unserved bread showed a decrease (see Table 2) during the summer, thanks to specific actions introduced to reduce the inefficiencies, as in the case of fruit. In particular, the quantity of bread delivered to schools during summer was 5%–6% lower than in winter. The share of recovered bread, which already stood at a rather low level in the winter period, decreased by an additional 1.62% in the summer. This suggests that the measures taken to curb bread waste had positive results.
Table 2. Comparison between winter and summer menus: processed and unserved food, and inefficiency index.
Table 2. Comparison between winter and summer menus: processed and unserved food, and inefficiency index.
CategoryWinter Menu (92 Days)Summer Menu (33 Days)
Processed Food (kg)Unserved Food (kg)Inefficiency IndexProcessed Food (kg)Unserved Food (kg)Inefficiency Index
AB(B/A %)CD(D/C %)
Entrée9110.001981.8021.753610.00551.8015.29
Main course5466.00734.2413.432166.00226.6010.46
Side dish5466.00927.4416.972166.00955.6244.12
Fruit/Yogurt6832.50134.841.972707.509.420.35
Bread3644.00712.3919.551444.00188.1913.03
Other *--88.36----12.65--
Total30518.504579.0715.0012093.50 1944.2816.08
Note: *: Unutilized ingredients such as sauces, garnishes, etc.
From October to May an average of 510 meals a day were delivered to schools to serve about 480 children. The number of meals in excess was 5% to 6% to satisfy any possible request for additional food. During the period under analysis the food waste per student was 13.59 kg. Considering that a medium portion is equal to 0.134 kg, the total waste was about 101 portions per person.
Overall, one portion out of eight was not consumed by students. Results suggest that on a daily basis, 101 portions of entrées, 64 of main courses, 126 of side dishes, eight of fruit, and 90 of bread were not consumed. These unserved but fully edible portions would constitute an additional 64 complete––excluding fruit––and 62 incomplete meals per day (see Figure 2).
Figure 2. Daily meals obtained from the recovery of unserved food.
Figure 2. Daily meals obtained from the recovery of unserved food.
Sustainability 07 14745 g002
Given that a complete meal, without fruit, has a cost of 4.30 euros, without a recovery system the overall amount of unserved but fully edible portions would represent a loss of 381.90 euros per day (see Table 3). With the recovery system in place there are no additional charges for the school canteen while the beneficiary organizations have an economic benefit represented by the value of the recovered meals that they do not need to purchase.
Table 3. Recovered economic value.
Table 3. Recovered economic value.
EntréeMain CourseSide DishBreadMealEconomic Value
Quantity (num)Unit Cost (€)Quantity (num)Unit Cost (€)Quantity (num)Unit Cost (€)Quantity (num)Unit Cost (€)Cost (€)Average Daily Cost Recovered (€)
1011.50641.801260.70900.304.30381.90
Efficiency levels were also diversified within each food category. Considering the weighted average of every single dish, among the entrées, lasagna and tortellini showed the best results: in the case of lasagna the average number of unserved portions was 40, while for tortellini it was 73 (see Figure 3). These items were followed by soup, with an average of 103 unserved portions. Pasta and rice presented the worst results, with 113 and 130 portions remaining unconsumed.
Figure 3. Average number of unserved portions of entrées (per day).
Figure 3. Average number of unserved portions of entrées (per day).
Sustainability 07 14745 g003
During the interviews, attendants reported that students claimed to eat pasta and rice rather often at home, hence they did not wish to eat them in the canteen.
With regard to the main courses, cheese presented the lowest number of unserved portions (31), followed by pizza (32) and fish (40). Eggs (48) and meat (76) had the highest number of unserved portions (see Figure 4). Also in this case attendants reported that students used to eat those dishes rather frequently at home.
Food efficiency can be based on the composition of daily menus as well. The winter menu, which included pizza accompanied by meat, or cheese and raw vegetables, reported the lowest percentage of waste and hence, it was the most efficient. In this composition vegetables showed a lower surplus, while bread reported a higher number of unserved portions. The significant surplus of bread can be explained by the presence of pizza––an alternative––in the same menu. The quantity of bread served together with pizza did not change owing to the procurement specifications that were provided for standard rations for each type of product (see Table 4).
Figure 4. Average number of unserved portions of main courses (per day).
Figure 4. Average number of unserved portions of main courses (per day).
Sustainability 07 14745 g004
Table 4. Comparison between the more and less efficient compositions in the winter menu (kg and number of unserved portions).
Table 4. Comparison between the more and less efficient compositions in the winter menu (kg and number of unserved portions).
Winter Menu
CompositionProcessed FoodUnserved FoodInefficiency Index
Total kg (November to March) AAverage kg Per DayAverage portions Per DayTotal kg (November to March) BAverage kg Per DayAverage Portions Per DayB/A (%)
More EfficientEntréePizza margarita249.662.45208.892.22194
Main courseHam steak268.867.25607.751.94163
Side dishRaw vegetables249.662.452037.149.294715
Fruit 305.476.35509---0
Bread 162.8840.7250944.3811.1013927
Less EfficientEntréeRisotto with vegetables416104520135.1733.7916932
Main courseTurkey escalope with sage249.662.452037.059.267715
Side dishGreen beans with oil249.662.452053.8013.4511222
Fruit 305.476.355092.930.7351
Bread 162.8840.7250940.8910.2212825
The menu composition with the highest percentages of surplus, and therefore the highest rate of inefficiency, was the one that included risotto with vegetables, turkey escalope, green beans, and bread.
In the menu with tortellini in broth (one of the entrées with the lowest share of waste), boiled beef showed the highest surplus among the main courses at 84.63 kg, corresponding to 705 portions. Considering that tortellini broth is prepared with beef, the latter should be processed differently, in order to be more attractive.
In the summer menu one of the more efficient menus included pizza combined with a cold cut or cheese and raw vegetables. In this case bread waste was lower than in the winter period because of the smaller amount of product delivered to the canteen.
An additional similarity between the two seasonal menus is related to the combinations of dishes presenting the highest amount of unserved portions. The two combinations present rather similar food preparations: cold rice with vegetables, sliced turkey, and tomatoes for the summer menu and rice with vegetables, turkey escalope, and green beans for the winter menu (see Table 5).
Table 5. Comparison between the more and less efficient summer menu (kg and number of unserved portions).
Table 5. Comparison between the more and less efficient summer menu (kg and number of unserved portions).
Summer Menu
CompositionProcessed FoodUnserved FoodInefficiency Index
Total kg (April to May) AAverage kg per DayAverage Portions per DayTotal kg (April to May) BAverage kg per DayAverage Portions per DayB/A (%)
More EfficientEntréeWhite pizza with grana62.462.45204.104.10347
Main courseMozzarella67.267.25601.581.58132
Side dishRaw vegetables62.462.452014.9014.907524
Bread 40.7240.7250914.0214.0217534
Less EfficientEntréeRice with vegetables20810452044.2722.1411121
Main courseSliced turkey with rosemary124.862.452031.1515.5813025
Side dishTomatoes124.862.45209.374.69398
Bread 81.4440.725096.433.22408
In the analysis of the performances of the selected schools, the highest surplus per student (i.e., the lowest degree of efficiency) was recorded in Primary School 2, which had almost 15 kg of waste per capita. Secondary School 2 followed with 14.5 kg of waste per capita; Primary 3 and Primary 1 with 14 kg; Secondary 3 with 10.5 kg and Secondary 2 with 9 kg (see Table 6). Food waste in Secondary Schools 3 and 1 was significantly lower than in the other institutions. This difference could be related to the fact that the two schools are located in one of the lower-income neighborhoods of Verona. As reported by the teachers during the interviews, for some of the students, lunch at the canteen was the only complete meal of the day.
Table 6. Comparison among the six case studies: inefficiency index per school.
Table 6. Comparison among the six case studies: inefficiency index per school.
SchoolProcessed FoodUnserved FoodInefficiency Index
Total kg (November to May) AAverage kg Per DayTotal kg (November to May) BAverage kg Per DayB/A (%)
Primary 1651552.121371.3310.9721.05
Primary 2651252.09793.136.3512.18
Primary 3651452.122224.0117.7934.14
Secondary 1651752.14296.542.374.55
Secondary 2651252.101219.099.75 18.72
Secondary 3651252.09609.514.889.36

4. Discussion: The Causes of Food Waste

This paper highlights the relevance of food waste as defined in the case study. Unserved food amounts to 15% to 16% of the total amount of food delivered to the six schools under analysis. Food waste causes are numerous and diverse [25]; however, students’ and households’ lack of attention to dietary habits has to be included among the most relevant ones (see Table 7). Teacher interviews suggested that the majority of students consume packaged sweet and salty snacks, as well as sweetened sparkling beverages, during the mid-morning break. This type of food, which is not included in the healthy and balanced diet suggested by the Ministry [23], is often characterized by a high caloric content that affects the energy balance and often leads to a loss of appetite at lunchtime [33]. According to the interviews, during the lunch meal, students having packaged snacks and sweetened sparkling beverages during the mid-morning break consumed less food than students who had different types of food during the break. Therefore, results suggested that a significant group of students refused food because of a sense of satiety felt at the beginning of lunch.
An additional cause of food waste in school catering is related to the menu composition. A representative case is the menu including both bread and pizza; these are alternative products and should not be served in the same menu. A corrective action to prevent food waste could be avoiding the presence of alternative products in the same menu, as shown by the data.
A further element is the rigidity of the procurement specifications that set a fixed quantity for each product. Daily observations led to the identification of a number of critical situations. For instance, in the case of pizza and bread served together, food waste reduction could be ensured by adjusting bread quantities.
In some cases, it may be relevant to address the way food is presented. Boiled meat presents a significant level of inefficiency but it is also a basic ingredient for the preparation of tortellini (pasta), a dish with one of the lowest number of unserved portions. Despite the evidence, no corrective measures have been taken by the catering service. Beside these specific factors, there is also a general lack of tools to adjust system inefficiencies. Throughout the study period, the same menus were characterized by similar levels of waste. The rigidity of procurement specifications and the extremely limited flexibility in adjusting the different food preparations reduced the possibility of identifying actions based on students’ consumption habits. The introduction of corrective measures produced significant results in terms of improved managerial efficiency. The case of fruit distribution provides significant evidence: the remaining fruit was distributed to students as snacks during the afternoon. An additional example is the case of bread, where the revision of the purchased quantity resulted in a significant reduction of the amount of leftovers.
These interventions can be classified as preventive measures. The EU Waste Framework Directive [34] identifies a “waste hierarchy” based on five steps, ranked according to their environmental impact: prevention, reuse, recycling, recovery, and disposal. Prevention is clearly the primary objective, while the other options should be considered in the order indicated by the EU Directive. An alternative measure for managing the food waste remaining after the adoption of the necessary prevention strategies––as indicated in the case study identification section is represented by the recovery model based on the proximity principle designed and implemented by LMM.
Table 7. Food waste drivers in school catering.
Table 7. Food waste drivers in school catering.
Food waste driverDescription
Menu compositionSome menus present products with similar characteristics (i.e., bread and pizza) that should be considered as alternative dishes
Rigid procurement practicesThe standard quantity of each food product cannot be easily modified
Lack of attention to dietary habitsFamilies do not pay attention to balanced dietary habits
Meal presentationFood is presented in an unattractive manner
In light of the data that have been collected, school catering food waste might be divided in three categories (see Figure 5):
(a)
“avoidable” unserved food––unserved food thrown away because there is a lack of attention to dietary habits, limited flexibility in procurement, food is presented in an unattractive manner, or there are alternative products on the same menu;
(b)
“physiological” unserved food––unserved food, cooked in excess to ensure some extra portions to satisfy any possible requests for additional food, for facilitating the portioning activity;
(c)
food served but not consumed––waste arising from food served during the catering service but not completely consumed by students (dish leftovers).
In conclusion, as discussed above, from the point of view of food waste reduction, on points (a) and (c) it is possible to intervene with preventive measures, while on point (b) it is possible to intervene with recovery measures.
Figure 5. Typology of school catering waste, and corrective measures.
Figure 5. Typology of school catering waste, and corrective measures.
Sustainability 07 14745 g005

5. Conclusions

The work identified a significant level of inefficiency in the school catering service, measured as the amount of food processed and still perfectly edible but not served. The volume of food waste represented about 15.3% (6523.35 kg) of the total processed food. In other terms, 64 complete meals and 62 incomplete meals were wasted each day.
Among the causes identified in this study, four of them are more relevant than others because of their implications and impact on prevention: lack of attention to dietary habits, rigid food procurement specifications, menu composition, and meal presentation.
In order to increase catering efficiency, the study suggested an integrated strategy that involves the catering service and other key stakeholders such as families and local and national administrations. On the catering side, the research showed the need for at least two types of intervention: reduction of the rigidity of standard rations for each food type, to adjust the quantity of food when it is excessive; and revision of the menus to avoid alternative products being served on the same menu.
An additional measure to increase efficiency is represented by information campaigns aimed at improving dietary habits so as to decrease the consumption of products with high caloric content, such as sweet and salty snacks and sparkling beverages, which were identified as one of the reasons why students refuse meals.
Prevention alone is not sufficient to achieve an optimal allocation of resources; it should be integrated with recovery mechanisms to intervene and adjust the additional failures of the catering system. The work showed that a food recovery intervention model could lead to higher efficiency and to an economic use of resources, and therefore to an allocation of resources that does not allow for further improvements. Finally, the study suggested the need for further academic investigations into the different––and interrelated––dimensions of food waste including economic, environmental, nutritional, sociocultural, and technological aspects.

Author Contributions

Luca Falasconi developed the original idea, contributed to the research design, conducted data collection and supported data elaboration and analysis. Matteo Vittuari and Alessandro Politano contributed to the research design, carried out the literature review, supported data collection and carried out data elaboration and analysis. Andrea Segrè contributed with comments and revisions and edited for content. Authors contributed equally to writing the paper. All authors proofread and approved the final manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Evans, D.; Campbell, H.; Murcott, A. A brief pre-history of food waste and the social sciences. Sociol. Rev. 2012, 60, 5–26. [Google Scholar] [CrossRef]
  2. Food and Agriculture Organization of the United Nations (FAO). Food Loss Prevention in Perishable Crops; FAO Publishing: Rome, Italy, 1981. [Google Scholar]
  3. Food and Agriculture Organization of the United Nations (FAO). Global Food Losses and Food Waste; FAO Publishing: Rome, Italy, 2011. [Google Scholar]
  4. European Parliament (EP). Avoiding Food Waste: Strategies for Improving the Efficiency of the Food Chain in the EU; EP Publishing: Strasburg, France, 2011. [Google Scholar]
  5. Östergren, K.; Gustavsson, J.; Bos-Brouwers, H.; Timmermans, T.; Hansen, O.-J.; Møller, H.; Anderson, G.; O’Connor, C.; Soethoudt, H.; Quested, T.; et al. FUSIONS Definitional Framework for Food Waste; Wageningen University Publishing: Wageningen, The Netherlands, 2014. [Google Scholar]
  6. Environmental Protection Agency (EPA). Measuring Recycling: A Guide for State and Local Governments; EPA Publishing: Washington, DC, USA, 1997. [Google Scholar]
  7. Segrè, A.; Falasconi, L.; Politano, A.; Vittuari, M. Background Paper on the Economics of Food Loss and Waste. Available online: http://www.fao.org/fileadmin/user_upload/save-food/PDF/WorkingPaper/Background_Paper_2014.pdf (accessed on 30 October 2015).
  8. Bagherzadeh, M.; Inamura, M.; Jeong, H. Food waste along the food chain. OECD Food Agric. Fish. Pap. 2014. [Google Scholar] [CrossRef]
  9. Betz, A.; Buchli, J.; Göbel, C.; Müller, C. Food waste in the Swiss food service industry––Magnitude and potential for reduction. Waste Manag. 2015, 35, 218–226. [Google Scholar] [CrossRef] [PubMed]
  10. Göbel, C.; Langen, N.; Blumenthal, A.; Teitscheid, P.; Ritter, G. Cutting food waste through cooperation along the food supply chain. Sustainability 2015, 7, 1429–1445. [Google Scholar] [CrossRef]
  11. European Commission (EC). Preparatory Study on Food Waste across EU 27; EC Publishing: Brussels, Belgium, 2010. [Google Scholar]
  12. Food and Agriculture Organization of the United Nations (FAO). Food Losses and Waste in the Context of Sustainable Food Systems; FAO Publishing: Rome, Italy, 2014. [Google Scholar]
  13. Parfitt, J.; Barthel, M.; Macnaughton, S. Food waste within food supply chains: Quantification and potential for change to 2050. Philos. Trans. R. Soc. 2010, 365, 3065–3081. [Google Scholar] [CrossRef] [PubMed]
  14. Bräutigam, K.R.; Jörissen, J.; Priefer, C. The extent of food waste generation across EU-27: Different calculation methods and the reliability of their results. Waste Manag. Res. 2014, 32, 683–694. [Google Scholar] [CrossRef] [PubMed]
  15. Møller, H.; Hanssen, O.J.; Gustavsson, J.; Östergren, K.; Stenmarck, Å.; Dekhtyar, P. Report on Review of (Food) Waste Reporting Methodology and Practice; Wageningen University Publishing: Wageningen, The Netherlands, 2014. [Google Scholar]
  16. Engström, A.; Carlsson-Kanyama, R. Food losses in Food Service Institutions––Examples from Sweden. Food Policy 2004, 29, 203–213. [Google Scholar] [CrossRef]
  17. Waste & Resources Action Programme (WRAP). Food Waste in School; WRAP Publishing: London, UK, 2011. [Google Scholar]
  18. Sonnino, R.; McWilliam, S. Food Waste, Catering practices and public procurement: A case study of hospital food systems in Wales. Food Policy 2011, 36, 823–829. [Google Scholar] [CrossRef]
  19. Byker, C.J.; Farris, A.R.; Marcenelle, M.; Davis, G.C.; Serrano, E.L. Research brief food waste in a school nutrition program after implementation of new lunch program guidelines. J. Nutr. Educ. Behav. 2014, 46, 406–411. [Google Scholar] [CrossRef] [PubMed]
  20. Ferreira, M.; Liz Martins, M.; Rocha, R. Food waste as an index of foodservice quality. Brit. Food J. 2013, 115, 1628–1637. [Google Scholar] [CrossRef]
  21. Liz Martins, M.; Cunha, L.M.; Rodrigues, S.; Rocha, A. Determination of plate waste in primary school lunches by weighing and visual estimation methods: A validation study. Waste Manag. 2014, 34, 1362–1368. [Google Scholar] [CrossRef] [PubMed]
  22. Dânia, D.; Martins, M.L.; Rocha, A. Plate waste as an indicator of portion inadequacy at school lunch. Int. J. Agric. Biosyst. Sci. Eng. 2013, 79, 417–421. [Google Scholar]
  23. Gioventù, M.D.; Italiano, G. Il Governo dei Giovani. Available online: http://www.diamoglifuturo.it/$DFDisk/Documents/pdf/ilgovernodeigiovaninewdefinitvo_ott.pdf (accessed on 30 October 2015).
  24. Pascucci, S.; Cicatiello, C.; Franco, S.; Pancino, B.; Marino, D. Back to the future? Understanding change in food habits of farmers’ market customers. Int. Food Agribus. Man. 2011, 14, 105–126. [Google Scholar]
  25. Canali, M.; Östergren, K.; Amani, P.; Aramyan, L.; Sijtsema, S.; Korhonen, O.; Silvennoinen, K.; Moates, G.; Keith Waldron, K.; O’Connor, C. Drivers of Current Food Waste Generation, Threats of Future Increase and Opportunities for Reduction; Wageningen University Publishing: Wageningen, The Netherlands, 2014. [Google Scholar]
  26. Pareto, V. The New Theories of Economics. J. Polit. Econ. 1897, 5, 485–502. [Google Scholar] [CrossRef]
  27. Banco Alimentare. La Legge 155/2003, Una Legge Italiana All’avanguardia Al Fine Di Incoraggiare Le Donazioni Di Cibo Cotto E Fresco Ai Più Poveri. Available online: http://www.bancoalimentare.it/files/Legge_155_20032%282%29.pdf (accessed on 21 October 2015). (In Italian)
  28. Falasconi, L.; (Università di Bologna, Bologna, Italy). Lo spreco alimentare nella ristorazione scolastica: Focus group preliminare. 2010; unpublished internal project report. (In Italian) [Google Scholar]
  29. Falasconi, L.; (Università di Bologna, Bologna, Italy). Lo spreco alimentare nella ristorazione scolastica: Focus group intermedio. 2011; unpublished internal project report. (In Italian) [Google Scholar]
  30. Falasconi, L.; (Università di Bologna, Bologna, Italy). Lo spreco alimentare nella ristorazione scolastica: Focus group finale. 2011; unpublished internal project report. (In Italian) [Google Scholar]
  31. Segrè, A. Last Minute Market. La Banalità Del Bene E Altre Storie Contro Lo Spreco; Edizioni Pendragon: Bologna, Italy, 2010. (In Italian) [Google Scholar]
  32. Segrè, A.; Falasconi, L.; Morganti, E. Last Minute Market––Increasing the Economic, Social and Environmental Value of Unsold Products in the Food Chain. In Total Food. Sustainability of the Agri-Food Chain; RSC Publishig: Cambridge, UK, 2010; pp. 162–167. [Google Scholar]
  33. Morin, P.; Demers, K.; Gray-Donald, K.; Mongeau, L. Foods offered in Quebec school cafeterias: Do they promote healthy eating habits? Results of a provincial survey. Can. J. Public Health 2012, 103, 249–254. [Google Scholar]
  34. European Parliament; Council of the European Union. Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on Waste and Repealing Certain Directives. Available online: http://eur-lex.europa.eu/legal-content/EN/ALL/?uri=CELEX:32008L0098 (accessed on 30 October 2015).

Share and Cite

MDPI and ACS Style

Falasconi, L.; Vittuari, M.; Politano, A.; Segrè, A. Food Waste in School Catering: An Italian Case Study. Sustainability 2015, 7, 14745-14760. https://doi.org/10.3390/su71114745

AMA Style

Falasconi L, Vittuari M, Politano A, Segrè A. Food Waste in School Catering: An Italian Case Study. Sustainability. 2015; 7(11):14745-14760. https://doi.org/10.3390/su71114745

Chicago/Turabian Style

Falasconi, Luca, Matteo Vittuari, Alessandro Politano, and Andrea Segrè. 2015. "Food Waste in School Catering: An Italian Case Study" Sustainability 7, no. 11: 14745-14760. https://doi.org/10.3390/su71114745

Article Metrics

Back to TopTop