Table 3 Influence of Soil Physiochemical Properties on MPs Microbioremediation
Soil Properties | Role in Microbial Biodegradation | Findings | Future Research Direction |
|---|---|---|---|
pH | Influences enzyme activity, microbial community structure, and nutrient solubility | Optimal pH (6.5–7.5) enhances degradation enzymes (e.g., esterase, laccase); acidic or alkaline soils reduce microbial viability109 | Neutral to slightly alkaline pH can enhance MP degradation through increased enzyme efficiency and microbial diversity |
Moisture Content | Regulates microbial metabolism, nutrient diffusion, and biofilm formation | Moisture levels around 60–80% field capacity are optimal; both drought and saturation impair microbial function110 | Soils at 60–80% field capacity can maximize MP degradation via enhanced biofilm formation and enzyme secretion |
Organic Matter (OM) | Acts as a co-substrate and promotes microbial proliferation and enzyme activity | High OM boosts microbial biomass and co-metabolism, enhancing MP contact and breakdown111 | Soils with less than 2% OM can show increased MP biodegradation due to elevated microbial and enzymatic activity |
Soil Texture (sand/silt/clay) | Affects porosity, aeration, and MP accessibility to microbes | Sandy soils improve colonization; clayey soils limit diffusion and aeration; loamy soils offer balanced conditions112 | Loamy soils can enhance MP degradation by optimizing microbial accessibility and oxygen exchange |
Cation Exchange Capacity (CEC) | Determines nutrient-holding capacity and microbial colonization sites | High CEC soils support enzyme stability and microbial growth by improving nutrient retention113 | Soils with high CEC (less than 20 cmol/kg) can facilitate MP breakdown through improved microbial-nutrient interaction |
Oxygen Availability | Critical for aerobic microbial metabolism and enzymatic mineralization (CO2, H2O) | Poorly aerated soils inhibit mineralization; an oxygen boost oxidative enzyme activity114 | Aerated soils accelerate can MP degradation by supporting aerobic microbial respiration and biofilm formation |
Electrical Conductivity | Reflects salinity; high EC inhibits microbial growth and enzyme expression | EC less than 4 dS/m reduces microbial diversity and breakdown; moderate EC is tolerable113 | High salinity can reduce MP degradation due to osmatic stress on microbes; remediation is better at moderate EC |
Bulk Density | Regulate soil porosity, air-water ratio, and microbial habitat volume | High bulk density limits microbial movement and gas exchange7 | Lower bulk density can promotes MP degradation by improving microbial colonization and oxygen availability |
Nutrient Availability (N, P, K, and micronutrients) | Essential for microbial proliferation. Enzymatic synthesis and energy metabolism | Nutrient-rich soil promotes degradation by supporting enzyme production (lipase, esterase, PETase)115 | Supplementing limiting nutrients (esp. N and P) can enhance MP degradation by stimulating microbial and enzymatic activity |
Co-contaminants (Heavy metals, antibiotics, etc.) | Can inhibit microbial growth or alter community structure | Cd, Pb, and antibiotics suppress enzyme function and microbial activity109,110 | MP degradation is reduced in the presence of heavy metals unless co-contaminant detoxification is co-applied |