It has been thoroughly investigated how microbes break down naphthalene, and the mechanism of their aerobic and anaerobic naphthalene metabolism is well understood [6]. Figure 1 illustrates the mechanism of biofilm formation within soils. In polluted soils, both fungi and bacteria are prevalent, and both types of organisms play a role in the biodegradation of hydrocarbons. The ambient factors, number and kind of microorganisms, nature and chemical structure of the chemical compound being degraded, and rate of bioremediation of a contaminant are all factors [7]. The capacity of bacteria and fungi to break down naphthalene has been well investigated [8]. Many variables, including temperature, oxygen, pH, microbial load and strain, level of acclimation, accessibility of growth factors, the chemical structure of the substance, cellular transport characteristics, and chemical partitioning in growing media, affect the amount and pace of biodegradation [9]. In contrast to liquid medium, soil biodegrades PAHs with a different efficiency. According to several studies, sorption of highly lipophilic PAHs to soils inhibited biodegradation because this lowered the PAHs' availability to microorganisms [10]. Degraders should be able to obtain sufficient biomass and, ideally, mineralize and grow on PAHs as carbon and energy sources in polluted soil in order to eliminate PAHs [11]. That is, growth should clearly evident using PAH as a carbon source. Figure 1: Emulsification action mediated by microbes illustrated. Microbe-produced emulsifying agents aid absorption of hydrocarbon molecules more readily from the soil. Environmental pollutants known as polycyclic aromatic hydrocarbons (PAHs) as shown in Figure 2 are teratogenic, mutagenic, and carcinogenic. They have the ability to taint food, water, sludge, and soil. They pose a serious threat to people's health. Due to their persistence, PAHs are significant environmental hazards and frequently exist as pollutants in soil and water [6]. According to [PERSON] et al. [12], soil-found PAHs may be hazardous to many plants, microbes and invertebrates. Different chemical compounds, including naphthalene and phenanthrene, are found in insecticides, fungicides, detergents, dyes and mothballs [13]. In production areas, some of the discharge includes heavy metal compounds that have a tendency to bioaccumulate due to recalcitrance within soil pores. These pollutants, when present affect the biogeochemical cycle, disrupt microbial biodiversity and eventually harm human life [14; 15]. According to [PERSON] et al. [16], PAHs are frequently discovered in polluted soils, and it is necessary to develop methods that may be used in the rehabilitation of these sites, where PAHs, particularly those with high molecular weight, represent threats to human health and the environment. Due to the risk they represent to human health and the delicate balance of the environment, PAHs and other oil products are of significant interest. Through the soil and subsequently the air, there may be seepage into the groundwater [17]. These inquiries into this investigation for the cleanup of the specific fraction--naphthalene--were motivated by these worries. A number of studies reviewed employed enrichment methods for naphthalene utilizing microorganisms [18; 19; 20]. For identification, the molecular method of 16 SrRNA analysis was prevalent following culture. Species identified in the studies included _Pseudomonas_ sp., _Geobacillus_- and a specie of _Bacillus cereus_. There was a general ability of microbes in mixed culture to have quickened degradation rates, even in anoxic conditions [21; 22]. The sites for samples may have varied greatly yet, the ability of these microbes remained unhindered pointing to a versatile way of handling the issue of pollution by hydrocarbon compounds.