Efforts to prevent losses and counterattack insect dammaging in crops by means of chemical control often contribute to the selection of resistant populations. Resistance to agricultural insecticides have been reported since the early 20th century. In the last decade, some products have been developed with the aim of mitigating the harmful effects of field management on producers and the environment. However, insecticides with different modes of action (MoA) have been reported as prone to generating field resistance and, within a few years, losing their effectiveness. The difficulties in the control management are aggravated due to the occurrence of insect’s resistance to various insecticides. Certain active substances can induce molecular modifications, including point mutations, in the genome of pest insects, are associated to resistance in field populations. The resistance mechanisms categorized by genetic mutations are particularly useful as they enable the analysis of the evolution and spread of the corresponding resistance. Additionally, it serves as a basis for the development of molecular markers that can be used for early detection of the resistance in early infestation phases. Accordingly, it allows diagnosis for preemptive decisions to alternate between products with different MoA and their application methods, contributing to practices that enhance sustainable production management initiatives. Along with the need to reduce pesticides, as ruled by international conventions, diagnostic methods for detecting insecticide resistance are increasingly in demand, especially because of the decreasing effectiveness of insecticides. Some diagnostic methods for this purpose are under development and a few already being offered as services to worldwide cultivated crops. In this review, we will focus on the main diagnostic methodologies using molecular markers, their advancements, and the outlook for the development of resistance diagnostic tools. Furthermore, we discuss the impact of insecticide resistance on coffee, a global market agricultural commodity, towards implementing effective management strategies to maintain the efficacy of chemical products and promote sustainable agricultural and pest control practices.The global view of inseticides in agricultureChemicals were historically the primary method of pest control in global agriculture and remain nowadays at this same status. The use of pesticides allows for less damage of cultivated species and, consequently, increased production. Nonetheless, the use of large quantities of these molecules, estimated at approximately 2 million tons annually [1], implies in economical drawbacks. According to data from the Food and Agriculture Organization of the United Nations (FAO) for 2021-2022, Brazil is the leading country in general pesticide use for agriculture, with 719.51 thousand tons, followed by the United States with 417.39 thousand tons and Indonesia with 283.30 thousand tons [2].Included in this account, insecticides represent a heavy burden to producers, besides having direct consequences for health and the environment. The impacts of insecticides on human health are more severe when workers are directly exposed to the products, considering that the knowledge of health risks is still insufficient for workers to change their handling practices [3]. It is proven that pesticide poisoning can cause effects on the human body such as diarrhea, headaches, dizziness, and in more severe cases, it can contribute to the development of neurological problems and carcinogenic diseases [4], [5]. Beyond human health, the environmental impacts of insecticide application are also severe, as the lack of specificity affects non-target insects that play important roles in ecosystems, such as pollinators [4] and other animals like birds and fish [6], [7]. Additionally, insecticides contaminate water [8], soil [9] and food [10], [11], causing damage to the entire trophic chain. Finally, the excessive use of insecticides can lead to the development of resistant target insect populations.The insecticide resistance problemThe first reports of insecticide resistance appeared around 1914, where resistance to sulfur was observed in scale insects. [12]. Resistance to insecticides remained at low frequency until the introduction and expansion of synthetic organic insecticides such as DDT, cyclodienes and organophosphates, between the 40s and 50s [13]. From the 60s onwards, insecticide resistance began to be considered an impact fator of the use and effectiveness of a wide range of chemical compounds. New chemicals were introduced onto the market in attempt to circumvent the situation, although, in many cases they had the same chemical class as those already existing [14]. In this way, in 1984 the Insecticide Resistance Action Committee (IRAC) was formed together with other organizations in attempt to establish adequate management of resistance. In 1998, IRAC began to develop a classification scheme for agricultural chemicals based on the so-called Modes of Action (MoA), a tool that initially classified acaricides, that is currently extended to cover biologicals and insecticides as the main basis for managing resistance [13].The most recent reports on the global use of insecticides show this ranking is led by Indonesia, the United States, China and Brazil, with 116,405 thousand tons, 72,985 thousand tons, 70,126 thousand tons and 59,587 thousand tons, respectively [2]. Consequently, known resistance in a wide variety of pest insects are closely related to the most cultivated crops in these countries. In Indonesia, the main reports of resistance are in Spodoptera frugiperda , with resistance to insecticides in the chemical groups of organophosphates, avermectins, pyrethroids, spinosyns, and diamides, and in Plutella xylostella , with resistance detected to organophosphate and pyrethroid insecticides [15]. In Brazil, there are insecticide resistance...