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Understanding the Relationship Between Tourists’ Consumption Behavior and Their Consumption Substitution Willingness Under Unusual Environment

Keheng xiang.

1 China Institute of Regulation Research, Zhejiang University of Finance and Economics, Hangzhou, 310018, People’s Republic of China

2 School of Hotel and Tourism Management, The Hong Kong Polytechnic University, Kowloon, 999077, Hong Kong, Special Administrative Region of China

3 Zhejiang Technical Institute of Economics, Hangzhou, 310018, People’s Republic of China

Chonghuan Xu

4 School of Business Administration, Zhejiang Gongshang University, Hangzhou, 310018, People’s Republic of China

Introduction

Understanding the relationship between tourists’ consumption behavior and their willingness to substitute consumption in unusual environments can promote tourists’ sustainable consumption behavior. This study explores the internal relationship between tourists’ willingness to engage in sustainable consumption behavior and the substitution of tourism consumption willingness in an unusual environment and the related factors.

Through qualitative and quantitative mixed research, this study first invited 32 interviewees related to the tourism industry to conduct in-depth and focus group interviews and extracted a research model based on the push-pull theoretical model (PPM) through three rounds of coding of grounded theory. Then, through questionnaire design, pre-release, and formal release, 268 valid questionnaires were collected using a convenience sampling method, and the hypothesis and its mediating effect were verified using a structural equation model.

Further quantitative analysis and verification showed that being in an unusual environment had a positive effect on tourists’ perception of crisis awareness, safety risk, and willingness to engage in sustainable consumption behavior. However, the results did not support the unusual environment positively affecting the substitution of tourism consumption willingness, the psychological transformation cost, and the fixed consumption habit negatively affecting the substitution of tourism consumption willingness. In this study, two mediating variables were used to verify the indirect effect of being in an unusual environment and the substitution of tourism consumption willingness. The results showed that the mediating effect was significant.

This study explored an action mechanism model aimed at guiding tourists’ willingness for sustainable consumption, based on the environment and consumption behavior, and provided relevant countermeasures for the government and business decision-makers, enterprises, and investors in the tourism sector.

Carbon emissions and ecological sustainability in the process of tourism have become a common concern of the international community. The role of tourists in sustainable consumption and the integration of economic development and ecological civilization are both important. Sustainable tourists are green travel tourists who consider environmental protection during their travels. At present, the huge increase in consumption has brought great pressure to the human living environment. Tourists’ behavior and choice preference in travel are the keys to promoting sustainable ecotourism. Tourist activity includes accommodation, tours, and entertainment, all of which consume a certain amount of energy and contribute to carbon emissions. Furthermore, the potential safety and crisis of tourists during tourism consumption process under unusual environment, to a certain extent, lead to the enhancement of tourists’ self-protection consciousness and the formation of negative attitude, which will prompt tourists to have different consumption behavior that may cause the waste of resources. Understanding the relationship between tourists’ consumption behavior in an unusual environment and their willingness to substitute consumption may make visitors more willing to engage in sustainable tourism consumption.

This study follows the scientific and normative research procedure, starting with micro psychological variables, constructing a theoretical model, and putting forward a research hypothesis based on pushing, pulling, mooring, and other variable elements and breaks away from the previous decision-making mode of tourists’ sustainable consumption behavior and psychology. Thus far, studies have often focused on sustainable tourism behavior, psychological attribution, empirical research, and influencing factors. Research on the intrinsic willingness and effect of tourists’ consumption behavior under special circumstances has been neglected, so this research provides facts that rely on planned behavior theory and attitude (behavior) situational theory research paradigm and takes the unusual environment as the situational element. It provides a new research perspective for opening the internal “black box” of the micro psychological decision-making of sustainable consumption in the tourism industry. In this study, tourists’ sustainable consumption refers to their conscious choice of sustainable and environment-friendly tourism behavior during travel. From the perspective of connotation, tourists’ sustainable consumption includes reducing direct environmental pollution caused by tourism and consciously engaging in responsible tourism. In terms of denotation, sustainable consumption includes the whole continuum of tourist behavior, such as the choice of types of tourism with low energy consumption and low pollution. In this study, a theoretical model was built based on grounded theory and the push-pull theoretical model (PPM), and the internal mechanism of the willingness of tourists in an unusual environment to engage in sustainable consumption behavior and their consumption substitution willingness was studied using mixed quantitative and qualitative research methods.

The main contributions of this paper are summarized as follows:

  • We examined the internal mechanism determining tourists’ willingness to engage in sustainable consumption in an unusual environment.
  • We found substitutable behavioral effects and factors that affect tourists and their paths of influence.
  • We explored the micro psychological variables in tourist consumption behavior willingness and introduced tourists’ psychological variables and situational environmental variables for the first time, which expands the situational research on empirical analysis of sustainable consumption behavior.

The remainder of this paper is organized as follows. Literature Review provides a literature review. Theoretical Model Construction discusses the research methods and theoretical models. Model Construction and Hypotheses presents the hypotheses. Results of the Analysis and Hypothesis Testing provides the results analysis and hypothesis testing. Finally, Conclusions presents the discussion and conclusions.

Literature Review

The unusual environment.

In the context of the concept of the unusual environment proposed by Zhang, 1 the unusual environment refers to an environment outside of people’s daily life, study, and work (including both the natural and cultural environments). As Zhang noted, the psychological and behavioral characteristics of tourists in an unusual environment are abnormal. In a related study, Rogers introduced the concept of the usual environment, pointing out that it is often a complex environmental concept that includes geographical boundaries, frequency of access, and the scope of people’s daily activities (living, working, studying, etc.) and that the usual environment is a unique situation as a whole, with its own history and significance, which is to some extent a function of geographical distance. 2 De San Eugenio Vela et al proposed that the usual environment represents a space or place and that space is an abstract physical concept; they also examined individual details, such as the visiting frequency of attractors (for calculating distance) and the perception of the usual environment through a super-large sample survey. 3

In academic studies, the dimensions of the current environmental situation are usually understood to include economic, information, cultural, cognitive, and economic dimensions. 4 , 11 Belk proposed that being in an unusual environment means to encounter strangeness and feeling unsafe, leading tourists, in general, to try to overcome the psychological distance to their usual environment by making more efforts to reduce strangeness, which also takes into consideration behavioral sunk costs. 5 McKercher pointed out from the perspective of physical distance that the sunk cost contained in the unusual environment more or less affected tourists’ choice of destination and their consumption there. 6 Research on the information dimension of an unusual environment focuses on issues such as chaos and asymmetric information; for example, Beales et al suggested that in an unusual environment, a lack of understanding of the price and quality of goods could easily lure visitors to tourist traps. 7 Gursoy noted that tourists rely on second-hand information channels more than they would in their usual environment, thus leading to chaos, information overload, and fuzzy information. 8 Lu found that tourists’ information search and filtering costs are higher in the non-habitual environment. 9 Regarding the cultural dimension, there is a higher incidence of cultural conflict than in the usual environment. Crompton noted that cultural distance caused discomfort, conflict, and discrimination in an unusual environment and investigated the source of cultural distance between the usual routine environment and that of the tourist destination. 10 Ye also proposed that cultural distance acts as a buffer in cross-cultural communication between hosts and guests, reducing conflict between them and concluded that cultural differences between habitual and unusual environments are important representations of the tourism activity space. 12 In terms of the cognitive dimension of an unusual environment, researchers have mainly focused on environmental perception and cognition, including risk safety, familiarity, and strangeness. For example, Cohen mentioned in as early as 1972 that tourists sought both familiarity and strangeness in the process of social contact with host countries. 13 To give another example, Mitchell and Greatorex proposed that the unusual environment accompanied by strangeness would increase tourists’ risk perception, while the environment cover could reduce such perception. 14 As for the empirical analysis of the unusual environment, Chen proposed that usual and unusual environments have the function of switching and projecting, with two combined effects of active passivity and positive passivity, which will generate the perception of insecurity and discomfort. The experience of tourism is a combination of the time and space of tourists’ (non) unusual environment and (non) leisure time. 15 Hares et al pointed out that tourists have barriers to sustainable consumption in unusual environments, so they seldom pay attention to environmental impacts or interests in their tourism decision-making. 16 In an unusual environment, because their identity is unknown, the moral constraints of tourists are relaxed, their self-discipline is lower, and behavior that do not occur in the habitual environment occur easily.

In summary, information chaos and cultural conflict in an unusual environment will lead to confusion in tourists’ cognition and a decrease in their sense of experience, psychological strangeness and sense of crisis and the corresponding psychological adjustments and behavioral decisions to respond to the surrounding tourism environment. Therefore, the theoretical model constructed in this study is based on the relevant research on the information and cognitive dimensions in an unusual environment, deepening and expanding the empirical analysis of tourists’ consumption behavior and willingness to substitute consumption.

Sustainable Consumption Behavior

In terms of the mechanism model of sustainable consumption willingness, research has typically focused on overload tourism in Europe, and studies on the mechanism and countermeasures for sustainable tourism saturation have been from the perspectives of policy, organization, institution, and behavior. 17 There have also been studies on models of relevant decision-making mechanisms to promote the implementation of sustainable consciousness by identifying potential factors in sustainable tourism, 18 such as determining the driving factors in specific tourism environments to formulate rules for the precision and standardization of sustainable tourism for tourists. Since the role of architecture is often neglected in research on sustainable tourism, to achieve the promotion and penetration of sustainable tourism, the internal mechanism architecture of tourists and the environment should be changed. 19 In general, the current sustainable tourism consumption mechanism model carries out relevant research by examining the internal potential factors in attitude and behavior from an objective perspective and how it can be applied in practice.

In recent years, studies of the factors influencing sustainable consumption willingness have focused on consumer behavior and cognition, such as Lao, 20 who concluded that consumers’ innovation consciousness has a significant impact on sustainable consumption intention. Lu et al found that consumers’ personality characteristics have a significant impact on their moral beliefs and that some dimensions of consumers’ moral beliefs have a significant predictive effect on their willingness to buy sustainable products. 21 Pinto et al examined how the salience of personal and social identity changes the relationship between sustainable consumption and intention types. 22 The results show that when personal identity is significant, the intention to transcend the self has more influence on sustainable consumption than the intention to promote one’s self-interest. When social identity is significant, the influence of intention to transcend the self and promote one’s self-interest in sustainable consumption are similar. Nguyen et al theoretically developed and tested two key regulators of the relationship between sustainable consumption intentions and behavior from the perspective of consumer behavior, that is, the availability of sustainable products and personal consumption expenditure (PCE). 23

Substitution of Tourism Consumption Willingness

There are many forms of consumption substitution. This study focuses on consumption substitution, that is, alternative consumption or consumer behavior, when choosing substitutes. In an unusual environment, tourists’ perception of safety risks will be enhanced, and the sense of insecurity and strangeness will prompt them to choose other forms of tourism to replace the original type of tourism or to engage in alternative tourism behavior. Consumption substitution in this study is based on the concept of substitution in Porter’s five forces model, 24 which holds that substitution is the process by which one product or service replaces another to achieve certain needs for the buyer and that substitution analysis is equally applicable to products and processes. The object of substitution here usually refers to the category (category substitution), and the substitution originally referred to by Porter is concerned with consumer products. This study extends Porter’s concept of substitutes by examining the transformation of the mode of consumption (consumption substitution behavior). As few studies have considered the issue of consumption substitution, this study examines consumption substitution behavior in the process of participating in tourism activity. This type of tourism substitution behavior is the result of tourists’ attention and awareness of environmental protection. It is one of the behavioral results of promoting tourists’ green consumption and it can transform tourists’ intention of green consumption behavior into a process of consumption substitution.

Previous studies that have examined similar issues include an examination of the migration of purchase channels by Reinartz et al 25 and a paper by Ratneshwar et al 26 on how to provide consumers with alternative product platforms and to offer a comparison standard for products in alternative schemes. Consumption substitution is generally a transformation of long-term trends, usually occurring at an industry level. This study examines the corresponding consumption mode and behavior substitution.

The Push-Pull Theoretical Model (PPM)

The PPM model (pull, push, and mooring) began with the study of the earliest migration behavior. Heberle summarized the structure and spatial distribution of population migration mechanisms, which gave rise to the initial push-pull theory of population migration. 27 Moon found further factors in migration theory, such as those that encourage people to leave their original habitats, for example, if their former residence had a negative effect on their lives. 28 Some scholars believe that the PPM model is also an effective approach for analyzing the relationship between consumer motivation and behavior. Therefore, it has been introduced to the field and the factors that influence consumer behavior are studied around the three factors “push”, “pull” and “mooring”.

For example, Goossens studied the motivation of tourists and their emotion-oriented destination selection decisions using the PPM model and proposed that tourists are driven by their emotional needs and interests. 29 In recent years, scholars have turned to the PPM model more frequently to study tourism consumers. For example, Kim et al examined the push and pull factors that increase visitors to South Korea’s national parks. 30 The results of their factor analysis showed that there were four push factors: appreciating nature as a family, escaping the obligations of daily life, engaging in exploration, and establishing a friendship. The three pull factors were the core tourism resources: information, facility convenience, and transportation/accessibility. In another study, Klenosky used the means-ends theory to examine the relationship between driving and pulling factors that motivate and guide travel behavior. 31 Jung et al tested the conversion adaptation behavior of PPM in tourists’ choice of airlines and concluded that PPM is directly related to tourists’ willingness to change airlines. 32 Poor service, opaque prices, low levels of customer satisfaction, and weak trust push tourists away from existing airlines. The attraction of alternative options, opportunities, and price concessions can motivate tourists to choose new routes, while other factors such as high alternative costs, limited choice trends, and low priority alternative costs, have anchoring effects.

Theoretical Model Construction

Overall design.

This study designed a qualitative and quantitative research based on the literature review of the above three important variables and in conjunction with the theoretical model of PPM. It attempted to find explanatory variables through a qualitative analysis, constructed a theoretical framework for the PPM, and then verified the framework through a quantitative analysis.

There are no definite categories, scales, or related theoretical assumptions available for studying sustainable consumption behavior patterns. In a preliminary investigation and interviews, many respondents pointed out the lack of clear boundaries and connotations of sustainable consumption behavior, especially sustainable consumption in travel, as everyone had a different understanding of the issues involved. It was obvious that this could give rise to misunderstandings if a structured questionnaire were to be administered without taking this into account. As this could affect the sample of the quantitative research directly, as well as the reliability and validity of the results, a mixed research method was adopted in the present study. A qualitative research method was first used to establish a theoretical framework and was then combined with variable detection and qualitative research results, which were proposed and verified using a quantitative research method.

This study first used a semi-structured interview, a qualitative approach, and sampling theory to select the interview objectives. Based on grounded theory, an exploratory study was conducted to collect verbatim transcripts of interviews from a representative sample of the public. Through open coding, spindle coding, and selective coding of the verbatim transcripts using the MAXQDA2018 software package, a correlation model, and the influencing factor theory of tourists’ willingness to engage in sustainable consumption and substitutive behavior were constructed. In the process of analyzing verbatim manuscripts, a continuous comparative analysis was adopted to refine and revise the theories continuously until the theories and concepts were saturated. The concepts were verified with the variables after sorting out the theories. After verification, the related variables were measured for concept, model hypothesis, and model validation.

Category Extraction and Theoretical Model Construction

A total of 32 invited tourism industry experts, scholars, and professionals (middle-aged and young teachers) participated in the survey. A combination of individual in-depth interviews and focus group interviews was used. Overall, there were 16 one-on-one interviews (each 30 to 45 minutes) and 4 focus group interviews with an average of 4 people in each group (each about 1 hour 30 minutes). Participants provided consent before participating in this research and to record the interviews. The interviews were transcribed using a recording software, and the total length of the interview transcripts was 180,000 words. This study randomly selected two-thirds of the interviews for consistency, using the theoretical concepts of the saturation test and trend chart. In open coding category extraction, only concepts that were repeated more than thrice in setting the initial concepts were selected, while less frequently occurring concepts were eliminated. Table 1 shows part of the initial concepts and categories. Owing to a space problem, for each of the initial categories, only the raw data of the three original materials and the corresponding initial concepts were selected. The main axis coding mined and extracted potential logical relations between categories. Table 2 shows the open coding categories. This study classifies different categories according to their conceptual interrelations and logical relations and summarizes eight main categories. The typical relational structures of the main categories in this study are listed in Table 3 .

Initial Concepts and Categories

Categorization of Open Coding

Typical Relational Structure of the Main Categories

This study identified the core category of sustainable consumption behavior and the consumption substitution willingness. The storyline around the core category can be summarized as an unusual environment, sustainable consumption behavior psychological costs, and fixed consumption. The study used the PPM theoretical model to identify the thrust factors (push) that can promote sustainable consumption behavior. Pull factors for sustainable consumption behavior include urging tourists to choose alternative tourism consumption types include a sense of risk to safety and crisis cognition. The psychological transformation cost and consumption habits of tourists have an anchoring effect (mooring) in this model, which will hinder the formation of tourists’ willingness to consume instead of traveling. Therefore, the theoretical model developed in this study is consistent with the PPM model. A specific theoretical model based on PPM is shown in Figure 1 . To test the saturation of theories and concepts, one-third of the interview records were used for the theoretical saturation test. Neither new categories and relationships nor new factors in the five main categories were found. Figure 2 shows the trend consistency chart of categories. The number of new categories shows a linear trend distribution and the number of new categories of interviewees from P9 to P16 is greatly reduced, indicating that the categories of interviewees have obvious internal consistency. The above theoretical model based can thus be considered theoretically saturated.

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This study is based on the theoretical model of PPM.

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Trend chart of category consistency.

Model Construction and Hypotheses

Measurement and analysis of variables, push factors.

The usual environment: Based on Ajzen’s theory of planned behavior (TPB), 33 , 34 individual environmental behavioral willingness is considered the first psychological variable. In this study, the concept of the usual environment is understood in a manner similar to that proposed by Gursoy et al 8 and Crompton, 10 with an emphasis on the information dimension and the related characteristics of the cultural dimension, that is, that in unusual circumstances, a situation of information asymmetry and chaos occurs, with conflicts resulting from cultural distance and discomfort. Therefore, based on the environmental behavior scale proposed by Stern and the four dimensions identified in the literature review (economy, information, culture, and cognition), seven question options were set.

Pull Factors

Sustainable consumption behavior: Stern et al argued that tourists’ sustainable consumption behavior was affected by environmental values and social norms, combining the attitude - behavior - situational theory with a focus on the individual environmental behavior associated with external situation factors. 35 Recently, many scholars have studied and analyzed the situational factors that affect behavior, as the paper by Stern et al, who proposed that environment and policy support can influence consumer behavior. 36 Therefore, with reference to the environmental behavior scale proposed by Stern et al and the appropriate modification of Ajzen’s theory of planned behavior scale, eight sustainable consumption behavior measurement questions were designed based on the perspectives of housing, travel, tourism, shopping, and entertainment.

The willingness of tourism consumption substitution: Consumption substitution in this study is the concept of total substitution in Porter’s five-force model. 24 With reference to the new environmental paradigm (NEP) scale developed by Dunlap and combined with the results of the existing literature review, six options (mainly situational measurement items for consumption to replace tourism behavioral intentions) were designed.

Crisis and safety risk perception: based on the NEP scale developed by Dunlap et al and the results of the existing literature review, seven options for crisis and risk safety perception were designed (mainly for the perception and judgment of non-sustainable tourism). 37

Anchoring Factors

Psychological transformation costs and fixed consumption: Conversion costs are faced in the conversion of one-time costs. 38 , 39 Related studies have shown that conversion costs are important factors in the process of consumers’ offline to online channel migration. Therefore, because of the cost of the transformation of psychological perception, the migration behavior of tourists may be suppressed. 40 , 41 With reference to Dunlap’s NEP scale and combined with the findings of existing literature, six items of psychological transformation cost and fixed consumption were designed (mainly measuring the anchoring effect of benefit perception).

Research Model and Research Hypothesis

Using grounded theory and the PPM as this study’s theory correlation model, the usual role is the thrust of the unusual environment variables; positive roles are crisis and security risk perception, sustainable consumption behavior, and the willingness to substitute tourism consumption. 38 , 42 As variables of pull forces, crisis and security risk perception have a positive influence on sustainable consumer behavior. 43–47 Psychological transformation costs and fixed consumption have a negative impact on the substitution of willingness to consume tourism. 48 , 49 To ensure the accuracy of the model and hypothesis construction, two mediating variables were introduced into this study: crisis and safety risk perception and sustainable consumption behavior. It is assumed that these two variables play a mediating role in influencing consumption substitution willingness in an unusual environment. The research hypotheses are presented in Table 4 .

Hypothesis of This Study

The research model of this study was constructed through the above theoretical analysis and research hypotheses, as shown in Figure 3 .

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Research model.

Questionnaire Design and Descriptive Statistics

This study randomly recruited 15 ordinary tourists to conduct focus group discussions on the outcome and impact variables and invited 6 professors from the academic tourism studies field and 3 experts from the tourism industry to analyze the contents and questions of the focus group discussions. The results of the discussions of the tourists, academic professors, and experts were fully summarized and refined. The relevant outcome and influence variables were selected, which confirmed the results of the literature review. On this basis, this study designed the initial questionnaire, which was distributed by researchers in the field of tourism as part of the pre-test. The questionnaire’s content structure and topics were inspected and evaluated using the SPSS 24.0 software reliability test data and deleted if they did not conform to the standard question based on the results of the test. Moreover, part of the subject expressions was also adjusted in the multi-item colloquial correction and in the green tourism consumption concepts; further, notes were added to the scene and concept descriptions.

Considering that hotel accommodation is an obligatory choice for overnight tourists in an unusual environment and their consumption behavioral willingness is more representative, overnight tourists traveling in Hangzhou were selected as the objects of the survey. The convenience sampling method was adopted to represent the front desk of H&H Hotels among mainstream budget hotels. The front desk service staff cooperated with the sharing of a questionnaire link for tourists to fill in and submit on their mobile phones.

From July 15, 2019, to July 20, 2019, five members of this group in Hangzhou, China, gathered a total of 280 questionnaires. After deleting incomplete samples, there remained 268 valid questionnaires, which gave an effective response rate of 95.7%. The sample ratio was roughly 51.6:48.4 and the age group best represented was between 25 and 45 years (64.8%), the level of education was bachelor’s degree holders (67.8%), and the monthly income bracket was RMB 5500–8000 (56.7%). The sample thus conformed to the next-stage characteristics of travel tourist properties. The variable descriptions and statistical descriptions are presented in Table 5 .

Variable and Statistical Description

According to the different use purposes, a confirmatory factor analysis (CFA) was performed to verify the theoretical model, that is, to test the ability of the model to fit the actual data with pre-defined factors. First, an exploratory factor analysis was carried out on the behavioral variables and then the measurement model was tested through CFA to ensure the reliability and validity of the model. Finally, the SEM model was used to verify the research hypothesis and the bootstrap method was used to test the indirect effect sizes of the two mediation routes to ensure the effectiveness of the mediation variable test.

Results of the Analysis and Hypothesis Testing

Testing the measurement model.

To measure the reliability and validity, a CFA was performed on the measurement model. CFA is a research method that determines whether the correspondence between measurement factors and measurement items (scale items) is consistent with the predictions of the researchers. Its main purpose is to analyze the validity of convergence and to verify the measurement items belonging to the same factor at the time of measurement. In this study, AVE (average variance extracted) and CR (composite reliability) were combined for analysis. If the AVE of each factor is greater than 0.5 and the CR value is greater than 0.7, it indicates good polymerization validity. Simultaneously, this study checked whether the factor load coefficient corresponding to each measurement item was greater than 0.7.

In general, the factor load of the CFA analysis was between 0.5 and 0.95, indicating that the model has good adaptability. Table 6 lists the factor loads of all the variables. All factor loads from Y1 to X28 were between 0.5 and 0.95, so all the questions were retained. The combined reliability was greater than 0.5 and the mean variation extraction was greater than 0.5. The combination reliability of all the potential variables was above 0.7, indicating that the internal consistency of each variable was good. The AVE of all the variables exceeded the minimum value of 0.5 and the correlation coefficient between all the variables was less than the square root of the AVE ( Table 7 ), indicating that the measurement model had good aggregation and discriminant validity.

Reliability and Validity Tests of the Measurement Model

Correlation Coefficient Matrix Between Variables

Note : The value on the diagonal of the matrix is the square root of the average variance extract.

Analysis of the Structural Model Results

Figure 4 shows the influence path of the structure model and its normalized path coefficient, and Table 8 lists the results of hypothesis testing. The unusual environment had a significant positive impact on tourists’ perception of crisis and safety risk (score = 0.392, t = 4.4, p < 0.001) and on their sustainable consumption behavior (score = 0.243, t = 3.0, p < 0.001) but no significant impact on substitution of tourism consumption willingness (p >0.5). Therefore, H1 and H2 are supported, while H3 was not. The perception of crisis and safety risk had a significant positive affect on the substitution of tourism consumption willingness (score = 0.355, t = 3.4, p < 0.001), so hypothesis H4 is supported. The willingness to engage in sustainable consumption behavior had a significant positive affect on the substitution of tourism consumption willingness (score = 0.494, t = 4.8, p <0.001), so hypothesis H5 is supported. However, the psychological transformation cost and the fixed consumption habit had no significant influence on the willingness to replace tourism with consumption (ie, score = 0.021, t = 0.3, p > 0.5), so hypothesis H6 is not supported.

Results of the Hypothesis Test: Direct Action

Notes : (1) *** represents the P value less than 0.001 for significance level (P < 0.001). (2) solid line arrow indicates that the influence path is established, dotted line arrow indicates that the influence path is not established.

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Analysis results of the influence path of the structural model.

Because there are two parallel mediating variables in this model, to verify their reliability, the indirect effect size of the two mediating routes was tested using the bootstrap method. The test data are presented in Table 9 . The results show that P < 0.01, indirect effect size > 0.01, and there is a significant mediating effect.

Results of Hypothesis Testing Mediation

Conclusions

Conclusions and discussion.

Through a mixture of qualitative research based on grounded theory and quantitative model verification, this study explores the willingness of tourists to engage in sustainable consumption behavior in an unusual environment and the substitution of tourism consumption willingness. 50 , 51 The results show that, first, being in an unusual environment has a positive relationship with tourists’ perceptions of crisis and safety risk. 52 Tourists can consume instead of going through problem identification, cognition, and the prediction of an unusual environment. 53 , 54 Being in an unusual environment will prompt tourists to review their knowledge and attitudes toward sustainable consumption and construct and strengthen values for sustainable consumption by themselves. 55–59 Crisis and safety risk perceptions are positively correlated with the substitution of tourism consumption willingness. 60 , 61 Tourists can identify the crisis and safety risks and make decisions on their own crisis interests to enhance the substitution of tourism consumption willingness to reduce travel. However, willingness to engage in sustainable consumption behavior is positively correlated with the substitution of willingness to consume tourism. The values of sustainable consumption held by tourists will promote changes in tourists’ own consumption mode and will be influenced by social norms, promoting willingness to replace tourism with consumption. 62 , 63

Second, as an intervening variable, crisis and safety risk awareness has a significant effect on sustainable consumption behavior, as strangeness in the usual environment will increase tourists’ perception of risk and strengthen their willingness to consume as an alternative to tourism. Therefore, crisis and safety risk perception positively regulate the relationship between the environment and consumption behavior to engage in the substitution of tourism consumption willingness. 64 As for the mediating variable of willingness to engage in sustainable consumption behavior, this can also positively adjust the relationship between the unusual environment and the substitution of tourism consumption willingness. In an unusual environment, tourists’ ecological and sustainable tourism values are easy to awaken, and the substitution of tourism consumption willingness will be significantly enhanced. 65

Third, as the mooring effect in PPM model theory has not been confirmed, the psychological transformation costs and fixed consumption of tourists are mainly affected by mindset and tourists’ own interest decision-making, but the correlation between them and the substitution of tourism consumption willingness has not been confirmed. 66 , 67 The unusual environment directly acting on the substitution of tourism consumption willingness has not been confirmed. The study found that an unusual environment plays a correlating role with two mediating variables, namely, the perception of risks to safety and sustainable consumption behavior, through a crisis.

The theoretical contribution of this study is mainly reflected in two aspects: First, it introduces a new environmental variable and uses this variable as the core to build an understanding of the substitution of tourism consumption willingness. This theoretical structural model and the use of the two mediating variables in moderator variable correlation functions extends and expands the current academic focus on the single perspective of the usual environment and may be conducive to the further study of the usual environment as a variable in tourists’ travel behavior and experiences. However, tourists’ psychological and situational environmental variables are introduced for the first time, expanding, and enriching the situational and empirical research on sustainable consumption behavior.

In the process of planning and development of tourist attractions, the government should pay attention to the “push” effect under an unusual environment to create a familiar and safe tourism environment for tourists, design suitable instructions, and create guidelines to form rich and varied publicity channels to promote the generation of sustainable tourism under unusual environment. Tourism enterprises should reduce redundant facilities and high-energy tourist items in the process of developing tourist attractions. The generation of sustainable tourism behavior requires tourists to integrate their own accurate identification under unusual environments, establish the mentality of safety risk cognition, and replace tourism behavior that may have an impact on the ecological environment with sustainable tourism consumption behavior.

Limitations

As related studies have found, tourism is a low-frequency activity that has different rates of consumption and frequency of revisiting. 68 The apparent time-limited characteristic of tourism activity may dampen tourists’ enthusiasm toward the idea of sustainable consumption and, from the usual environment to the usual circumstances, not only is the change geographical but tourists’ individual behavior patterns and psychology also change. 69 , 70 In a heterogeneous environment, tourists’ personal sustainable consumption behavior pattern will also change. Since this is a dynamic game process, it is also one of the research limitations of this study; one of its hidden assumptions is that it treats the willingness of tourists to engage in sustainable consumption and sustainable consumption behavior as inevitable, while in fact, there is a large gap between tourists’ willingness and their actual behavior. Although tourists may engage in sustainable consumption in different environments and situations, this does not necessarily represent a full implementation. The relevant laws and ways to positively motivate sustainable consumption in tourists also need to be further examined through in-depth studies. Although the willingness to engage in sustainable consumption and consumer behavior has been the subject of a great deal of research, 70–72 there is still need for further study of the effect of being in a heterogeneous environment similar to the usual environment. In addition, dynamic game research on tourists’ sustainable consumption behavior in unusual environments also needs to be further discussed.

Funding Statement

This research is supported by the Philosophy and Social Science Foundation of Zhejiang Province (21NDJC083YB), National Natural Science Foundation of China (71702164), Natural Science Foundation of Zhejiang Province (LY20G010001). Soft Science Research Program of Science and Technology Department of Zhejiang, China (2021C35059), Philosophy and Social Science Planning Special Project of Zhejiang Province (20GXSZ26YB).

Ethics Statement

We declare that participants in our research study allow us to use their data for academic research and publication. All the participants were anonymous and their data was protected. All participants provided informed consent and this study was conducted in accordance with the Declaration of Helsinki. All the programs in our research study were approved by the Institutional Review Board of Zhejiang University of Finance and Economics.

The authors declare that they have no conflicts of interest for this work.

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  • Karen A. Hudson-Edwards   ORCID: orcid.org/0000-0003-3965-2658 1 ,
  • Deanna Kemp 2 , 3 ,
  • Luis Alberto Torres-Cruz   ORCID: orcid.org/0000-0001-8482-0070 4 ,
  • Mark G. Macklin 5 , 6 , 7 , 8 ,
  • Paul A. Brewer   ORCID: orcid.org/0000-0003-0834-8848 9 ,
  • John R. Owen 3 ,
  • Daniel M. Franks   ORCID: orcid.org/0000-0003-1217-2128 8 , 10 ,
  • Eva Marquis   ORCID: orcid.org/0000-0001-9526-1008 1 &
  • Christopher J. Thomas 5  

Nature Reviews Earth & Environment ( 2024 ) Cite this article

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Mining generates 13 billion tonnes per year of potentially toxic wet slurry waste, called tailings, commonly deposited in tailings storage facilities (TSF). Since 1915, 257 TSF failures have occurred, releasing a total of ~250 million m 3 of tailings, destroying areas up to ~5,000 km 2 , killing an estimated 2,650 people and impacting ~317,000 people through displacement, property damage, and risks to livelihoods and health. In this Review, we provide an interdisciplinary approach to understanding the causes, effects and response to TSF failures, applying a disaster risk reduction framework. TSF failures can occur owing to earthquakes, overtopping, weak foundations and liquefaction, among other mechanisms. The severities and volumes of TSF failures have increased since the year 2000, owing to increasing mine waste generation from the exploitation of larger, lower-grade deposits. Despite the increasingly severe impacts, the mining industry has been hesitant to use the term ‘disaster’ to analyse TSF failure, presumably to avoid liability. TSF failures should be considered as disasters when they cause severe disruption to the functioning of ecological and social systems. Future research should build on attempts to link tailings facility locations to situated risk factors by improving spatial and time series analysis, reducing reliance on corporate disclosures, and increasing the visibility of priority locations and patterns of concern.

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Valenta, R. K. et al. Decarbonisation to drive dramatic increase in mining waste — options for reduction. Resour. Conserv. Recycl. 190 , 106859 (2023).

Article   CAS   Google Scholar  

Franks, D. M. et al. Tailings facility disclosures reveal stability risks. Sci. Rep. 11 , 5353 (2021).

Franks, D. M. et al. in Towards Zero Harm : A Compendium of Papers Prepared for the Global Tailings Review (eds Oberle, B. et al.) 84–108 (Global Tailings Review, 2020).

Hudson-Edwards, K. A. Tackling mine wastes. Science 352 , 288–290 (2016).

Macklin, M. G. et al. Impacts of metal mining on river systems: a global assessment. Science 381 , 1345–1350 (2023).

International Commission on Large Dams (ICOLD). Tailings dams: risk of dangerous occurrences — lessons learnt from practical experiences (UN, 2001).

World Mine Tailings Failures. State of world mine tailings portfolio 2020. World Mine Tailings Failures https://worldminetailingsfailures.org/ (2024).

Center for Science in Public Participation. TSF failures (1915-2016). CSP 2 http://www.csp2.org/tsf-failures-from-1915 (2022).

Piciullo, L., Størrosten, E. B., Liu, Z., Nadim, F. & Lacasse, S. A new look at the statistics of tailings dam failures. Eng. Geol. 303 , 106657 (2022).

Article   Google Scholar  

Fernandes, G. W. et al. Deep into the mud: ecological and socio-economic impacts of the dam breach in Mariana, Brazil. Nat. Conserv. 14 , 35–45 (2016).

Buch, A. C., Sautter, K. D., Marques, E. D. & Silva-Filho, E. V. Ecotoxicological assessment after the world’s largest tailing dam collapse (Fundão dam, Mariana, Brazil): effects on oribatid mites. Environ. Geochem. Health 42 , 3575–3595 (2020).

Aska, B., Franks, D. M., Stringer, M. & Sonter, L. J. Biodiversity conservation threatened by global mining wastes. Nat. Sustain. 7 , 23–30 (2023).

Clarkson, L. & Williams, D. Critical review of tailings dam monitoring best practice. Int. J. Min. Reclam. Environ. 34 , 119–148 (2020).

Lèbre, E. et al. Source risks as constraints to future metal supply. Environ. Sci. Technol. 53 , 10571–10579 (2019).

Lèbre, E. et al. The social and environmental complexities of extracting energy transition metals. Nat. Commun. 11 , 4823 (2020).

Guimarāes, R. N., Moreira, V. R., Cruz, J. R. A., Saliba, A. P. M. & Amaral, M. C. S. History of tailings dam failure: impacts on access to safe water and influence on the legislative framework. Sci. Total Environ. 852 , 158536 (2022).

Kossoff, D. et al. Mine tailings dams: characteristics, failure, environmental impacts, and remediation. Appl. Geochem. 51 , 229–245 (2014).

Franks, D. M., Boger, D. V., Côte, C. M. & Mulligan, D. R. Sustainable development principles for the disposal of mining and mineral processing wastes. Resour. Policy 36 , 114–122 (2011).

Byrne, P. et al. Water quality impacts and river system recovery following the 2014 Mount Polley mine tailings dam spill, British Columbia, Canada. Appl. Geochem. 91 , 64–74 (2018).

Agência Nacional de Águas. Encarte especial sobre a bacia do Rio Doce — Rompimento da barragem em Mariana / MG https://projetoriodoce.fgv.br/node/18761 (2016).

do Carmo, F. F. et al. Fundão tailings dam failures: the environment tragedy of the largest technological disaster of Brazilian mining in global context. Perspect. Ecol. Conserv. 15 , 145–151 (2017).

Google Scholar  

Silveira, F. A., Gama, E. M., Dixon, K. W. & Cross, A. T. Avoiding tailings dam collapses requires governance, partnership and responsibility. Biodivers. Conserv. 28 , 1933–1934 (2019).

Rotta, L. H. S. et al. The 2019 Brumadinho tailings dam collapse: possible cause and impacts of the worst human and environmental disaster in Brazil. Int. J. Appl. Earth Obs. Geoinf. 90 , 102119 (2020).

Santamarina, J. C., Torres-Cruz, L. A. & Bachus, R. C. Why coal ash and tailings dam disasters occur. Science 364 , 526–528 (2019).

The Church of England. Investor mining and tailings safety initiative. The Church of England https://www.churchofengland.org/investor-mining-tailings-safety-initiative (2019).

Church of England Pensions Board (CoE) & Council on Ethics of the Swedish National Pension Funds. Letter to board chairs and chief executive officers of listed extractive companies https://www.churchofengland.org/news-and-media/finance-news/investors-give-mining-companies-45-days-full-disclosure-tailings (2019).

International Council on Mining and Metals (ICMM), United Nations Environment Programme (UNEP) & Principles for Responsible Investment (PRI). Global Tailings Review https://globaltailingsreview.org/ (2020).

International Council on Mining and Metals (ICMM), United Nations Environment Programme (UNEP) & Principles for Responsible Investment (PRI). Global Industry Standard on Tailings Management https://www.unep.org/resources/report/global-industry-standard-tailings-management (2020).

United Nations Office for Disaster Risk Reduction. Sendai framework terminology on disaster risk reduction. UNDRR https://www.undrr.org/terminology/disaster (2023).

Rana, N. in ICOLD Annual Meeting 2023 (2023).

Roche, C., Thygesen, K. & Baker, E. Mine tailings storage: safety is no accident. GRID - Arendal https://www.grida.no/publications/383 (2017).

Smith, L. Hydrogeology and Mineral Resource Development (The Groundwater Project, 2021).

Blight, G. Geotechnical Engineering for Mine Waste Storage Facilities (CRC and Balkema, 2010).

Morrison, K. F. Tailings Management Handbook : A Lifecycle Approach (ed. Morrison, K. F.) 3–12 (Society for Mining, Metallurgy and Exploration, 2022).

Wickland, B. Tailings Management Handbook : A Lifecycle Approach (ed. Morrison, K. F.) 133–139 (Society for Mining, Metallurgy and Exploration, 2022).

Veenstra, R. L. Tailings Management Handbook : A Lifecycle Approach (ed. Morrison, K. F.) 121–132 (Society for Mining, Metallurgy and Exploration, 2022).

Vick, S. G. Planning, Design, and Analysis of Tailings Dams (BiTech Publishers Ltd., 1990).

Brouwer, K. J. & Smyth, G. L. in CIM 2017 Convention, Montreal, April 30 - May 3 https://www.knightpiesold.com/sites/en/assets/File/CIM%202017%20-%20Mount%20Polley%20Tailings%20Dam%20Failure.pdf (2017).

Morrill, J. et al. Safety First : Guidelines for Responsible Mine Tailings Management (Earthworks, MiningWatch Canada and London Mining Network, 2022).

Owen, J. R., Kemp, D., Lèbre, É., Svobodova, K. & Pérez Murillo, G. Catastrophic tailings dam failures and disaster risk disclosure. Int. J. Disaster Risk Reduct. 42 , 101361 (2020).

Kemp, D., Owen, J. R., Kemp, D. & Lèbre, É. Tailings facility failures in the global mining industry: will a ‘transparency turn’ drive change? Bus. Strategy Environ. 30 , 122–134 (2021).

dos Santos, R. S. P. & Milanez, B. The construction of the disaster and the “privatization” of mining regulation: reflections on the tragedy of the Rio Doce Basin, Brazil. Vibrant Virtual Braz. Anthropol. 14 , 127–149 (2017).

Fourie, A., Verdugo, R., Bjelkevik, A., Torres-Cruz, L. A. & Znidarcic, D. In Proc. 20th International Conference on Soil Mechanics and Geotechnical Engineering (eds Jaksa, M. & Rahman, M.) 121–183 (Australian Geomechanics Society, 2022).

Robertson, P. K., de Melo, L., Williams, D. J. & Wilson, G. W. Report of the Expert Panel on the Technical Causes of the Failure of Feijão Dam I https://bdrb1investigationstacc.z15.web.core.windows.net/assets/Feijao-Dam-I-Expert-Panel-Report-ENG.pdf (2019).

Morgenstern, N. R., Vick, S. G. & van Zyl, D. Report on Mount Polley Tailings Storage Facility Breach (Province of British Columbia, 2015).

Sánchez, L. E. et al. Impacts of the Fundão Dam failure: a pathway to sustainable and resilient mitigation https://doi.org/10.2305/IUCN.CH.2018.18.en (International Union for Conservation of Nature, 2018).

Githiria, J. M. & Onifade, M. The impact of mining on sustainable practices and the traditional culture of developing countries. J. Environ. Stud. Sci. 10 , 394–410 (2020).

Ministry of Energy and Mines of British Columbia. Mount Polley Mine Tailings Storage Facility Breach August 4 , 2014 (Mining and Minerals Resources Division of the Ministry of Energy and Mines of the Province of British Columbia, 2015).

Comitê Independente de Assessoramento Extraordinário de Apuração (CIAEA). Executive summary of the independent investigation report, failure of dam 1 of the Córrego do Feijão Mine — Brumadinho, MG (Vale S.A., 2020).

Hopkins, A. & Kemp, D. Credibility Crisis : Brumadinho and the Politics of Mining Industry Reform (Wolters Kluwer, 2021).

Vick, S. G. Dam safety risk – from deviance to diligence. In Geo-Risk 2017 19–30 (American Society of Civil Engineers, 2017).

Verweijen, B. & Lauche, K. How many blowouts does it take to learn the lessons? An institutional perspective on disaster development. Saf. Sci. 111 , 111–118 (2019).

Hart, P. T. After Fukushima: reflections on risk and institutional learning in an era of mega-crises. Public Adm. 91 , 101–113 (2013).

Amoah, P., Eweje, G. & Bathurst, R. Understanding grand challenges in sustainability implementation within mining in developing countries. Soc. Bus. 10 , 123–149 (2020).

France, J. W. et al. Independent Forensic Team Report Oroville Dam Spillway Incident (California Department of Water Resources, 2018).

Muñoz, V. & Hoekstra, D. Tailings Management Handbook : A Lifecycle Approach Vol. 20 (ed. Morrison, K. F.) 361–385 (Society for Mining, Metallurgy & Exploration, 2022).

Trottier, M. O., Franklin, K., Portocarrero, J., Dufault, D. & Millar, R. The impact of climate change on extreme events for operation and closure of tailings facilities. In Tailings and Mine Waste 2023 881–888 (AusIMM, 2023).

Labonté-Raymond, P.-L., Pabst, T., Bussière, B. & Bresson, É. Impact of climate change on extreme rainfall events and surface water management at mine waste storage facilities. J. Hydrol. 590 , 125383 (2020).

Clohan, C. & Kidner, E. Tailings Management Handbook : A Lifecycle Approach (ed. Morrison, K. F.) 211–220 (Society for Mining, Metallurgy and Exploration, 2022).

de Paiva, C. A., da Fonseca Santiago, A. & do Prado Filho, J. F. Content analysis of dam break studies for tailings dams with high damage potential in the Quadrilátero Ferrífero, Minas Gerais: technical weaknesses and proposals for improvements. Nat. Hazards 104 , 1141–1156 (2020).

Wisner, B., Blaikie, P., Cannon, T. & Davis, I. At Risk : Natural Hazards, People’s Vulnerability and Disasters 2nd edn (Routledge, 2003).

Ferson, S., Migueles, C. P., Sanini, M. T. F., Gambirage, C. & da Silva, J. C. I’m aware: informed mining: risk reduction through enhanced public and institutional risk awareness https://gtr.ukri.org/projects?ref=ES%2FT003537%2F1#/tabOverview (2023).

Kemp, D. in Towards Zero Harm : A Compendium of Papers Prepared for the Global Tailings Review (eds Oberle, B. et al.) 37–46 (Global Tailings Review, 2020).

Hoffman, S. M. & Oliver-Smith, A. E. Catastrophe and Culture : The Anthropology of Disaster (SAR Press, 2002).

Lewin, J. & Macklin, M. Metal mining and floodplain sedimentation in Britain. Int. Geomorphol. 1986 , 1009–1027 (1987).

Macklin, M. G. et al. A geomorphological approach to the management of rivers contaminated by metal mining. Geomorphology 79 , 423–447 (2006).

Miller, J. R. The role of fluvial geomorphic processes in the dispersal of heavy metals from mine sites. J. Geochem. Explor. 58 , 101–118 (1997).

Lewin, J., Davies, B. & Wolfenden, P. in River Channel Changes (ed. Gregory, K. J.) 353–367 (Wiley, 1977).

Hudson-Edwards, K. A., Macklin, M. G. & Taylor, M. P. 2000 years of sediment-borne heavy metal storage in the Yorkshire Ouse basin, NE England, UK. Hydrol. Process. 13 , 1087–1102 (1999).

Macklin, M. G. & Dowsett, R. B. The chemical and physical speciation of trace metals in fine grained overbank flood sediments in the Tyne basin, north-east England. Catena 16 , 135–151 (1989).

Lawrence, S. et al. Society and sediment in the mining rivers of California and Australia. Water Hist. 13 , 45–73 (2021).

Hudson-Edwards, K. A., Macklin, M. G., Miller, J. R. & Lechler, P. J. Sources, distribution and storage of heavy metals in the Rio Pilcomayo, Bolivia. J. Geochem. Explor. 72 , 229–250 (2001).

Clement, A. J. H. et al. The environmental and geomorphological impacts of historical gold mining in the Ohinemuri and Waihou river catchments, Coromandel, New Zealand. Geomorphology 295 , 159–175 (2017).

Foulds, S. A. et al. Flood-related contamination in catchments affected by historical metal mining: an unexpected and emerging hazard of climate change. Sci. Total Environ. 476 , 165–180 (2014).

Macklin, M. Fluxes and storage of sediment-associated heavy metals in floodplain systems: assessment and river basin management issues at a time of rapid environmental change. Floodplain Process. 13 , 441–459 (1996).

Dennis, I. A., Macklin, M. G., Coulthard, T. J. & Brewer, P. A. The impact of the October-November 2000 floods on contaminant metal dispersal in the River Swale catchment, North Yorkshire, UK. Hydrol. Process. 17 , 1641–1657 (2003).

Macklin, M. G. et al. The long term fate and environmental significance of contaminant metals released by the January and March 2000 mining tailings dam failures in Maramures County, upper Tisa Basin, Romania. Appl. Geochem. 18 , 241–257 (2003).

Bird, G. et al. River system recovery following the Novat-Rosu tailings dam failure, Maramures County, Romania. Appl. Geochem. 23 , 3498–3518 (2008).

Buch, A. C., Sims, D. B., Correia, M. E. F., Marques, E. D. & Silva-Filho, E. V. Preliminary assessment of potential pollution risks in soils: case study of the Córrego do Feijão Mine dam failure (Brumadinho, Minas Gerais, Brazil). Int. J. Min. Reclamat. Environ . https://doi.org/10.1080/17480930.2023.2226474 (2023).

Hudson-Edwards, K. A. et al. The impact of tailings dam spills and clean-up operations on sediment and water quality in river systems: the Rios Agrio-Guadiamar, Aznalcollar, Spain. Appl. Geochem. 18 , 221–239 (2003).

Byrne, P., Wood, P. J. & Reid, I. The impairment of river systems by metal mine contamination: a review including remediation options. Crit. Rev. Environ. Sci. Technol. 42 , 2017–2077 (2012).

Hudson-Edwards, K. A., Jamieson, H. E., Charnock, J. M. & Macklin, M. G. Arsenic speciation in waters and sediment of ephemeral floodplain pools, Ríos Agrio–Guadiamar, Aznalcóllar, Spain. Chem. Geol. 219 , 175–192 (2005).

Hudson-Edwards, K. A. et al. Origin and fate of vanadium in the Hazeltine Creek catchment following the 2014 Mount Polley mine tailings spill in British Columbia, Canada. Environ. Sci. Technol. 53 , 4088–4098 (2019).

Palau, J. et al. Release of trace elements during bioreductive dissolution of magnetite from metal mine tailings: potential impact on marine environments. Sci. Total Environ. 788 , 147579 (2021).

Grimalt, J. O., Ferrer, M. & Macpherson, E. The mine tailing accident in Aznalcollar. Sci. Total Environ. 242 , 3–11 (1999).

Lásló, F. in Management of Intentional and Accidental Water Pollution (eds Dura, G. & Simeonova, F.) 43–50 (2006).

Furlan, J. P. R. et al. Occurrence and abundance of clinically relevant antimicrobial resistance genes in environmental samples after the Brumadinho Dam disaster, Brazil. Sci. Total Environ. 726 , 138100 (2020).

Omachi, C. Y. et al. Atlantic forest loss caused by the world´s largest tailing dam collapse (Fundão Dam, Mariana, Brazil). Remote Sens. Appl. Soc. Environ. 12 , 30–34 (2018).

Política, Economia, Mineração, Ambiente e Sociedade (PoEMAS). Antes fosse mais leve a carga: avaliação dos aspectos econômicos, políticos e sociais do desastre da Samarco/Vale/BHP em Mariana (MG) Relatório Final (PoEMAS, 2015).

Garris, H. W. et al. Short-term microbial effects of a large-scale mine-tailing storage facility collapse on the local natural environment. PLoS ONE 13 , e0196032 (2018).

Giongo, A. et al. Adaption of microbial communities to the hostile environment in the Doce River after the collapse of two iron ore tailings dams. Heliyon 67 , e04778 (2020).

Hatam, I. et al. The bacterial community of Quesnel Lake sediments impacted by a catastrophic mine tailings spill differ in compositions from those at undisturbed locations — two years post-spill. Sci. Rep. 9 , 2705 (2019).

de Miguel, R. J., Oliva-Paterna, F. J., Gálvez-Bravo, L. & Fernández-Delgado, C. Habitat quality affects the condition of Luciobarbus sclateri in the Guadiamar River (SW Iberian Peninsula): effects of disturbances by the toxic spill of the Aznalcóllar mine. Hydrobiologia 700 , 85–97 (2013).

Gabriel, F. Â. et al. Contamination and oxidative stress biomarkers in estuarine fish following a mine tailing disaster. PeerJ 8 , e10266 (2020).

Weber, A. A. et al. Effects of metal contamination on liver in two fish species from a highly impacted neotropical river: a case study of the Fundão Dam, Brazil. Ecotoxicol. Environ. Saf. 190 , 110165 (2020).

Salvador, G. N. et al. Influences of multiple anthropogenic disturbances coupled with a tailings dam rupture on spatiotemporal variation in fish assemblages of a tropical river. Freshw. Biol. 67 , 1708–1724 (2022).

Owen, J. R. et al. Increasing mine waste will induce land cover change that results in ecological degradation and human displacement. J. Environ. Manag. 351 , 119691 (2024).

Shandro, J., Jokinen, L., Stockwell, A., Mazzei, F. & Winkler, M. S. Risks and impacts to First Nation health and the Mount Polley mine tailings dam failure. Int. J. Indig. Health 12 , 84–201 (2017).

Araújo, R. M. et al. Identification of victims of the collapse of a mine tailing dam in Brumadinho. Forensic Sci. Res. 12 , 580–589 (2023).

Vormittag, E., Saldiva, P., Anastacio, A. & Barbosa, F. High levels of metals/metalloids in blood and urine of residents living in the area affected by the dam failing in Barra Longa, District, Brazil: a preliminary human biomonitoring study. Environ. Toxicol. Pharmacol. 83 , 103556 (2021).

Queiroz, H. M. et al. Manganese: the overlooked contaminant in the world largest mine tailings dam collapse. Environ. Int. 146 , 106284 (2021).

Fernandes, C. S., Santos, A. C., Santos, G. R. & Teixeira, M. C. Environmental arsenic in a changing world. In Proc. 7th International Congress and Exhibition on Arsenic in the Environment 203–204 (2019).

Thompson, F. et al. Severe impacts of the Brumadinho Dam failure (Minas Gerais, Brazil) on the water quality of the Paraopeba River. Sci. Total Environ. 705 , 135914 (2020).

Liu, H., Probst, A. & Liao, B. Metal contamination of soils and crops affected by the Chenzhou lead/zinc mine spill (Hunan, China). Sci. Total Environ. 339 , 153–166 (2005).

Xu, D. et al. Effects of soil properties on heavy metal bioavailability and accumulation in crop grains under different farmland use patterns. Sci. Rep. 12 , 9211 (2022).

Kawabe, Y., Komai, T. & Sakamoto, Y. Exposure estimation of heavy metals in Japan — risk analysis by Geo-environmental Risk Assessment Model. J. Min. Mater. Process. Inst. Jpn. 119 , 427–433 (2003).

CAS   Google Scholar  

Xu, Z., Ito, L., dos Muchangos, L. S. & Tokai, A. Health risk assessment and cost–benefit analysis of agricultural soil remediation for tailing dam failure in Jinding mining area, SW China. Environ. Geochem. Health 45 , 3759–3775 (2022).

Ruhl, L. et al. Survey of the potential environmental and health impacts in the immediate aftermath of the coal ash spill in Kingston, Tennessee. Environ. Sci. Technol. 43 , 6326–6333 (2009).

WISE Uranium Project. Chronology of major tailings dam failures. World Information Service of Energy https://www.wise-uranium.org/mdaf.html (2024).

Renforth, P. et al. Contaminant mobility and carbon sequestration downstream of the Ajka (Hungary) red mud spill: the effects of gypsum dosing. Sci. Total Environ. 421 , 253–259 (2012).

Gao, T., Wang, X. C., Chen, R., Ngo, H. H. & Guo, W. Disability adjusted life year (DALY): a useful tool for quantitative assessment of environmental pollution. Sci. Total Environ. 511 , 268–287 (2015).

Neves, A. C. D. O., Nunes, F. P., de Carvalho, F. A. & Fernandes, G. W. Neglect of ecosystems services by mining, and the worst environmental disaster in Brazil. Perspect. Ecol. Conserv. 14 , 24–27 (2016).

Vergilio, C. D. et al. Metal concentrations and biological effects from one of the largest mining disasters in the world (Brumadinho, Minas Gerais, Brazil). Sci. Rep . https://doi.org/10.1038/s41598-020-62700-w (2020).

Czajkowski, M. et al. Estimating environmental and cultural/heritage damages of a tailings dam failure: the case of the Fundão Dam in Brazil. J. Environ. Econ. Manag. 121 , 102849 (2023).

The Church of England. The Investor Mining and Tailings Safety Initiative. The Church of England https://www.churchofengland.org/about/leadership-and-governance/national-church-institutions/church-england-pensions-board/pensions (2022).

United Nations Economic Commission for Europe. UNECE launches online toolkit and training for strengthening mine tailings safety. UNECE https://unece.org/environment-policy/industrial-accidents/online-toolkit-and-training-strengthening-mine-tailings (2021).

Milanez, B., Ali, S. H. & de Oliveira, J. A. P. Mapping industrial disaster recovery: lessons from mining dam failures in Brazil. Extr. Ind. Soc. 8 , 100900 (2021).

Hund, K. et al. Minerals for climate action: the mineral intensity of the clean energy transition. World Bank Group https://elibrary.worldbank.org/doi/abs/10.1596/40002 (2020).

O’Regan, B. & Moles, R. Using system dynamics to model the interaction between environmental and economic factors in the mining industry. J. Clean. Prod. 14 , 689–707 (2006).

Valenta, R. K., Kemp, D., Owen, J. R., Corder, G. D. & Lebre, E. Re-thinking complex orebodies: consequences for the future world supply of copper. J. Clean. Prod. 220 , 816–826 (2019).

Comerio, M. C. Housing issues after disasters. J. Conting. Crisis Manag. 5 , 166–178 (2002).

Hein, W. et al. Climate change and natural disasters: government mitigation activities and public property demand response. Land Use Policy 82 , 436–443 (2019).

Kellenberg, D. & Mobarak, A. M. The economics of natural disasters. Annu. Rev. Resour. Econ. 3 , 297–312 (2011).

Collenteur, R. A., de Moel, H., Jongman, B. & Di Baldassarre, G. The failed-levee effect: do societies learn from flood disasters? Nat. Hazards 76 , 373–388 (2015).

Alexander, D. The study of natural disasters, 1977–97: some reflections on a changing field of knowledge. Disasters 21 , 284–304 (2002).

Turner, J. et al. Heavy metals and As transport under low and high flows in the River Guadiamar three years after the Aznalcóllar tailings dam failure: implications for river recovery and management. Cuad. de Invest. Geográfica 28 , 31–47 (2002).

Eriksson, N. & Adamek, P. The tailings pond failure at the Aznalcóllar mine, Spain. In Sixth International Symposium in Environmental Issues and Wate Management in Energy and Mineral Production 109–116 (Routledge, 2000).

Turner, J. N., Brewer, P. A. & Macklin, M. G. Fluvial-controlled metal and As mobilisation, dispersal and storage in the Río Guadiamar, SW Spain and its implications for long-term contaminant fluxes to the Doñana wetlands. Sci. Total Environ. 394 , 144–161 (2008).

Macklin, M. G. et al. Physical stability and rehabilitation of sustainable aquatic and riparian ecosystems in the Río Guadiamar, Spain, following the Aznalcóllar mine tailings dam failure. In Mine, Water and Environment. International Mine Water Association Congress 271–278 (International Mine Water Association, 1999).

Akcil, A. A new global approach of cyanide management: international cyanide management code for the manufacture, transport, and use of cyanide in the production of gold. Miner. Process. Extr. Metall. Rev. 31 , 135–149 (2010).

Golder Associates. Mount Polley rehabilitation and remediation strategy. Remediation Plan https://imperialmetals.com/assets/docs/mt-polley/2019-03-golder-remediation-plan.pdf (2017).

Márquez-Ferrando, R., Pleguezuelos, J. M., Santos, X., Ontiveros, D. & Fernández-Cardenete, J. R. Recovering the reptile community after the mine-tailing accident of Aznalcóllar (southwestern Spain). Restor. Ecol. 17 , 660–667 (2009).

Campanharo, Í. F. et al. Effects of forest restoration techniques on community diversity and aboveground biomass on area affected by mining tailings in Mariana, southeastern Brazil. Res. Ecol. 2 , 22–30 (2020).

Sun, W. et al. An extensive review on restoration technologies for mining tailings. Environ. Sci. Pollut. Res. 25 , 33911–33925 (2018).

McMahen, K., Anglin, C. D., Lavkulich, L. M., Grayston, S. J. & Simard, S. W. Small-volume additions of forest topsoil improve root symbiont colonization and seedling growth in mine reclamation. Appl. Soil Ecol. 180 , 104622 (2022).

Beck, H. E. et al. Present and future Köppen-Geiger climate classification maps at 1-km resolution. Sci. Data 5 , 180214 (2018).

Vallance, S. & Carlton, S. First to respond, last to leave: communities’ roles and resilience across the ‘4Rs’. Int. J. Disaster Risk Reduct. 14 , 27–36 (2015).

LaLone, M. D. Neighbors helping neighbors: an examination of the social capital mobilization process for community resilience to environmental disasters. J. Appl. Soc. Sci. 6 , 209–237 (2012).

Murphy, B. L. Locating social capital in resilient community-level emergency management. Nat. Hazards 41 , 297–315 (2007).

Downing, T. E., Shi, G. Q., Zaman, M. & Garcia-Downing, C. Improving post-relocation support for people resettled by infrastructure development. Impact Assess. Proj. Apprais. 39 , 357–365 (2021).

Price, S. et al. Risk and value in benefit-sharing with displaced people: looking back 40 years, anticipating the future. Soc. Change 50 , 447–465 (2020).

Cernea, M. The risks and reconstruction model for resettling displaced populations. World Dev. 25 , 1569–1587 (1997).

Downing, T. E. Avoiding New Poverty : Mining-induced Displacement and Resettlement Vol. 52 (IIED, 2002).

Vanclay, F. Project-induced displacement and resettlement: from impoverishment risks to an opportunity for development? Impact Assess. Proj. Apprais. 35 , 3–21 (2017).

Saharan, V. in Strategic Disaster Risk Management in Asia (eds Ha, H. et al.) 193–206 (Springer, 2015).

Lyra, M. G. Challenging extractivism: activism over the aftermath of the Fundão disaster. Extr. Ind. Soc. 6 , 897–905 (2019).

Owen, J. R. & Kemp, D. A return to responsibility: a critique of the single actor strategic model of CSR. J. Environ. Manag. 341 , 118024 (2023).

Zanini, M. T. F., Migueles, C. P., Gambriage, C. & Silva, J. Barriers to local community participation in mining projects: the eroding role of power imbalance and information asymmetry. Resour. Policy 86 , 104283 (2023).

Marais, L. et al. The catastrophic failure of the Jagersfontein tailings dam: an industrial disaster 150 years in the making. Int. J. Disaster Risk Reduct. 109 , 104585 (2024).

Pearce, T. D. et al. Climate change and mining in Canada. Mitig. Adaption Strateg. Glob. Change 16 , 347–368 (2010).

Jin, J., Song, C., Zhang, X. & Lv, X. Ageing deformation of tailings dams in seasonally frozen soil areas under freeze-thaw cycles. Sci. Rep. 9 , 15033 (2019).

Armstrong, M., Petter, R. & Petter, C. Why have so many tailings dams failed in recent years? Resour. Policy 63 , 101412 (2019).

Vaughan, D. The Challenger Launch Decision : Risky Technology, Culture, and Deviance at NASA . (Univ. of Chicago Press, 2016).

Williams, D. J. Lessons from tailings dam failures — where to go from here? Minerals 11 , 853 (2021).

Snow, R. E. in Tailings Management Handbook : A Life-cycle Approach . (ed. Morrison, K. F.) Ch 4, 41-64 (Society for Mining, Metallurgy & Exploration, 2022).

Sako, C. H. & Pabst, T. Experimental and numerical evaluation of the critical degree of saturation and critical exposure time of acid generating filtered tailings. Appl. Geochem. 155 , 105726 (2023).

Vargas, C. C. & Campomanes, G. P. Practical experience of filtered tailings technology in Chile and Peru: an environmentally friendly solution. Minerals 12 , 889 (2022).

Torres-Cruz, L. A. & O’Donovan, C. Public remotely sensed data raise concerns about history of failed Jagersfontein Dam. Sci. Rep. 13 , 4953 (2023).

Grebby, S. et al. Advanced analysis of satellite data reveals ground deformation precursors to the Brumadinho Tailings Dam collapse. Commun. Earth Environ. 2 , 2 (2021).

Ouellet, S. M., Dettmer, J., Olivier, G., DeWit, T. & Lato, M. Advanced monitoring of tailings dam performance using seismic noise and stress models. Commun. Earth Environ. 3 , 301 (2022).

Lumbroso, D. et al. DAMSAT: an eye in the sky for monitoring tailings dams. Mine Water Environ. 40 , 113–127 (2021).

Innis, S. et al. The development and demonstration of a semi-automated regional hazard mapping tool for tailings storage facility failures. Resources 11 , 82 (2022).

International Council on Mining and Metals (ICMM). Member disclosures on progress towards conformance with the Global Industry Standard on Tailings Management (ICMM, 2023).

Lèbre, E., Corder, G. D. & Golev, A. Sustainable practices in the management of mining waste: a focus on the mineral resource. Miner. Eng. 107 , 34–42 (2017).

Kinnunen, P., Karhu, M., Yli-Rantala, E., Kivikytö-Reponen, P. & Mäkinen, J. A review of circular economy strategies for mine tailings. Clean. Eng. Technol. 8 , 100499 (2022).

Simonsen, A. M. T., Solismaa, S., Hansen, H. K. & Jensen, P. E. Evaluation of mine tailings’ potential as supplementary cementitious materials based on chemical, mineralogical and physical characteristics. Waste Manag. 102 , 710–721 (2020).

Ahmari, S. & Zhang, L. Durability and leaching behavior of mine tailings-based geopolymer bricks. Constr. Build. Mater. 44 , 743–750 (2013).

Karhu, M. et al. Mining tailings as a raw material for glass-bonded thermally sprayed ceramic coatings: microstructure and properties. J. Eur. Ceram. Soc. 40 , 4111–4121 (2020).

Kinnunen, P. et al. Recycling mine tailings in chemically bonded ceramics — a review. J. Clean. Prod. 174 , 634–649 (2018).

Gou, M., Zhou, L. & Then, N. W. Y. Utilization of tailings in cement and concrete: a review. Sci. Eng. Compos. Mater. 26 , 449–464 (2019).

Bullock, L. A., Yang, A. D. & Darton, R. C. Kinetics-informed global assessment of mine tailings for CO 2 removal. Sci. Total Environ. 808 , 152111 (2022).

Golev, A. et al. Ore-sand: a potential new solution to the mine tailings and global sand sustainability crises https://doi.org/10.14264/503a3fd (The University of Queensland, 2022).

Segura-Salazar, J. & Franks, D. M. Ore-sand co-production from Newcrest’s Cadia East HydroFloat Reject: an exploratory study https://doi.org/10.14264/96249f6 (The University of Queensland, 2023).

Li, Y., Li, S., Zhao, X., Pan, X. & Guo, P. Separation and purification of high-purity quartz from high-silicon iron ore tailing: an innovative strategy for comprehensive utilization of tailings resources. Process. Saf. Environ. Prot. 169 , 142–148 (2023).

Kinnunen, P. H.-M. & Kaksonen, A. H. Towards circular economy in mining: opportunities and bottlenecks for tailings valorization. J. Clean. Prod. 288 , 153–160 (2019).

Martens, E. et al. Toward a more sustainable mining future with electrokinetic in situ leaching. Sci. Adv. 7 , eabf9971 (2021).

Visual Capitalist. Visualizing the importance of environmental management in mining. Visual Capitalist https://www.visualcapitalist.com/sp/environmental-and-mining/ (2020).

Cacciuttolo, C. & Atencio, E. In-pit disposal of mine tailings for a sustainable mine closure: a responsible alternative to develop long-term green mining solutions. Sustainability 15 , 6481 (2023).

MSHA. MSHA metal and nonmetal tailings and water impoundment inspection form https://www.resolutionmineeis.us/documents/fundao-2016 (2009).

Islam, K. & Murakami, S. Global-scale impact analysis of mine tailings dam failures: 1915-2020. Glob. Environ. Change 70 , 102361 (2021).

Rudolph, T. & Coldewey, W. Implications of earthquakes on the stability of tailings dams. pebblescience http://www.pebblescience.org/OLD-SITE/pdfs/Tailings_dam.pdf (1971).

Ishihara, K., Yasuda, S. & Yoshida, Y. Liquefaction-induced flow failure of embankments and residual strength of silty sands. Soils Found. 30 , 69–80 (1990).

Fundão Tailings Dam Review Panel. Report on the Immediate Causes of the Failure of the Fundão Dam (Fundão Tailings Dam Review Panel, 2016).

Schneider, U., Becker, A., Finger, P., Rustemeier, E. & Ziese, M. GPCC full data monthly product version 2020 at 0.5°: monthly land-surface precipitation from rain-gauges built on GTS-based and historical data. GPCC Full Data Monthly Product Version 2020 https://doi.org/10.5676/DWD_GPCC/FD_M_V2020_050 (2020).

Giardini, D. et al. in International Handbook of Earthquake & Engineering Seismology . 81B, International Geophysics Series (eds Lee, W. et al.) 1233–1239 (Academic, 2003).

Genevois, R. & Tecca, P. R. in Environmental Management Geo-water and Engineering Aspects (eds Chowdhury, R. N. & Sivakumar, M.) 23–36 (Balkema, 1993).

Alexander, D. E. Northern Italian dam failure and mudflow, July 1985. Disasters 10 , 3–7 (1986).

Takahashi, T. in Debris Flow (ed. International Association for Hydro-Environment Engineering and Research (IAHR)) 92–99 (Balkema, 1991).

van Niekerk, H. J. & Viljoen, M. J. Causes and consequences of the Merriespruit and other tailings-dam failures. Land Degrad. Dev. 16 , 201–212 (2005).

Lucchi, G. in Stava-Tesero La Ricostruzione e la Memoria 23–49 (Fondazione Stava 1985, 2011).

Fondazione Stava 1985. https://www.stava1985.it/ (2002).

Simeoni, L., Tosatti, G., Lucchi, G. & Longo, M. The Stava catastrophic failure of July 19, 1985 (Italy): technical-scientific data and socioeconomic aspects. CSE J. 1 , 17–30 (2017).

Chandler, R. J. & Tasatti, G. The Stava tailings dams failure, Italy, July 1985. Proc. Inst. Civ. Eng. 113 , 67–79 (1995).

Meyer Jr., V., Mamédio, D. F. & Adrião, M. in Universities and Sustainable Communities: Meeting the Goals of the Agenda 2030. 384-399 (Springer, 2020).

McDermott, R. K. & Sibley, J. M. The Aznalcóllar tailings dam accident - A case study. Miner. Resour. Eng. 9, 101-118 (2000).

Alonso, E. E. The failure of the Aznalcóllar tailings dam in SW Spain. Mine Water Environ. 40, 209–224 (2021).

Pirulli, M., Barbero, M., Marchelli, M. & Scavia, C. The failure of the Stava Valley tailings dams (Northern Italy): numerical analysis of the flow dynamics and rheological properties. Geoenvironmental Disasters https://doi.org/10.1186/s40677-016-0066-5 (2017).

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Acknowledgements

The contribution of D.K. was in part supported by the Australian Research Council grant LP200301160. The authors are grateful to A. Amanda Andrade for her feedback on an early draft of the manuscript. K.A.H.-E., D.K., D.M.F. and E.M. acknowledge the QUEX Institute ( https://www.exeter.ac.uk/global/quex/ ) for helping to facilitate our collaboration.

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The powdery inorganic waste material remaining after the combustion of mineral materials.

(BAP). Best available practices for tailings storage facilities, which include monitoring of physical mechanisms and human factors that could result in tailings storage facility failures.

(GISTM). The global standard developed by the United Nations Environment Programme (UNEP), International Council on Mining and Metals (ICMM) and Principles for Responsible Investment (PRI) in 2020 that requires operators to be responsible for, and prioritize the safety of, TSF throughout its life cycle.

The glassy siliceous waste materials remaining after the smelting of metal ores.

Finely crushed rock and processing fluids left over after the economic materials of the mined resource have been extracted; they can contain potentially toxic, corrosive and radioactive components.

TSF barriers constructed to hold back the tailings; it is the part of the TSF that has the highest tendency to fail.

(TSF). Engineered facility designed to contain tailings; it can be an open pit, a dammed impoundment or an underground void.

TSF failures that cause severe impacts and result in serious disruption to social, environmental and economic systems.

Failures of the dam or other part of the storage facility designed to hold back the tailings in the TSF.

Mined rock that does not contain ore minerals at sufficient grades to be economic and does not undergo mineral processing.

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The food production–consumption chain: Fighting food insecurity, loss, and waste with technology

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  • Dhruv Grewal 1 , 3 , 5 ,
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The UN’s Sustainable Development Goal (SDG) 12 seeks to achieve sustainable food production and consumption, including reduced food loss and waste; SDG 2 proposes the goal of zero hunger. In pursuit of these goals, technology arguably has a central role, at every level of the food value chain. To establish this role, the authors identify and examine current technologies aimed at increasing food production and suitably redistributing unused food, as tactics to combat food loss and waste, with the shared end goal of reducing food insecurity. A proposed 2 × 2 typology illustrates how existing technologies can influence food production, distribution, and consumption, as well as influence the stakeholders in the food production–consumption chain. These insights also inform a research and development agenda pertaining to the need for technology applications that can increase food production and/or reduce food waste effectively enough to achieve the goal of zero hunger.

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Achieving sustainable food production and consumption and reducing food loss and waste represent central features of the UN’s Sustainable Development Goal (SDG) 12; zero hunger is the primary objective for SDG 2. Both priorities reflect relevant concerns about both global food insecurity and staggering estimates of food loss and waste; according to the U.S. Department of Agriculture’s Economic Research Service ( 2010 , p. 1), about 30% of the 430 billion pounds of food available goes uneaten, amounting to $162 billion in food lost, or “1.2 pounds of food per person per day.” Other estimates similarly approximate that one-third of all food produced gets wasted and that farms lose 20 billion pounds of food annually (FoodPrint 2018 ), due to overplanted fields, damage to crops from pests and weather, or low market prices that make it unprofitable to harvest and transport products (Azevedo 2021 ). Yet globally, nearly 200 million people lack “consistent access to enough food for an active, healthy life” (Brown et al. 2019 , p. 980; see also Gustafson 2022 ; UNWFP 2021 ), and 600 million people suffer from hunger (Bernabe 2022 ).

Both (i) food loss, i.e. edible food—post harvest—that is available for human consumption, but then is not consumed, and (ii) food waste, which is a subset of food loss, occurs after customers acquire food, but then goes unconsumed (Buzby et al. 2014 , p. 5), are pressing issues. For example, end-consumers might buy and cook more than is needed, then discard the excess. Retailers engage in excessive ordering (Buzby et al. 2014 ; U.S. Department of Agriculture 2023 ), struggle to store food, and discard unattractive or blemished food (Grewal et al. 2019 ). At the farm level, food gets destroyed by pests or weather; issues in harvesting, drying, or processing foods also leads to inefficient production (Buzby et al. 2014 ; U.S. Department of Agriculture 2023 ). Yet oversupply also can have negative downstream effects, if insufficient post-harvest preservation leads to substantial losses of abundant harvests (Azevedo 2021 ).

In this sense, increasing food production is necessary to combat global food insecurity, but it is not sufficient to eliminate world hunger (Azevedo 2021 ), which also requires reducing food waste. According to the preceding statistics, retrieving wasted food would provide more than four times what is needed to relieve undernutrition and hunger worldwide (Azevedo 2021 ). Yet such a complex, persistent, global challenge needs innovative approaches, for which technology might be key. We argue that technological innovations, directed at different parts of the food chain, can establish new means for expanding the metaphorical food pie (i.e., increase production and reduce inefficient production) and effectively distributing that food pie in ways that reduce food waste and loss (SDG 12) and move toward the goal of zero hunger (SDG 2).

Some companies already are testing pertinent new technologies. Consider food production to start. In Kenya, the Seed Trade Association’s Mbegu (Seed) Choice program aims to help farmers select appropriate seeds that match their land and weather conditions, as well as their crop preferences. By inputting information pertaining to the country, ecological zone, and crop details, farmers receive personalized, optimal seed recommendations (Senthilingam 2017 ). In China, ongoing laboratory experiments seek to develop seeds that can yield greater output, using fewer resources (e.g., water), even in extreme weather conditions (Kaizhi 2022 ; Pultarova 2022 ). One engineered wheat crop, Lunyan 502, grown from seeds developed in outer space, offers 11% greater yield than traditional Chinese-grown wheat, uses less input, and provides greater resistance to pests. In a partnership, tractor company John Deere and drone-based transportation company Volocopter developed the VoloDrone, which features a tank and sprayer that can dispense appropriate amounts of fertilizers, pesticides, and anti-frost chemicals from the air. Recent efforts aim to expand its capacities, such as sowing seeds (Etherington 2019 ). In addition to increasing usage efficiency of seeds, frost control, pesticides, and so on, this technology offers new methods to reach croplands with challenging topography (Mohan 2020 ). VoloDrone also might facilitate sustainable farming practices, such as ecological farming, by spreading natural materials where they are most needed.

Turning to food redistribution, we find technologies by Food for All (United States) and Too Good to Go (United Kingdom) that help restaurants sell or donate food, at substantial discounts, in the hour before they close; Food Rescue (United States) relies on an algorithm to connect sources of food donations with homeless shelters and other organizations that aid populations that are food insecure (Bozhinova 2018 ). Such technology-enabled food (re)distribution tools can benefit both the supply side (decreasing the amount of wasted food) and the demand side (getting resources to people who need them).

Artificial intelligence (AI) also has turbocharged the impact of such technological solutions, due to its relative advantages over prior methods (e.g., better, more cost-effective predictions; Davenport et al. 2021 ) and access to higher quality and expanded data. Cocoa growers in Ghana had been struggling with poor efficiency, due to climate change and new diseases and pests, but a newly developed, AI-based predictive crop monitoring platform called CocoaSense helps them manage and monitor crops by providing “weather-based advisory and promote[s] climate-smart agriculture. In addition, farmers benefited from timely and dependable pest and disease alerts” ( www.cropin.com ). Farmers using the platform reported a threefold increase in efficiency. This tool relies on AI and its predictive capabilities, which in turn depends on the availability of good data gathered from both farm sensors and satellites.

Another example involves Lumitics, which works with hotels like The Four Seasons in Singapore and airlines like Etihad, using AI to track exactly which foods are being wasted. When food gets thrown in garbage cans, a combination of cameras, sensors, and AI technology determine the type of food discarded (e.g., steak, bananas) and the reason (e.g., spoiled, uneaten, scraps). The service providers then can identify avoidable waste, which gives chefs insights into how to order the food for their menus more efficiently. For example, Lumitics technology might show hotels that they do not need so many croissants on their breakfast buffet or reveal to airlines that they can order fewer box lunches—strategic choices that reduce food waste (and costs) without affecting food quality or service standards. The increased food available in the system also might be rerouted to consumers who are food insecure (Gunia 2021 ).

In line with these real-world, current examples, we examine the entire food production–consumption chain, Footnote 1 starting with crop inputs and moving through the chain to end-consumers’ waste and disposal choices (Fig.  1 ). Building on insights from practice and relevant literature, we predict how technology might influence all stages of the production–consumption chain, in ways that enhance inputs and increase food production, optimize food (re)distribution, and reduce loss and waste in various stages to combat food insecurity. In turn, we propose a 2 × 2 typology of how technologies determine the food pie, according to the stakeholders in the food production–consumption chain they target. This typology reflects findings from interviews with eight key informants in the food industry (see Appendix 1 ), triangulated with extant literature.

figure 1

Food production–consumption chain

In turn, this article offers three contributions. First, we prioritize the role of technology (including – but not restricted to—AI) for reducing food insecurity, loss, and waste. Technology can increase the amount of food produced, help distribute existing food more equitably, and thus minimize loss and waste. Second, we propose a typology of how existing technologies affect the metaphorical food pie and which stakeholders they target. With this typology, we identify critical technological gaps pertaining to efforts to reduce food insecurity, loss, and waste. Third, we offer an agenda for further research in this area.

The food production–consumption chain

The food production–consumption chain consists of five (somewhat overlapping) stages (Fig.  1 ). First, the food input stage involves decisions about food inputs, whether to plant crops, which types of seeds or fertilizer to use, and so on. Second, the actual growing or food production stage differs by crop. Some take longer to grow, while others grow quickly; some products can be grown across multiple seasons, but others have only a single growing season. After the food is grown, it must be harvested. Third, food processing involves the transformation of agricultural products into food (e.g., rice gets cleaned, husked, polished, and suitably packaged). Processing encompasses any steps needed to make the food suitable for distribution and ultimate consumption. We thus define processing broadly, to encompass many different forms, from grinding grain to make flour, to home cooking, to complex industrial methods that produce convenience foods. Fourth, distributors (midrange entities, intermediaries), including retailers, restaurants, governments, and public entities, acquire food that has been processed for their use. Fifth, the last stage culminates with end-consumers, who engage in consumption, disposal, and waste practices.

Food loss and waste occurs across all stages of this chain, but they become relatively more intense in later stages. In the United States, approximately 43% of total food waste comes from households and 40% from retailers (e.g., grocery stores, food service companies, restaurants). Thus, less than 20% of food waste occurs at farms (food inputs, growing, harvesting stages) or during processing (Recycle Track Systems 2023 ). These statistics vary somewhat by country and region. Globally, about 14% of food waste occurs during transportation between the harvesting and retail stages, but this percentage is higher in less industrialized countries where technology to keep food fresh during transport is less accessible. For example, only about 5–6% of food is wasted between harvest and retail in Australia and New Zealand, whereas it reaches 20–21% in Central and South Asia (Global Agriculture, 2019 ). Block et al. ( 2016 ) thus suggest that improvements to food distribution systems (food input, growing, production) should have greater impacts in developing countries, but reducing food waste at the retailer and consumer stages is more critical in industrialized countries. That is, technology should have substantive impacts on all stages of the food value chain, but those impacts also may vary by region.

Objectives across the food production–consumption chain

To specify improvement objectives, we turn to buyer–seller literature as it applies to the food production–consumption chain. Distinct buyer–seller relationships appear throughout the entire food production–consumption chain, such that the entities that provide food inputs to food producers represent sellers, while the food producers are buyers. Then food producers function as sellers that interact with food processors as buyers.

Buyer–seller relationships generally seek both pie expansion (Jap, 1999 ) and pie sharing (Jap, 2001 ). Pie expansion refers “to the collaborative process of creating mutually beneficial strategic outcomes between buyers and suppliers” (Jap, 1999 , p. 461), such that the joint benefits (i.e., benefits pie) expands more than could have been achieved if buyers or suppliers were working in isolation. A key driver of pie expansion is enhanced buyer–seller coordination (Anderson & Narus, 1990 ; Dwyer et al., 1987 ; Heide & John, 1992 ; Jap, 1999 ), such that the parties share information, opportunities, and knowledge that help them generate competitive advantages and the overall value available to them. In line with resource-based theory, greater outcomes (bigger pies) result from the dyadic resources that arise from coordinated, collaborative efforts. To combat food insecurity, pie expansion would imply that more food gets produced throughout the food production–consumption chain. When two entities work jointly to create mutually beneficial strategic outcomes related to food production, the food pie, as well as the profits for both parties, likely expand.

In contrast, pie sharing involves the division of the value created in a buyer–seller dyad, often viewed “as a competitive process… [that] emanates from game theoretic research in economics and psychology” (Jap, 2001 , p. 86). Equality and equity guide pie sharing, in line with equity theory (Walster et al., 1978 ), “which states that people judge an outcome as fair when the ratio of their own resources and output equals the ratio of resources and output of comparison others” (Jap, 2001 , p. 89). The fight against food insecurity also relates to equity, because it requires that people who endure food insecurity attain suitable relief.

So when is pie expansion the primary objective, relative to pie sharing? Block et al., ( 2016 ; e.g., their Fig. 2) outline concerns across the food production–consumption chain, such that in the initial stages, concerns (and objectives) primarily relate to pie expansion, but in the later stages of the chain, concerns (and objectives) pertain primarily to pie sharing. Such reasoning is consistent with research in other marketing domains. In studies of product lifecycles for example, Lumpkin and Dess ( 2001 ) find that in earlier lifecycle stages, firms focus on proactiveness, to gain market opportunities, but in later stages, they prioritize aggressiveness, to deal with competition.

Consistent with these insights, we propose that in the initial stages of the chain (i.e., food input, production, and processing), the objective is pie expansion, so beneficial uses of technology would promote buyer–seller coordination. In later stages (i.e., food distribution and end-consumers), the objective is pie sharing, and beneficial uses of technology would entail equity-oriented food sharing. We describe these various stages of the production–consumption chain, together with examples of how technologies might promote coordinated pie expansion efforts or equity-oriented pie sharing endeavors, next.

Additionally, as noted earlier, food-related issues vary in different countries, and, thus technology that helps to expand the pie versus more equitably share the pie will also be more/less effective in different countries. For example, in developing countries such as Mexico and Ethiopia, food insecurity and undernourishment are key issues, and, thus, technology that could expand the food pie in these countries would be highly impactful. On the other hand, in highly developed countries such as the United States and Australia, food waste is a more prevalent issue, so technology aimed at more equitably distributing the pie would be more impactful in these countries. Further, technologies that would allow for more efficient and reliable transportation of food across longer distances could benefit consumers in a broad range of countries, as it could allow the oversupply of food in more developed countries, i.e. food that is currently going to waste in the United States, for example, to be more effectively shared with consumers in underdeveloped countries, thereby increasing the food pie in those countries.

Early stages: Pie expansion

Food inputs.

The food production–consumption chain starts with food inputs; as discussed, the central challenge for this stage is finding efficient ways to increase food production. Some optimal combination of inputs will lead to the greatest or highest quality output, thereby increasing the food pie, but knowledge gaps make it difficult to discern, define, and update such optimal combinations. Some technology solutions (Eastwood et al., 2019 ) require monetization, such that they only benefit farmers who pay (at least partially) for them. Currently, these technology solutions may be out of reach for some farmers, particularly (i) smaller farmers, and (ii) farmers in developing countries. However, we also note that the key benefit of AI is that it lowers the cost of prediction (Agrawal et al., 2018 ), and so as AI advances, it is likely that the costs associated with some of these technology solutions will decrease, thereby making them more accessible to more farmers. In other cases, third parties—such as government agencies or nongovernmental organizations-intervene to cover the costs of obtaining these technology solutions. We present three examples that differ in both the levels of complexity and involvement of the farmer and technology provider.

First, using AI-enabled technology, Solena analyzes soil and creates customized solutions to help farmers increase their crop outputs and maximize crop quality. Once farmers receive a sampling kit from Solena, they send back a soil sample, then wait to receive customized biofertilizers that promise to increase their soil productivity and crop yield. Solena then maintains relationships with these farmers, offering follow-up analyses to ensure that the soil remains healthy and able to support efficient growth patterns. On average, Solena users – which includes small farmers—report a 30% increase in their profits.

Second, Dimitra Incorporated’s blockchain platform integrates a host of technologies (e.g., mobile, satellite and drone imagery, machine learning, AI). Its associated app grants farmers a host of functionalities, ranging from access to crop inputs, to financing, to insurance, to advanced farming education modules.

Third, Krish-e consulting (Farming-as-a-Service, provided by the Mahindra Group, India as an “affordable service”) provides advice pertaining to virtually every aspect of farming, from preparing the land prior to sowing seeds to which fertilizers and treatments to use on planted crops. To demonstrate its effectiveness, Krish-e asks farmers to assign some portion of their land to following its advice completely, then compare this land’s output with the output from the balance of farmer’s land (on which the farmer maintains conventional practices). Discussions with a key respondent Footnote 2 at Krish-e indicate that the output from land worked in accordance with its advice is typically significantly greater than the output obtained from conventional methods. Mahindra also has observed an increase in income per acre, from US$63 to US$186, among farmers who embraced Krish-e–assisted farming techniques (Grand View Market Research, 2023 ).

Solena, Dimitra, and Krish-e all facilitate better coordination, such that food producers are more likely to source suitable inputs (seeds, fertilizers, pesticides) from their sellers. Solena enables food producers to identify and order suitable, customized biofertilizers; Krish-e and Dimitra offer technological solutions that align food producers and their inputs to realize improved crops. In these food input stages, beneficial uses of technology primarily would promote buyer–seller coordination and thus encourage pie expansion, as we theorized. Such services can extend to smaller farmers, either due to extensive use of AI, or due to financial support from a third party.

  • Food production

In the food production stage, efficiency and waste mitigation are relevant concerns. If farmers have determined the inputs to use, they now must manage their growing process (e.g., how much to irrigate, when to harvest) to achieve maximal or the highest quality output. First, they need information about how to manage the growing process, which may come from learning and previous experience but also might be achieved with the help of technology that provides relevant data. Second, farmers must constantly monitor pertinent conditions, such as weather or pestilence threats, that can rapidly, substantially change over the course of a growing season. Farmers then need to respond appropriately, according to the unique conditions they face. Thus, they likely would benefit from AI-based predictions about future conditions (Davenport et al., 2021 ; Guha et al., 2021 , 2023 ).

Increasing the pie—that is, the amount of food grown—also requires reducing inefficient production. Farmers can avail themselves of technology that relies on cloud computing, AI, and machine learning technologies to gain insight into their crop production and management processes. For example, a company called Arugga (Israel) has developed an AI-supported robot called Polly that uses visual data to determine which tomato plants are ready to be pollinated. Its efforts thus produce better results than solely human involvement (20% yield improvement). Additional technological tools being added to Polly promise to integrate pest and disease detection capabilities too (Kontzer, 2021 ).

Some technology applications enhance both efficiency and quality. The CropIn ag-ecosystem technology company provides, in addition to its previously mentioned CocoaSense platform, a cloud computing solution for individual farmers and producers, large companies, governments, and nonprofits (Shu, 2022 ). In partnership with the Alliance for Green Revolution in Africa, it works to help farms achieve efficient resource usage, leading to two key benefits. First, efficiency increases: More crop output gets produced with a given input. Second, crop quality improves, which typically translates into higher prices. In our discussions with a key respondent at CropIn, we learned that these benefits emerge primarily after the farming operations and data are digitized, which enables CropIn to make real-time recommendations at the crop or farm level, in accordance with its prediction capabilities (driven by AI) about weather, pests, and so forth.

As shown in Fig.  1 , food producers also might deal directly with end-consumers (i.e., direct-to-consumer [DTC] sales), by shipping produce directly to consumers or participating in local farmers’ markets. Farmer Jones Farm ( 2023 ) in northern Ohio (United States) ships boxes of vegetables straight from the farm to consumers’ front doors and leverages technological platforms to manage this process. The U.S. Department of Agriculture estimates that in 2015, approximately 115,000 U.S. farms engaged in DTC sales, which earned them annual sales of $3 billion (Kaplan, 2018 ), higher prices per product, and closer consumer relationships (Kaplan, 2018 ). A key respondent, employed by a large Asian conglomerate, suggested other versions of this model, in which large intermediaries donate pertinent apps to farmers, who use them to estimate crop quality. If crop quality is extremely high, the larger intermediary might transact directly with the farmers, leading to better price realization. Otherwise, farmers can sell to smaller intermediaries, who screen and curate the produce for quality, then bring the acceptable items to the larger intermediary, which does not want the burden of screening many submissions of uneven quality. These efforts feed forward and increase production, through the quantity produced and improved quality.

Another pressing challenge arises when market conditions are such that farmers harvest crops to clear land but do not bring the produce to market, because they will not earn sufficient economic returns to justify such efforts. Predictive technology might help farmers time their harvests appropriately, so that the market is more likely to support sufficient returns; other technology tools might grant them access to alternate markets. For example, a Qualcomm-supported app called FarmPrecise issues constantly updated reports, customized to specific firms, that provide (among other information) five-day weather forecasts and market price trend reports. A key informant at Qualcomm explained that FarmPrecise gives farmers information that enables them to speed up or delay their visits to market, so they can sell their crops on days on which prices are highest.

A third challenge relates directly to waste reduction. For example, Taranis uses technology and AI to analyze high resolution photographs taken by drones, planes, and satellites, which have been uploaded to Google Cloud, and thereby determines the health of crops at the literal leaf level. The results get posted to farmers’ individual Taranis dashboards, enabling them to address any unhealthy plants immediately and reduce crop losses (Beyer, 2022 ). In another example, Agerpoint uses AI to identify and provide insights about any crop photographed through its app, including plant health, disease presence, potential remedial actions, and future inputs needed, all of which can help reduce waste. For example, rather than uniformly applying pesticide to all areas, the Agerpoint app helps farmers identify select areas that need pesticide, thus reducing pesticide usage and costs. Note that Agerpoint works at a relatively affordable price point, affordable due to its use of AI (rather than human experts) (“impact [of our product] is about access and affordability.” — CEO Agerpoint; Pixel Scientia, 2023 ).

Arugga, CropIn, and Agerpoint each facilitates better coordination between food input sellers and food producer buyers, such that food producers buy more suitable inputs (seeds, fertilizers, pesticides) from the sellers. FarmPrecise also enables coordination between food producers and food processors, by helping food producers decide which foods to sell to which market. Through these efforts, parties engaged in the food production stage focus on pie expansion, and beneficial uses of technology should promote buyer–seller coordination. Similar to what was earlier noted, the use of AI improves access and affordability.

Food processing

To depict the food processing stage, we use the example of rice crops. Retailers and restaurants buy rice in bags, so some prior member of the supply chain must have purchased the rice crop, processed it, and packed it into bags. Such efforts are critical to increasing the longevity of farm produce, parceling out and packaging the crop yields, and thus making them accessible to downstream actors such as retailers or restaurants. In this processing stage, both efficiency and waste reduction considerations are prominent.

Regarding efficiency, food processors need to account for various demands, including the need to ensure that the food retains its taste and nutrition, establish an extended shelf life, and still maintain cost effectiveness. Furthermore, most producers separate their crops into products for human consumption and those designated for other purposes, such as feeding livestock. But such sorting processes are cumbersome and challenging; determining whether an apple can sell in the grocery store or instead should be designated for a horse farm requires much skill. The sorting technology provider TOMRA relies on multiple technologies—x-ray, near-infrared spectroscopy, cameras, machine learning/AI, and even lasers—to support its automated sorting tool. The tool gauges various attributes of different crops to ensure that each piece of fruit or vegetable gets sorted efficiently and sent to the appropriate market channel (Sharma, 2019 ).

Regarding waste, food processors not only need to minimize any food losses due to their processing efforts but also account for and mitigate waste-related issues further downstream in the food chain, related to shelf-life considerations, quality, and appropriate packaging. For crops processed as frozen foods for example, this stage must address the risk that the products might be subject to unsupportable temperatures and humidity levels, in which case they could develop ice crystals. The Xsense monitoring system constantly keeps track of the conditions surrounding frozen packages. If a freezer malfunctions and temperatures rise, the system alerts relevant actors and even can be programmed to initiate corrective actions (e.g., lowering the temperature using emergency controls) to avoid losses of the frozen items (Jackson, 2016 ).

In some cases, efficiency and waste are closely linked, and so some technological solutions address both elements. For example, One Third leverages AI-enabled cameras, installed in handheld scanners, to gauge the freshness and quality of various foods. Then processors can prioritize those items that are closer to spoiling and must be shipped immediately, while holding on to less mature produce for processing later. Or they might send the nearly expired products to nearby markets, and ship less ripe items to more distant recipients, because the latter are more likely to make the long trip still intact. The scanners are more efficient than human labor in detecting items at risk of spoiling, and the resulting recommendations effectively reduce the risk of waste due to spoilage (Moran, 2023 ). Thus, in seeking to achieve both increased efficiency and reduced waste, technology solutions can provide relevant, customized, real-time information, as well as identify factors that trigger waste and enable real-time interventions to avoid it. In effect, One Third facilitates better coordination between food producers and downstream entities, so that food processors can make suitable decisions about which foods to send where. As we theorized, in the food processing stage, like the prior stages, the focus is on pie expansion, and beneficial uses of technology involve encouraging buyer–seller coordination.

Later stages: Pie sharing

Food distribution.

Food distribution gets conducted by entities like restaurants, retailers, and institutions (e.g., armed forces, universities) that buy food from food processors. Despite their different methods for acquiring and distributing food, they all purchase it from upstream actors in the food supply chain, then sell or provide it to end-consumers. The focus in this stage, from a food insecurity standpoint, is on waste reduction. For example, as expiration dates for food items approach, distributors might seek ways to reduce food waste and bolster their public relations by donating edible food.

Several illustrative articles explore factors that might affect food waste among distribution entities, as we summarize in Table  1 . Companies in the food service and grocery industries likely recognize the existence and moral burden of food waste, but they appear to do relatively little to decrease it (Gruber et al., 2016 ; Martin-Rios et al., 2018 ; Vizzoto et al., 2021 ), nor do they seem to realize the potential benefits, such as the cost savings they could obtain (Principato et al., 2018 ). Frontline workers and managers perceive their own lack of power or capacity to make changes to food waste systems, as well as a lack of time and other resources (Gruber et al., 2016 ; Sakaguchi et al., 2018 ). In restaurants, several factors contribute to food waste; establishments with meat-based menus and fewer seats tend to have more waste (Principato et al., 2018 ). Reducing plate sizes, leveraging social cues, and signage focused on being mindful can be effective at reducing food waste among customers dining in restaurants and university food halls (Kallbekken & Sælen, 2013 ; Pinto et al., 2018 ).

Few studies of food waste involving distribution entities identify a role for technology, though various technology applications could be effective. For example, by integrating the Gander technology platform into their in-house processes, Irish retailers can assign steep discounts to food approaching its expiration date. These offerings can be especially appealing to food-insecure populations because the items in question are fully edible but available at very low prices (Belfasttelegraph.com, 2022 ). Cisco’s “AI for good” program supports RePlate (Connor, 2021 ) by identifying an intermediary to pick up food that otherwise would be thrown away; the intermediary then transports the food to nonprofit groups that serve food-insecure populations (Bernabe, 2022 ). Food providers, including the San Francisco International Airport and various restaurants, log details about food they have available and initiate the pick-up. The data collected by RePlate also can help these entities identify common types of waste (e.g., if they constantly have bread left over, they might order less from the bakery). Furthermore, RePlate’s site tracks the specific needs of charitable organizations, to avoid situations in which it delivers food items that the nonprofit cannot use. By tracking both push (i.e., available food items) and pull (i.e., actual demand) factors, RePlate seeks to find an optimal balance that reduces food waste.

Food Bank Singapore works with distribution entities to reroute edible food to consumers. However, a key respondent whom we interviewed noted that many of these consumers expressed dissatisfaction with the program, for two reasons. First, recipients did not have any say in what food they received. Second, the donated food was left outside of their homes, highlighting their food insecure status, with negative impacts on their self-worth. To address both issues, Food Bank Singapore installed vending machines in prominent locations (which they call Food Pantry 2.0), allowing recipients to make their own selection of food items and to retrieve them at any time that was convenient (and perhaps when others are not around).

Technology applications like Gander and RePlate encourage equity-oriented food sharing, by reducing frictions that may prevent food from being diverted from those who have surpluses, to those who are food insecure. This approach aligns with equity theory and with our prediction that in the food distribution stage, the focus is on pie sharing, and beneficial uses of technology could reduce frictions related to equity-oriented food sharing.

End consumers

Various articles explore factors that determine food waste among consumers (Appendix 2 ). For example, plate size and plate materials both exert significant impacts on consumers’ food waste; bigger plates and those made of disposable materials increase waste (Wansink & van Ittersum, 2013 ; Williamson et al., 2016 ). Situational factors also have a role; Parker et al. ( 2018 ) find that when consumers contribute to and consume collective assortments of food (e.g., potlucks), food waste is substantial. Social norms seemingly lead consumers to feel compelled to bring enough food for the entire group. But if each person brings that much food, the result is likely excessive amounts of food, much of which goes to waste. Psychological factors, such as identity-signaling motivations, also influence food waste (Block et al., 2016 ; Grewal et al., 2019 ). Consumers avoid purchasing unattractive, but perfectly edible, produce, whether because thoughts of consuming “ugly” produce undermine self-perceptions (Grewal et al., 2019 ) or because they anticipate an inferior taste. Anthropomorphism, such as displaying produce with a smiling face, can help overcome these negative perceptions, and in-store signage that refers to it as “ugly” as opposed to “imperfect” may make consumers more willing to purchase (Cooremans & Geuens, 2019 ; Mookerjee et al., 2021 ). The negative impacts of food imperfections appear to apply solely to non-processed food, such as produce (Suher et al., 2021 ), whereas for processed foods, imperfections evoke beliefs that the processing has been performed by a human, which can enhance perceptions (Parker et al., 2018 ).

Although consumers feel anxiety about wasting food, they also often over-purchase, which leads to food waste (Evans, 2012 ). At the household level, positive intentions to lower food waste and more knowledge about how to consume leftovers safely can reduce food waste (Visschers et al., 2016 ), but even if with such positive intentions and knowledge, some consumers feel unable to achieve this goal. For example, busy consumers sense insufficient time available to shop effectively, such that they cannot take an inventory before going to the store, make a shopping list, or plan meals. Others likely are unaware of options for redistributing food to others. Consumers’ mistakes related to food, despite their best intentions, can lead to waste at different steps in their consumption journey, including improper preplanning, ineffective shopping in store, improper storage or cooking, inefficient consumption, and not enough focus on suitably disposing of edible or useful food (Block et al., 2016 ; Principato et al., 2021 ).

Price promotions arguably nudge consumers to buy relatively more, which could increase food waste, leading one U.K. legislator to suggest that “supermarkets should move away from offers such as ‘buy one get one free’ to help end the ‘morally repugnant’ waste of millions of tons of food” (Guardian, 2014 ). Yet recent research challenges this assumption (van Lin et al., 2023 ), so more research is needed to determine the actual effects of price promotions.

To date, very little research has considered the potential impact of technology on end-consumers’ food waste, despite the emergence of real-world tools, such as apps that maintain inventories of consumers’ food purchases, remind them of expiration dates, and suggest recipes to use already purchased food. The Nosh app, enabled by AI, helps consumers scan barcodes and other information, then provides suitable recipe information that reflects the food expiration dates. It also offers summary information about consumers’ food buying and wasting habits (Silberling, 2021 ). Other apps connect consumers with nonprofits or other consumers that would benefit from redistributed food. On the Olio app (United Kingdom), households can register any surplus food they have, then receive prompts on their mobile devices to check their pantries and refrigerators for such items regularly. Also on this app, other users can request any posted excess food, which usually happens quickly, such that sharers get rid of unwanted clutter in their kitchens, and requestors receive ready access to available items. In the United States, Feeding America hosts an app for consumers with extra food, but the recipients in this case are local nonprofit organizations. Volunteers collect posted items and deliver them to the nearby shelter or food pantry. With another approach, the Cooklist app encourages consumers to use up the food items they have purchased by allowing them to scan their grocery receipts, then providing them with notifications of likely spoilage dates, as well as ideas for meals and recipes that feature the purchased items.

These apps focus on local, rather than a regional or global, redistribution. Thus, transportation is a persistent challenge for redistributing surplus food from consumers who likely live in higher income areas to consumers who are food insecure and often live in lower income regions. How could European consumers, for example, redistribute surplus food to African consumers in need? Some previously discussed food processing technologies (e.g., Xsense monitoring, One Third) might help address transportation challenges; partnerships of transportation firms and food redistribution technology could have significant impacts. Technology applications like Olio and Feeding America encourage equity-oriented food sharing, such that the focus is on pie sharing, and similar to the food distribution stage, beneficial uses of technology would reduce friction related to equity-oriented food sharing.

Consumers’ actual behaviors: Survey data

As mentioned in the preceding discussion, the majority of food waste occurs at the consumer stage of the food production-consumption chain, particularly in developed countries such as the United States. Therefore, a good understanding of consumer’s food waste behaviors is critical to gaining a better grasp on ways though which technology could help to reduce waste at this stage. To understand consumers’ actual food waste behaviors, we conducted a survey on Academic Prolific with 353 adult participants (M age  = 42.59 years, 47.6% men). Most respondents were in North America (United States or Canada 94.1%), but other global regions also were represented (Asia 2.3%, Europe 2%, Middle or South America 0.8%, Australia 0.3%, and 0.6% elected to not disclose). The average household size 2.66 people (SD = 1.64), and the average number of children under the age of 18 years in the house was 0.5 (SD = 0.981). Thus, the sample includes respondents both with and without younger children in the house. The survey goals were to understand consumers’ perceptions of their food waste behaviors, their awareness of and interest in using technologies to redistribute food, and their perceptions of restaurants that actively work to reduce food waste. We also sought to identify any food growing behaviors.

To determine if some factors correlate more strongly with certain food waste behaviors, we measured participants’ social consciousness (5 items, Flewelling et al., 1993 , α = 0.646), altruism (4 items, adapted from Rushton et al., 1981 , α = 0.726), technology readiness (4 items, adapted from Parasuraman & Colby, 2014 , α = 0.876), frequency of financial and time donations (1 = “never,” 7 = “very frequently”), political ideology (1 = “extremely conservative,” 7 = “extremely liberal”), and demographic information (education, income, household size, age, gender).

To start, we asked participants to describe their food disposal behaviors, including what types of food, how much typically is wasted (i.e., not consumed) in their household, and how they disposed of that food. Many participants described produce that spoiled before they had the chance to consume it: “I recently purchased a large amount of fresh fruit from a grocery store that ended up going bad before I had a chance to eat it. I had purchased a variety of apples, oranges, and grapes, but I quickly realized that I had overestimated how much I could consume before it spoilt.” Others cited diet changes or purchases of new options that they decided to try but ended up not liking, such as a participant who said, “Lately I have been trying to change my eating habits to make them healthier and I have bought healthy foods that I have not liked and have had to discard them.”

In the next section of the survey, we asked participants to rate the amount of food waste they produce (1 = “very little,” 7 = “a great deal”), how much edible and non-edible food waste they have (1 = “very little,” 7 = “a great deal”), how frequently they think about food waste (1 = “never,” 7 = “very frequently”), and how important they perceive food waste issues to be (1 = “not at all important,” 7 = “very important”). They described disposal or donation behaviors in more detail. A one-sample T-test relative to the scale midpoint (4) indicated that, overall, participants perceive that they produce a fairly small amount of food waste (M foodwaste  = 2.87; SD = 1.32; t (352) = -16.16, p  < 0.001). Regarding edible and non-edible food, a paired sample t-test reveals that they discard significantly more non-edible food (M non-edible  = 3.40; SD = 1.65) than edible food (M edible  = 1.95; SD = 1.17; t (352) = -15.904, p  < 0.001). One-sample T-tests compared with scale midpoints (4) showed that participants recognize food waste as an important issue (M important  = 5.27, SD = 1.51; t (352) = 15.864, p  < 0.001) but do not think about it frequently (M frequency  = 4.11, SD = 1.54; t (352) = 1.348, p  = 0.179). Thus, many consumers view food waste as important, but they perceive little food waste in their personal life. This self-reported measure could be inaccurate of course; their actual food waste may be higher than reported. Our survey results indicate limited opportunities to reroute food from consumers to those who are relatively more food insecure. Still, it may be useful to clarify why consumers choose to reroute edible food that otherwise would go to waste.

Therefore, we consider what consumers do with such food and identify influences on the extent to which consumers would be willing to use technology-enabled apps to reroute edible, otherwise wasted food. Most participants report that, at some point in the last month, they threw away unused food (95.5%); most of the discarded food is inedible, so this high percentage makes sense. Relatively few donated unused food (15%), and none had sold it. Among those who donated food in the past month, most provided it to people in need (directly to the person or through a food bank/charitable organization), and some donated to friends or family members. Donation boxes at their workplaces, houses of worship, or children’s schools provided sites for redistributing food; they make it convenient for people to donate, because consumers do not have to go out of their way or put in much effort and can simply drop off excess food at places they already visit regularly. This result indicates that consumers may be more likely to donate excess food if it is convenient to do so. If technology could make food donation more convenient, it might have a significant impact on the overall amount of food donated.

Two apps, Meal Connect and Cooklist, aim to reduce food waste at the consumer level by making it convenient for consumers to redistribute unwanted food. We asked about participants’ awareness of and willingness to use these two apps, including their general awareness of apps that allowed for the redistribution of unused food (1 = “not at all aware,” 7 = “very aware”) and if they had ever used such an app (yes/no). After providing descriptions of Meal Connect and Cooklist, we asked about participants’ likelihood of using each app (1 = “very unlikely,” 7 = “very likely”) and willingness to pay a monthly fee to use it (sliding scale, $0–$20).

Awareness of the apps was low. Specifically, only 2.5% of participants had used an app to redistribute unused food, and awareness was virtually nonexistent (M awareness  = 1.47, SD = 1.08, one-sample t (352) = -44.151, p  < 0.001 [scale midpoint of 4]). Once we explained the apps, they expressed low to moderate willingness to use either Meal Connect (M likleymealconnect  = 4.11, SD = 1.98, one-sample t (352) = 1.023, p  = 0.307 [scale midpoint of 4]) or Cooklist (M likleycooklist  = 3.70, SD = 2.15, one-sample t (352) = -2.628, p  = 0.009 [scale midpoint of 4]). The amount they were willing to pay for the apps also was low (M WTPmealconnect  = $1.37, SD = 2.31; M WTPcooklist  = $1.36, SD = 2.52). In essence, few people know about these apps, and once aware of them, consumers appear only somewhat willing to use them and not willing to pay for them. Thus, the greatest barriers to using technology to reduce waste and redistribute food efficiently might not be creating the technologies but rather determining how to increase awareness and usage intentions surrounding them. The value of using the app also needs to be communicated effectively to consumers. According to prior research, establishing trust between a food redistribution app and its users is another important criterion, particularly for consumers who receive the food and may face social stigma (de Almedia Oroski and da Silva 2023 ). App developers should consider these issues when creating their technology and aim to keep the identity of food recipients anonymous when possible.

We checked for individual differences that might determine the extent to which consumers would use or pay for such technology apps. According to the results of multiple regression analyses (see Table  2 ), willingness to use these apps is higher among participants who score high on social consciousness, altruism, and technology readiness, as well as people who frequently make financial, but not time, donations. Political ideology has a significant impact on willingness to use Meal Connect (not Cooklist though), such that those who identify as more liberal are significantly more likely to use it. In terms of demographic variables, neither education nor income level exerts much impact on the likelihood of using or willingness to pay for either app. Younger consumers and participants who self-report more food waste seem more likely to use and more willing to pay. These starting points signal some factors that may drive the extent to which people adopt technology-enabled apps and thus topics for further research.

Finally, a notably substantial proportion of participants, 34.6%, grow some of their own food, ranging from small herb gardens to large, dedicated plots for produce. Among those who do not grow their own food, about 71% have considered it. As is reasonable, most participants who report growing their own food live in a single-family home (83.6%). It is unclear the extent to which home-grown food can affect food insecurity, as we discuss in more detail subsequently.

Two points emerge from the preceding discussion. First, as is the case for distribution entities, the key challenge for end-consumers is reducing waste. Technology applications can assist in determining suitable orders and moving food to consumers who are food insecure (rather than being disposed of in the trash). Second, relative to end consumers, it may be more beneficial to focus on distribution entities, which deal with substantially more food that could be rerouted to consumers dealing with food insecurity.

Technology configurations that influence the food pie and stakeholders

Building on the preceding examples, we propose a 2 × 2 typology of technology applications, categorized in relation to how they affect the food pie (pie expansion vs. pie sharing) and the stakeholders (producers vs. consumers) toward which the technology is oriented. That is, technologies can be used to increase the food pie, through increased production and/or efficiency (i.e., reduced inefficiencies). They also might encourage more equitable (re)distribution of the food pie, such as by enabling food sharing with nonprofits. The focal stakeholder in the food production–consumption chain that is targeted by the technology in turn can be separated into two clusters that face distinct issues: producers, which include food processors and farmers, versus customers, which include distribution entities and end consumers (Table  3 ). By assigning technologies to this typology, we shed light on technological gaps in efforts to reduce food insecurity, loss, and waste.

In the upper left corner, Quadrant 1 relates to technologies targeted toward producers in the initial stages of the food production–consumption chain, most of which seek to increase food production by facilitating coordination, such as when Krish-e, CropIn, and One Third link producers and input entities, to increase the size of the pie. Other examples include applications like FarmPrecise, which work with producers to ensure that food is not lost due to weather or rotting, during and after harvesting. Reducing food loss in effect increases the size of the food pie. We note substantial interest in this quadrant; increased food production may increase the amount of food available to those who are food insecure.

Next, Quadrant 2 relates to technologies geared toward producers that work to enhance the equitable distribution of the food pie. As may be expected, and as Table  3 indicates, technologies in this quadrant are relatively sparse (as mentioned previously, we find that producers appear more focused on pie expansion than pie sharing in practice). Some producers sell directly to consumers through farmers’ markets or roadside stands, and technology might enable such DTC sales and increase efficiency, which could help to decrease prices for end consumers and make products more accessible. Producers often have food that they are unable to sell to retailers (e.g., “ugly,” oversupply). Technology such as apps might allow producers to redistribute these unsellable products to consumers who are food insecure, rather than letting the food go to waste. Some apps represent initiative along these lines, such as the Flashfood app that gives food producers in the United States and Canada the opportunity to send food that has been rejected by grocery stores directly to consumers in need (Bozhinova, 2018 ). Similarly, MisFits Market (United States; Central and South America) and Imperfect Foods (United States) apps work directly with producers and sell “ugly” produce (and other food items, such as meat and seafood) to consumers at deeply discounted prices in weekly subscription boxes (Richardson, 2021 ). In Indonesia, Sayurbox technology allows producers to sell directly to end consumers, which cuts intermediary costs and allows food to be sold at lower prices (Deloitte Southeast Asia Innovation Team, 2022 ). These examples imply that producers might be more directly involved in the equitable distribution of food, but these technology interventions seem less likely to move the needle, in terms of feeding those who are food insecure.

In the upper right of Table  3 , Quadrant 3 includes technologies that enable customers to expand the food pie. This quadrant is sparsely populated; because consumers and distributors focus more on pie sharing, they seem less motivated to increase the size of the global food pie. An exception might pertain to end consumers interested in gardening, as an attempt to produce some food. Apps that help end consumers increase the foods they grow fall into this quadrant (Dove, 2022 ). The Seed to Spoon app uses GPS locations to help consumers determine which vegetables, fruits, or herbs can grow in their region, then alerts them to regional pests and diseases (to reduce inefficient production). Similarly, Moon & Garden uses phases of the moon, together with weather information, to advise consumers on “next day care” for their gardens that can increase production and harvests. Distributors are typically not involved in the production of food, so technologies in this quadrant focus primarily on end consumers.

Quadrant 4, in the lower right corner of Table  3 , relates to technologies that enable customers to support more equitable distributions of the food pie, including the Olio and Feeding America apps, which maintain listings of consumers with food surpluses, then connect them with nonprofits or other consumers to redistribute excess food before it spoils. Distributors also might use technology-enabled apps to make connections with charities, homeless shelters, and other organizations in need of the food, which reduces the amount of food discarded. With the Gander app, Irish retailers assign steep discounts to food approaching its expiration date, making such foods especially appealing to food-insecure populations. All these technology applications help reduce frictions that pose barriers to equity-based food redistribution. We also highlight the substantial interest in this quadrant. Customers are fairly motivated to share edible, to-be-wasted food with those who are food insecure. Our expectation, based on our interviews and survey, is that more benefits would accrue from focusing on distribution entities like retailers and restaurants, which have relatively more food surpluses that can be shared. Because such a large percentage of food waste involves consumers and retailers, the applications listed in this quadrant are especially important for efforts to reduce food insecurity and waste.

The contrast between quadrant 1 versus quadrant 4 is stark. Noting that in developing countries, the focus is more on “expanding the food pie”, and so the technology initiatives in quadrant 1 relate substantially to those in developing countries. Over time, as AI advances and the cost of prediction is further reduced, the application and impact of these technology initiatives will only increase. In contrast, noting that in developed countries, there are benefits to better “share the – already large – food pie”, the technology initiatives in quadrant 4 relate substantially to those in developed countries.

Research and practice agenda

Many questions related to food expansion and the equitable redistribution of food remain unanswered. We outline some of these questions, organized by quadrants in the 2 × 2 typology from Table  3 . The proposed research agenda is summarized in Table  4 .

Quadrant 1: Technology oriented toward producers to expand the food pie

The key challenges in Quadrant 1 include how to produce relatively more or higher quality crops, holding the inputs fixed, and then how to reduce waste during the crop production process. This area has received relatively substantial research interest, especially with a practice focus, and various investment and technology firms focus on developing relevant solutions. These (non-trivial) efforts continue, reflecting the challenges related to the underlying technology and also organizational issues (e.g., how to get smaller farms to digitize operations). And then the critical issue is how to further expand application of, and access to, these technology inittaives; the advance of AI may well be key to this point.

Beyond coordination issues, other topics of interest relate to efficiency, equity, and ethics. For example, researchers could address how to achieve better (AI-driven) predictions of crop growth, pestilence, and containment; distinguish the impact of offering some farmers access to extreme productivity, while other farmers lack such access; and consider potential issues with creating disease-resistant crops in outer space, albeit with potentially unforeseen side effects.

Quadrant 2: Technology oriented toward producers for more equitable distribution of the food pie

This quadrant is sparsely populated; most technology applications relating to producers focus on pie expansion. As indicated by Tables 2 and 3 , very little academic literature focuses on such issues. Because food producers typically seek to expand the food pie, continued research might examine which types of producers are relatively more open to working with consumers who are food insecure. To motivate producers, local, state, or national (government) incentives might be needed. Research should identify which aspects of such programs effectively encourage and incentivize producers to engage in alternative distribution for some portions of their crops.

Quadrant 3: Technology oriented toward customers to expand the food pie

This quadrant is also sparsely populated, challenged by the reality that customers typically are not involved in food production or determining the size of the food pie. Even if some consumers grow food, this effort typically constitutes only a small fraction of total food needs. Still, these activities appear to be gaining in popularity. Covington ( 2022 ), describing the growing trend of urban farming, notes that “if you live in a city, chances are the topic of urban farming has come up once or twice in conversation or at community meetings. These small, but larger than a home garden sites have become a popular way for communities to bring fresh produce, eggs, and meat to the people living around them.” Urban farms tend to appear in shared spaces in apartment complexes, such as rooftop gardens or vertical farming approaches.

We envision two main impacts of technology in this quadrant. First, it might function as an enabler that helps consumers who already have chosen to grow their own food, by providing them with incisive, suitable information. For example, Gardroid targets novice consumers, with little experience growing vegetables, providing them with step-by-step guidance related to various aspects (e.g., how many days before the plant is ready, spacing between plants, which types of plants harmonize). Academic research has started to consider the effects of increased consumer production, but continued research is important to determine how to expand the impact of current technologies and which other technologies are needed. Emerging technologies like virtual reality might help promote urban farming; Parikh et al., ( 2022 , p. 1) argue that virtual reality platforms can “support farmer knowledge transfer and innovation that transcend the physical constraints of traditional agricultural extension based on on-farm demonstrations.”

Second, technology might inspire or motivate more consumers to engage in growing food, such as inspirational communications that trigger goals (Grewal et al., 2023 ) or gamification. The survey revealed that approximately one-third (34.6%) of respondents currently grow food; among those who did not, 71% had considered it, signaling strong interest among consumers. Research is needed to identify the most effective ways to motivate these consumers to engage in growing practices. Further research also might define optimal forms of inspirational content for specific target segments. In addition, gamification studies could define which games best encourage people to grow their own food, in line with Kawazoe et al.’s ( 2021 ) description of a gamification platform for urban vegetable gardens.

Such considerations also might extend farther across the production–consumer chain. Retailers like Whole Foods already source local produce from local farms, so tactics that increase overall food production by such local farms could have expanded benefits. Some restaurants grow their own food (e.g., farm-to-table restaurants), so the technology we note previously could facilitate their efforts too. Tender Greens, a fast-food chain in Southern California, grows much of its own produce (strawberries, squash, bell peppers) in on-site vertical gardens (Peters, 2015 ). Rosemary’s, an Italian restaurant in New York City, has a rooftop farm that grows both produce and herbs (Durrani, 2016 ). Despite the extensive potential benefits of growing their own food, including a larger food pie and potentially diminished costs, few restaurants adopt this practice, perhaps due to anticipated difficulties or resources (i.e., time) needed. Technologies that enhance restaurants’ capabilities to increase their own food production in convenient ways thus could be very beneficial.

Quadrant 4: Technology oriented toward customers for more equitable distribution of the food pie

In this quadrant, we note four main challenges, related to (1) motivating customers to share food, (2) reducing frictions related to sharing food (perhaps the most important point), (3) making sharing more acceptable to consumers who are food insecure (i.e., recipients), and (4) evoking behavioral changes by motivating customers to modify their consumption practices to waste less food. As Tables 2 and 3 reveal, much prior research has focused on issues related to this quadrant, but very little has considered the impact of technology. Because most food waste occurs here, it is crucial to find ways to influence food waste at this stage of the chain.

First, we largely have assumed that intermediaries and consumers are motivated to provide access to their unused or surplus food to others who need it. We find evidence in support of this assumption from our survey, at least among end consumers. Their motivations could stem from societal norms or public relations benefits. But we need a better, perhaps more nuanced, understanding of the key drivers of actors’ willingness to route food that otherwise would be wasted to consumers struggling with food insecurity. A key question relates to differences in their willingness to pay any costs incurred to share food. Even if consumers appear motivated to share surplus food, they likely do not want to incur costs to do so. Our survey indicates very low willingness to pay for food redistribution apps, which presents a challenge for organizations that are trying to develop such apps. Further research should identify ways to communicate the added value of these apps, in ways that can motivate consumers to be willing to pay more.

Second, we need research to determine how technology might be leveraged to reduce frictions related to sharing food, for both entities like restaurants and individual consumers. A key source of friction relates to matching unused food with consumers who need it. Apps like Olio and MealConnect facilitate such connections for local populations. For end consumers, especially those with relatively little surplus food, the benefits of using technology apps are relatively lower. That is, they incur greater per unit costs to transfer food, as well as lesser costs of having food go waste. As such, trying to increase the benefits of using these apps (relative to the costs of using them) might help nudge both restaurants and individual consumers to use them. A recent study with blood donors offers some potential insights: When blood donors receive messages that thank them for their donations and also indicate that their blood had been delivered to a patient in need that day, it increased their likelihood to donate blood in the future by enhancing their relationship investment and relationship quality perceptions toward the blood donation service (Shehu et al. 2024 ). Similarly, food donation apps might alert food donors when a recipient receives their donation. The relationship investment and quality perceptions of the app in turn could increase among users, such that the benefits of donating start to outweigh the costs of using the app. We call for research into whether these types of messages can nudge various entities to use food redistribution apps.

Third, consumers may value food access in general, but how people receive food matters. As noted previously, Food Bank 2.0 represents a technology-driven solution for sharing food in ways that help food recipients preserve their sense of dignity (e.g., neighbors do not know that the food has been donated) and retain their choice (e.g., choose which foods they receive and reject, even if all the food is free). Further research could clarify how technology might help expand such applications.

Fourth, we need research insights into potential ways to nudge customers toward behaviors that involve less waste—both for business customers like restaurants and individual consumers. Reduced waste requires accurate predictions of consumption rates, as well as demand among food-insecure populations. Such predictive abilities must be precise with regard to both the quantity and types of food (e.g., demand for protein versus carbs). Food apps like Nosh and Cooklist represent initial attempts to provide suitable information that can change behaviors. Noting the powerful capacities of AI (Davenport et al., 2021 ; Guha et al., 2021 , 2023 ), we call for research into effective deployments of AI-powered apps to predict usage and demand, which in turn identify behaviors to help reduce food waste. Research into food journeys for consumers and distribution customers also could define the stage of the food journey (e.g., pre-shopping, in-store, storage, cooking, food consumption) in which waste is most prevalent.

As an initial gauge of the impact of efforts to reduce food waste at an entity (i.e. restaurant/retailer) level, we asked survey participants whether knowing that a restaurant or retailer was actively working to reduce food waste would affect their likelihood of visiting it (1 = “less likely to visit,” 7 = “more likely to visit”) and willingness to pay (1 = “less likely to pay a slightly higher price,” 7 = “more likely to pay a slightly higher price”). The one sample t-tests (scale midpoints at 4) revealed that participants were more likely to visit a restaurant/retailer that was working to reduce food waste (M likely  = 5.66, SD = 1.17, t (352) = 26.62, p  < 0.001) and even willing to pay slightly higher prices (M likelyWTP  = 4.90, SD = 1.33, t (352) = 12.682, p  < 0.001). Thus, efforts focused on reducing food waste seemingly can enhance consumer perceptions of the distribution entities. Examining this point and its implications would provide helpful insights.

As noted previously, some apps, such as Too Good to Go, allow restaurants to sell surplus food to consumers at discounted prices at the end of the business day. These apps have been popular (Too Good to Go has 5 million users and nearly 11,000 restaurants on the app) and offer great potential to decrease food waste. Yet consumers also have reported issues with these apps, which could undermine their perceptions and potentially lead consumers to view the technologies as merely “greenwashing” attempts (rather than meaningful efforts to decrease food insecurity). For example, one user reported that after using the app to order from a local smoothie shop, she encountered a rude employee who had no idea what she was talking about when she went to pick up her meal (Martichoux, 2021 ). The user noted that Too Good to Go immediately issued a refund and seemed prepared to deal with this issue, potentially because it is common. For these apps to be truly effective in reducing food waste, restaurants (and their stakeholders) must understand how to leverage the apps and establish effective processes to serve consumers who are food insecure.

Finally, straddling multiple quadrants is the issue of local versus regional impact. Many of the technology applications we have described offer local impacts, largely due to the very nature of food industries that invariably must deal with perishability concerns and transport cost concerns. On the producer side, technology solutions such as CropIn can be applied globally, and it already operates across farmlands in Asia and Africa, but the benefits are local. That is, it helps increase food production in certain areas but has virtually no impact in regions where CropIn is not being deployed. On the customer side, similarly, technology applications can be deployed globally, but the impact is relatively local. The Olio technology solution is available in the United Kingdom and Singapore, but when deployed in the United Kingdom, it only helps U.K. consumers who are food insecure, without affecting consumers in Singapore. Two implications emerge. First, even if the impacts are local, the technology-related and platform-related learnings one derives may then apply across countries, implying indirect regional impact. Second, we need additional research to find ways to address food insecurity at a regional (and ultimately global) level. As an initial conjecture, we propose that such issues are less about technology, and more about food transfers across regions, which implies political and interorganizational considerations.

With this article, we seek an in-depth understanding of the crucial role of technology, and notably AI, in fighting food loss and waste at every level of the food value chain, while also helping redistribute any unused food to consumers who are relatively food insecure. We introduce a 2 × 2 typology to illustrate how existing technologies influence the food pie (pie expansion vs. pie sharing) and which stakeholders (customers vs. producers) the technology targets. In line with this framework, we outline a research agenda for how technology might affect the full production–consumption value chain, with a view to increasing or redistributing the food pie, and with the goal of better serving people who are relatively food insecure. We hope this article and the ideas put forth stimulate further research into the role of technology as it relates to the UN’s SDGs 2 and 12, regarding sustainable food production and consumption patterns and the goal of zero hunger.

Data Availability

Results available upon request.

We focus on food production pertaining to agriculture, as opposed to livestock or aquaculture.

Appendix 1 provides more details about the discussions with key respondents.

Agrawal, A., Gans, J., & Goldfarb, A. (2018). A simple tool to start making decisions with the help of AI (pp. 2–7). Harvard Business Review.

Anderson, J. C., & Narus, J. A. (1990). A model of distributor firm and manufacturer firm working partnerships. Journal of Marketing, 54 (April), 42–58.

Article   Google Scholar  

Azevedo, C. (2021). Addressing food waste plays a role in ending hunger . Rise Against Hunger.

Belfasttelegraph.com (2022). Gander app helps retailers address food waste at store level . Belfast Telegraph.

Bernabe, D. (2022). How A.I. technologies could help resolve food insecurity . Fortune .

Beyer, L. (2022). Taranis named Planet Labs PBC’s agricultural partner of the year . PR Newswire.

Block, L. G., Punam, K. A., Vallen, B., Williamson, S., Birau, M. M., Grinstein, A., Haws, K. L., LaBarge, M. C., Lamberton, C., Moore, E. S., Moscato, E. M., Reczek, R. W., & Tangari, A. H. (2016). The squander sequence: Understanding food waste at each stage of the consumer decision-making process. Journal of Public Policy & Marketing, 35 (2), 292–304.

Bozhinova, K. (2018). 16 apps helping companies and consumers prevent food waste . GreenBiz.

Brown, A. G., Esposito, L. E., Fisher, R. A., Nicastro, H. L., Tabor, D. C., & Walker, J. R. (2019). Food insecurity and obesity: Research gaps, opportunities, and challenges. Translational Behavioral Medicine, 9 (5), 980–987.

Buzby, J. C., Wells, H. F., & Hyman, J. (2014). The estimated amount, value, and calories of postharvest food losses at the retail and consumer levels in the United States . United States Department of Agriculture.

Connor, E. (2021). Cisco data scientists work with nonprofit partner Replate to improve food recovery and delivery to communities in need . Cisco Blogs.

Cooremans, K., & Geuens, M. (2019). Same but different: Using anthropomorphism in the battle against food waste. Journal of Public Policy & Marketing, 38 (2), 232–245.

Covington, L. (2022). What is urban farming ? The Spruce Eats.

Davenport, T., Guha, A., & Grewal, D. (2021). How to design an AI marketing strategy: What the technology can do today—and what’s next. Harvard Business Review, 99 (July-August), 42–47.

Google Scholar  

de Almeida Oroski, F., & da Silva, J. M. (2023). Understanding food waste-reducing platforms: A mini-review. Waste Management & Research, 41 (4), 816–827.

Deloitte Southeast Asia Innovation Team (2022). The future of agrifood tech in Southeast Asia: Agriculture in the digital decade . KrASIA.

Dove, J. (2022). The best gardening apps for 2022 . Digital Trends.

Durrani, S. (2016). 6 restaurants that pick the food right from their own garden . Business Insider .

Dwyer, F. R., Schurr, P., & Oh, S. (1987). Developing buyer-seller relationships. Journal of Marketing, 51 (April), 11–27.

Eastwood, C., Ayre, M., Nettle, R., & Rue, B. D. (2019). Making sense in the cloud: Farm advisory services in a smart farming future. NJAS–Wageningen Journal of Life Sciences , 90–91. https://doi.org/10.1016/j.njas.2019.04.004 (December, 10009298. Retrieved September 3, 2023 from).

Etherington, D. (2019). Volocopter and John Deere team up for a crop-spraying autonomous agricultural drone . Tech Crunch.

Evans, D. (2012). Beyond the throwaway society: Ordinary domestic practice and a sociological approach to household food waste. Sociology, 46 (1), 41–56.

Farmer Jones Farm. (2023). Vegetable Boxes . Farmer Jones Farm.

Flewelling, R. L., Paschall, M. J., & Ringwalt, C. L. (1993). SAGE Baseline Survey . Research Triangle Park, NC: Research Triangle Institute.

FoodPrint. (2018). The problem of food waste . Food Print.

Global Agriculture (2019). FAO: 14% of the world’s food is lost between harvest and retail . Global Agriculture.

Grand View Market Research. (2023). Farming as a service. Market size, share & trends analysis report by service type (farm management solutions, production assistance, access to markets), by delivery model, by end user, by region, and segment forecasts, 2023–2030 . Market Analysis Report .

Grewal, L., Hmurovic, J., Lamberton, C., & Reczek, R. W. (2019). The self-perception connection: Why consumers devalue unattractive produce. Journal of Marketing, 83 (1), 89–107.

Grewal, D., Ahlbom, C.-P., Noble, S. M., Shankar, V., Narang, U., & Nordfält, J. (2023). The impact of in-store inspirational (vs. deal-oriented) communication on overall sales: The importance of activating goal-completion mindsets. Journal of Marketing Research, 60 (6), 1071–1094.

Gruber, V., Holweg, C., & Teller, C. (2016). What a waste! Exploring the human reality of food waste from the store manager’s perspective. Journal of Public Policy & Marketing, 35 (1), 3–25.

Guardian. (2014). Buy-one-get-one-free offers ‘should be scrapped to cut food waste’ . The Guardian.

Guha, A., Grewal, D., Kopalle, P. K., Haenlein, M., Schneider, M., Jung, H., Moustafa, R., Hegde, D. R., & Hawkins, G. (2021). How artificial intelligence will affect the future of retailing. Journal of Retailing, 97 (1), 28–41.

Guha, A., Bressgott, T., Grewal, D., Mahr, D., Wetzel, M., & Schweiger, E. (2023). How artificiality and intelligence affect voice assistant evaluations. Journal of the Academy of Marketing Science, 51 (2), 843–866.

Gunia, A. (2021). This startup founder’s AI-powered garbage cans are helping to reduce food waste-and improve bottom lines . Time.

Gustafson, S. (2022). Global food insecurity hits all-time high: 2022 Global Report on Food Crises released . Food Security Portal.

Heide, J. B., & John, G. (1992). Do norms matter in marketing relationships? Journal of Marketing, 56 (April), 32–44.

Jackson, T. (2016). Could tech reduce food waste and help feed the world ? BBC.

Jap, S. D. (1999). Pie-expansion efforts: Collaboration processes in buyer–supplier relationships. Journal of Marketing Research, 36 (4), 461–475.

Jap, S. D. (2001). ‘Pie sharing’ in complex collaboration contexts. Journal of Marketing Research, 38 (1), 86–99.

Kaizhi, L. (2022). Sowing seeds of food security . China Today .

Kallbekken, S., & Sælen, H. (2013). ‘Nudging’ hotel guests to reduce food waste as a win-win environmental measure. Economic Letters, 119 (3), 325–327.

Kaplan, D. A. (2018). 4 direct-to-consumer models shifting the supply chain . Supply Chain Dive.

Kawazoe, M. T., Lauer, A. G., & Silva, N. B. F. (2021). UrbanVG: A gamification encouraging urban vegetable garden platform. 2021 IEEE Symposium on Computers and Communications (ISCC) , Athens, Greece, pp. 1–6.

Kim, M. J., & Hall, C. M. (2020). Can sustainable restaurant practices enhance customer loyalty? The roles of value theory and environmental concerns. Journal of Hospitality and Tourism Management, 43 (June), 127–138.

Kontzer, T. (2021). Unstung heroes: Startup’s AI-powered tomato pollinator gives bees a break . Nvidia.

Lumpkin, G. T., & Dess, G. G. (2001). Linking two dimensions of entrepreneurial orientation to firm performance: The moderating role of environment and industry life cycle. Journal of Business Venturing, 16 (5), 429–451.

Martichoux, A. (2021). App lets you buy leftover restaurant food. Is it worth it ? Newsnation .

Martin-Rios, C., Demen-Meier, C., Gössling, S., & Cornuz, C. (2018). Food waste management innovations in the foodservice industry. Waste Management, 79 , 196–206.

Mohan, C. (2020). VoloDrone, the futuristic drone for agricultural use . Krishi Jagran.

Mookerjee, S., Cornil, Y., & Hoegg, J. (2021). From waste to taste: How ‘ugly’ labels can increase purchase of unattractive produce. Journal of Marketing, 85 (3), 62–77.

Moran, C. D. (2023). 6 notable tech updates from the National Retail Federation’s 2023 show . Grocery Dive .

Parasuraman, A., & Colby, C. (2014). An updated and streamlined technology readiness index: TRI 2.0. Journal of Service Research, 18 (1), 1–16.

Parikh, T., Egendorf, S. P., Murray, I., Jamali, A., Yee, B., Lin, S., Cooper-Smith, K., Parker, B., Smiley, K., & Kao-Kniffin, J. (2022). Greening the virtual smart city: Accelerating peer-to-peer learning in urban agriculture with virtual reality environments. Frontiers in Sustainable Cities, 3 (February), 1–7.

Parker, J. R., Umashankar, N., & Schleicher, M. (2018). How and why the collaborative consumption of food leads to overpurchasing, overconsumption, and waste. Journal of Public Policy & Marketing, 38 (2), 154–171.

Peters, A. (2015). This Hollywood restaurant grows your food next to your table . Fast Company .

Pinto, R. S., dos Santos Pinto, R. M., Melo, F. F. S., Campos, S. S., & Cordovil, C. M. D. S. (2018). A simple awareness campaign to promote food waste reduction in a university canteen. Waste Management, 76 , 28–38.

Pixel Scientia (2023). Measuring the natural world with Kevin Lang from Agerpoint . Pixel Scientia Labs.

Principato, L., Pratesi, C. A., & Secondi, L. (2018). Towards zero waste: An exploratory study on restaurant managers. International Journal of Hospitality Management, 74 (August), 130–137.

Principato, L., Mattia, G., Di Leo, A., & Pratesi, C. A. (2021). The household wasteful behavior framework: A systematic review of consumer food waste. Industrial Marketing Management, 93 , 641–649.

Pultarova, T. (2022). How China is creating new foods in space . BBC.

Recycle Track Systems. (2023). Food waste in America in 2023 . Recycle Track Systems.

Richardson, K. (2021). These apps aim to reduce the social and environmental impacts of food waste . Shareable.

Rushton, J. P., Chrisjohn, R. D., & Fekken, G. C. (1981). The altruistic personality and the self-report altruism sale. Personality and Individual Differences, 1 , 292–302.

Sakaguchi, L., Pak, N., & Potts, M. D. (2018). Tackling the issue of food waste in restaurants: Options for measurement method, reduction, and behavioral change. Journal of Cleaner Production, 180 (April), 430–436.

Senthilingam, M. (2017). The tech solutions to end global hunger . CNN.

Sharma, S. (2019). How artificial intelligence is revolutionizing food processing business ? Medium.

Shehu, E., Veseli, B., Clement, M. & Winterich, K. (2024). Improving blood donor retention and donor relationships with past donation use appeals. Journal of Service Research, 27(3), 346–363.

Shu, C. (2022). Agritech company CropIn launches its cloud platform to digitize the agricultural industry . Tech Crunch.

Silberling, A. (2021). Nosh uses AI to help people and businesses cut down on their food waste . Tech Crunch.

Suher, J., Szocs, C., & van Ittersum, K. (2021). When imperfect is preferred: The differential effect of aesthetic imperfections on choice of processed and unprocessed foods. Journal of the Academy of Marketing Science, 49 , 903–924.

U.S. Department of Agriculture. (2023). Food Waste FAQs . USDA. https://www.usda.gov/foodwaste/faqs

U.S. Department of Agriculture’s Economic Research Service. (2010). Food Loss . USDA. https://www.ers.usda.gov/data-products/food-availability-per-capita-data-system/food-loss

UNWFP. (2021). 8 facts to know about food waste and hunger . UNWFP.

van Lin, A., Aydinli, A., Bertini, M., van Herpen, E., & von Schuckmann, J. (2023). Does cash really mean trash? An empirical investigation into the effect of retailer price promotions on household food waste. Journal of Consumer Research, 50 (3), 1–20 .

Visschers, V. H. M., Wickli, N., & Siegrist, M. (2016). Sorting out food waste behaviour: A survey on the motivators and barriers of self-reported amounts of food waste in households. Journal of Environmental Psychology, 45 (March), 66–78.

Vizzoto, F., Testa, F., & Iraldo, F. (2021). Strategies to reduce food waste in the foodservices sector: A systematic review. International Journal of Hospitality Management, 95 , 1–10.

Walster, E., Walster, G. W., & Berscheid, E. (1978). Equity: Theory and Research . Allyn and Bacon.

Wansink, B., & van Ittersum, K. (2013). Portion size me: Plate-size induced consumption norms and win-win solutions for reducing food intake and waste. Journal of Experimental Psychology: Applied, 19 (4), 320–332.

Williamson, S., Block, L. G., & Keller, P. A. (2016). Of waste and waists: The effect of plate material on food consumption and waste. Journal of the Association for Consumer Research, 1 (1), 147–160.

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Department of Marketing, Babson College, Babson Park, MA, 02457, USA

Dhruv Grewal

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Stephanie M. Noble

Tecnológico de Monterrey, Mexico City, Mexico

Darla Moor School of Business, University of South Carolina, Columbia, SC, USA

Abhijit Guha

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Grewal, D., Guha, A., Noble, S.M. et al. The food production–consumption chain: Fighting food insecurity, loss, and waste with technology. J. of the Acad. Mark. Sci. (2024). https://doi.org/10.1007/s11747-024-01040-x

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  5. Best Tourist places to visit in Leh City , Ladakh || Leh explore complete tour and guide

  6. Tourism's Invisible Burden

COMMENTS

  1. Consumer behaviour in tourism: Concepts, influences and opportunities

    There are important minority groups within society whose diverse tourism consumption patterns and needs are still under-researched, thereby hindering effective marketing; however the situation in some segments has been improving. For example, there is growing interest in understanding the travel behaviour (and constraints) ...

  2. Changes in Consumption Patterns of Tourists After the COVID ...

    Henceforth, tourist consumption patterns will also change, as tourists are resilient and will adapt their behaviour to travel safely. It is important for destinations to rethink and redesign travel journeys and experiences in light of the proposed changes in tourist behaviour. Accurate information should be provided to potential visitors ...

  3. JTAER

    The COVID-19 pandemic has entailed an unprecedented health crisis with significant economic impacts in many sectors worldwide. The tourism sector has been one of the most affected, with significant impacts on the number of cancelled reservations, a decrease in international travel and changes in consumption behaviour. This study aims to analyse the main changes in promotion and marketing in ...

  4. Full article: Tourist Consumption Behavior: An Unsolved Puzzle

    The Special Issue Articles. The present special issue on tourist consumption behavior: An unsolved puzzle is planned to grow acquaintance concerning tourist behavior's critical facets. Though several global publications highlighting consumers' preferences, behavior, and traits, this special issue further enriches this emerging body of knowledge.

  5. "Are We There Yet?": Mindful Consumption and Tourist ...

    The shifts in tourist behavior and consumption patterns of tourism goods and services can be primarily attributed to the increased awareness among tourists (Lee et al., 2021). Tourist awareness improves the tourism sector, the environment, and local communities.

  6. Understanding the Relationship Between Tourists' Consumption Behavior

    The willingness of tourism consumption substitution: ... tourists' personal sustainable consumption behavior pattern will also change. Since this is a dynamic game process, it is also one of the research limitations of this study; one of its hidden assumptions is that it treats the willingness of tourists to engage in sustainable consumption ...

  7. PDF Changes in Consumption Patterns of Tourists After the COVID ...

    e impact on the tourism industry is colossal worldwide; however, on the demand side, some changes are taking place in consumer behaviour, entailing changes in the consumption patterns in the years to come, and will shape a new consumer, even after the COVID-19 pandemic disap-pears. New words and habits have become part of everyone's life, as the

  8. Unveiling the Untapped Potential of Green Consumption in Tourism

    This paper aims to systematically review the existing literature to better understand multiple, complex facets of green consumption behaviour in the tourism sector and identify areas for future research. This review followed the PRISMA approach and analysed 92 studies published between 2009 and 2023 in high-impact journals. The present systematic review of scholarly studies on green ...

  9. Tourist Perception of the Value of Time on Holidays: Implications for

    In the context of environmentally sustainable tourism, time-saving technologies have implications for tourist travel behavior and patterns of tourist activities at a destination. Becker (1965) argues that technology has improved the productivity of time and this in turn may influence the reallocation of time toward further consumption.

  10. Consumer behaviour in tourism: Concepts, influences and opportunities

    We examine the development of and scope for future research on nine key concepts, including decision-making, values, motivations, self-concept and personality, expectations, attitudes, perceptions, satisfaction, trust and loyalty. We then examine three important external influences on tourism behaviour, technology, Generation Y and the rise in ...

  11. SDG 12: Ensuring sustainable consumption and production patterns in tourism

    One such partner is the One Planet network, helping to support partners accelerate the shift to sustainable consumption and production patterns across sectors - outlined in SDG 12 - through a global trust fund. There is a particular and clear connection between Goal 12 and tourism.

  12. PDF Table of Contents

    Table of Contents. Through March 2024, consumer spending on travel remains strong, and passenger traffic has soared1. New patterns and trends have emerged in travel related areas such as supply-demand and consumer habits. To further strengthen the growth of the tourism market, and achieve high-quality and sustainable development, the World ...

  13. Economics of tourist's consumption behaviour: Some evidence from

    Summary and conclusion. This paper seeks to analyse tourist consumption behaviour from an economics perspective, using consumption data of landed tourists from New Zealand, the UK, the USA and Japan in Australia. The results show that, overall, there are wide variations in consumption patterns among tourists from the four countries.

  14. The global pattern of tourism demand

    ABSTRACT. The chapter begins with an overview of how global tourism demand has grown from 1950 to the present day. The focus is on the pattern of inbound and outbound tourism across the world in the five regions that have been defined by the United Nations World Tourism Organisation. The main factors which influence the pattern of global ...

  15. Consumer Behavior in e-Tourism

    Abstract. Tourism scholars have extensively investigated tourists' behavior; from motivations to actual choices and consumption patterns, the way tourists behave has relevant implications for theory and practice. In e-Tourism, consumer behavior encompasses the wide range of tourists' behaviors supported by technologies and happens at ...

  16. PDF Changes in Consumption Patterns and Tourist Promotion after the COVID

    as our consumption patterns [20]. The pandemic gave rise to a new and fundamental dimension in the tourism product: health security [21-24]. In other words, exposure to COVID-19 and the risk of contagion must be minimal in the consumption and production of tourist activity. In their study, Campbell et al. [25] warn of different threats derived

  17. Habitus, Capital, and Patterns of Taste in Tourism Consumption:

    Investigating tourism consumption within Bourdieu's empirical paradigm, this article explores the development of a model of sociological choice in tourism consumption. ... Habitus, Capital, and Patterns of Taste in Tourism Consumption: A Study of Western Tourism Consumers in India. Rafiq Ahmad View all authors and affiliations. Volume 38 ...

  18. Tourists' Expenditure Behaviour: The Influence of Satisfaction and the

    Alegre J., Pou L. (2004), 'Micro-economic determinants of the probability of tourism consumption', Tourism Economics, Vol 10, No 2, pp 125-144. ... 'Visitation of tourism attractions and tourist expenditure patterns - repeat versus first-time visitors', Asia Pacific Journal of Tourism Research, Vol 1, No 1, pp 61-68. Crossref.

  19. Determinants of Chinese households' tourism consumption: Evidence from

    Further, the level of tourism consumption is presumably shaped by objective and subjective factors (Wang & Davidson, 2010). Plog suggested incorporating psychological dimensions because they can convey an individual's internal workings. Including these factors is indispensable to a clear understanding of tourists' consumption patterns.

  20. Baseline Report on the Integration of Sustainable Consumption and

    Advancing sustainable consumption and production (SCP) patterns is therefore essential if the sector is to contribute effectively to sustainable development. UNWTO and UN Environment embarked on this research project with the objective to gain insights on the much needed integration of SCP into tourism policies.

  21. Understanding energy consumption patterns of tourist attractions and

    Also, the skewed shape of the sample distribution might be due to the aggregation of very different sub-categories. A closer examination of the sub-categories reveals more distinct energy consumption patterns in terms of energy use per tourist (Fig. 2). Download : Download full-size image; Fig. 2.

  22. Land

    Community-based tourism (CBT) aims to offer responsible travel to natural areas, conserving the environment, sustaining local communities' well-being, and promoting environmental and cultural education. The long-term sustainability of CBT depends on its ability to enhance local livelihoods while protecting natural landscapes. For the Kamoro indigenous tribe in Papua, Indonesia, CBT offers a ...

  23. Tourism Consumption

    Consumption is widely considered as an indicator of status and identity and as a means of social discrimination (Sharpley, 2002: 316; Gabriel and Lang, 2006: 37); thus, tourism consumption can also be considered as a means of displaying the identity, standing out in a group, or adapting oneself to a group.

  24. (PDF) Changes in Consumption Patterns and Tourist Promotion after the

    The tourism sector has been one of the most affected, with significant impacts on the number of cancelled reservations, a decrease in international travel and changes in consumption behaviour ...

  25. China's Consumer Spending Shifts to Services Over Goods in 'Experience

    Betting on a tourism revival, he wound down a production line making metal bars in 2021 and shifted investment to producing container-sized cabins, often used as guest houses.

  26. Tailings storage facilities, failures and disaster risk

    Mining generates 13 billion tonnes per year of potentially toxic wet slurry waste, called tailings, commonly deposited in tailings storage facilities (TSF). Since 1915, 257 TSF failures have ...

  27. The food production-consumption chain: Fighting food ...

    The UN's Sustainable Development Goal (SDG) 12 seeks to achieve sustainable food production and consumption, including reduced food loss and waste; SDG 2 proposes the goal of zero hunger. In pursuit of these goals, technology arguably has a central role, at every level of the food value chain. To establish this role, the authors identify and examine current technologies aimed at increasing ...