4.2. Removal of Pesticides
Given the possible risk to human health, pesticide poisoning of water has drawn a lot of attention. Many academics have recently shown interest in the removal of pesticides from water. Scanning electron microscopy (SEM), FT-IR, X-ray photoelectron spectroscopy, and Brunauer–Emmet–Teller theory (BET) were used to investigate the mesoporous ACS, and it was shown to be highly efficient at cleaning water of contaminants. In fact, it removed 11 pesticides from water better than commonly used adsorbents, such as graphitized carbon black (GCB), activated carbon (AC), C18, and primary secondary amine (PSA) adsorbent. The inclusion of functional groups such as oxygen, nitrogen, and benzene ring bonds dramatically affected adsorption.
Pesticides can be removed via a variety of techniques, including as adsorption, oxidation, enzymatic biodegradation, and photocatalytic degradation. Starch-derived mesoporous activated carbon adsorption is recognized as a highly effective method due to its low starting cost, ease of operation, flexibility, simplicity of design, and insensitivity to harmful pollutants. It is also one of the few methods capable of removing pollutants while remaining unaffected by them. Additionally, it is one of the few methods that can clear contaminants without being harmed by them, making it an extremely helpful tool
[67][151].
4.3. Removal of Heavy Metal Ions
Industrial wastewater and groundwater often contain various inorganic components, including arsenic (As), cadmium (Cd), chromium (Cr), cobalt (Co), copper (Cu), lead (Pb), mercury (Hg), nickel (Ni), zinc (Zn), and others
[68][153]. Modified starches demonstrated substantial adsorption capabilities towards heavy metals by replacing hydroxyl groups with chemically active groups
[16][55]. A wide range of starch derivatives with amino, amide, carboxyl and other groups were synthesized and used in water treatment
[69][154]. Corn starch, for example, can be cross-linked and carboxymethylated to actively capture harmful divalent cations, which include Cu, Pb, Cd, and Hg ions present in water. By distributing 1% of the starch for a couple of minutes and then filtering the starch–metal complex, it was possible to efficiently remove about several hundred ppm of these metal ions from water at a low degree of substitution of carboxymethyl groups
[18][57]. The starch can be easily restored through weak acidic washing, and the success of metal removal depends on avoiding highly acidic metal solutions. Increasing the levels of carboxymethylation and cross-linking can enhance the metal scavenging activity of starch, making it suitable for industrial applications
[23][41][70][71][72][62,64,155,156,157].
Furthermore, starch can be used for the removal of heavy metal ions by grafting it with various vinyl monomers, including acrylic acid (AA), acrylic amide (AM), acrylonitrile, alkylmethacrylates, methylacrylonitrile, vinyl ketones, and 2-(dimethylamino) ethylacrylate. These polymers, despite their loosely crosslinked network structure and hydrophilic side groups, exhibit remarkable water absorption and retention capabilities
[73][158].
4.4. Removal of Dye
The manufacturing processes of industries, like the leather, paper, and textile industries, release extremely dangerous and carcinogenic chemicals into wastewater. The release of waste dyes from textile finishing poses a significant threat to both natural water resources and human well-being.
[36][83]. Polymers, and more specifically biopolymers, have a wide structure that affords several binding sites for dye molecules. This helps to neutralize the charge that the dye molecules carry, which in turn enables effective precipitation. In applications involving the coagulation of blood, biopolymers are the material of choice since, in contrast to traditional coagulants, they do not pose a threat to human health and have a lower impact on the environment
[74][176].
Starch is a key component in enhancing the quality of the overall nanocomposite due to its amylose chains, which have a strong affinity for anionic dye molecules. A highly recommended alternative method for removing anionic-charged dyes involves using a mixture of starch, chitosan, and glutaraldehyde in specific proportions. This mixture works by utilizing the attractive properties of starch and chitosan to effectively remove the dyes
[74][176]. The combination of starch and chitosan creates electrostatic and hydrophobic interactions that provide benefits in dye removal effects compared to just chitosan alone. These chitosan starch nanocomposites have the potential of 90% in the removal of anionic-charged dye through coagulation-flocculation
[75][76][77][177,178,179].
4.5. Removal of Pharmaceutical Pollutants
The discharge of trace amounts of pharmaceuticals into ecosystems is acknowledged as a serious environmental issue, resulting in persistent and immediate impacts on the environment
[78][195]. Starch-Mg/Al-layered double hydroxide (S-Mg/Al LDH) is a synthesized composite utilized in the adsorption of non-steroidal anti-inflammatory drugs (NSAIDs) found in various water and wastewater sources. This adsorbent performs well due to its efficiency and high adsorption rate. S-Mg/Al LDH also showed good reusability performance when tested with optimized experimental parameters.
To remove tetracycline, carboxymethyl-starch-grafted magnetic bentonite
[79][198], starch-stabilized magnetic nanocomposite
[80][199], magnetic starch polyurethane polymer nanocomposite
[81][200], and magnetic starch nanocomposite
[82][201] were created. Shen et al.
[79][198] compared corn-starch-grafted magnetic bentonite (SMB) to carboxymethyl-starch-grafted magnetic bentonite (CSMB) and discovered that the CSMB had a 28% higher tetracycline adsorption capacity compared to SMB. Regarding recyclability, the adsorption capacities of CSMB experienced a decrease of over 20% after the initial cycle due to the destructive effects of nitric acid treatment on some of the functional structures, resulting in a loss of adsorption capacity.
Other pharmaceutical pollutants, such as fluvastatin
[83][197], dox
[38][90], and bovine serum albumin
[84][202], have also been investigated using starch-based adsorbents. The removal of fluvastatin can be accomplished using the magnetic MOF–starch hydrogel created by Mohamed and Mahmoud
[83][197]. The magnetic MOF–starch hydrogel was developed via microwave irradiation and demonstrated several remarkable properties. It exhibits a maximum equilibrium adsorption capacity of 782.05 mg/g, a high surface area of 528.39 m
2/g, a mesoporous structure with a pore size of 2.90 nm, and a highly crystalline structure. Within this system, three types of bonding are expected to occur.
5. Conclusions
The effective use of starch for wastewater treatment comes from its vast availability and sustainability as a natural polysaccharide. In wastewater treatment applications, modified starch products have showed promise in the removal of a range of contaminants, including oil, organic solvents, pesticides, heavy metal ions, dyes, and pharmaceutical pollutants. An example of innovative use of starch-based materials is the development of raspberry-like starch-based polymer microspheres. These microspheres are created through Pickering polymerization and grafting of poly(ethylene imine) (PEI) onto amino-functionalized composite particles. These microspheres not only have the capability to separate oil and water, but they also exhibit simultaneous removal of Cr(VI) and Indigo carmine. The efficiency of oil and water separation is influenced by the dosage of PEI. The resulting composite particles possess unique characteristics, such as rough structures, distinctive surface wettability, and positive charge. This combination enables them to simultaneously separate water-in-oil (W/O) and oil-in-water (O/W) emulsions within a specific dosage range of PEI. Moreover, the amino-functionalized composite particles carry a positive charge, which enhances their ability to effectively absorb anionic water-soluble pollutants. The removal rate of these pollutants during the oil/water separation process can reach nearly 90%.