Full article ">Figure 1
<p>Graphene and its derivatives (reproduced with permission from [<a href="#B13-carbon-10-00092" class="html-bibr">13</a>]).</p> Full article ">Figure 2
<p>Different synthesis methods for graphene-based materials (reproduced with permission from [<a href="#B35-carbon-10-00092" class="html-bibr">35</a>]).</p> Full article ">Figure 3
<p>Different sources of antibiotics in wastewater.</p> Full article ">Figure 4
<p>Diagram depicting AMP wastewater treatment via the C<sub>3</sub>N<sub>4</sub>-MoS<sub>2</sub>/3DG flow-through system, enhanced by the addition of trace amounts of H<sub>2</sub>O<sub>2</sub> and electricity generation by the air cathode. (Reproduced with permission from [<a href="#B94-carbon-10-00092" class="html-bibr">94</a>]).</p> Full article ">Figure 5
<p>GO-based NM88B/GO/SA aerogels for antibiotic-contaminated wastewater (reproduced with permission from [<a href="#B95-carbon-10-00092" class="html-bibr">95</a>]).</p> Full article ">Figure 6
<p>A schematic of the experimental design included the following steps: (1) Synthesizing graphene oxide (GO) from raw graphite flakes via oxidation via a modified Hummers method. (2) Obtaining the resulting GO. (3) Copper oxide-doped reduced graphene oxide (CuO–rGO) was synthesized from synthesized GO and an aqueous CuSO<sub>4</sub>·5H<sub>2</sub>O solution, and (4) zinc oxide-doped reduced graphene oxide (ZnO–rGO) was synthesized from synthesized GO and an aqueous ZnSO<sub>4</sub>·7H<sub>2</sub>O solution through a series of thermal chemical reactions. (5) The chemical and physical properties of GO, CuO–rGO, and ZnO–rGO were characterized via standard microscopic and spectroscopic techniques, including SEM, TEM, ATR-FTIR, and XPS. (6) Batch adsorption experiments were conducted to remove textile dyes (rhodamine 6G (R-6G) and malachite green (MG)) and antibiotics (amoxicillin (AMOX) and tetracycline (TC)) from aqueous solutions via GO, CuO–rGO, and ZnO–rGO adsorbents, followed by analysis via UV–visible spectroscopy. (7) Mathematical modeling and kinetics were applied to study the batch adsorption of textile dyes (R-6G, MG) and antibiotics (AMOX, TC) on GO, CuO–rGO, and ZnO–rGO. (8) Analyzing functional group changes on the GO, CuO–rGO, and ZnO–rGO adsorbents after adsorption of the textile dyes and antibiotics via ATR-FTIR. (Reproduced with permission from [<a href="#B99-carbon-10-00092" class="html-bibr">99</a>]).</p> Full article ">Figure 7
<p>Diagrammatic representation of the synthesis process for free-standing graphene oxide (GO), Ti<sub>3</sub>C<sub>2</sub>Tx, and GO/Ti<sub>3</sub>C<sub>2</sub>Tx composite membranes (reproduced with permission from [<a href="#B101-carbon-10-00092" class="html-bibr">101</a>]).</p> Full article ">Figure 8
<p>Influence of various factors on the tetracycline adsorption efficiency of the Cu/PANI/GO nanocomposite: (<b>a</b>) pH and zeta potential, (<b>b</b>) mass dosage (mg), (<b>c</b>) presence of interfering ions, (<b>d</b>) synergistic impact of Cu nanoparticles and polyaniline on the adsorption efficiency, and (<b>e</b>) reusability of the Cu/PANI/GO nanocomposite over four consecutive cycles under optimal conditions (reproduced with permission from [<a href="#B102-carbon-10-00092" class="html-bibr">102</a>]).</p> Full article ">Figure 9
<p>Removal of norfloxacin (<b>A</b>), tetracycline (<b>B</b>), and flumequine (<b>C</b>) via activated inorganic peroxides with magnetic graphene MG0.2 (reproduced with permission from [<a href="#B88-carbon-10-00092" class="html-bibr">88</a>]).</p> Full article ">Scheme 1
<p>Three steps of this systematic literature review following PRISMA, 2020 [<a href="#B92-carbon-10-00092" class="html-bibr">92</a>].</p> Full article ">