
Heavy metals (HMs) are persistent and toxic environmental pollutants that pose critical risks toward human health and environmental safety. Their efficient elimination from water and wastewater is essential to protect public health, ensure environmental safety, and enhance sustainability. In the recent decade, nanomaterials have been developed extensively for rapid and effective removal of HMs from water and wastewater and to address the certain economical and operational challenges associated with conventional treatment practices, including chemical precipitation, ion exchange, adsorption, and membrane separation. However, the complicated and expensive manufacturing process of nanoparticles and nanotubes, their reduced adsorption capacity due to the aggregation, and challenging recovery from aqueous solutions limited their widespread applications for HM removal practices. Thus, the nanofibers have emerged as promising adsorbents due to their flexible and facile production process, large surface area, and simple recovery. A growing number of chemical modification methods have been devised to promote the nanofibers' adsorption capacity and stability within the aqueous systems. This paper briefly discusses the challenges regarding the effective and economical application of conventional treatment practices for HM removal. It also identifies the practical challenges for widespread applications of nanomaterials such as nanoparticles and nanotubes as HMs adsorbents. This paper focuses on nanofibers as promising HMs adsorbents and reviews the most recent advances in terms of chemical grafting of nanofibers, using the polymers blend, and producing the composite nanofibers to create highly effective and stable HMs adsorbent materials. Furthermore, the parameters that influence the HM removal by electrospun nanofibers and the reusability of adsorbent nanofibers were discussed. Future research needs to address the gap between laboratory investigations and commercial applications of adsorbent nanofibers for water and wastewater treatment practices are also presented.
Citation: Maryam Salehi, Donya Sharafoddinzadeh, Fatemeh Mokhtari, Mitra Salehi Esfandarani, Shafieh Karami. Electrospun nanofibers for efficient adsorption of heavy metals from water and wastewater[J]. Clean Technologies and Recycling, 2021, 1(1): 1-33. doi: 10.3934/ctr.2021001
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Heavy metals (HMs) are persistent and toxic environmental pollutants that pose critical risks toward human health and environmental safety. Their efficient elimination from water and wastewater is essential to protect public health, ensure environmental safety, and enhance sustainability. In the recent decade, nanomaterials have been developed extensively for rapid and effective removal of HMs from water and wastewater and to address the certain economical and operational challenges associated with conventional treatment practices, including chemical precipitation, ion exchange, adsorption, and membrane separation. However, the complicated and expensive manufacturing process of nanoparticles and nanotubes, their reduced adsorption capacity due to the aggregation, and challenging recovery from aqueous solutions limited their widespread applications for HM removal practices. Thus, the nanofibers have emerged as promising adsorbents due to their flexible and facile production process, large surface area, and simple recovery. A growing number of chemical modification methods have been devised to promote the nanofibers' adsorption capacity and stability within the aqueous systems. This paper briefly discusses the challenges regarding the effective and economical application of conventional treatment practices for HM removal. It also identifies the practical challenges for widespread applications of nanomaterials such as nanoparticles and nanotubes as HMs adsorbents. This paper focuses on nanofibers as promising HMs adsorbents and reviews the most recent advances in terms of chemical grafting of nanofibers, using the polymers blend, and producing the composite nanofibers to create highly effective and stable HMs adsorbent materials. Furthermore, the parameters that influence the HM removal by electrospun nanofibers and the reusability of adsorbent nanofibers were discussed. Future research needs to address the gap between laboratory investigations and commercial applications of adsorbent nanofibers for water and wastewater treatment practices are also presented.
Plasma physics simply refers to the study of a state of matter consisting of charged particles. Plasmas are usually created by heating a gas until the electrons become detached from their parent atom or molecule. In addition, plasma can be generated artificially when a neutral gas is heated or subjected to a strong electromagnetic field. The presence of free charged particles makes plasma electrically conductive with the dynamics of individual particles and macroscopic plasma motion governed by collective electromagnetic fields [1].
Nonlinear partial differential equations (NPDE) in the fields of mathematics and physics play numerous important roles in theoretical sciences. They are the most fundamental models essential in studying nonlinear phenomena. Such phenomena occur in plasma physics, oceanography, aerospace industry, meteorology, nonlinear mechanics, biology, population ecology, fluid mechanics to mention a few. We have seen in [2] that the authors studied a generalized advection-diffusion equation which is a NPDE in fluid mechanics, characterizing the motion of buoyancy propelled plume in a bent-on absorptive medium. Moreover, in [3], a generalized Korteweg-de Vries-Zakharov-Kuznetsov equation was studied. This equation delineates mixtures of warm adiabatic fluid, hot isothermal as well as cold immobile background species applicable in fluid dynamics. Furthermore, the authors in [4] considered a NPDE where they explored important inclined magneto-hydrodynamic flow of an upper-convected Maxwell liquid through a leaky stretched plate. In addition, heat transfer phenomenon was studied with heat generation and absorption effect. The reader can access more examples of NPDEs in [5,6,7,8,9,10,11,12,13,14,15,16].
In order to really understand these physical phenomena it is of immense importance to solve NPDEs which govern these aforementioned phenomena. However, there is no general systematic theory that can be applied to NPDEs so that their analytic solutions can be obtained. Nevertheless, in recent times scientists have developed effective techniques to obtain viable analytical solutions to NPDEs, such as inverse scattering transform [16], simple equation method [17], Bäcklund transformation [18], F-expansion technique [19], extended simplest equation method[20], Hirota technique [21], Lie symmetry analysis [22,23,24,25,26,27], bifurcation technique [28,29], the (G′/G)-expansion method [30], Darboux transformation [31], sine-Gordon equation expansion technique [32], Kudryashov's method [33], and so on.
The (2+1)-dimensional Bogoyavlensky-Konopelchenko (BK) equation given as
utx+6αuxuxx+3βuxuxy+3βuyuxx+αuxxxx+βuxxxy=0, | (1.1) |
where parameters α and β are constants, is a special case of the KdV equation in [34] which was introduced as a (2+1)-dimensional version of the KdV and it is described as an interaction of a long wave propagation along x-axis and a Riemann wave propagation along the y-axis [35]. In addition to that, few particular properties of the equation have been explored. The authors in [36] provided a Darboux transformation for the BK equation and the obtained transformation was used to construct a family of solutions of this equation. In [37], with 3β replaced by 4β and uy=vx in (1.1), the authors integrated the result once to get
ut+αuxxx+βvxxx+3αu2x+4βuxvx=0,uy−vx=0. | (1.2) |
Further, they utilized Lie group theoretic approach to obtain solutions of the system of Eq (1.2). They also engaged the concept of nonlinear self-adjointness of differential equations in conjunction with formal Lagrangian of (1.2) for constructing nonlocal conservation laws of the system. In addition, various applications of BK equation (1.1) were highlighted in [37]. Further investigations on certain particular cases of (1.1) were also carried out in [38,39].
In [40], the 2D generalized BK equation that reads
utx+k1uxxxx+k2uxxxy+2k1k3k2uxuxx+k3(uxuy)x+γ1uxx+γ2uxy+γ3uyy=0 | (1.3) |
was studied and lump-type and lump solutions were constructed by invoking the Hirota bilinear method. Liu et al. [41] applied the Lie group analysis together with (G′/G)-expansion and power series methods and obtained some analytic solutions of (1.3).
Yang et al. [42] recently examined a generalized combined fourth-order soliton equation expressed as
α(6uxuxx+uxxxx)+β[3(uxut)x+uxxxt]+γ[3(uxuy)x+uxxxy]+δ1uyt+δ2uxx+δ3uxt+δ4uxy+δ5uyy+δ6utt=0, | (1.4) |
with constant parameters α,β and γ which are not all zero, whereas all constant coefficients δi,1≤i≤6, are arbitrary. It was observed that Eq (1.4) comprises three fourth-order terms and second-order terms that consequently generalizes the standard Kadomtsev-Petviashvili equation. Soliton equations are known to have applications in plasma physics and other nonlinear sciences such as fluid mechanics, atomic physics, biophysics, nonlinear optics, classical and quantum fields theories.
Assuming α=0, β=1, γ=0 and δ1=δ2=1, δ3=δ4=δ5=δ6=0, the authors gain an integrable (1+2)-dimensional extension of the Hirota-Satsuma equation commonly referred to as the Hirota-Satsuma-Ito equation in two dimensions[43] given as
uty+uxx+3(uxut)x+uxxxt=0 | (1.5) |
that satisfies the Hirota three-soliton condition and also admits a Hirota bilinear structure under logarithmic transformation presented in the form
u=2(lnf)x,where(D3xDt+DyDt+D2x)f⋅f=0, | (1.6) |
whose lump solutions have been calculated in [44]. On taking parameters α=1, β=0, γ=0 along with δ1=δ4=δ6=0 whereas δ2=δ3=δ5=1, they eventually came up with a two dimensional equation[42]:
utx+6uxuxx+uxxxx+uxxxy+3(uxuy)x+uxx+uyy=0, | (1.7) |
which is called a two-dimensional generalized Bogoyavlensky-Konopelchenko (2D-gBK) equation. We notice that if one takes α=β=1 in Eq (1.1) with the introduction of two new terms uxx and uyy, the new generalized version (1.7) is achieved.
In consequence, we investigate explicit solutions of the new two-dimensional generalized Bogoyavlensky-Konopelchenko equation (1.7) of plasma physics in this study. In order to achieve that, we present the paper in the subsequent format. In Section 2, we employ Lie symmetry analysis to carry out the symmetry reductions of the equation. In addition, direct integration method will be employed in order to gain some analytic solutions of the equation by solving the resulting ordinary differential equations (ODEs) from the reduction process. We achieve more analytic solutions of (1.7) via the conventional (G′/G)-expansion method as well as Kudryashov's technique. In addition, by choosing suitable parametric values, we depict the dynamics of the solutions via 3-D, 2-D as well as contour plots. Section 3 presents the conservation laws for 2D-gBK equation (1.7) through the multiplier method and in Section 4, we give the concluding remarks.
In this section we in the first place compute the Lie point symmetries of Eq (1.7) and thereafter engage them to generate analytic solutions.
A one-parameter Lie group of symmetry transformations associated with the infinitesimal generators related to (\real{gbk}) can be presented as
ˉt=t+ϵξ1(t,x,y,u)+O(ϵ2),ˉx=x+ϵξ2(t,x,y,u)+O(ϵ2),ˉy=y+ϵξ3(t,x,y,u)+O(ϵ2),ˉu=u+ϵϕ(t,x,y,u)+O(ϵ2). | (2.1) |
We calculate symmetry group of 2D-gBK equation (1.7) using the vector field
R=ξ1(t,x,y,u)∂∂t+ξ2(t,x,y,u)∂∂x+ξ3(t,x,y,u)∂∂y+ϕ(t,x,y,u)∂∂u, | (2.2) |
where ξi,i=1,2,3 and ϕ are functions depending on t, x, y and u. We recall that (2.2) is a Lie point symmetry of Eq (1.7) if
R[4](utx+6uxuxx+uxxxx+uxxxy+3(uxuy)x+uxx+uyy)|Q=0=0, | (2.3) |
where Q=utx+6uxuxx+uxxxx+uxxxy+3(uxuy)x+uxx+uyy. Here, R[4] denotes the fourth prolongation of R defined by
R[4]=R+ηt∂ut+ηx∂ux+ηy∂uy+ηtx∂utx+ηxx∂uxx+ηyy∂uyy+ηxxxx∂uxxxx+ηxxxy∂uxxxy, | (2.4) |
where coefficient functions ηt, ηx, ηy, ηxt, ηxx, ηxy, ηyy, ηxxxx and ηxxxy can be calculated from [22,23,24].
Writing out the expanded form of the determining equation (2.3), splitting over various derivatives of u and with the help of Mathematica, we achieve the system of linear partial differential equations (PDEs):
ξ3x=0,ξ1x=0,ξ1y=0,ξ2u=0,ξ1u=0,ξ3u=0,ξ1tt+5ξ2yy=0,ξ1t+5ϕu=0,5ξ2x−ξ1t=0,5ξ2y−2ξ1t=0,5ξ3y−3ξ1t=0,3ϕxx−ξ3yy=0,ξ3t−3ϕx+2ξ2y=0,4ξ1t−5ξ2t+30ϕx+15ϕy=0,ϕtx+ϕxx+ϕxxxx+ϕxxxy+ϕyy=0. |
The solution of the above system of PDEs is
ξ1=A1+A2t,ξ2=F(t)+15A2(x+2y),ξ3=A4−45A2t+3A3t+35A2y,η=G(t)−15A2u+A3x−415A2y−2A3y+13yF′(t), |
where A1–A3 are arbitrary constants and F(t), G(t) are arbitrary functions of t. Consequently, we secure the Lie point symmetries of (1.7) given as
R1=∂∂t,R2=∂∂y,R3=3F(t)∂∂x+yF′(t)∂∂u,R4=3t∂∂y+(x−2y)∂∂u,R5=G(t)∂∂u,R6=15t∂∂t+(3x+6y)∂∂x+(9y−12t)∂∂y−(4y+3u)∂∂u. | (2.5) |
We contemplate the exponentiation of the vector fields (2.5) by computing the flow or one parameter group generated by (2.5) via the Lie equations [22,23]:
dˉtdϵ=ξ1(ˉt,ˉx,ˉy,ˉu),ˉt|ϵ=0=t,dˉxdϵ=ξ2(ˉt,ˉx,ˉy,ˉu),ˉx|ϵ=0=x,dˉydϵ=ξ3(ˉt,ˉx,ˉy,ˉu),ˉy|ϵ=0=y,dˉudϵ=ϕ(ˉt,ˉx,ˉy,ˉu),ˉu|ϵ=0=u. |
Therefore, by taking F(t)=G(t)=t in (2.5), one computes a one parameter transformation group of 2D-gBK (1.7). Thus, we present the result in the subsequent theorem.
Theorem 2.1. Let Tiϵ(t,x,y,u),i=1,2,3,…,6 be transformations group of one parameter generated by vectors R1,R2,R3…,R6 in (2.5), then, for each of the vectors, we have accordingly
T1ϵ:(˜t,˜x,˜y,˜u)⟶(t+ϵ1,x,y,u),T2ϵ:(˜t,˜x,˜y,˜u)⟶(t,x,y+ϵ2,u),T3ϵ:(˜t,˜x,˜y,˜u)⟶(t,3ϵ3t+x,y,ϵ3y+u),T4ϵ:(˜t,˜x,˜y,˜u)⟶(t,x,3ϵ4t+y,u+(x−2y)ϵ4−3ϵ24t),T5ϵ:(˜t,˜x,˜y,˜u)⟶(t,x,y,ϵ5t+u),T6ϵ:˜t,˜x,˜y,˜u)⟶(te15ϵ6,(2e9ϵ6−e3ϵ6−e15ϵ6)t+xe3ϵ6+(e9ϵ6−e3ϵ6)y,(2e9ϵ6−2e15ϵ6)t+ye9ϵ6,19[(4e18ϵ6−6e12ϵ6+2)t+(3−3e12ϵ6)y+9u]e−3ϵ6), |
where ϵ∈R is regarded as the group parameter.
Theorem 2.2. Hence, suppose u(t,x,y)=Θ(t,x,y) satisfies the 2D-gBK (1.7), in the same vein, the functions given in the structure
u1(t,x,y)=Θ(t−ϵ1,x,y,z),u2(t,x,y)=Θ(t,x,y−ϵ2,z,u),u3(t,x,y)=Θ(t,x−3ϵ3t,y)−ϵ3y,u4(t,x,y)=Θ(t,x,3ϵ4t+y)−(x−2y)ϵ4+3ϵ24t,u5(t,x,y)=Θ(t,x,y)−ϵ5t,u6(t,x,y)=Θ[te15ϵ6,(2e9ϵ6−e3ϵ6−e15ϵ6)t+xe3ϵ6+(e9ϵ6−e3ϵ6)y,(2e9ϵ6−2e15ϵ6)t+ye9ϵ6]−23te12ϵ6+49te18ϵ6+29t−13ye12ϵ6+13y |
will do, where ui(t,x,y)=Tϵi⋅Θ(t,x,y),i=1,2,3,…,6 with ϵ<<1 regarded as any positive real number.
In this subsection, we utilize symmetries (2.5) with a view to reduce Eq (1.7) to ordinary differential equations and thereafter obtain the analytic solutions of Eq (1.7) by solving the respective ODEs.
Case 1. Invariant solutions via R1–R3
Taking F(t)=1/3, we linearly combine translational symmetries R1–R3 as R=bR1+cR2+aR3 with nonzero constant parameters a, b and c. Subsequently utilizing the combination reduces 2D-gBK equation (1.7) to a PDE with two independent variables. Thus, solution to the characteristic equation associated with the symmetry R leaves us with invariants
r=ct−ay,s=cx−by,θ=u. | (2.6) |
Now treating θ above as the new dependent variable as well as r, s as new independent variables, (1.7) then transforms into the PDE:
c2θrs+6c3θsθss+c4θssss−3ac2θsθsr−6bc2θsθss−3ac2θrθss−ac3θsssr−bc3θssss+c2θss+a2θrr+2abθsr+b2θss=0. | (2.7) |
We now utilize the Lie point symmetries of (2.7) in a bid to transform it to an ODE. From (2.7), we achieve three translation symmetries:
Q1=∂∂r,Q2=∂∂s,Q3=∂∂θ. |
The linear combination Q=Q1+ωQ2 (ω≠0 being an arbitrary constant) leads to two invariants:
z=s−ωr,θ=Θ, | (2.8) |
that secures group-invariant solution Θ=Θ(z). Thus, on using these invariants, (2.7) is transformed into the fourth-order nonlinear ODE:
(c2−ωc2+a2ω2−2baω+b2)Θ″(z)−6(βbc2−βc2aω−c3)Θ′(z)Θ″(z)+(c3aω+c4−bc3)Θ⁗(z)=0, |
which we rewrite in a simple structure as
AΘ″(z)−BΘ′(z)Θ″(z)+CΘ⁗(z)=0, | (2.9) |
where A=c2−ωc2+a2ω2−2baω+b2, B=6(bc2−c2aω−c3), C=c3aω+c4−bc3 and z=cx+(aω−b)y−cωt.
In this section, we seek travelling wave solutions of the 2D-gBK equation (1.7).
A. Elliptic function solution of (1.7)
On integrating equation (2.9) once, we accomplish a third-order ODE:
AΘ′(z)−12BΘ′2(z)+CΘ‴(z)+C1=0, | (2.10) |
where C1 is a constant of integration. Multiplying Eq (2.10) by Θ″(z), integrating once and simplifying the resulting equation, we have the second-order nonlinear ODE:
12AΘ′(z)2−16BΘ′(z)3+12CΘ″(z)2+C1Θ′(z)+C2=0, |
where C2 is a constant of integration. The above equation can be rewritten as
Θ″(z)2=B3CΘ′(z)3−ACΘ′(z)2−2C1CΘ′(z)−2C2C. | (2.11) |
Letting U(z)=Θ′(z), Eq (2.11) becomes
U′(z)2=B3CU(z)3−ACU(z)2−2C1CU(z)−2C2C. | (2.12) |
Suppose that the cubic equation
U(z)3−3ABU(z)2−6C1BU(z)−6C2B=0 | (2.13) |
has real roots c1–c3 such that c1>c2>c3, then Eq (2.12) can be written as
U′(z)2=B3C(U(z)−c1)(U(z)−c2)(U(z)−c3), | (2.14) |
whose solution with regards to Jacobi elliptic function [45,46] is
U(z)=c2+(c1−c2)cn2{√B(c1−c2)12Cz,Δ2},Δ2=c1−c2c1−c3, | (2.15) |
with (cn) being the elliptic cosine function. Integration of (2.15) and reverting to the original variables secures a solution of 2D-gBK equation (1.7) as
u(t,x,y)=√12C(c1−c2)2B(c1−c3)Δ8{EllipticE[sn(B(c1−c3)12Cz,Δ2),Δ2]}+{c2−(c1−c2)1−Δ4Δ4}z+C3, | (2.16) |
with z=cx+(aω−b)y−cωt and C3 a constant of integration. We note that (2.16) is a general solution of (1.7), where EllipticE[p;q] is the incomplete elliptic integral [46,47] expressed as
EllipticE[p;q]=∫p0√1−q2r21−r2dr. |
We present wave profile of periodic solution (2.16) in Figure 1 with 3D, contour and 2D plots with parametric values a=−4, b=0.2, c=−0.1, ω=0.1, c1=100, c2=50.05, c3=−60, B=10, C=70, where t=1 and −10≤x,y≤10.
However, contemplating a special case of (2.9) with B=0, we integrate the equation twice and so we have
CΘ″(z)+AΘ(z)+K1z+K2=0, | (2.17) |
where K1 and K2 are integration constants. Solving the second-order linear ODE (2.17) and reverting to the basic variables, we achieve the trigonometric solution of 2D-gBK equation (1.7) as
u(t,x,y)=A1sin(√a2ω2−ω(2ab+c2)+b2+c2z√c3(aω−b+c))+A2cos(√a2ω2−ω(2ab+c2)+b2+c2z√c3(aω−b+c))−K1z+K2a2ω2−ω(2ab+c2)+b2+c2, | (2.18) |
with A1 and A2 as the integration constants as well as z=cx+(aω−b)y−cωt. We depict the wave dynamics of periodic solution (2.18) in Figure 2 via 3D, contour and 2D plots with dissimilar parametric values a=1, b=0.2, c=−0.1, ω=0.1, A1=20, A2=−2, K1=1, K2=10, where t=2 and −10≤x,y≤10.
B. Weierstrass elliptic solution of 2D-gBK equation (1.7)
We further explore Weierstrass elliptic function solution of (1.7), which is a technique often involved in getting general exact solutions to NPDEs [47,48]. In order to accomplish this, we use the transformation
U(z)=W(z)+AB | (2.19) |
and transform the nonlinear ordinary differential equation (NODE) (2.12) to
W2ξ=4W3−g2W−g3,ξ=√B12Cz, | (2.20) |
with the invariants g2 and g3 given by
g2=−12A2B2−24C1Bandg3=−8A3B3−24AC1B2−24C2B. |
Thus, we have the solution of NODE (2.12) as
U(z)=AB+℘(√112C(z−z0);g2;g3), | (2.21) |
where ℘ denotes the Weierstrass elliptic function [46]. In consequence, integration of (2.21) and reverting to the basic variables gives the solution of 2D-gBK equation (1.7) as
u(t,x,y)=AB(z−z0)−√12BCζ[√B12C(z−z0);g2,g3], | (2.22) |
with arbitrary constant z0, z=cx+(aω−b)y−cωt and ζ being the Weierstrass zeta function [46]. We give wave profile of Weierstrass function solution (2.22) in Figure 3 with 3D, contour and 2D plots using parameter values a=1, b=0.2, c=−0.1, ω=0.1, A=10, B=−2, z0=0, C=1, C1=1, C2=10, where t=2 and −10≤x,y≤10.
This part of the study furnishes the solution of 2D-gBK equation (1.7) through the use of Kudryashov's approach [33]. This technique is one of the most prominent way to obtain closed-form solutions of NPDEs. Having reduced Eq (1.7) to the NODE (2.9), we assume the solution of (2.9) as
Θ(z)=N∑n=0BnQn(z), | (2.23) |
with Q(z) satisfying the first-order NODE
Q′(z)=Q2(z)−Q(z). | (2.24) |
We observe that the solution of (2.24) is
Q(z)=11+exp(z). | (2.25) |
The balancing procedure for NODE (2.9) produces N=1. Hence, from (2.23), we have
Θ(z)=B0+B1Q(z). | (2.26) |
Now substituting (2.26) into (2.9) and using (2.24), we gain a long determining equation and splitting on powers of Q(z), we get algebraic equations for the coefficients B0 and B1 as
Q(z)5:2aB1c3ω+aB21c2ω−2bB1c3−bB21c2+2B1c4+B21c3=0,Q(z)4:2bB1c3−2aB1c3ω−aB21c2ω+bB21c2−2B1c4−B21c3=0,Q(z)3:a2B1ω2−2abB1ω+25aB1c3ω+12aB21c2ω+b2B1−25bB1c3−12bB21c2+25B1c4+12B21c3−B1c2ω+B1c2=0,Q(z)2:2abB1ω−a2B1ω2−5aB1c3ω−2aB21c2ω−b2B1+5bB1c3+2bB21c2−5B1c4−2B21c3+B1c2ω−B1c2=0,Q(z):a2B1ω2−2abB1ω+aB1c3ω+b2B1−bB1c3+B1c4−B1c2ω+B1c2=0. | (2.27) |
The solution of the above system gives
B0=0,B1=−2c,a=2bω−c3ω∓√c2ω2(c4−4c2+4ω−4)2ω2. | (2.28) |
Hence, the solution of 2D-gBK equation (1.7) associated with (2.28) is given as
u(t,x,y)=−2c1+exp{cx+(aω−b)y−cωt}. | (2.29) |
The wave profile of solution (2.29) is shown in Figure 4 with 3D, contour and 2D plots using parameter values a=1, b=−0.2, c=20, ω=0.05, B0=0 with t=7 and −6≤x,y≤6.
We reckon the (G′/G)-expansion technique [30] in the construction of analytic solutions of 2D-gBK equation (1.7) and so we contemplate a solution structured as
Θ(z)=M∑j=0Bj(Q′(z)Q(z))j, | (2.30) |
where Q(z) satisfies
Q″(z)+λQ′(z)+μQ(z)=0 | (2.31) |
with λ and μ taken as constants. Here, B0,…,BM are parameters to be determined. Utilization of balancing procedure for (2.9) produces M=1 and as a result, the solution of (1.7) assumes the form
Θ(z)=B0+B1(Q′(z)Q(z)). | (2.32) |
Substituting the value of Θ(z) from (2.32) into (2.9) and using (2.31) and following the steps earlier adopted, leads to an algebraic equation in B0 and B1, which splits over various powers of Q(z) to give the system of algebraic equations whose solution is secured as
B0=0,B1=2c,a=16bω−B31λ2ω±√Ω0+64B21ω3−64B21ω2+4B31μω16ω2, |
where Ω0=B61λ4ω2−8B61λ2μω2−16B41λ2ω2+16B61μ2ω2+64B41μω2. Thus, we have three types of solutions of the 2D-gBK equation (1.7) given as follows:
When λ2−4μ>0, we gain the hyperbolic function solution
u(t,x,y)=B0+B1(Δ1A1sinh(Δ1z)+A2cosh(Δ1z)A1cosh(Δ1z)+A2sinh(Δ1z)−λ2), | (2.33) |
with z=cx+(aω−b)y−cωt, Δ1=12√λ2−4μ together with A1, A2 being arbitrary constants. The wave profile of solution (2.33) is shown in Figure 5 with 3D, contour and 2D plots using parameter values a=3, b=0.5, c=10, ω=−0.1, B0=0, λ=−0.971, μ=10, A1=5, A2=1, where t=10 and −10≤x,y≤10.
When λ2−4μ<0, we achieve the trigonometric function solution
u(t,x,y)=B0+B1(Δ2A2cos(Δ2z)−A1sin(Δ2z)A1cos(Δ2z)+A2sin(Δ2z)−λ2), | (2.34) |
with z=cx+(aω−b)y−cωt, Δ2=12√4μ−λ2 together with A1 and A2 are arbitrary constants. The wave profile of solution (2.34) is shown in Figure 6 with 3D, contour and 2D plots using parameter values a=1, b=0.5, c=0.3, ω=0.3, B0=0, λ=−0.971, μ=2, A1=5, A2=1 with t=10 and −10≤x,y≤10.
When λ2−4μ=0, we gain the rational function solution
u(t,x,y)=B0+B1(A2A1+A2z−λ2), | (2.35) |
with z=cx+(aω−b)y−cωt and A1, A2 being arbitrary constants. We plot the graph of solution (2.35) in Figure 7 via 3D, contour and 2D plots using parametric values a=1, b=1.01, c=100, ω=0.1, B0=10, λ=10, A1=3, A2=10, where t=2.4 and −5≤x,y≤5.
Case 2. Group-invariant solutions via R4
Lagrange system associated with the symmetry R4=3t∂/∂y+(x−2y)∂/∂u is
dt0=dx0=dy3t=du(x−2y), | (2.36) |
which leads to the three invariants T=t,X=x,Q=u+(y2/3t)−(xy/3t). Using these three invariants, the 2D-gBK equation (1.7) is reduced to
18TQXQXX+3TQTX+3TQXX+3XQXX+3QX+3TQXXXX−2=0. | (2.37) |
Case 3. Group-invariant solutions via R1,R2andR5
We take G(t)=1 and by combining the generators R1,R2 as well as R5, we solve the characteristic equations corresponding to the combination and get the invariants X=x, Y=y−t with group-invariant u=Q(X,Y)+t. With these invariants, the 2D-gBK equation (1.7) transforms to the NPDE
QXX+QYY−QXY+3QXQXY+3QYQXX+6QXQXX+QXXXX+QXXXY=0, | (2.38) |
whose solution is given by
Q(X,Y)=2A2tanh[A2X+A2(12−12√16A42−24A22−3−2A22)Y+A1]+A3, | (2.39) |
with arbitrary constants A1–A3. Thus, we achieve the hyperbolic solution of (1.7) as
u(t,x,y)=t+2A2tanh[12A2(t−y)√16A42−24A22−3+12(4t−4y)A32+12(y+2x−t)A2+A1]+A3. | (2.40) |
The wave profile of solution (2.40) is shown in Figure 8 with 3D, contour and 2D plots using parameter values A1=70.1, A2=−30, A3=0, where t=0.5 and −10≤x,y≤10.
Besides, symmetries of (2.38) are found as
P1=∂∂X,P2=∂∂Y,P3=∂∂Q,P4=(13X+23Y)∂∂X+Y∂∂Y+(23X−2Y−13Q)∂∂Q. |
Now, the symmetry P1 furnishes the solution Q(X,Y)=f(z), z=Y. So, Eq (2.38) gives the ODE f″(z)=0. Hence, we have a solution of (1.7) as
u(t,x,y)=t+A0(y−t)+A1, | (2.41) |
with A0, A1 as constants. Further, the symmetry P2 yields Q(X,Y)=f(z), z=X and so Eq (2.38) reduces to
f″(z)+6f′(z)f″(z)+f⁗(z)=0. | (2.42) |
Integration of the above equation three times with respect to z gives
f′(z)2+2f(z)3+f(z)2+2A0f(z)+2A1=0, | (2.43) |
and taking constants A0=A1=0 and then integrating it results in the solution of (1.7) as
u(t,x,y)=t−12{1+tan(12A1−12x)2}. | (2.44) |
The wave profile of solution (2.44) is shown in Figure 9 with 3D, contour and 2D plots using parameter values A1=40, t=3.5 and −10≤x≤10.
On combining P1–P3 as P=c0P1+c1P2+c2P3, we accomplish
Q(X,Y)=c2c0X+f(z),wherez=c0Y−c1X. | (2.45) |
Using the newly acquired invariants (2.45), Eq (2.38) transforms to the NODE:
c0c21f″(z)+6c21c2f″(z)−3c0c1c2f″(z)+c20c1f″(z)+c30f″(z)+6c20c21f′(z)f″(z)−6c0c31f′(z)f″(z)+c0c41f⁗(z)−c20c31f⁗(z)=0. | (2.46) |
Engaging the Lie point symmetry P4, we obtain
Q(X,Y)=X−2Y+Y−1/3f(z)withz=Y−1/3(X−Y), | (2.47) |
and Eq (2.38) reduces to the NODE
6zf′(z)+z2f″(z)−18f′(z)2−9f(z)f″(z)+4f(z)−18zf′(z)f″(z)−12f‴(z)−3zf⁗(z)=0. | (2.48) |
Case 4. Group-invariant solutions via R6
Lie point symmetry R6 dissociates to the Lagrange system
dt15t=dx3x+6y=dy9y−12t=du−(4y+3u), |
which gives
u=t−1/5Q(T,X)−29t−13y,withT=(2t+y)t−3/5andX=(x−t−y)t−1/5. | (2.49) |
Substituting the expression of u in (1.7), we obtain the NPDE
5QTT−3TQTX−XQXX−2QX+15QXQTX+15QTQXX+5QTXXX=0, | (2.50) |
which has two symmetries:
P1=∂∂Q,P2=∂∂X+115T∂∂Q. |
The symmetry P2 gives Q(X,Y)=f(z)+(1/15)TX, z=T and hence (2.50) reduces to
75f″(z)−4z=0. |
Solving the above ODE and reverting to the basic variables gives the solution of (1.7) as
u(t,x,y)=15√t{(2t+y)(x−t−y)15t4/5+2(2t+y)3225t9/5+(2t+y)t3/5A1+A2}−2t9−y3, | (2.51) |
where A1 and A2 are integration constants. The wave profile of solution (2.51) is shown in Figure 10 with 3D, contour and 2D plots using parameter values A1=−0.3, A2=−50 with t=1.1 and −10≤x,y≤10.
Next, we invoke the symmetry P1+P2. This yields Q(X,Y)=f(z)+X+(1/15)TX,z=T. Consequently, we have the transformed version of (2.50) as
75f″(z)−4z−15=0. |
Solving the above ODE and reverting to basic variables gives the solution of (1.7) as
u(t,x,y)=15√t{(2t+y)(x−t−y)15t4/5+2(2t+y)3225t9/5+(2t+y)210t6/5+(2t+y)t3/5A1+A2}−2t9−y3. | (2.52) |
The wave profile of solution (2.52) is shown in Figure 11 with 3D, contour and 2D plots using parameter values A1=−3.6, A2=50 with t=1.1 and −10≤x,y≤10.
In this section, we construct the conservation laws for 2D-gBK equation (1.7) by making use of the multiplier approach [22,49,50], but first we give some basic background of the method that we are adopting.
Consider the n independent variables x=(x1,x2,…,xn) and m dependent variables u=(u1,u2,…,um). The derivatives of u with respect to x are defined as
uαi=Di(uα),uαij=DjDi(ui),…, | (3.1) |
where
Di=∂∂xi+uαi∂∂uα+uαij∂∂uαj+⋯,i=1,...,n, | (3.2) |
is the operator of total differentiation. The collection of all first derivatives uαi is denoted by u(1), i.e., u(1)={uαi},α=1,...,m,i=1,...,n. In the same vein u(2)={uαij},α=1,...,m,i,j=1,...,n and u(3)={uαijk} and likewise u(4) etc. Since uαij=uαji, u(2) contains only uαij for i≤j.
Now consider a kth-order system of PDEs:
Gα(x,u,u(1),…,u(k))=0,α=1,2,…,m. | (3.3) |
The {Euler-Lagrange operator}, for every α, is presented as
δδuα=∂∂uα+∑s≥1(−1)sDi1…Dis∂∂uαi1i2…is,α=1,…,m. | (3.4) |
An n-tuple T=(T1,T2,…,Tn), such that
DiTi=0 | (3.5) |
holds for all solutions of (3.3) is known as the conserved vector of system (3.3).
The multiplier Ωα(x,u,u(1),…) of system (3.3) has the property that
DiTi=ΩαGα | (3.6) |
holds identically [22]. The determining equations for multipliers are obtained by taking the variational derivative of (3.6), namely
δδuα(ΩαGα)=0. | (3.7) |
The moment multipliers are generated from (3.7), the conserved vectors can be derived systematically using (3.6) as the determining equation.
Conservation laws of 2D-gBK equation (1.7) are derived by utilizing second-order multiplier Ω(t,x,y,u,ut,ux,uy,uxx,uxy), in Eq (3.7), where G is given as
G≡utx+6uxuxx+uxxxx+uxxxy+3(uxuy)x+uxx+uyy, |
and the Euler operator δ/δu is expressed in this case as\newpage
δδu=∂∂u−Dt∂∂ut−Dx∂∂ux−Dy∂∂uy+DtDx∂∂utx+DxDy∂∂uxy+D2x∂∂uxx+D2y∂∂uyy+D4x∂∂uxxxx+D3xDy∂∂uxxxy. |
Expansion of Eq (3.7) and splitting on diverse derivatives of dependent variable u gives
Ωu=0,Ωx=0,Ωyy=0,Ωyux=0,Ωuxux=0,Ωtux=0,Ωut=0,Ωuxx=0,Ωuxy=0,Ωuy=0. | (3.8) |
Solution to the above system of equations gives Ω(t,x,y,u,ut,ux,uy,uxx,uxy) as
Ω(t,x,y,u,ut,ux,uy,uxx,uxy)=C1ux+f1(t)y+f2(t), | (3.9) |
with C1 being an arbitrary constant and f1(t), f2(t) being arbitrary functions of t. Using Eq (3.6), one obtains the following three conserved vectors of Eq (1.7) that correspond to the three multipliers ux,f1(t) and f2(t):
Case 1. For the first multiplier Q1=ux, the corresponding conserved vector (Tt1,Tx1,Ty1) is given by
Tt1=12u2x,Tx1=12u2x+2u3x−12u2xx−12uxxuxy+12uxuxxy+uxxxux+12uxxxuy+12uuxxxy+12uuyy+uuxuxy+2uyu2x,Ty1=12uyux−uuxuxx−12uuxy−12uuxxxx. |
Case 2. For the second multiplier Q2=f1(t), we obtain the corresponding conserved vector (Tt2,Tx2,Ty2) as
Tt2=uxf1(t)y,Tx2=3yf1(t)u2x+3yf1(t)uxuy−yf′1(t)u+yf1(t)ux+yf1(t)uxxx+yf1(t)uxxy,Ty2=uyf1(t)y−uf1(t). |
Case 3. Finally, for the third multiplier Q3=f2(t), the corresponding conserved vector (Tt3,Tx3,Ty3) is
Tt3=uxf2(t),Tx3=3u2xf2(t)+3uxuyf2(t)−uf′2(t)+uxf2(t)+uxxxf2(t)+uxxyf2(t),Ty3=uyf2(t). |
Remark 3.1. We notice that this method assists in the construction of conservation laws of (1.7) despite the fact that it possesses no variational principle [51]. Moreover, the presence of arbitrary functions in the multiplier indicates that 2D-gBK (1.7) has infinite number of conserved vectors.
In this paper, we carried out a study on two-dimensional generalized Bogoyavlensky-Konopelchenko equation (1.7). We obtained solutions for Eq (1.7) with the use of Lie symmetry reductions, direct integration, Kudryashov's and (G′/G)-expansion techniques. We obtained solutions of (1.7) in the form of algebraic, rational, periodic, hyperbolic as well as trigonometric functions. Furthermore, we derived conservation laws of (1.7) by engaging the multiplier method were we obtained three local conserved vectors. We note here that the presence of the arbitrary functions f1(t) and f2(t) in the multipliers, tells us that one can generate unlimited number of conservation laws for the underlying equation.
The authors state no conflicts of interest.
[1] |
Liao J, Chen J, Ru X, et al. (2017) Heavy metals in river surface sediments affected with multiple pollution sources, South China: Distribution, enrichment and source apportionment. J Geochem Explor 176: 9-19. doi: 10.1016/j.gexplo.2016.08.013
![]() |
[2] |
Zhaoyong Z, Xiaodong Y, Shengtian Y (2018) Heavy metal pollution assessment, source identification, and health risk evaluation in Aibi Lake of northwest China. Environ Monit Assess 190: 1-13. doi: 10.1007/s10661-017-6437-x
![]() |
[3] |
Shikazono N, Tatewaki K, Mohiuddin KM, et al. (2012) Sources, spatial variation, and speciation of heavy metals in sediments of the Tamagawa River in Central Japan. Environ Geochem Health 34: 13-26. doi: 10.1007/s10653-011-9409-z
![]() |
[4] |
Xia F, Zhang M, Qu L, et al. (2018) Risk analysis of heavy metal concentration in surface waters across the rural-urban interface of the Wen-Rui Tang River, China. Environ Pollut 237: 639-649. doi: 10.1016/j.envpol.2018.02.020
![]() |
[5] | Kaizer A, Osakwe S (2011) Physicochemical characteristics and heavy metal levels in water samples from five river systems in Delta State, Nigeria. J Appl Sci Environ Manag 14: 83-87. |
[6] |
Islam MS, Ahmed MK, Raknuzzaman M, et al. (2015) Heavy metal pollution in surface water and sediment: A preliminary assessment of an urban river in a developing country. Ecol Indic 48: 282-291. doi: 10.1016/j.ecolind.2014.08.016
![]() |
[7] |
Ouyang W, Wang Y, Lin C, et al. (2018) Heavy metal loss from agricultural watershed to aquatic system: A scientometrics review. Sci Total Environ 637-638: 208-220. doi: 10.1016/j.scitotenv.2018.04.434
![]() |
[8] |
Chowdhury S, Mazumder MAJ, Al-Attas O, et al. (2016) Heavy metals in drinking water: Occurrences, implications, and future needs in developing countries. Sci Total Environ 569-570: 476-488. doi: 10.1016/j.scitotenv.2016.06.166
![]() |
[9] |
Santos-Echeandía J, Prego R, Cobelo-García A (2008) Influence of the heavy fuel spill from the Prestige tanker wreckage in the overlying seawater column levels of copper, nickel and vanadium (NE Atlantic Ocean). J Mar Syst 72: 350-357. doi: 10.1016/j.jmarsys.2006.12.005
![]() |
[10] | Holt MS (2000) Sources of chemical contaminants and routes into the freshwater environment. Food Chem Toxicol 38: 21-27. |
[11] |
Salehi M, Aghilinasrollahabadi K, Esfandarani MS (2020) An investigation of stormwater quality variation within an industry sector using the self-reported data collected under the stormwater monitoring program. Water 12: 1-16. doi: 10.3390/w12113185
![]() |
[12] |
Aghilinasrollahabadi K, Salehi M, Fujiwara T (2021) Investigate the influence of microplastics weathering on their heavy metals uptake in stormwater. J Hazard Mater 408: 124439. doi: 10.1016/j.jhazmat.2020.124439
![]() |
[13] |
Li F, Zhang J, Cao T, et al. (2018) Human health risk assessment of toxic elements in farmland topsoil with source identification in Jilin province, China. Int J Environ Res Public Health 15: 1040. doi: 10.3390/ijerph15051040
![]() |
[14] |
Edelstein M, Ben-Hur M (2018) Heavy metals and metalloids: Sources, risks and strategies to reduce their accumulation in horticultural crops. Sci Hortic 234: 431-444. doi: 10.1016/j.scienta.2017.12.039
![]() |
[15] |
Le Roux W, Chamier J, Genthe B, et al. (2018) The reach of human health risks associated with metals/metalloids in water and vegetables along a contaminated river catchment: South Africa and Mozambique. Chemosphere 199: 1-9. doi: 10.1016/j.chemosphere.2018.01.160
![]() |
[16] | Akpor OB, Ohiobor GO, Olaolu TD (2015) Heavy metal pollutants in wastewater effluents: sources, effects and remediation. Adv Biosci Bioeng 2: 37-43. |
[17] |
Khan K, Lu Y, Khan H, et al. (2013) Health risks associated with heavy metals in the drinking water of Swat, northern Pakistan. J Environ Sci 25: 2003-2013. doi: 10.1016/S1001-0742(12)60275-7
![]() |
[18] |
Salehi M, Jafvert CT, Howarter JA, et al. (2018) Investigation of the factors that influence lead accumulation onto polyethylene: Implication for potable water plumbing pipes. J Hazard Mater 347: 242-251. doi: 10.1016/j.jhazmat.2017.12.066
![]() |
[19] |
Ahamed T, Brown SP, Salehi M (2020) Investigate the role of biofilm and water chemistry on lead deposition onto and release from polyethylene: an implication for potable water pipes. J Hazard Mater 400: 123253. doi: 10.1016/j.jhazmat.2020.123253
![]() |
[20] |
DeSimone D, Sharafoddinzadeh D, Salehi M (2020) Prediction of children's blood lead levels from exposure to lead in schools' drinking water-A case study in Tennessee, USA. Water 12: 1826. doi: 10.3390/w12061826
![]() |
[21] | Proctor CR, Rhoads WJ, Keane T, et al. (2020) Considerations for large building water quality after extended stagnation. AWWA Water Sci 2: e1186. |
[22] |
El-Kady AA, Abdel-Wahhab MA (2018) Occurrence of trace metals in foodstuffs and their health impact. Trends Food Sci Technol 75: 36-45. doi: 10.1016/j.tifs.2018.03.001
![]() |
[23] |
Al Osman M, Yang F, Massey IY (2019) Exposure routes and health effects of heavy metals on children. Biometals 32: 563-573. doi: 10.1007/s10534-019-00193-5
![]() |
[24] |
Rehman K, Fatima F, Waheed I, et al. (2018) Prevalence of exposure of heavy metals and their impact on health consequences. J Cell Biochem 119: 157-184. doi: 10.1002/jcb.26234
![]() |
[25] |
Mohammadi AA, Zarei A, Majidi S, et al. (2019) Carcinogenic and non-carcinogenic health risk assessment of heavy metals in drinking water of Khorramabad, Iran. MethodsX 6: 1642-1651. doi: 10.1016/j.mex.2019.07.017
![]() |
[26] |
Edwards M, Triantafyllidou S, Best D (2009) Elevated blood lead in young children due to lead-contaminated drinking water: Washington, DC, 2001-2004. Environ Sci Technol 43: 1618-1623. doi: 10.1021/es802789w
![]() |
[27] |
Jain NB, Laden F, Guller U, et al. (2005) Relation between blood lead levels and childhood anemia in India. Am J Epidemiol 161: 968-973. doi: 10.1093/aje/kwi126
![]() |
[28] | Mahurpawar M (2015) Effects of heavy metals on human health. Int J Res Granthaalayah 2350: 2394-3629. |
[29] | Martin S, Griswold W (2009) Human health effects of heavy metals. Environ Sci Technol Briefs Citizens 15: 1-6. |
[30] | Lamm SH, Kruse MB (2005) Arsenic ingestion and bladder cancer mortality-What do the dose-response relationships suggest about mechanism? Hum Ecol Risk Assess 11: 433-450. |
[31] |
Viet PH, Sampson ML, Buschmann J, et al. (2008) Contamination of drinking water resources in the Mekong delta floodplains: Arsenic and other trace metals pose serious health risks to population. Environ Int 34: 756-764. doi: 10.1016/j.envint.2007.12.025
![]() |
[32] |
Volety AK (2008) Effects of salinity, heavy metals and pesticides on health and physiology of oysters in the Caloosahatchee Estuary, Florida. Ecotoxicology 17: 579-590. doi: 10.1007/s10646-008-0242-9
![]() |
[33] |
Yoo JW, Cho H, Lee KW, et al. (2021) Combined effects of heavy metals (Cd, As, and Pb): Comparative study using conceptual models and the antioxidant responses in the brackish water flea. Comp Biochem Physiol Part-C Toxicol Pharmacol 239: 108863. doi: 10.1016/j.cbpc.2020.108863
![]() |
[34] | Jakimska A, Konieczka P, Skora K, et al. (2011) Bioaccumulation of metals in tissues of marine animals. J Environ Stud 20: 1117-1125. |
[35] |
Kononova ON, Bryuzgina GL, Apchitaeva OV, et al. (2019) Ion exchange recovery of chromium (VI) and manganese (Ⅱ) from aqueous solutions. Arab J Chem 12: 2713-2720. doi: 10.1016/j.arabjc.2015.05.021
![]() |
[36] |
Gupta B, Deep A, Tandon SN (2002) Recovery of chromium and nickel from industrial waste. Ind Eng Chem Res 41: 2948-2952. doi: 10.1021/ie010934b
![]() |
[37] |
Wang D, Li Y, Li Puma G, et al. (2017) Photoelectrochemical cell for simultaneous electricity generation and heavy metals recovery from wastewater. J Hazard Mater 323: 681-689. doi: 10.1016/j.jhazmat.2016.10.037
![]() |
[38] |
Baltazar C, Igarashi T, Villacorte-tabelin M, et al. (2018) Arsenic, selenium, boron, lead, cadmium, copper, and zinc in naturally contaminated rocks: A review of their sources, modes of enrichment, mechanisms of release, and mitigation strategies. Sci Total Environ 645: 1522-1553. doi: 10.1016/j.scitotenv.2018.07.103
![]() |
[39] | Baltazar C, Sasaki R, Igarashi T, et al. (2017) Simultaneous leaching of arsenite, arsenate, selenite and selenate, and their migration in tunnel-excavated sedimentary rocks: I. Column experiments under intermittent and unsaturated flow. Chemosphere 186: 558-569. |
[40] |
Shao H, Freiburg JT, Berger PM, et al. (2020) Mobilization of trace metals from caprock and formation rocks at the Illinois Basin - Decatur Project demonstration site under geological carbon dioxide sequestration conditions. Chem Geol 550: 119758. doi: 10.1016/j.chemgeo.2020.119758
![]() |
[41] |
Feng W, Guo Z, Xiao X, et al. (2019) Atmospheric deposition as a source of cadmium and lead to soil-rice system and associated risk assessment. Ecotoxicol Environ Saf 180: 160-167. doi: 10.1016/j.ecoenv.2019.04.090
![]() |
[42] |
Feng W, Guo Z, Peng C, et al. (2019) Atmospheric bulk deposition of heavy metal(loid)s in central south China: Fluxes, influencing factors and implication for paddy soils. J Hazard Mater 371: 634-642. doi: 10.1016/j.jhazmat.2019.02.090
![]() |
[43] | Rajamohan R, Rao TS, Anupkumar B, et al. (2010) Distribution of heavy metals in the vicinity of a nuclear power plant, east coast of India: With emphasis on copper concentration and primary productivity. Indian J Mar Sci 39: 182-191. |
[44] |
Nieva NE, Borgnino L, García MG (2018) Long term metal release and acid generation in abandoned mine wastes containing metal-sulphides. Environ Pollut 242: 264-276. doi: 10.1016/j.envpol.2018.06.067
![]() |
[45] |
Karnchanawong S, Limpiteeprakan P (2009) Evaluation of heavy metal leaching from spent household batteries disposed in municipal solid waste. Waste Manag 29: 550-558. doi: 10.1016/j.wasman.2008.03.018
![]() |
[46] | Ribeiro C, Scheufele FB, Espinoza-Quinones FR, et al. (2018) Biomaterials A comprehensive evaluation of heavy metals removal from battery industry wastewaters by applying bio- residue, mineral and commercial adsorbent materials. Biomaterials 53: 7976-7995. |
[47] |
Al-Khashman O, Shawabkeh RA (2009) Metal distribution in urban soil around steel industry beside Queen Alia Airport, Jordan. Environ Geochem Health 31: 717-726. doi: 10.1007/s10653-009-9250-9
![]() |
[48] |
Jeong H, Choi JY, Lee J, et al. (2020) Heavy metal pollution by road-deposited sediments and its contribution to total suspended solids in rainfall runoff from intensive industrial areas. Environ Pollut 265: 115028. doi: 10.1016/j.envpol.2020.115028
![]() |
[49] | City D, Das M, Ahmed K, et al. (2009) Heavy metals in industrial effluents (tannery and textile) and adjacent rivers heavy metals in industrial effluents (tannery and textile) and adjacent rivers of Dhaka City, Bangladesh. Terr Aquat Environ Toxicol 5: 8-13. |
[50] | Halimoon N (2010) Removal of heavy metals from textile wastewater using zeolite. Environment Asia 3: 124-130. |
[51] |
Saha P, Paul B (2019) Human and ecological risk assessment: an international assessment of heavy metal toxicity related with human health risk in the surface water of an industrialized area by a novel technique. Hum Ecol RISK Assess 25: 966-987. doi: 10.1080/10807039.2018.1458595
![]() |
[52] |
Hepburn E, Northway A, Bekele D, et al. (2018) A method for separation of heavy metal sources in urban groundwater using multiple lines of evidence. Environ Pollut 241: 787-799. doi: 10.1016/j.envpol.2018.06.004
![]() |
[53] |
Ning CC, Gao PD, Wang BQ, et al. (2017) Impacts of chemical fertilizer reduction and organic amendments supplementation on soil nutrient, enzyme activity and heavy metal content. J Integr Agric 16: 1819-1831. doi: 10.1016/S2095-3119(16)61476-4
![]() |
[54] |
Fan Y, Li Y, Li H, et al. (2018) Evaluating heavy metal accumulation and potential risks in soil-plant systems applied with magnesium slag-based fertilizer. Chemosphere 197: 382-388. doi: 10.1016/j.chemosphere.2018.01.055
![]() |
[55] |
Defarge N, Vendômois JS De, Séralini GE (2018) Toxicity of formulants and heavy metals in glyphosate-based herbicides and other pesticides. Toxicol Rep 5: 156-163. doi: 10.1016/j.toxrep.2017.12.025
![]() |
[56] |
Clark BN, Masters SV, Edwards M (2015) Lead release to drinking water from galvanized steel pipe coatings. Environ Eng Sci 32: 713-721. doi: 10.1089/ees.2015.0073
![]() |
[57] | McFadden M, Giani R, Kwan P, et al. (2011) Contributions to drinking water lead from galvanized iron corrosion scales. J Am Water Works Assoc 103: 76-89. |
[58] | Salehi M, Li X, Whelton AJ (2017) Metal accumulation in representative plastic drinking water plumbing systems. J Am Water Works Assoc 109: E479-E493. |
[59] |
Salehi M, Abouali M, Wang M, et al. (2018) Case study: Fixture water use and drinking water quality in a new residential green building. Chemosphere 195: 80-89. doi: 10.1016/j.chemosphere.2017.11.070
![]() |
[60] |
Salehi M, Odimayomi T, Ra K, et al. (2020) An investigation of spatial and temporal drinking water quality variation in green residential plumbing. J Build Environ 169: 106566. doi: 10.1016/j.buildenv.2019.106566
![]() |
[61] |
Sakson G, Brzezinska A, Zawilski M (2018) Emission of heavy metals from an urban catchment into receiving water and possibility of its limitation on the example of Lodz city. Environ Monit Assess 190: 1-15. doi: 10.1007/s10661-018-6648-9
![]() |
[62] | Chief K, Artiola JF, Beamer P, et al. (2016) Understanding the Gold King Mine Spill. Superfund Res, The University of Arizona. |
[63] |
Nemati M, Hosseini SM, Shabanian M (2017) Novel electrodialysis cation exchange membrane prepared by 2- acrylamido-2-methylpropane sulfonic acid; Heavy metal ions removal. J Hazard Mater 337: 90-104. doi: 10.1016/j.jhazmat.2017.04.074
![]() |
[64] |
Abdullah N, Yusof N, Lau WJ, et al. (2019) Recent trends of heavy metal removal from water/wastewater by membrane technologies. J Ind Eng Chem 76: 17-38. doi: 10.1016/j.jiec.2019.03.029
![]() |
[65] |
Wang N, Qiu Y, Hu K, et al. (2021) One-step synthesis of cake-like biosorbents from plant biomass for the effective removal and recovery heavy metals: Effect of plant species and roles of xanthation. Chemosphere 266: 129129. doi: 10.1016/j.chemosphere.2020.129129
![]() |
[66] |
Rahman ML, Wong ZJ, Sarjadi MS, et al. (2021) Poly(hydroxamic acid) ligand from palm-based waste materials for removal of heavy metals from electroplating wastewater. J Appl Polym Sci 138: 49671. doi: 10.1002/app.49671
![]() |
[67] |
Kurniawan TA, Chan GYS, Lo W hung, et al. (2006) Comparisons of low-cost adsorbents for treating wastewaters laden with heavy metals. Sci Total Environ 366: 409-426. doi: 10.1016/j.scitotenv.2005.10.001
![]() |
[68] |
Bottero JY, Rose J, Wiesner MR (2006) Nanotechnologies: Tools for sustainability in a new wave of water treatment processes. Integr Environ Assess Manag 2: 391-395. doi: 10.1002/ieam.5630020411
![]() |
[69] | Grün AY, App CB, Breidenbach A, et al. (2018) Effects of low dose silver nanoparticle treatment on the structure and community composition of bacterial freshwater biofilms. PLoS One 13: e0199132. |
[70] |
Xu J, Cao Z, Zhang Y, et al. (2018) Chemosphere A review of functionalized carbon nanotubes and graphene for heavy metal adsorption from water: Preparation, application, and mechanism. Chemosphere 195: 351-364. doi: 10.1016/j.chemosphere.2017.12.061
![]() |
[71] |
Lu C, Chiu H (2006) Adsorption of zinc (Ⅱ) from water with purified carbon nanotubes. Chemical Eng Sci 61: 1138-1145. doi: 10.1016/j.ces.2005.08.007
![]() |
[72] |
Deliyanni EA, Bakoyannakis DN, Zouboulis AI, et al. (2003) Sorption of As (V) ions by akaganeite-type nanocrystals. Chemosphere 50: 155-163. doi: 10.1016/S0045-6535(02)00351-X
![]() |
[73] |
Tavker N, Yadav VK, Yadav KK, et al. (2021) Removal of cadmium and chromium by mixture of silver nanoparticles and nano-fibrillated cellulose isolated from waste peels of citrus sinensis. Polymers 13: 1-14. doi: 10.3390/polym13020234
![]() |
[74] |
Shahrashoub M, Bakhtiari S (2021) The efficiency of activated carbon/magnetite nanoparticles composites in copper removal: Industrial waste recovery, green synthesis, characterization, and adsorption-desorption studies. Microporous Mesoporous Mater 311: 110692. doi: 10.1016/j.micromeso.2020.110692
![]() |
[75] |
Li Z, Gong Y, Zhao D, et al. (2021) Enhanced removal of zinc and cadmium from water using carboxymethyl cellulose-bridged chlorapatite nanoparticles. Chemosphere 263: 128038. doi: 10.1016/j.chemosphere.2020.128038
![]() |
[76] |
Ademola Bode-Aluko C, Pereao O, Kyaw HH, et al. (2021) Photocatalytic and antifouling properties of electrospun TiO2 polyacrylonitrile composite nanofibers under visible light. Mater Sci Eng B Solid-State Mater Adv Technol 264: 114913. doi: 10.1016/j.mseb.2020.114913
![]() |
[77] | Li QH, Dong M, Li R, et al. (2021) Enhancement of Cr(VI) removal efficiency via adsorption/photocatalysis synergy using electrospun chitosan/g-C3N4/TiO2 nanofibers. Carbohydr Polym 253. |
[78] |
Hamad AA, Hassouna MS, Shalaby TI, et al. (2020) Electrospun cellulose acetate nanofiber incorporated with hydroxyapatite for removal of heavy metals. Int J Biol Macromol 151: 1299-1313. doi: 10.1016/j.ijbiomac.2019.10.176
![]() |
[79] | Lu X, Wang C, Wei Y (2009) One-dimensional composite nanomaterials: Synthesis by electrospinning and their applications. Nano Micro Small 5: 2349-2370. |
[80] |
Peng S, Jin G, Li L, et al. (2016) Multi-functional electrospun nanofibres for advances in tissue regeneration, energy conversion & storage, and water treatment. Chem Soc Rev 45: 1225-1241. doi: 10.1039/C5CS00777A
![]() |
[81] |
Zhang Y, Duan X (2020) Chemical precipitation of heavy metals from wastewater by using the synthetical magnesium hydroxy carbonate. Water Sci Technol 81: 1130-1136. doi: 10.2166/wst.2020.208
![]() |
[82] |
Stec M, Jagustyn B, Słowik K, et al. (2020) Influence of high chloride concentration on pH control in hydroxide precipitation of heavy metals. J Sustain Metall 6: 239-249. doi: 10.1007/s40831-020-00270-x
![]() |
[83] |
Barakat MA (2011) New trends in removing heavy metals from industrial wastewater. Arab J Chem 4: 361-377. doi: 10.1016/j.arabjc.2010.07.019
![]() |
[84] |
Xu H, Min X, Wang Y, et al. (2020) Stabilization of arsenic sulfide sludge by hydrothermal treatment. Hydrometallurgy 191: 105229. doi: 10.1016/j.hydromet.2019.105229
![]() |
[85] |
Carro L, Barriada JL, Herrero R, et al. (2015) Interaction of heavy metals with Ca-pretreated Sargassum muticum algal biomass: Characterization as a cation exchange process. Chem Eng J 264: 181-187. doi: 10.1016/j.cej.2014.11.079
![]() |
[86] | Carolin CF, Kumar PS, Saravanan A, et al. (2017) Efficient techniques for the removal of toxic heavy metals from aquatic environment: A review. Biochem Pharmacol 5: 2782-2799. |
[87] |
Fu F, Wang Q (2011) Removal of heavy metal ions from wastewaters: A review. J Environ Manage 92: 407-418. doi: 10.1016/j.jenvman.2010.11.011
![]() |
[88] |
Keng PS, Lee SL, Ha ST, et al. (2014) Removal of hazardous heavy metals from aqueous environment by low-cost adsorption materials. Environ Chem Lett 12: 15-25. doi: 10.1007/s10311-013-0427-1
![]() |
[89] |
Ma J, Qin G, Zhang Y, et al. (2018) Heavy metal removal from aqueous solutions by calcium silicate powder from waste coal fly-ash. J Clean Prod 182: 776-782. doi: 10.1016/j.jclepro.2018.02.115
![]() |
[90] |
Zhao M, Xu Y, Zhang C, et al. (2016) New trends in removing heavy metals from wastewater. Appl Microbiol Biotechnol 100: 6509-6518. doi: 10.1007/s00253-016-7646-x
![]() |
[91] |
Uddin MK (2017) A review on the adsorption of heavy metals by clay minerals, with special focus on the past decade. Chem Eng J 308: 438-462. doi: 10.1016/j.cej.2016.09.029
![]() |
[92] |
Hayati B, Maleki A, Najafi F, et al. (2017) Super high removal capacities of heavy metals (Pb2+ and Cu2+) using CNT dendrimer. J Hazard Mater 336: 146-157. doi: 10.1016/j.jhazmat.2017.02.059
![]() |
[93] |
Jellali S, Azzaz AA, Jeguirim M, et al. (2021) Use of lignite as a low-cost material for cadmium and copper removal from aqueous solutions: Assessment of adsorption characteristics and exploration of involved mechanisms. Water 13: 164. doi: 10.3390/w13020164
![]() |
[94] |
Wang S, Terdkiatburana T, Tadé MO (2008) Adsorption of Cu(Ⅱ), Pb(Ⅱ) and humic acid on natural zeolite tuff in single and binary systems. Sep Purif Technol 62: 64-70. doi: 10.1016/j.seppur.2008.01.004
![]() |
[95] |
Brown PA, Gill SA, Allen SJ (2000) Metal removal from wastewater using peat. Water Res 34: 3907-3916. doi: 10.1016/S0043-1354(00)00152-4
![]() |
[96] |
Sadovsky D, Brenner A, Astrachan B, et al. (2016) Biosorption potential of cerium ions using Spirulina biomass. J Rare Earths 34: 644-652. doi: 10.1016/S1002-0721(16)60074-1
![]() |
[97] |
Ho YS, McKay G (2003) Sorption of dyes and copper ions onto biosorbents. Process Biochem 38: 1047-1061. doi: 10.1016/S0032-9592(02)00239-X
![]() |
[98] |
Javanbakht V, Alavi SA, Zilouei H (2014) Mechanisms of heavy metal removal using microorganisms as biosorbent. Water Sci Technol 69: 1775-1787. doi: 10.2166/wst.2013.718
![]() |
[99] |
Huang Y, Wu D, Wang X, et al. (2016) Removal of heavy metals from water using polyvinylamine by polymer-enhanced ultrafiltration and flocculation. Sep Purif Technol 158: 124-136. doi: 10.1016/j.seppur.2015.12.008
![]() |
[100] |
Wang R, Guan S, Sato A, et al. (2013) Nanofibrous microfiltration membranes capable of removing bacteria, viruses and heavy metal ions. J Memb Sci 446: 376-382. doi: 10.1016/j.memsci.2013.06.020
![]() |
[101] |
Jia TZ, Lu JP, Cheng XY, et al. (2019) Surface enriched sulfonated polyarylene ether benzonitrile (SPEB) that enhances heavy metal removal from polyacrylonitrile (PAN) thin-film composite nanofiltration membranes. J Memb Sci 580: 214-223. doi: 10.1016/j.memsci.2019.03.015
![]() |
[102] | Bakalár T, Búgel M, Gajdošová L (2009) Heavy metal removal using reverse osmosis. Acta Montan Slovaca 14: 250-253. |
[103] | Abdullah N, Tajuddin MH, Yusof N (2019) Forward osmosis (FO) for removal of heavy metals. Nanotechnol. Water Wastewater Treat 2019: 177-204. |
[104] |
Abdullah N, Yusof N, Lau WJ, et al. (2019) Recent trends of heavy metal removal from water/wastewater by membrane technologies. J Ind Eng Chem 76: 13-38. doi: 10.1016/j.jiec.2019.03.029
![]() |
[105] |
Huang J, Yuan F, Zeng G, et al. (2017) Influence of pH on heavy metal speciation and removal from wastewater using micellar-enhanced ultrafiltration. Chemosphere 173: 199-206. doi: 10.1016/j.chemosphere.2016.12.137
![]() |
[106] |
Fang X, Li J, Li X, et al. (2017) Internal pore decoration with polydopamine nanoparticle on polymeric ultrafiltration membrane for enhanced heavy metal removal. Chem Eng J 314: 38-49. doi: 10.1016/j.cej.2016.12.125
![]() |
[107] |
Landaburu-aguirre J, Pongr E, Keiski RL (2009) The removal of zinc from synthetic wastewaters by micellar-enhanced ultrafiltration: statistical design of experiments. Desalination 240: 262-269. doi: 10.1016/j.desal.2007.11.077
![]() |
[108] |
Reza M, Emami S, Amiri MK, et al. (2021) Removal efficiency optimization of Pb2+ in a nanofiltration process by MLP-ANN and RSM. Korean J Chem Eng 38: 316-325. doi: 10.1007/s11814-020-0698-8
![]() |
[109] | Azimi A, Azari A, Rezakazemi M, et al. (2017) Removal of heavy metals from industrial wastewaters: a review. Chem Bio Eng Rev 4: 37-59. |
[110] |
Abdullah N, Tajuddin MH, Yusof N (2019) Forward osmosis (FO) for removal of heavy metals. Nanotechnol Water Wastewater Treat 2019: 177-204. doi: 10.1016/B978-0-12-813902-8.00010-1
![]() |
[111] |
Chung T, Li X, Ong RC, et al. (2012) Emerging forward osmosis (FO) technologies and challenges ahead for clean water and clean energy applications. Curr Opin Chem Eng 1: 246-257. doi: 10.1016/j.coche.2012.07.004
![]() |
[112] |
Behdarvand F, Valamohammadi E, Tofighy MA, et al. (2021) Polyvinyl alcohol/polyethersulfone thin-film nanocomposite membranes with carbon nanomaterials incorporated in substrate for water treatment. J Environ Chem Eng 9: 104650. doi: 10.1016/j.jece.2020.104650
![]() |
[113] | Leaper S, Abdel-Karim A, Gorgojo P (2021) The use of carbon nanomaterials in membrane distillation membranes: a review. Front Chem Sci Eng 1-20. |
[114] |
Liu X, Hu Q, Fang Z, et al. (2009) Magnetic chitosan nanocomposites: a useful recyclable tool for heavy metal ion removal. Langmuir 25: 3-8. doi: 10.1021/la802754t
![]() |
[115] |
Türkmen D, Erkut Y, Öztürk N, et al. (2009) Poly (hydroxyethyl methacrylate) nanobeads containing imidazole groups for removal of Cu (Ⅱ) ions. Mater Sci Eng 29: 2072-2078. doi: 10.1016/j.msec.2009.04.005
![]() |
[116] |
Saeed K, Haider S, Oh T, et al. (2008) Preparation of amidoxime-modified polyacrylonitrile (PAN-oxime) nanofibers and their applications to metal ions adsorption. J Memb Sci 322: 400-405. doi: 10.1016/j.memsci.2008.05.062
![]() |
[117] |
Huang S, Chen D (2009) Rapid removal of heavy metal cations and anions from aqueous solutions by an amino-functionalized magnetic nano-adsorbent. J Hazard Mater 163: 174-179. doi: 10.1016/j.jhazmat.2008.06.075
![]() |
[118] |
Madadrang CJ, Kim HY, Gao G, et al. (2012) Adsorption Behavior of EDTA-Graphene Oxide for Pb (Ⅱ) Removal. ACS Appl Mater Interfaces 4: 1186-1193. doi: 10.1021/am201645g
![]() |
[119] |
Perez-aguilar NV, Diaz-flores PE, Rangel-mendez JR (2011) The adsorption kinetics of cadmium by three different types of carbon nanotubes. J Colloid Interface Sci 364: 279-287. doi: 10.1016/j.jcis.2011.08.024
![]() |
[120] |
Alsaadi MA, Mamun AA, Alam Z (2016) Removal of cadmium from water by CNT-PAC composite: effect of functionalization. Nano 11: 1650011. doi: 10.1142/S1793292016500119
![]() |
[121] |
Leudjo A, Pillay K, Yangkou X (2017) Nanosponge cyclodextrin polyurethanes and their modification with nanomaterials for the removal of pollutants from wastewater: A review. Carbohydr Polym 159: 94-107. doi: 10.1016/j.carbpol.2016.12.027
![]() |
[122] |
Dichiara AB, Webber MR, Gorman WR, et al. (2015) Removal of copper ions from aqueous solutions via adsorption on carbon nanocomposites. ACS Appl Mater Interfaces 7: 15674-15680. doi: 10.1021/acsami.5b04974
![]() |
[123] |
Ahmad SZN, Wan Salleh WN, Ismail AF, et al. (2020) Adsorptive removal of heavy metal ions using graphene-based nanomaterials: Toxicity, roles of functional groups and mechanisms. Chemosphere 248: 126008. doi: 10.1016/j.chemosphere.2020.126008
![]() |
[124] |
Baby R, Saifullah B, Hussein MZ (2019) Carbon nanomaterials for the treatment of heavy metal-contaminated water and environmental remediation. Nanoscale Res Lett 14: 1-17. doi: 10.1186/s11671-019-3167-8
![]() |
[125] |
Ali S, Aziz S, Rehman U, et al. (2019) Efficient removal of zinc from water and wastewater effluents by hydroxylated and carboxylated carbon nanotube membranes: Behaviors and mechanisms of dynamic filtration. J Hazard Mater 365: 64-73. doi: 10.1016/j.jhazmat.2018.10.089
![]() |
[126] |
Bankole MT, Abdulkareem AS, Mohammed IA, et al. (2019) Selected heavy metals removal from electroplating wastewater by purified and polyhydroxylbutyrate functionalized carbon nanotubes adsorbents. Sci Rep 9: 1-19. doi: 10.1038/s41598-018-37899-4
![]() |
[127] |
Qu Y, Deng J, Shen W, et al. (2015) Responses of microbial communities to single-walled carbon nanotubes in phenol wastewater treatment systems. Environ Sci Technol 49: 4627-4635. doi: 10.1021/es5053045
![]() |
[128] |
Li Y, Liu F, Xia B, et al. (2010) Removal of copper from aqueous solution by carbon nanotube/calcium alginate composites. J Hazard Mater 177: 876-880. doi: 10.1016/j.jhazmat.2009.12.114
![]() |
[129] |
Park S, Kim Y (2010) Adsorption behaviors of heavy metal ions onto electrochemically oxidized activated carbon fibers. Mater Sci Eng A 391: 121-123. doi: 10.1016/j.msea.2004.08.074
![]() |
[130] |
Yang J, Hou B, Wang J, et al. (2019) Nanomaterials for the removal of heavy metals from wastewater. Nanomaterials 9: 424. doi: 10.3390/nano9030424
![]() |
[131] |
Sitko R, Turek E, Zawisza B, et al. (2013) Adsorption of divalent metal ions from aqueous solutions using graphene oxide. Dalt Trans 42: 5682-5689. doi: 10.1039/c3dt33097d
![]() |
[132] |
Xu T, Qu R, Zhang Y, et al. (2021) Preparation of bifunctional polysilsesquioxane/carbon nanotube magnetic composites and their adsorption properties for Au (Ⅲ). Chem Eng J 410: 128225. doi: 10.1016/j.cej.2020.128225
![]() |
[133] |
Li S, Wang W, Liang F, et al. (2017) Heavy metal removal using nanoscale zero-valent iron (nZVI): Theory and application. J Hazard Mater 322: 163-171. doi: 10.1016/j.jhazmat.2016.01.032
![]() |
[134] |
Fu F, Dionysiou DD, Liu H (2014) The use of zero-valent iron for groundwater remediation and wastewater treatment: A review. J Hazard Mater 267: 194-205. doi: 10.1016/j.jhazmat.2013.12.062
![]() |
[135] |
Karabelli D, Ünal S, Shahwan T, et al. (2011) Preparation and characterization of alumina-supported iron nanoparticles and its application for the removal of aqueous Cu2+ ions. Chem Eng J 168: 979-984. doi: 10.1016/j.cej.2011.01.015
![]() |
[136] |
Huang P, Ye Z, Xie W, et al. (2013) Rapid magnetic removal of aqueous heavy metals and their relevant mechanisms using nanoscale zero valent iron (nZVI) particles. Water Res 47: 4050-4058. doi: 10.1016/j.watres.2013.01.054
![]() |
[137] |
Shaba EY, Jacob JO, Tijani JO, et al. (2021) A critical review of synthesis parameters affecting the properties of zinc oxide nanoparticle and its application in wastewater treatment. Appl Water Sci 11: 1-41. doi: 10.1007/s13201-021-01370-z
![]() |
[138] |
Wu Q, Zhao J, Qin G, et al. (2013) Photocatalytic reduction of Cr (VI) with TiO2 film under visible light. Appl Catal B Environ 142-143: 142-148. doi: 10.1016/j.apcatb.2013.04.056
![]() |
[139] |
Sun Q, Li H, Niu B, et al. (2015) Nano-TiO2 immobilized on diatomite: characterization and photocatalytic reactivity for Cu2+ removal from aqueous solution. Procedia Eng 102: 1935-1943. doi: 10.1016/j.proeng.2015.01.334
![]() |
[140] |
Sheela T, Nayaka YA, Viswanatha R, et al. (2012) Kinetics and thermodynamics studies on the adsorption of Zn(Ⅱ), Cd(Ⅱ) and Hg(Ⅱ) from aqueous solution using zinc oxide nanoparticles. Powder Technol 217: 163-170. doi: 10.1016/j.powtec.2011.10.023
![]() |
[141] |
Mahdavi S, Jalali M, Afkhami A (2013) Heavy metals removal from aqueous solutions using TiO2, MgO, and Al2O3 nanoparticles. Chem Eng Commun 200: 448-470. doi: 10.1080/00986445.2012.686939
![]() |
[142] |
Lai CH, Chen CY (2001) Removal of metal ions and humic acid from water by iron-coated filter media. Chemosphere 44: 1177-1184. doi: 10.1016/S0045-6535(00)00307-6
![]() |
[143] |
Oliveira LCA, Petkowicz DI, Smaniotto A, et al. (2004) Magnetic zeolites: a new adsorbent for removal of metallic contaminants from water. Water Res 38: 3699-3704. doi: 10.1016/j.watres.2004.06.008
![]() |
[144] |
Yavuz CT, Mayo JT, Yu WW, et al. (2006) Low-field magnetic separation of monodisperse Fe3O4 nanocrystals. Science 314: 964-967. doi: 10.1126/science.1131475
![]() |
[145] |
Chang Y, Chen D (2005) Preparation and adsorption properties of monodisperse chitosanbound Fe3O4 magnetic nanoparticles for removal of Cu(Ⅱ) ions. J Colloid Interface Sci 283: 446-451. doi: 10.1016/j.jcis.2004.09.010
![]() |
[146] |
Liu J, Zhao Z, Jiang G (2008) Coating Fe3O4 magnetic nanoparticles with humic acid for high efficient removal of heavy metals in water. Environ Sci Technol 42: 6949-6954. doi: 10.1021/es800924c
![]() |
[147] |
Bian Y, Bian Z, Zhang J, et al. (2015) Effect of the oxygen-containing functional group of graphene oxide on the aqueous cadmium ions removal. Appl Surf Sci 329: 269-275. doi: 10.1016/j.apsusc.2014.12.090
![]() |
[148] |
Yoon Y, Park WK, Hwang T, et al. (2016) Comparative evaluation of magnetite-graphene oxide and magnetite-reduced graphene oxide composite for As(Ⅲ) and As(V) removal. J Hazard Mater 304: 196-204. doi: 10.1016/j.jhazmat.2015.10.053
![]() |
[149] |
Mokhtari F, Salehi M, Zamani F, et al. (2016) Advances in electrospinning: The production and application of nanofibres and nanofibrous structures. Text Prog 48: 119-219. doi: 10.1080/00405167.2016.1201934
![]() |
[150] | Yang Z, Peng H, Wang W, et al. (2010) Crystallization behavior of poly(ε-caprolactone)/layered double hydroxide nanocomposites. J Appl Polym Sci 116: 2658-2667. |
[151] | Esfandarani MS, Johari MS (2010) Producing porous nanofibers. Nanocon 2010. Olomouc, Czech Republic, Oct 12th-14th. |
[152] |
Guseva I, Bateson TF, Bouvard V, et al. (2016) Human exposure to carbon-based fibrous nanomaterials: A review. Int J Hyg Environ Health 219: 166-175. doi: 10.1016/j.ijheh.2015.12.005
![]() |
[153] |
Ming Z, Feng S, Yilihamu A, et al. (2018) Toxicity of carbon nanotubes to white rot fungus Phanerochaete chrysosporium. Ecotoxicol Environ Saf 162: 225-234. doi: 10.1016/j.ecoenv.2018.07.011
![]() |
[154] |
Zang L, Lin R, Dou T, et al. (2019) Electrospun superhydrophilic membranes for effective removal of Pb(ii) from water. Nanoscale Adv 1: 389-394. doi: 10.1039/C8NA00044A
![]() |
[155] | Liu L, Luo X, Ding L, et al. (2019) Application of nanotechnology in the removal of heavy metal from water. In: Luo X, Deng F, Nanomaterials for the Removal of Pollutants and Resources Reutilization, Elsevier Inc., 83-147. |
[156] |
Chitpong N, Husson SM (2017) Polyacid functionalized cellulose nanofiber membranes for removal of heavy metals from impaired waters. J Memb Sci 523: 418-429. doi: 10.1016/j.memsci.2016.10.020
![]() |
[157] |
Feng Q, Wu D, Zhao Y, et al. (2018) Electrospun AOPAN/RC blend nanofiber membrane for efficient removal of heavy metal ions from water. J Hazard Mater 344: 819-828. doi: 10.1016/j.jhazmat.2017.11.035
![]() |
[158] |
Karthik R, Meenakshi S (2015) Removal of Cr(VI) ions by adsorption onto sodium alginate-polyaniline nanofibers. Int J Biol Macromol 72: 711-717. doi: 10.1016/j.ijbiomac.2014.09.023
![]() |
[159] |
Chitpong N, Husson SM (2017) High-capacity, nanofiber-based ion-exchange membranes for the selective recovery of heavy metals from impaired waters. Sep Purif Technol 179: 94-103. doi: 10.1016/j.seppur.2017.02.009
![]() |
[160] |
Avila M, Burks T, Akhtar F, et al. (2014) Surface functionalized nanofibers for the removal of chromium (VI) from aqueous solutions. Chem Eng J 245: 201-209. doi: 10.1016/j.cej.2014.02.034
![]() |
[161] |
Esfandarani MS, Johari MS, Amrollahi R, et al. (2011) Laser induced surface modification of clay-PAN composite nanofibers. Fibers Polym 12: 715-720. doi: 10.1007/s12221-011-0715-y
![]() |
[162] |
Saleem H, Trabzon L, Kilic A, et al. (2020) Recent advances in nanofibrous membranes: Production and applications in water treatment and desalination. Desalination 478: 114178. doi: 10.1016/j.desal.2019.114178
![]() |
[163] |
Huang L, Manickam SS, McCutcheon JR (2013) Increasing strength of electrospun nanofiber membranes for water filtration using solvent vapor. J Memb Sci 436: 213-220. doi: 10.1016/j.memsci.2012.12.037
![]() |
[164] |
Zhuang S, Zhu K, Wang J (2021) Fibrous chitosan/cellulose composite as an efficient adsorbent for Co(Ⅱ) removal. J Clean Prod 285: 124911. doi: 10.1016/j.jclepro.2020.124911
![]() |
[165] |
Kakoria A, Sinha-Ray S, Sinha-Ray S (2021) Industrially scalable Chitosan/Nylon-6 (CS/N) nanofiber-based reusable adsorbent for efficient removal of heavy metal from water. Polymer 213: 123333. doi: 10.1016/j.polymer.2020.123333
![]() |
[166] |
ZabihiSahebi A, Koushkbaghi S, Pishnamazi M, et al. (2019) Synthesis of cellulose acetate/chitosan/SWCNT/Fe3O4/TiO2 composite nanofibers for the removal of Cr(VI), As(V), Methylene blue and Congo red from aqueous solutions. Int J Biol Macromol 140: 1296-1304. doi: 10.1016/j.ijbiomac.2019.08.214
![]() |
[167] |
Surgutskaia NS, Martino AD, Zednik J, et al. (2020) Efficient Cu2+, Pb2+ and Ni2+ ion removal from wastewater using electrospun DTPA-modified chitosan/polyethylene oxide nanofibers. Sep Purif Technol 247: 116914. doi: 10.1016/j.seppur.2020.116914
![]() |
[168] |
Li Y, Li M, Zhang J, et al. (2019) Adsorption properties of the double-imprinted electrospun crosslinked chitosan nanofibers. Chinese Chem Lett 30: 762-766. doi: 10.1016/j.cclet.2018.11.005
![]() |
[169] |
Yang D, Li L, Chen B, et al. (2019) Functionalized chitosan electrospun nano fiber membranes for heavy-metal removal. Polymer 163: 74-85. doi: 10.1016/j.polymer.2018.12.046
![]() |
[170] |
Rezaul M, Omer M, Alharth NH, et al. (2019) Composite nanofibers membranes of poly (vinyl alcohol)/ chitosan for selective lead (Ⅱ) and cadmium (Ⅱ) ions removal from wastewater. Ecotoxicol Environ Saf 169: 479-486. doi: 10.1016/j.ecoenv.2018.11.049
![]() |
[171] |
Brandes R, Brouillette F, Chabot B (2021) Phosphorylated cellulose/electrospun chitosan nanofibers media for removal of heavy metals from aqueous solutions. J Appl Polym Sci 138: 50021. doi: 10.1002/app.50021
![]() |
[172] |
Begum S, Yuhana NY, Saleh NM, et al. (2021) Review of chitosan composite as a heavy metal adsorbent: Material preparation and properties. Carbohydr Polym 259: 117613. doi: 10.1016/j.carbpol.2021.117613
![]() |
[173] |
Ki CS, Gang EH, Um IC, et al. (2007) Nanofibrous membrane of wool keratose/silk fibroin blend for heavy metal ion adsorption. J Memb Sci 302: 20-26. doi: 10.1016/j.memsci.2007.06.003
![]() |
[174] |
O'Connell DW, Birkinshaw C, O'Dwyer TF (2008) Heavy metal adsorbents prepared from the modification of cellulose: A review. Bioresour Technol 99: 6709-6724. doi: 10.1016/j.biortech.2008.01.036
![]() |
[175] |
Habiba U, Afifi AM, Salleh A, et al. (2017) Chitosan/(polyvinyl alcohol)/zeolite electrospun composite nanofibrous membrane for adsorption of Cr6+, Fe3+ and Ni2+. J Hazard Mater 322: 182-194. doi: 10.1016/j.jhazmat.2016.06.028
![]() |
[176] |
Phan DN, Lee H, Huang B, et al. (2019) Fabrication of electrospun chitosan/cellulose nanofibers having adsorption property with enhanced mechanical property. Cellulose 26: 1781-1793. doi: 10.1007/s10570-018-2169-5
![]() |
[177] |
Homayoni H, Ravandi SAH, Valizadeh M (2009) Electrospinning of chitosan nanofibers: Processing optimization. Carbohydr Polym 77: 656-661. doi: 10.1016/j.carbpol.2009.02.008
![]() |
[178] |
Li L, Li Y, Cao L, et al. (2015) Enhanced chromium (VI) adsorption using nanosized chitosan fibers tailored by electrospinning. Carbohydr Polym 125: 206-213. doi: 10.1016/j.carbpol.2015.02.037
![]() |
[179] |
Managheb M, Zarghami S, Mohammadi T, et al. (2021) Enhanced dynamic Cu(Ⅱ) ion removal using hot-pressed chitosan/poly (vinyl alcohol) electrospun nanofibrous affinity membrane (ENAM). Process Saf Environ Prot 146: 329-337. doi: 10.1016/j.psep.2020.09.013
![]() |
[180] |
Pereao O, Uche C, Bublikov PS, et al. (2021) Chitosan/PEO nanofibers electrospun on metallized track-etched membranes: fabrication and characterization. Mater Today Chem 20: 100416. doi: 10.1016/j.mtchem.2020.100416
![]() |
[181] |
Razzaz A, Ghorban S, Hosayni L, et al. (2016) Chitosan nanofibers functionalized by TiO2 nanoparticles for the removal of heavy metal ions. J Taiwan Inst Chem Eng 58: 333-343. doi: 10.1016/j.jtice.2015.06.003
![]() |
[182] |
Yang D, Li L, Chen B, et al. (2019) Functionalized chitosan electrospun nanofiber membranes for heavy-metal removal. Polymer 163: 74-85. doi: 10.1016/j.polymer.2018.12.046
![]() |
[183] |
Li Y, Qiu T, Xu X (2013) Preparation of lead-ion imprinted crosslinked electro-spun chitosan nanofiber mats and application in lead ions removal from aqueous solutions. Eur Polym J 49: 1487-1494. doi: 10.1016/j.eurpolymj.2013.04.002
![]() |
[184] |
Chitpong N, Husson SM (2017) Polyacid functionalized cellulose nanofiber membranes for removal of heavy metals from impaired waters. J Memb Sci 523: 418-429. doi: 10.1016/j.memsci.2016.10.020
![]() |
[185] |
Huang M, Tu H, Chen J, et al. (2018) Chitosan-rectorite nanospheres embedded aminated polyacrylonitrile nanofibers via shoulder-to-shoulder electrospinning and electrospraying for enhanced heavy metal removal. Appl Surf Sci 437: 294-303. doi: 10.1016/j.apsusc.2017.12.150
![]() |
[186] |
Li L, Li Y, Cao L, et al. (2015) Enhanced chromium(VI) adsorption using nanosized chitosan fibers tailored by electrospinning. Carbohydr Polym 125: 206-213. doi: 10.1016/j.carbpol.2015.02.037
![]() |
[187] |
Li Y, Zhang J, Xu C, et al. (2016) Crosslinked chitosan nanofiber mats fabricated by one-step electrospinning and ion-imprinting methods for metal ions adsorption. Sci China Chem 59: 95-105. doi: 10.1007/s11426-015-5526-3
![]() |
[188] |
Li Y, Xu C, Qiu T, et al. (2014) Crosslinked electro-spun chitosan nanofiber mats with Cd(Ⅱ) as template ions for adsorption applications. J Nanosci Nanotechnol 15: 4245-4254. doi: 10.1166/jnn.2015.10197
![]() |
[189] |
Haider S, Park SY (2009) Preparation of the electrospun chitosan nanofibers and their applications to the adsorption of Cu(Ⅱ) and Pb(Ⅱ) ions from an aqueous solution. J Memb Sci 328: 90-96. doi: 10.1016/j.memsci.2008.11.046
![]() |
[190] |
Yang D, Li L, Chen B, et al. (2019) Functionalized chitosan electrospun nano fiber membranes for heavy-metal removal. Polymer 163: 74-85. doi: 10.1016/j.polymer.2018.12.046
![]() |
[191] |
Stephen M, Catherine N, Brenda M, et al. (2011) Oxolane-2, 5-dione modified electrospun cellulose nanofibers for heavy metals adsorption. J Hazard Mater 192: 922-927. doi: 10.1016/j.jhazmat.2011.06.001
![]() |
[192] |
Thamer BM, Aldalbahi A, Moydeen AM, et al. (2019) Fabrication of functionalized electrospun carbon nanofibers for enhancing lead-ion adsorption from aqueous solutions. Sci Rep 9: 1-15. doi: 10.1038/s41598-019-55679-6
![]() |
[193] |
Pereao OK, Bode-Aluko C, Ndayambaje G, et al. (2017) Electrospinning: polymer nanofibre adsorbent applications for metal ion removal. J Polym Environ 25: 1175-1189. doi: 10.1007/s10924-016-0896-y
![]() |
[194] |
Kampalanonwat P, Supaphol P (2010) Preparation and adsorption behavior of aminated electrospun polyacrylonitrile nanofiber mats for heavy metal ion removal. ACS Appl Mater Interfaces 2: 3619-3627. doi: 10.1021/am1008024
![]() |
[195] |
Chen C, Li F, Guo Z, et al. (2019) Preparation and performance of aminated polyacrylonitrile nanofibers for highly efficient copper ion removal. Colloids Surf A 568: 334-344. doi: 10.1016/j.colsurfa.2019.02.020
![]() |
[196] |
Martín DM, Faccini M, García MA, et al. (2018) Highly efficient removal of heavy metal ions from polluted water using ion- selective polyacrylonitrile nano fibers. J Environ Chem Eng 6: 236-245. doi: 10.1016/j.jece.2017.11.073
![]() |
[197] |
Zhao R, Li X, Sun B, et al. (2015) Preparation of phosphorylated polyacrylonitrile-based nanofiber mat and its application for heavy metal ion removal. Chem Eng J 268: 290-299. doi: 10.1016/j.cej.2015.01.061
![]() |
[198] |
Saeed K, Park SY, Oh TJ (2011) Preparation of hydrazine-modified polyacrylonitrile nanofibers for the extraction of metal ions from aqueous media. J Appl Polym Sci 121: 869-873. doi: 10.1002/app.33614
![]() |
[199] |
Hu Y, Wu XY, He X, et al. (2019) Phosphorylated polyacrylonitrile-based electrospun nanofibers for removal of heavy metal ions from aqueous solution. Polym Adv Technol 30: 545-551. doi: 10.1002/pat.4490
![]() |
[200] |
Zheng P, Shen S, Pu Z, et al. (2015) Electrospun fluorescent polyarylene ether nitrile nanofibrous mats and application as an adsorbent for Cu2+ removal. Fibers Polym 16: 2215-2222. doi: 10.1007/s12221-015-5425-4
![]() |
[201] |
Wang X, Min M, Liu Z, et al. (2011) Poly(ethyleneimine) nanofibrous affinity membrane fabricated via one step wet-electrospinning from poly(vinyl alcohol)-doped poly(ethyleneimine) solution system and its application. J Memb Sci 379: 191-199. doi: 10.1016/j.memsci.2011.05.065
![]() |
[202] |
Sang Y, Li F, Gu Q, et al. (2008) Heavy metal-contaminated groundwater treatment by a novel nanofiber membrane. Desalination 223: 349-360. doi: 10.1016/j.desal.2007.01.208
![]() |
[203] |
Martín DM, Ahmed MM, Rodríguez M, et al. (2017) Aminated Polyethylene Terephthalate (PET) nanofibers for the selective removal of Pb(Ⅱ) from polluted water. Materials 10: 1352. doi: 10.3390/ma10121352
![]() |
[204] |
Ma Z, Ji H, Teng Y, et al. (2011) Engineering and optimization of nano- and mesoporous silica fibers using sol-gel and electrospinning techniques for sorption of heavy metal ions. J Colloid Interface Sci 358: 547-553. doi: 10.1016/j.jcis.2011.02.066
![]() |
[205] |
Saxena N, Prabhavathy C, De S, et al. (2009) Flux enhancement by argon-oxygen plasma treatment of polyethersulfone membranes. Sep Purif Technol 70: 160-165. doi: 10.1016/j.seppur.2009.09.011
![]() |
[206] |
Bahramzadeh A, Zahedi P, Abdouss M (2016) Acrylamide-plasma treated electrospun polystyrene nanofibrous adsorbents for cadmium and nickel ions removal from aqueous solutions. J Appl Polym Sci 133: 42944. doi: 10.1002/app.42944
![]() |
[207] |
Yarandpour MR, Rashidi A, Eslahi N, et al. (2018) Mesoporous PAA/dextran-polyaniline core-shell nanofibers: Optimization of producing conditions, characterization and heavy metal adsorptions. J Taiwan Inst Chem Eng 93: 566-581. doi: 10.1016/j.jtice.2018.09.002
![]() |
[208] |
Wang J, Pan K, He Q, et al. (2013) Polyacrylonitrile/polypyrrole core/shell nanofiber mat for the removal of hexavalent chromium from aqueous solution. J Hazard Mater 244: 121-129. doi: 10.1016/j.jhazmat.2012.11.020
![]() |
[209] |
Zhang S, Shi Q, Christodoulatos C, et al. (2019) Adsorptive filtration of lead by electrospun PVA / PAA nanofiber membranes in a fixed-bed column. Chem Eng J 370: 1262-1273. doi: 10.1016/j.cej.2019.03.294
![]() |
[210] |
Gore P, Khraisheh M, Kandasubramanian B (2018) Nanofibers of resorcinol-formaldehyde for effective adsorption of As (Ⅲ) ions from mimicked effluents. Environ Sci Pollut Res 25: 11729-11745. doi: 10.1007/s11356-018-1304-z
![]() |
[211] |
Allafchian AR, Shiasi A, Amiri R (2017) Preparing of poly (acrylonitrile co maleic acid) nanofiber mats for removal of Ni (Ⅱ) and Cr (VI) ions from water. J Taiwan Inst Chem Eng 80: 563-569. doi: 10.1016/j.jtice.2017.08.029
![]() |
[212] |
Aliabadi M, Irani M, Ismaeili J, et al. (2014) Design and evaluation of chitosan/ hydroxyapatite composite nanofiber membrane for the removal of heavy metal ions from aqueous solution. J Taiwan Inst Chem Eng 45: 518-526. doi: 10.1016/j.jtice.2013.04.016
![]() |
[213] |
Jiang M, Han T, Wang J, et al. (2018) Removal of heavy metal chromium using cross-linked chitosan composite nano fiber mats. Int J Biol Macromol 120: 213-221. doi: 10.1016/j.ijbiomac.2018.08.071
![]() |
[214] |
Feng Q, Wu D, Zhao Y, et al. (2018) Electrospun AOPAN/RC blend nanofiber membrane for efficient removal of heavy metal ions from water. J Hazard Mater 344: 819-828. doi: 10.1016/j.jhazmat.2017.11.035
![]() |
[215] |
Lin Y, Cai W, Tian X, et al. (2011) Polyacrylonitrile/ferrous chloride composite porous nanofibers and their strong Cr-removal performance. J Mater Chem 21: 991-997. doi: 10.1039/C0JM02334E
![]() |
[216] |
Huang M, Tu H, Chen J, et al. (2018) Chitosan-rectorite nanospheres embedded aminated polyacrylonitrile nanofibers via shoulder-to-shoulder electrospinning and electrospraying for enhanced heavy metal removal. Appl Surf Sci 437: 294-303. doi: 10.1016/j.apsusc.2017.12.150
![]() |
[217] |
Irani M, Reza A, Ali M (2012) Removal of cadmium from aqueous solution using mesoporous PVA/TEOS/APTES composite nanofiber prepared by sol-gel/electrospinning. Chem Eng J 200-202: 192-201. doi: 10.1016/j.cej.2012.06.054
![]() |
[218] |
Li L, Wang F, Lv Y, et al. (2018) Halloysite nanotubes and Fe3O4 nanoparticles enhanced adsorption removal of heavy metal using electrospun membranes. Appl Clay Sci 161: 225-234. doi: 10.1016/j.clay.2018.04.002
![]() |
[219] |
Min L, Yang L, Wu R, et al. (2019) Enhanced adsorption of arsenite from aqueous solution by an iron-doped electrospun chitosan nanofiber mat: Preparation, characterization and performance. J Colloid Interface Sci 535: 255-264. doi: 10.1016/j.jcis.2018.09.073
![]() |
[220] |
Xiao S, Ma H, Shen M, et al. (2011) Excellent copper (Ⅱ) removal using zero-valent iron nanoparticle-immobilized hybrid electrospun polymer nanofibrous mats. Colloids Surfaces A Physicochem Eng Asp 381: 48-54. doi: 10.1016/j.colsurfa.2011.03.005
![]() |
[221] |
Wu S, Li F, Wang H, et al. (2010) Effects of poly (vinyl alcohol) (PVA) content on preparation of novel thiol-functionalized mesoporous PVA/SiO2 composite nano fiber membranes and their application for adsorption of heavy metal ions from aqueous solution. Polymer 51: 6203-6211. doi: 10.1016/j.polymer.2010.10.015
![]() |
[222] |
Aliahmadipoor P, Ghazanfari D, Gohari RJ, et al. (2020) Preparation of PVDF/FMBO composite electrospun nanofiber for effective arsenate removal from water. RSC Adv 10: 24653-24662. doi: 10.1039/D0RA02723E
![]() |
[223] |
Haddad MY, Alharbi HF (2019) Enhancement of heavy metal ion adsorption using electrospun polyacrylonitrile nanofibers loaded with ZnO nanoparticles. J Appl Polym Sci 136: 47209. doi: 10.1002/app.47209
![]() |
[224] |
Sahoo SK, Panigrahi GK, Sahoo JK, et al. (2021) Electrospun magnetic polyacrylonitrile-GO hybrid nanofibers for removing Cr(VI) from water. J Mol Liq 326: 115364. doi: 10.1016/j.molliq.2021.115364
![]() |
[225] |
Liu F, Wang X, Chen B, et al. (2017) Removal of Cr (VI) using polyacrylonitrile/ferrous chloride composite nanofibers. J Taiwan Inst Chem Eng 70: 401-410. doi: 10.1016/j.jtice.2016.10.043
![]() |
[226] |
Ho YS, McKay G (1999) Pseudo-second order model for sorption processes. Process Biochem 34: 451-465. doi: 10.1016/S0032-9592(98)00112-5
![]() |
[227] |
Toor M, Jin B (2012) Adsorption characteristics, isotherm, kinetics, and diffusion of modified natural bentonite for removing diazo dye. Chem Eng J 187: 79-88. doi: 10.1016/j.cej.2012.01.089
![]() |
[228] |
Neghlani PK, Rafizadeh M, Taromi FA (2011) Preparation of aminated-polyacrylonitrile nanofiber membranes for the adsorption of metal ions: Comparison with microfibers. J Hazard Mater 186: 182-189. doi: 10.1016/j.jhazmat.2010.10.121
![]() |
[229] | Zhang J, Xue CH, Ma HR, et al. (2020) Fabrication of PAN electrospun nanofibers modified by tannin for effective removal of trace Cr(Ⅲ) in organic complex from wastewater. Polymers 12: 1-17. |
[230] |
Morillo Martín D, Faccini M, García MA, et al. (2018) Highly efficient removal of heavy metal ions from polluted water using ion-selective polyacrylonitrile nanofibers. J Environ Chem Eng 6: 236-245. doi: 10.1016/j.jece.2017.11.073
![]() |
[231] |
Zhang S, Shi Q, Korfiatis G, et al. (2020) Chromate removal by electrospun PVA/PEI nanofibers: Adsorption, reduction, and effects of co-existing ions. Chem Eng J 387: 124179. doi: 10.1016/j.cej.2020.124179
![]() |
[232] |
Yarandpour MR, Rashidi A, Eslahi N, et al. (2018) Mesoporous PAA/dextran-polyaniline core-shell nanofibers: Optimization of producing conditions, characterization and heavy metal adsorptions. J Taiwan Inst Chem Eng 93: 566-581. doi: 10.1016/j.jtice.2018.09.002
![]() |
[233] |
Zhu F, Zheng YM, Zhang BG, et al. (2021) A critical review on the electrospun nanofibrous membranes for the adsorption of heavy metals in water treatment. J Hazard Mater 401: 123608. doi: 10.1016/j.jhazmat.2020.123608
![]() |
[234] | Xu Y, Li X, Xiang HF, et al. (2020) Large-Scale Preparation of polymer nanofibers for air filtration by a new multineedle electrospinning device. J Nanomater 2020: 1-7. |
[235] |
Wang X, Lin T, Wang X (2014) Scaling up the production rate of nanofibers by needleless electrospinning from multiple ring. Fibers Polym 15: 961-965. doi: 10.1007/s12221-014-0961-x
![]() |
[236] |
Kenry, Lim CT (2017) Nanofiber technology: current status and emerging developments. Prog Polym Sci 70: 1-17. doi: 10.1016/j.progpolymsci.2017.03.002
![]() |
[237] |
Tlili I, Alkanhal TA (2019) Nanotechnology for water purification: Electrospun nanofibrous membrane in water and wastewater treatment. J Water Reuse Desalin 9: 232-247. doi: 10.2166/wrd.2019.057
![]() |
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2. | Mehmet Pakdemirli, Symmetry analysis of the constant acceleration curve equation, 2023, 78, 0932-0784, 517, 10.1515/zna-2023-0049 | |
3. | Sixing Tao, Lie symmetry analysis, particular solutions and conservation laws of a (2+1)-dimensional KdV4 equation, 2023, 20, 1551-0018, 11978, 10.3934/mbe.2023532 |