Inert waste in mining refers to solid waste materials generated during mining and construction activities that do not undergo significant physical, chemical, or biological transformation when deposited and do not adversely react with other materials, leach harmful substances, or pose a risk of contamination to soil, surface water, or groundwater under normal environmental conditions. In bauxite, gold, iron ore, and diamond mining, inert waste typically includes overburden rock and soil that does not contain significant sulfide mineral content, construction and demolition debris such as concrete and masonry, non-reactive waste rock devoid of acid-generating minerals, and certain low-grade ore stockpiles that do not present leachability concerns. The classification of mine waste as inert is of significant regulatory and practical importance, as inert waste can generally be disposed of in less engineered and less costly waste storage facilities than non-inert or hazardous waste, which requires lined containment and active leachate collection systems. Regulatory frameworks in jurisdictions such as the European Union, Australia, and various African nations require formal geochemical testing and classification of mine waste streams to determine their acid-generating potential and leachability characteristics before classifying them as inert. This involves tests such as the Net Acid Generation (NAG) test, acid-base accounting (ABA), and leachate extraction tests. Even materials classified as inert must be managed to avoid physical instability, erosion, or dust generation. Proper segregation, characterization, and placement of inert waste is an important component of mine waste management plans and is essential for achieving compliant and cost-effective mine closure outcomes.