Patent Application
20180345247
Industrial wastewaters usually contain substances that are severely harmful to the environment. For example, textile dyeing is a chemically intensive process which consumes large quantities of water. In a typical dyeing process, 50-100% of dye is fixed on the fiber, and the unfixed dyes are discharged into the dye-baths or into the wastewater from the subsequent textile-washing operations. To comply with stringent discharge limits, multi-step and complicated treatment is usually required. Among different methods available for dye removal or other contaminant, adsorption is a highly efficient and low-cost process. Numerous types of adsorbent such as activated carbon, silica, zeolite, kaolinite, bentonite, etc. have been employed for the adsorption techniques, but in some cases the adsorbents are prohibitively expensive or in other cases they are not suitable for the application. As a result, there's a need to continue to develop and identify cheaper adsorbent materials with higher performance but a lower cost.
Halloysite is natural-mineral clay with hollow nanotubular structure. It is abundant in many countries such as China, the United States, Brazil and France. As a result, they are one of the cheapest existing adsorbents in many regions of the world. Halloysite structure has collected notable properties in material science due to its special features of large surface area, unique tubular structure, high porosity, high length-to-diameter ratio, and high receptor surface chemistry, which have made this nanomaterial to be utilized as an adsorbent material. This substance naturally contains aluminosilicate nanotubes with a 1:1 Al:Si ratio and a stoichiometry of Al2Si2O5(OH)4.nH2O. Halloysite consist of octahedral sheet of Al—OH groups on the internal surface and siloxane groups (Si—O—Si) on the external surface. These variances have led to a negatively charged outer surface and a positively charged inner lumen at pH range of 2 to 8.
Modification of phyllosilicates clay minerals, especially halloysite and kaolinite to improve capacity or enhance the activity of these as adsorbent, is subject of numerous patents. The first step typically involves washing off the powder to remove impurities such as iron, which often mask the active sites, and then followed by activation with coupling agent. The common coupling agents are from silane coupling agent group. Silane coupling agents are used attaching organic components to inorganic base material. The activation sites are terminated by adding an organic component such as amines. This step is the distinctive difference between most of the patents.
Patent “CN 102492173 B” uses catalysts for aminolysis ester groups. At first, ester group is activated, and then followed by aminolysis. Patent “CN 103087553 A” introduces an active amino group onto surface of halloysite nanotubes which is already activated by silane coupling agent. Surface modification terminated by grafting maleic anhydride on the surface of the halloysite nanotubes. Patent “CN 104119704 A” teaches the modification of halloysite nanotubes with silane group by adding epoxy resins to produce a nanocomposite material. This patent uses halloysite nanotubes to improve mechanical and thermal properties of epoxy resins. Patent “CN 103923497 A” uses a unique chemistry to combine halloysite with bentonite. The new clay will have the special features and properties of both ingredients and can be used in numerous applications. Patent “CN 102343101A” describes a method to functionalize kaolin nanotube-antisense oligonucleotide as a medicine carrier. For silane coupling agent, 3-aminopropyl triethoxysilane was selected and the functionalized group was created by reacting with antisense oligonucleotides. The product is claimed to be a stable function of halloysite nanotube antisense oligonucleotide solution. Patent “CN 103509161 A” recommended the use of aminopropyttriethoxysilane (APTES) for silane coupling agent. Surface amination was carefully controlled by surface atom transfer radical polymerization and the final product was a composite material. Patent “U.S. Pat. No. 6,080,319 A” teaches the use of organoclay with naturally positive or negative charge on the surface as a sorbent. However, this patent does not advocate the use of silane as coupling agent, but instead modification is performed with at least one of an organic ionic compound in stoichiometric excess and an amphoteric surfactant. Qu, R., et al. (2006) investigated divergent synthetic route to modify silica till generation 4 for adsorption of metal ion. The long-time procedure for synthetic route is limitation of their investigation which it improved with convergent synthetic route in our patent.
Scheme 1: Halloysite-NH2
Scheme 2: Halloysite-amino terminated dendritic polymer via divergent synthetic route
Scheme 3: Halloysite-carboxylic acid terminated group
Scheme 4: Halloysite-amino terminated dendritic polymer via convergent synthetic route with COOH activation
Scheme 5: Halloysite-amino terminated dendritic polymer via convergent synthetic route with MA activation
Scheme 6: Halloysite-amino terminated dendritic polymer
The new approach in the modification of halloysite using dendritic polymer includes dendrimer as well as hyperbranched polymer. Dendritic polymers adsorb contaminant from wastewater in two ways: binding with the abundant functional end groups, and encapsulating in the interior between the branches. To introduce amine-terminated dendritic polymer on the surface of halloysite, aminosilane agents such as (3-Aminopropyl) triethoxysilane (APTES) are used to functionalize the halloysite in the process of silanization. In this case, amino groups are introduced on the surface of halloysite, which could act as the core for the synthesis of the dendritic structure on the halloysite via divergent or convergent synthetic route.
Modification Method Via Divergent and Convergent Dendritic Synthetic Route: Modification in Divergent Synthetic Route:
1. The first modification step to modify is changed all hydroxyl groups to amine group by (3-Aminepropyl) triethoxysilane (APTES).
2. In next step, amine dendritic groups are added via divergent synthesis from zero to nth generation by repeating the Michael addition of methyl acrylate and amidation of the esters groups with ethylenediamine. Scheme 2 shows first Michael addition of methyl acrylate to reach Generation G0.5 followed by amidation of the esters groups to terminate to Generation G1. By following the same Michael addition of methyl acrylate followed by amidation of the esters groups Generation G1.5 and G2 can be reached which is also presented in Scheme 2. By repeating the same steps G2.5 and G3 will be produced which has more active sites compare to previous generations. The reaction and termination could be continued to create generation nth of the modified HNTs. It worth to note that either or both methyl acrylate and ester group could be replace with equivalent components in any generation. It seems that third generation could be the sufficient modification for most applications.
Modification in Convergent Synthetic Route:
Four different strategy could be applied in convergent synthetic route:
1. Surface modification by convergent method for halloysite nanotube (HNT), compromising steps of: (1) purification of HNTs with hydrochloric acid solution followed by water washing and drying; (2) introducing amino group on surface of the acidified HNT by adding silane coupling agent solution; (3) adding carboxylic acid terminated dendritic groups via convergent synthesis.
2. Surface modification by convergent method for halloysite nanotube (HNT), compromising steps of: (1) purification of HNTs with hydrochloric acid solution followed by water washing and drying; (2) introducing amino group on surface of the acidified HNT by adding silane coupling agent solution; (3) adding amine dendritic groups by the Michael addition of methyl acrylate (MA), (4) adding amino terminated dendritic polymer via convergent synthesis.
3. Surface modification by convergent method for halloysite nanotube (HNT), compromising steps of (1) purification of HNTs with hydrochloric acid solution followed by water washing and drying; (2) converting all hydroxyl group to carboxylic acid group by adding a dicarboxylic acid; (3) adding amine terminated dendrimer to carboxylic acid group.
4. Surface modification by convergent method for halloysite nanotube (HNT), compromising steps of: (1) purification of HNTs with hydrochloric acid solution followed by water washing and drying; (2) introducing amino group on surface of the acidified HNT by adding silane coupling agent solution; (3) converting all amine group to carboxylic acid group by adding a dicarboxylic acid; (4) adding amino terminated dendritic polymer via convergent synthesis.
In third and fourth convergent synthetic route all hydroxyl and amino groups are first converted to carboxylic acid groups with different type of carboxylic acid. The list of carboxylic acid is listed in Table 1.
The chemical reaction is illustrated in Scheme 3.
The application of the functionalized halloysite could be effective for removal of heavy metal cations from the soil or aqueous solution.
Furthermore, this modification could be utilized for convergent synthetic route in dendritic strategy as revealed in Scheme 4.
The final dendritic structure on functionalized halloysite is illustrated in Scheme 6.
Surface Charge: Zeta Potential of Halloysite Nanotube
The zeta potential values of different samples are reported in Table 2. These results indicate that the surface of raw halloysite is negatively charged and as the generation of the amine dendritic structure on halloysite increases, the overall surface charge increases up to +25.30 (mV) for generation three (HNTG3). The modified halloysite through convergent method also showed the same behaviour and the grafting of different generations of PPI and PAMAM to halloysite also resulted in more positive surface, which strongly confirms the existence of amine groups in the structure of the modified halloysite. These negative and positive charges are useful for adsorption of cationic or anionic contaminant, respectively.
Surface Charge: Zeta Potential of Silica
The zeta potential values of different silica samples and modified ones are reported in Table 3. Silica G1 is modified in divergent synthetic route and silica-convergent is modified according to Claim 2.
Acid Dye Removal for HNT
The removal efficiencies of C.I. Acid Red 1 (AR1), C.I. Acid Red 42 (AR42), Acid Blue 92 (AB92) and Methyl orange (MO) AR1, AR42, AB92 and MO by halloysite modified via divergent and convergent methods are shown in
The improvement in dye removal (%) after grafting of dendritic structures on the halloysite can be seen in
Heavy Metal Ion Adsorption for HNT
The effect of time, dendrimer generation, and adsorbent dosage on Fe2+ removal using the amine terminated halloysite modified by divergent route are respectively represented in
Acid Dye Removal for Silica
Surface modification by divergent method for silica compromising steps of: (1) purification of silica with hydrochloric acid solution followed by water washing and drying; (2) introducing amino group on surface of the acidified silica by adding silane coupling agent solution (Silica APTES); (3) adding amine dendritic groups via divergent synthesis by the Michael addition of methyl acrylate (MA) and amidation of the esters groups with ethylene diamine (ED) (Silica G1).
Heavy Metal Ion Adsorption for HNT in Convergent Method by Carboxylic Acid Linkage
One of the most important parameters affecting the adsorption capacity is the pH adsorption. The effect of pH on the adsorption of Cr (III) shown in
Acid Dye Adsorption for HNT in Convergent Method by Carboxylic Acid Linkage
Carboxylic acid group were synthesized into the halloysite nano tube (HNT); then amine-terminated dendritic hyperbranched polymer with convergent method reacted with carboxylic acid functionalized halloysite. Raw halloysite were washed with HCL and functionalized with 3-amino poropyltriethoxysilane (APTES), HNT-NH2 was reacted with succinic anhydride in order to make carboxylic acid group in to the structure. Then amine terminated group added to HNT-COOH in convergent method.
Adsorption capacity was investigated by new synthesis adsorption. The optimum adsorbent dosage and pH for dye removal of CI ACID RED 1 were obtained to be 0.5 g/l and 3, respectively. The dye removal for modified HNT in convergent synthetic route at different pH reveal in
