Degradation of soil quality is an inevitable consequence of modifications to the characteristics of the soil that contribute to a decrease in ecosystem services. Numerous stressors, including chemical, biological, and physical ones, as well as those originating from both natural and artificial sources. The most prevalent kind of soil contamination that contaminates soil biota is agrochemicals. Soil is the most common place for xenobiotic dumping, which makes it the most probable source of other natural resources' pollution, such as surface and ground waters, based on the results of several studies. The danger to the environment posed by polluted soils is influenced by a variety of biological and physicochemical mechanisms that regulate the mobility and transformation of pesticides. However, species that are both above and below ground and are vital to the functioning of soil are seriously threatened by the insecticides' ability to linger in soil. Using living soil biota selectively is one of the effective ways to clean soil. This procedure is known as. In the past, chemical residues in soil have been removed or their toxicity decreased by the use of bioremediation. Even though microbes are frequently used in bioremediation, some well-known soil fauna, such as earthworms, contribute significantly to the disintegration and purification of substances. Because they change the state of the People consider earthworms to be soil engineers. Earthworms are capable of soil, help break down pesticide residues in one of two ways: directly by releasing detoxifying enzymes into their digestive tracts or indirectly by favorably influencing microbial communities that have the ability to break down pesticides. The earthworm-supported breakdown of pesticides is mostly limited to the worms' processed soil and gut milieu. Histological alterations brought on by pollutants are believed to be a sensitive method of determining the test organism's direct exposure to certain chemical contaminants. This study's objective was to ascertain how the pesticide methiocarb affected earthworms. After ten days of exposure to sublethal dosages (200 and 400 mg/kg), earthworms underwent several histological changes. such as villi fusion, tearing of the body wall, as well as the breakdown of the cuticle and circular muscle layer. They also become less able to dig in the ground.