1. Introduction
As early as 4500 years ago, humans already knew how to use pesticides in order to prevent pest damage to their crops, the earliest documented instance of pest control being Sumerians’ use of sulfur compounds to get rid of harmful insects. Alternative, non-chemical approaches were pursued in ancient times too. Around 1200 BC, the Chinese were already using predatory ants to protect citrus groves from caterpillars and woodboring beetles. Further, the ancient Egyptians relied upon assembling lines of human drovers in order to repeal locust swarms.
Pesticides may be defined as chemical substances, biological agents (such as viruses or bacteria), antimicrobials and disinfectants that can be used against pests with the purpose of protecting crops from decreases in yield or quality [
1]. The efficient use of pesticides has ancillary benefits that include saving time and manpower [
2,
3]. Besides, pesticide use is sometimes the only feasible way of suppressing insect vectors spreading prevalent diseases. For instance, Ross [
4] pointed out that DDT has been shown, over the past 60 years, to be one of the very few affordable and effective tools against malaria-transmitting mosquitoes. Additionally, the use of insecticide-treated bed nets has been observed to lead to a decrease in the incidence of malaria infection and in infant mortality, as shown for instance in Lindblade et al. [
5].
However, while the benefits of pesticide use include higher crop yields and mitigating the spread of vector-borne diseases, their downsides include the accumulation of toxic residues in food products. In 2016, the U.S. Department of Agriculture reported that pesticide residues exceeding tolerance levels set forth by the U.S. Environmental Protection Agency were detected in 0.46 percent (48 samples) of the total samples tested (10,365 samples). In 2006, Lu et al. [
6] had measured dietary exposure to organophosphorus in a group of 23 elementary-school-age children through urinary biomonitoring and found that the median urinary concentrations of the specific metabolites for malathion and chlorpyrifos decreased to non-detectable levels immediately after the introduction of organic diets, and remained so until the conventional diets were reintroduced. Other studies have established that prolonged exposure to pesticides is associated with serious health problems such as respiratory problems, memory disorders, dermatological conditions [
7], depression, neurological deficits [
8], miscarriages and birth defects [
9].
There is now overwhelming evidence that pesticide residue buildup leads to undesirable environmental side effects. A quantitative analysis designed to predict amounts of pesticides that would reach surface waters has been conducted in the U.S. as early as the 1970s [
10]. According to a study of the U.S. Geological Survey that was conducted from 1992 to 2001, pesticides have been found to pollute virtually every lake, river and stream in the United States. In Calcutta, India’s third-largest city, more than 90 percent of water and fish samples taken from a variety of sources contained traces of at least one, but more often of several pesticides [
11]. Further, frequent pesticide use favors the selection of resistant pests [
12], while also leading to a loss of environmental biodiversity. These matters constitute clear, actionable evidence for the necessity of minimizing pesticide use. As shown in
Figure 1, which aggregates data available from PubMed, it is clear that the drawbacks of pesticide use are already well understood by researchers worldwide.
A 2018 food and beverage survey of almost 1600 consumers conducted by L.E.K Consulting found that 93% of the consumers wanted to eat healthily at least some of the time, while 63% were trying to eat healthily most or all of the time, from which one can extrapolate that most consumers want all-natural and organic foods at least some of the time. However, the most in-demand foods were those which went one step further and did not contain artificial ingredients or preservatives either. This has been interpreted as reflecting consumers’ growing desire to look beyond generic all-natural claims and truly understand the specifics and origin of the food they purchase. Healthy eating has, then, become a mainstream trend, with food products being increasingly expected to meet certain attributes of health, ethics and sustainability, which strengthens the belief that it is time to rethink the standards and practices used for food production.
Eyhorn et al. asserted that agricultural practices need to change in order to meet the United Nations Sustainable Development Goals by 2030, and that organic agriculture should be an important part of the strategy devised to achieve these goals [
13]. Subsequently, driven by the customer demand for healthy food and sustainable development, farmers have (re)discovered alternative ways of farming. Instead of pesticides, for instance, they are using organic farm inputs as foliar fertilizers, not only adding nutrients at all stages of crop growth, but also mitigating pest infestation [
14], with the subsequent produce fetching premium prices on the market [
15].
Agricultural subsidies are one of the most commonly used policy tools for governmental support of agriculture [
16]. As the demand for organic food is increasing steadily, the U.S. Department of Agriculture is now providing organic producers with subsidies, up to a maximal yearly amount of
$20,000, via the Environmental Quality Incentives Program carried through the Natural Resources Conservation Service. However, the applicants need to be certified as organic producers first. The prospective organic producers can also apply for the Farmer’s Market Promotion Program, which provides grants for up to more than
$100,000 for projects which increase consumer access to farming products. For the organic farmers planning to export their produce outside of the United States, the government provides further loan and grant programs. For example, the Facility Guarantee Program gives payment guarantees to establish distribution facilities for agricultural products abroad. The expected outcomes of these subsidies are increased supply levels, product diversity and price stability, along with opportunities for employment and land use.
China’s agricultural subsidy policies had their beginning in the 1950s. From 1980 to 1992, subsidizing agriculture was not a top priority for the government. In 2005, the Ministry of Commerce of the People’s Republic of China promulgated the Interim Measures for the Administration of Funds for the Promotion of Trade in Agricultural, Light and Textile Products [
17]. From 2006, the Agricultural and Light Textile Products Trade Promotion Fund Project has been providing certified organic producers with appropriate funding. In 2020, the Ministry of Agriculture and Rural Affairs, together with the Ministry of Finance, finished implementing the ecology-oriented reform of the subsidies policy in China.
Most sustainability research concerning organic supply chains, potentially providing insights for further policy development, has been focused on their structure and performances [
18,
19,
20,
21,
22]. Consisting of various participants with vastly distinct interests, organic supply chains often have a dynamic structure. Kottila et al. [
23] pointed out that the main obstacles to the optimization of the organic food chain include poor information management, insufficient communication with customers, and the diverging objectives and needs of the participants in the chain. Additionally, the sustainability of supply chains traditionally focuses on its environmental dimension, but its social and economic integration have been studied only in terms of optimization [
24]. As shown in
Figure 2, external factors should also be considered in the analysis of the chain.
Evolutionary game theory (EGT), which is able to study the relationships between different participants to the supply chain (stakeholders) in an effective manner, has been applied in management, economics, sociology and other disciplines [
25]. Unlike classical game theory, EGT postulates that stakeholders keep on learning and dynamically adjust their actions according to previous successful behavior [
26]. This paper applies EGT to analysis of the formation and evolution of an organic supply chain which involves farmers, their customers and the government as the main stakeholders, allowing for the identification of proper stakeholder strategies when affected by the decisions of other participants in the supply chain. The main objectives are to identify the real-world conditions necessary to support a sustainable organic supply chain via a theoretical analysis of relatable, reliable models, and to analyze the outcomes obtained under different scenarios. The key contributions are two evolutionary game models to explain the dynamics of an organic supply chain, which represents a realistic approach to understanding the strategies of the government, farmer and customers, whose roles, functions and objectives all affect the chain dynamics. As a result, we provide a conceptual framework to help stakeholders adjust their actions dynamically, a feature which is not shared by other methods.
The remaining part of this paper is organized as follows. In
Section 2, we review the relevant literature, starting with a historical account of the development of EGT and continuing with relevant recent references concerned with the use of EGT in practical problems and with sustainable supply chain collaboration, respectively, and giving brief accounts of the results presented therein. In
Section 3, we introduce several core concepts of EGT and list our evolutionary model assumptions. We then propose the evolutionary scenarios for the interactions between the farmers and the government and between the farmers and their customers, respectively, and determine the associated replicator equations. In
Section 4, we analyze the evolutionary interactions via the linearization of the replicator equations in a vicinity of the equilibria, and find sufficient conditions to ensure the evolutionary stability of the respective strategies. The practical implications of these findings are then determined in
Section 5 via an analysis of the model parameters, with numerical simulations then performed for an organic supply chain defined ad hoc. Finally, directions for further research are provided in
Section 6.
3. Model Description
For further insights into the development of sustainable organic farming and into the evolution of an organic supply chain, we propose an EGT model which helps to analyze the dynamic process of stakeholder strategy selection. The farmers’ ultimate goal is to obtain maximal monetary benefits, while the selection of an organic strategy is affected by factors such as peer competition, government policies and consumer preferences. For the sake of simplicity, in this paper we choose the major stakeholders of the organic supply chain to be the farmers, their customers and the government.
Evolutionarily stable strategies (ESS) and replicator dynamics (RD) are two core concepts of EGT [
53]. An ESS is a strategy which, if adopted, cannot be invaded by any alternative competing strategy. In other words, if competing deviations can not affect the original, then the original represents an ESS. The concept of RD is used to express the evolutionary dynamics of an entity called a replicator, which has means of creating more or less accurate copies of itself. In EGT, replicators are strategies which compete for dominance according to the payoff yielded by the respective interactions between participants. If there is an occasional error deviation in the game, then the RD can restore it.
In an evolutionary game with
n strategies, let
represent the payoff matrix, in which
is the payoff when the strategy
i is played against the strategy
j,
. The popularity of each strategy, interpreted as the number of times the strategy is played, is given by
, and the corresponding fitness is computed by
. The average fitness of the population is denoted by
. Hence, the RD can be expressed by the following equation
in which
X denotes the proportion of strategy
s,
is its expected profit,
is the average profit of all strategies, and
denotes the change in the proportion of the strategy over time.
The construction of an evolutionary game model could help to analyze the behavioral characteristics of the strategic choices of stakeholders, who are weighing rational input and output benefits. As the government does not directly participate in the collaborative activities, it resorts to using macro-policies and incentives to promote cooperation in the organic supply chain and to attract more farmers to join in. Farmers may adopt an organic development strategy or stick to conventional farming, and consumer decisions may be volatile due to practical considerations. In this section, we consider a dynamic evolution model involving farmers, customers and the government as the stakeholders. The model assumptions are listed below.
Assumption 1. Each stakeholder is rational.
Assumption 2. No stakeholder can accurately obtain the strategic choices of the other stakeholders. Stakeholders can find optimal strategies only by continuously adjusting their respective strategic choices.
Assumption 3. Two different strategies are considered for farmers and customers, namely an organic strategy and a conventional strategy. For farmers, the organic strategy for means that they manage pests in their crops by using appropriate cropping techniques, biological control and natural pesticides; the conventional strategy means that synthetic fertilizers and pesticides are allowed. For customers, the organic strategy means that they prefer buying organic products; the conventional strategy means that they do not give preference to organic products.
Assumption 4. The governmental strategy set is (regulatory intervention, non-intervention). Governmental regulatory intervention includes subsidies for organic farming and penalty policies for conventional farming. Governmental non-intervention means that farmers are allowed to choose their strategy freely, without any subsequent administrative measures.
Assumption 5. In order to motivate the farmers to adhere to organic farming, the government provides different levels of subsidies and incentives according to the commitment of farmers to organic farming.
3.1. Description of the Interaction between Government and the Farmers
All symbols and notations used through this subsection in order to build and clarify our evolutionary model are indicated in
Table 1. Based on the above-mentioned assumptions and using the list of symbols indicated in
Table 1, we may then construct the payoff matrix of the interaction between farmers and the government as indicated in
Table 2.
Let us denote by
x the probability of governmental regulatory activities occurring and by
y the probability of farmers choosing the organic farming strategy. Denote also the expected profit of the government when adopting the regulatory intervention strategy by
, the expected profit of the government when adopting the non-intervention strategy by
and the average profit of the government by
. Moreover, let us denote by
and
the expected profits of farmers adopting the organic and conventional strategies, respectively, and by
the average profit of farmers. Then, the expected profits and the average profit of the government are given by
Similarly, the expected profits and average profit of the farmers are given by
Hence, from (
2) and (
3), the replicator equations for the strategies of the government and farmers, respectively, are given by
3.2. Description of the Interaction between Farmers and Customers
Similarly, all symbols and notations used throughout this subsection in order to build and clarify our evolutionary model are listed in
Table 3.
Based on our model assumptions and using the list of symbols indicated in
Table 3, we may construct the payoff matrix for the interaction between farmers and customers as in
Table 4.
Let us denote by
y the probability of a farmer selecting the organic strategy and by
z the probability of a customer selecting the organic strategy. Denote the expected profit of the farmer when adopting the organic strategy by
, the expected profit of the farmer when adopting the conventional strategy by
and the average profit of the farmer by
. Moreover, denote by
and
the expected profits of the customer selecting the organic and conventional strategies, respectively, and by
the average profit of the customers. Then the expected profits and the average profit of farmers are given by
Similarly, the expected profits and the average profit of customers are given by
Hence, from (
5) and (
6), the replicator equations for the farmers’ and customers’ strategies, respectively, are given by