S. No | Reference | Architecture | Application | Performance |
---|---|---|---|---|
1 | Ref. 53 Lei et al. (Porous boron nitride nanosheets for effective water cleaning) [53] | Exfoliated BN nanosheets | Absorption of dyes, organic solvents, and oils | Ethanol, Toluene, Pump oil, Used Engine oil, Ethylene Glycol absorption ranging between 2000–3300% |
2 | Ref. 40 Lei et al. (Boron nitride colloidal solutions, ultralight aerogels and freestanding membranes through one-step exfoliation and functionalization) [40] | Aerogel, free-standing membranes of BN nanosheets | Proof of concept | - |
3 | Ref. 54 Liu et al. (Multifunctional Polymer/Porous Boron Nitride Nanosheet Membranes for Superior Trapping Emulsified Oils and Organic Molecules) [54] | BN nanosheets incorporated into PVDF- Mixed matrix membrane | Oil–water separation, Dye and pharmaceutical rejection | Carbamazapine, ciprofloxacin, chlortetracycline: 100% removal upto a critical concentration of BN in the membranes |
4 | Ref. 55 Marichy et al. (Fabrication of BN membranes containing high density of cylindrical pores using an elegant approach) [55] | Free-standing BN membrane through atomic layer deposition | Proof of concept | - |
5 | Ref. 42 Abdikheibari et al. (Thin film nanocomposite nanofiltration membranes from amine functionalized-boron nitride/polypiperazine amide with enhanced flux and fouling resistance) [42] | BN nanosheets embedded in the Polyamide layer of a thin film composite membrane | Fouling resistance | 97% of the initial flux retained during filtration with 120 ppm humic acid solution |
6 | Ref. 56 Abdikheibari et al. (Novel thin film nanocomposite membranes decorated with few-layered boron nitride nanosheets for simultaneously enhanced water flux and organic fouling resistance) [56] | BN nanosheets deposited on top of the Polyamide layer of a thin film composite membrane | Fouling resistance | Sodium alginate and bovine serum albumin separation maintained over 92% over 3 cycles, 59% increase in fouling resistance on addition of BN |
7 | Ref. 60 Chen et al. (Functionalized boron nitride membranes with multipurpose and super-stable semi-permeability in solvents) [60] | BN nanosheets deposited onto a porous nylon support | Solvent separation | Permeation rates of 1.5 – 2.5 mmol m−2 h−1 of paraxylene over pyrene (0.5 mol m−2 h−1) after solvation with water, ethanol, acetone, hexane, toluene |
8 | Ref. 61 Chen et al. (Functionalized boron nitride membranes with ultrafast solvent transport performance for molecular separation) [61] | BN nanosheets deposited onto a porous nylon support | Dye rejection in organic solvents | 90–100% rejection of congo red, methylene blue, evans blue in methanol for certain concentrations of the dye solutions |
9 | Ref. 57 Gonzalez-Ortiz et al. (Development of novel h-BNNS/PVA porous membranes: Via Pickering emulsion templating) [57] | BN nanosheets incorporated into a Polyvinyl alcohol matrix through pickering emulsion templating | Fouling resistance | 76% rejection of polystyrene latex particles of 0.1 microns and 99.7% rejection of 1.2 micron size particles |
10 | Ref. 58 Low et al. (Fouling resistant 2D boron nitride nanosheet – PES nano filtration membranes) [58] | BN/PES mixed matrix membrane | Fouling resistance | Flux recovery ration of 100% after fouling with 1wt% humic acid |
11 | Ref. 59 Zahirifar et al. (Influence of hexagonal boron nitride nanosheets as the additives on the characteristics and performance of PVDF for air gap membrane distillation) [59] | BN/PVDF mixed matrix membrane | Enhanced thermal stability and permeance in membrane distillation | 99% rejection of 3.5 wt% NaCl solution, along with a water flux of 7.1 kg m−2 h−1 |
12 | Ref. 41 Chen et al. (Ultrafast, Stable Ionic and Molecular Sieving through Functionalized Boron Nitride Membranes) [41] | BN nanosheets deposited onto a porous cellulose ester support | Enhance ion-permeation rates/ to compare permeation rates of various ions | Permeation rates of 1 × 10−3 mol h−1 m−2 for glycerol, sucrose and Mn2+ ions while permeation rates of 1–10 mol h−1 m−2 for Na+, K+, Ca2+, Mg2+, Zn2+ |
13 | Ref. 43 Pendse et al. (Charged Layered Boron Nitride‐Nanoflake Membranes for Efficient Ion Separation and Water Purification) [43] | BN nanosheets deposited onto an anodized aluminium oxide porous support | Anion rejection | > 97% rejection for K2SO4, MgSO4 as well as for anionic dyes such as congo red |
14 | Ref. 62 Lin et al. (Graphite oxide/boron nitride hybrid membranes: The role of cross-plane laminar bonding for a durable membrane with large water flux and high rejection rate) [62] | BN and GO nanosheets alternately deposited onapolydopamine coated porous PES support | Stabilization of GO, dye rejection | 99.98% rejection of methylene blue, stable over 9 h |
15 | Ref. 63 Chen et al. (Bio-inspired Nanocomposite Membranes for Osmotic Energy Harvesting) [63] | BN/Aramid nanofiber composite membrane | Osmotic power generation | 0.6 Wm−2 power density, retained over 200 h |
16 | Ref. 64 Yazda et al. (High Osmotic Power Generation via Nanopore Arrays in Hybrid Hexagonal Boron Nitride/Silicon Nitride Membranes) [64] | BN/SiN hybrid membrane | Osmotic power generation | Varied between 10–30 pW depending on the pore spacing |
17 | Ref. 66 Das et al. (High flux and adsorption based non-functionalized hexagonal boron nitride lamellar membrane for ultrafast water purification) [66] | BN nanosheets deposited onto a PVDF porous support | Dye rejection | > 90% rejection of methyl orange and direct red-80, adsorption capacitites for bisphenol A, methyl orange and direct red-80: 125.7, 120.8, and 328.2 mg/g |
18 | Ref. 65 Keshebo et al. (Simultaneous exfoliation and functionalization of hexagonal boron nitride in the aqueous phase for the synthesis of high-performance wastewater treatment membrane) [65] | BN nanosheets deposited onto a porous nylon support | Dye rejection, fouling resistance | 90% rejection of methylene blue, rhodamine B and congo red, > 92% of initial flux maintained after 7 cycles |
31 | Ref. 67 Liang, G. et al. (Boron Nitride Ultrathin Fibrous Nanonets: One-Step Synthesis and Applications for Ultrafast Adsorption for Water Treatment and Selective Filtration of Nanoparticles) [67] | Nanonet made from BN nanofibres | Dye removal | 327.8 mg/g of methylene blue adsorbed in 1 min |
32 | Ref. 68 Liang, G. et al. (Controlled Fabrication of Ultrathin-Shell BN Hollow Spheres with Excellent Performance in Hydrogen Storage and Wastewater Treatment) [68] | BN Nanospheres | Hydrogen storage, dye removal | Adsorption capacity for basic yellow 1 and methylene blue- 191.7 and 116.5 mg/g, hydrogen uptake capacity up to 4.07 wt.% at 298 K and 10 MPa |
33 | Ref. 69 Liu et al. (Nanosheet-Structured Boron Nitride Spheres with a Versatile Adsorption Capacity for Water Cleaning) [69] | BN spheres | Heavy metals and organic dye removal | Adsorption capacities for malachite green and methylene blue—324 and 233 mg/g, for Cu2+, Pb2+, and Cd2+ are 678.7, 536.7, and 107.0 mg/g |
34 | Ref. 44 Li J et al. (Activated Boron Nitride as an Effective Adsorbent for Metal Ions and Organic Pollutants) [44] | Porous BN ribbons | Heavy metal, antibiotic, dye removal | Adsorption capacity for Co2+, Ni2+, Ce3+, and Pb2+—215, 235, 282 and 225 mg/g, for tetracycline, methyl orange and congo red and 300–400 mg/g |
35 | Ref. 75 Li Jie et al. (Chemical Activation of Boron Nitride Fibers for Improved Cationic Dye Removal Performance) [75] | BN fibres | Dye removal | Adsorption capacity for methylene blue was 392.2 mg/g |
36 | Ref 76 Song et al. (The Performance of Porous Hexagonal BN in High Adsorption Capacity towards Antibiotics Pollutants from Aqueous Solution) [76] | Rod like porous BN | Antibiotic removal | adsorption capacity for tetracycline—322.16 mg/g |
37 | Ref 79 Jei Li et al. (NaOH-Embedded Three-Dimensional Porous Boron Nitride for Efficient Formaldehyde Removal) [79] | 3D BN adsorbent | Formaldehyde adsorption | Adsorption capacity for formaldehyde > 350 mg/g |
38 | Ref 45 Yanming Xue et al. (Template-free synthesis of boron nitride foam-like porous monoliths and their high-end applications in water purification) [45] | Porous BN monolith | Heavy metal and dye removal | Adsorption capacity for rhodamine B and Cd2+ was 554 mg/g and 561 mg/g |
39 | Ref 80 Jun Yin et al. (Ultralight Three-Dimensional Boron Nitride Foam with Ultralow Permittivity and Superelasticity) [80] | BN foam | Proof of concept | - |
40 | Ref 84 Liu Z (Novel Multifunctional Cheese-like 3D Carbon-BN as a Highly Efficient Adsorbent for Water Purification) [84] | C-BN foam | Heavy metal and dye removal | Adsorption capacity for methylene blue and congo red was 402.25 mg/g and 307 mg/g, Cr3+ is 453.1 mg/g, Cd2+ and Ni2+ are 482.1 and 172.6 mg/g |
41 | Ref 86 Krishna Kumar et al. (Heavy Metal and Organic Dye Removal via a Hybrid Porous Hexagonal Boron Nitride-Based Magnetic Aerogel) [86] | BN nanosheets/Polyvinylalcohol foam | Heavy metal, dye removal | Adsorption capacity for Cr(VI), As(V), methylene blue, and acid orange was 833, 426, 415, 286 mg/g |
42 | Ref 87 Liu et al. (Layer‐by‐Layer Assembly Fabrication of Porous Boron Nitride Coated Multifunctional Materials for Water Cleaning) [87] | BN nanosheets deposited on cotton fabric or melamine | Oil–water separation | Adsorption ability for pump oil, white oil, and chloroform was in the range of 58–112 times its own weight |