article · Scientific Reports
phases, and the average crystal size increased from 54 nm for BA600 to 66 nm for BA800. Morphological analyses showed that BA600 had a denser aggregated structure, whereas BA800 exhibited coarser and more uniform particles. Under the optimum conditions of pH 6, adsorbent dose 0.1 g, and 298 K, equilibrium was reached within 60 min for BA600 and 80 min for BA800. The maximum adsorption capacities were 124.38 mg/g for BA600 and 90.58 mg/g for BA800. Zn(II) adsorption followed the pseudo-second-order kinetic model and the Langmuir isotherm and was found to be spontaneous, exothermic, and predominantly chemical in nature. After five adsorption/desorption cycles, the removal efficiencies decreased from 79.62 to 69.76% for BA600 and from 56.31 to 44.57% for BA800, corresponding to retention of 87.62% and 79.15% of their initial performance, respectively. In real wastewater, the adsorption capacities reached 110.40 mg/g for BA600 and 77.60 mg/g for BA800. These findings demonstrate that BA600, in particular, is an efficient adsorbent for Zn(II) removal from aqueous media.
This page summarises published work. The authoritative version sits with the publisher.
DOI: 10.1038/s41598-026-51234-2
Is something wrong with this record? Report it or request removal.
Discussion
Have you built on this work, tried to replicate it, or seen it applied in practice? Share what you know. Verified researchers and MARATTO™ domain experts can open a discussion, and any member can reply. Contributions are reviewed before they appear.
No discussion yet. Open the first thread.
New to MARATTO™? Create a free account.