Stone powder sludge is a waste by-product that is annually produced more than 7.5 million tons from the manufacturing process of crushed aggregates in Korea.
This study investigated the use of stone powder sludge as a substitute for fine aggregate in brick manufacturing through the CaO activation of the ground-granulated blast-furnace slag (GGBFS) system, which was found to be more suitable than portland cement for the proposed bricks that contained a large quantity of stone powder sludge.
Two of the proposed trial bricks satisfied the requirements of concrete building blocks, ASTM C55, for strength and water absorption at seven days of curing, while the cement brick, with the same quantity of stone powder sludge, failed to fulfill the requirement for water absorption.
The effect of the source of powder (grinding sludge or oxide scale), quantity of reducing agent cum lubricant, i.e., graphite powder, compaction parameters such as compaction pressure, compact weight and sintering parameters such as sintering temperature and time on reduction and densification characteristics were analysed using Taguchi based experimental design.
They are with 10 wt.% cement replaced by CMP sludge powder.
Several low cost adsorbent materials have been developed such as cellulosic orange peel waste, banana pith, rice husk, clay, neem leaf powder, powdered activated sludge, activated carbon, gram husk, coal bottom ash, bagasse fly ash, deoiled soya, red mud, and sawdust (Gupta and Suhas 2009).
The LED sludge powder was used to replace 5, 10, 20, and 30 wt.% of the cement, and the (5 × 5 × 5-cm3) sludge-blended cement mortar (SBCM) specimens were molded for a compressive strength test and other engineering property tests.
The preliminary study consisted of a scenario analysis where five scenarios were drawn out using substances which included spent coolant, tramp oil, solvent, powdered chips, and sludge [16].
The preliminary study consists of a scenario analysis where five scenarios are drawn out using substances such as spent coolant, tramp oil, solvent, powdered chips, and sludge, which are commonly found in the effluent waste.
Various physicochemical sludges obtained with various coagulant/flocculants (alum, FeCl3, and sepiolite) were experienced dry particulate (powder) form of the sludge was replaced at 0.5 1.5% w/w of the cement for 250 kg/m3 cement dosage.
The marble sludge dry powder retained on each sieve was weighed and is shown in Figure1.
