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Integrated review of the nexus between toxic elements in the environment and human health

  • Emerging pollutants in the environment due to economic development have become a global challenge for environmental and human health management. Potentially toxic elements (PTEs), a major group of pollutants, have been detected in soil, air, water and food crops. Humans are exposed to PTEs through soil ingestion, consumption of water, uptake of food crop products originating from polluted fields, breathing of dust and fumes, and direct contact of the skin with contaminated soil and water. The dose absorbed by humans, the exposure route and the duration (i.e., acute or chronic) determine the toxicity of PTEs. Poisoning by PTEs can lead to excessive damage to health as a consequence of oxidative stress produced by the formation of free radicals and, as a consequence, to various disorders. The toxicity of certain organs includes neurotoxicity, nephrotoxicity, hepatotoxicity, skin toxicity, and cardiovascular toxicity. In the treatment of PTE toxicity, synthetic chelating agents and symptomatic supportive procedures have been conventionally used. In addition, there are new insights concerning natural products which may be a powerful option to treat several adverse consequences. Health policy implications need to include monitoring air, water, soil, food products, and individuals at risk, as well as environmental manipulation of soil, water, and sewage. The overall goal of this review is to present an integrated view of human exposure, risk assessment, clinical effects, as well as therapy, including new treatment options, related to highly toxic PTEs.

    Citation: Rolf Nieder, Dinesh K. Benbi. Integrated review of the nexus between toxic elements in the environment and human health[J]. AIMS Public Health, 2022, 9(4): 758-789. doi: 10.3934/publichealth.2022052

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  • Emerging pollutants in the environment due to economic development have become a global challenge for environmental and human health management. Potentially toxic elements (PTEs), a major group of pollutants, have been detected in soil, air, water and food crops. Humans are exposed to PTEs through soil ingestion, consumption of water, uptake of food crop products originating from polluted fields, breathing of dust and fumes, and direct contact of the skin with contaminated soil and water. The dose absorbed by humans, the exposure route and the duration (i.e., acute or chronic) determine the toxicity of PTEs. Poisoning by PTEs can lead to excessive damage to health as a consequence of oxidative stress produced by the formation of free radicals and, as a consequence, to various disorders. The toxicity of certain organs includes neurotoxicity, nephrotoxicity, hepatotoxicity, skin toxicity, and cardiovascular toxicity. In the treatment of PTE toxicity, synthetic chelating agents and symptomatic supportive procedures have been conventionally used. In addition, there are new insights concerning natural products which may be a powerful option to treat several adverse consequences. Health policy implications need to include monitoring air, water, soil, food products, and individuals at risk, as well as environmental manipulation of soil, water, and sewage. The overall goal of this review is to present an integrated view of human exposure, risk assessment, clinical effects, as well as therapy, including new treatment options, related to highly toxic PTEs.



    Cell polarity refers to the asymmetric organization in the structure of cells and can enable cells to carry out specialized functions such as differentiation, migration and tissue development [1,2,3]. Disruption of cell polarity may lead to dysfunctionality of cells, which is usually a hallmark of human cancers [4,5]. Cell polarity always involves the localization of some specific signaling molecules to a proper location of the cell membrane [1,6], but the mechanism for achieving the localization remains controversial.

    The budding yeast Saccharomyces cerevisiae has been developed as an attractive model system to study cell polarization as its generation time is short and useful experimental tools are available in this system [1]. The axis of polarized growth is regulated by budding location at where a newborn cell emerges from the original cell. The polarization event of budding yeast involves a key polarity protein, Cdc42 GTPase, which is highly conserved from yeasts to humans and is critical in polarity establishment [7,8]. Cdc42 localizes at a site of polarized growth on the plasma membrane and interacts with several proteins to trigger downstream processes, resulting in the emergence and growth of a bud [1]. In a wild-type cell, the Cdc42 localization generally occurs in response to spatial cues that is dependent on cell type. However, yeast cells can still bud in the absence of spatial cues, but the bud site is selected at a fully random manner, so-called symmetry breaking [9,10]. A lot of previous experimental works have studied polarization in the absence of Rsr1, which connects the spatial cue and the downstream polarization pathway [9,11,12,13].

    Several mathematical models have been proposed to understand the mechanisms of achieving symmetry breaking in cell polarity [9,14,15,16,17]. More recently, in the geometric representation of a cell, studies [17,29] present bulk-surface reaction diffusion systems which incorporate cell membrane as surface and cytoplasm as bulk to investigate cell polarity in high dimensions. With the bulk-surface reaction diffusion models, classical linear stability analysis has been performed in literatures [17,30] and more recent approach, the local perturbation analysis, is also proposed [19,29]. Reaction-diffusion equation was always applied to model the budding process in yeast systems [14,15,16]. By the fact that the ratio of the diffusion rates of the cytoplasmic and membrane-bound Cdc42 is large, the Turing-type system became a possible mechanism for achieving symmetry breaking [14,16,18]. The key component of the Turing-type mechanism is the positive feedback loop in the cycle of Cdc42 and this concept was supported by a number of theoretical studies [14,16,17,18,19].

    Some experimental and theoretical studies indicated that negative feedback regulation exists during the formation of Cdc42 cluster [20,21,22,23,24]. Recent studies in [22,23,25] proposed that a delayed negative feedback may be important for maintaining the robustness of Cdc42 localization and the oscillating behavior of Cdc42 cluster during the process. However, cell polarization system with delayed negative feedback has not been studied with mathematical analysis in detail. In this paper, we first formulate a partial differential equation with positive and delayed negative feedback loops for studying cell polarization system. Then the Turing stability analysis is applied to identify the parameter conditions for achieving symmetry breaking during the process [14,26]. Our theoretical study provides us with several conditions for achieving a signaling cluster and simultaneously, these conditions include the constraint for the time delay in negative feedback loop. Numerical simulations are used to support our theoretical study and provide a full picture to understand the dynamics of cell polarization process. Also, our results support that the oscillating behavior of signaling cluster can be achieved by controlling the length of the time delay in negative feedback and the magnitude of positive feedback.

    This paper is organized as follows. In Section 2, we present a reaction-diffusion model of cell polarization with positive and delayed negative feedbacks. In Section 3, we perform the Turing stability analysis to the model proposed in Section 2 to derive the conditions for which cell polarity may emerge. Section 4 contains the studies of our numerical simulations. Finally, the conclusion is presented in Section 5.

    Here we consider a partial differential equation describing the dynamics of a polarized signaling molecule on the cell membrane (Figure 1). A recent study [29] of bulk-surface reaction diffusion models suggested that the geometry of the cell may affect the dynamics of polarized signaling molecules but here we assume that the cell is a sphere which is consistent with the situation of budding yeast. Under the assumption applied in [9,22], we consider that all cytoplasmic signaling molecules are inactive and all membrane-bound signaling molecules are active. The variable we consider here is the membrane-bound active form of the signaling molecules and the cytoplasmic inactive form of this molecule is modeled implicitly through the conservation of total molecules. This type of model was well applied to study Cdc42-GTPase cycle in budding yeast [9,22]. Most of the GTPase cycles have a common feature that enables them to switch between their active and inactive forms. The activation process is usually initiated by hydrolysis and can be reversed by Guanine nucleotide exchange factors (GEFs), which cause the GDP to dissociate from the GTP. For the membrane-bound form, GDIs release the GDP from the cell membrane to the cytoplasm through binding to the GTPase and it can also be reversed through the action of GDI displacement factors.

    Figure 1.  The spatial domains and feedback systems in the cell polarization model. A) Two-dimensional domain, represents the cell membrane, and simplified one-dimensional domain, represents the cross section of the cell membrane; B) System with a non-local positive feedback and delayed negative feedback. (): lateral diffusion; (): positive feedback; (): negative feedback; (): molecule transportation.

    The spatial domain in our model is the membrane of a cell of radius R μm denoted by M, which is a sphere (two-dimensional domain), or, for simplicity, we can only consider the cross section of the cell membrane, which is a circle (one-dimensional domain) (shown in Figure 1A). We use a variable a to represent the particle fractions of the membrane-bound active signaling molecules [9]. The dynamic of a is governed by a reaction-diffusion equation with the feedback functions F(,) and G():

    a(t,x)t=Dm2a(t,x)+F(a(t,x),^a2(t))(1ˆa(t))G(a(tτ,x))a(t,x), (2.1)

    with ˆa(t)=Ma(t,x) dSx/|M| and ^a2(t)=Ma2(t,x) dSx/|M|, respectively representing the average values of a and a2 over the cell membrane, and |M| equals to the total area of the domain M. The first term of the right-hand side represents the diffusion of signaling molecules with the lateral surface diffusion rate coefficient Dm and the Laplace operator 2 on the cell membrane.

    In our model, we assume that the total number of signaling molecules in the whole cell is conserved. With the fact that ˆa represents the total fractions of the membrane bound species, we obtain

    N=(ˆa+Fracc)N, (2.2)

    where Fracc is the fraction of cytoplasmic inactive signaling molecules and N is the total number of signaling molecules, including active and inactive forms, in the whole cell. Hence, by (2.2), Fracc=1ˆa. Due to the fast cytoplasmic diffusion, we assume that signaling molecules are uniformly distributed throughout the cytoplasm. By assuming the activation rate is proportional to the fraction of cytoplasmic signaling molecules, the term F(a,^a2)(1ˆa) in (2.1) is applied to model the activation process in the system.

    In budding yeast, there is a positive feedback loop to promote Cdc42 activation [9,22]. Here we assume that the activation rate is positively regulated by the active molecules a and thus the function F is an increasing function of a (Figure 1B). In this paper, we define the feedback function as

    F(a,^a2)=konk1+k2a21+k1+k2^a2. (2.3)

    This feedback function models multi-step cooperative interactions which has been used in several biological Turing type systems [26]. The nonlinear cooperativity is modeled by the term a2, the degree of cooperativity is 2 [22]. The function form in (2.3) depends on a non-local term ^a2 and the local density a. The feedback is mediated through a special type of molecules initially uniformly distributed in the cytoplasm, such as the Bem1 complex in the Cdc42 cycle of budding yeast [18,27]. The detailed derivation of this feedback function can be found in A.1.

    The observed oscillation and fluctuation of Cdc42 cluster support that the delayed negative feedback is involved in the cell polarization system of budding yeast [22]. We assume that the deactivation function G depends on the value of a(tτ,x) with a delay time of τ, as the deactivation rate varies with the activation level of Rga1, which may be regulated by the level of Cdc42 in budding yeast (Figure 1B). Here we apply a linear function to model the deactivation rate G in (2.1):

    G(a(tτ,x))=g1+g2a(tτ,x). (2.4)

    The studies in [11] show that the necessary condition for achieving Cdc42 localization is that the rate of activation grows faster with the increase in active Cdc42 than the rate of deactivation, so that the linear function is used here instead of higher order functions.

    In this section, the Turing stability analysis is applied to figure out the conditions of the parameters to achieve spontaneous cell polarization [26]. The analysis in this section can be applied for the system with general feedback functions F(a,^a2) and G(a(tτ,x)).

    For studying the stability of a homogeneous steady state solution, we first study a homogeneous steady state solution a0 of the system (2.1). Since a0 is homogeneous over space, ^a20=a20 and the solution a0 satisfies the following equation:

    0=F(a0,a20)(1a0)G(a0)a0. (3.1)

    Since F and G are positive functions, the right-hand side of (3.1) is negative when a0=1; the right-hand side of (3.1) is positive when a0=0. By the intermediate value theorem, at least one homogeneous positive steady state solution a0 exists between 0 and 1.

    Here we define a(t,x) as slightly perturbed functions from the homogeneous steady state a0:

    a(t,x)=a0+ϵa1(t,x), (3.2)

    where the perturbation amplitude ϵ1 is much smaller than the value of a0. After substituting (3.2) into Eq. (2.1) and applying Taylor expansion around a0, the leading terms satisfy the following system:

    a1t=Dm2a1+(FX1(a0,a20)a1+2a0^a1FX2(a0,a20))(1a0)G(a0)a1GX(a0)a0a1F(a0,a20)^a1, (3.3)

    where a1=a1(tτ,x); FX1 and FX2 denote the partial derivatives of F with respect to the first and the second arguments, respectively; GX denotes the first derivative of G. When the feedback functions (2.3) and (2.4) are considered, we obtain that FX1 is positive, FX2 is negative and GX is positive. A particular spatially periodic perturbation function, a1(t,x)=αeλtEw(x), is considered here. In the function, α is a nonzero parameters, w is a non-negative integer and Ew(x) is the w-th non-zero eigenfunction of the Laplace operator. Eq. (3.3) becomes

    λ=σwDm+(FX1+2a0FX2δ(w))(1a0)GGXa0eλτFδ(w), (3.4)

    where

    δ(w)={1if w=0,0if w>0,

    and the eigenvalue

    σw={w2/R2for the one-dimensional domain;2w2/R2for the two-dimensional domain,

    where R is the radius of the circle; FX1,FX2,F,G,GX are evaluated at (a0,a20).

    The emergence of cell polarity usually depends on the instability of the homogeneous steady state, which requires two conditions [16,26]:

    (1) If the perturbation is spatially homogeneous (w=0), the homogeneous steady state a0 is linearly stable. This condition is equivalent to that the real parts of all eigenvalues λ are negative when the wave number w is zero. This condition ensures that a homogeneous solution starting from a constant initial condition close to a0 will finally tend to a0.

    (2) The homogeneous steady state a0 is linearly unstable under a perturbation with a positive wave number w. This condition is equivalent to that there exists a positive integer w such that at least one λ satisfying (3.4) has a positive real part.

    These two conditions imply that the random perturbed homogeneous steady state are moving toward another inhomogeneous steady state for and only for positive wave lengths.

    Eq. (3.4) has a form

    λ=Aw+Beλτ, (3.5)

    where

    Aw=σwDm+(FX1+2a0FX2δ(w))(1a0)GFδ(w)

    and

    B=GXa0.

    According to [28], we can determine the signs of all possible λ by the following theorem:

    Theorem 1 (Theorem 4.7 from [28]). For Eq. (3.5), we have

    (a) If Aw+B>0, then there exists at least one λ with positive real part;

    (b) If Aw+B<0 and AwB0, then all λ have negative real parts;

    (c) If Aw+B<0 and AwB>0, then there exists

    τ=(B2A2w)1/2cos1(Aw/B)>0

    such that (1) all λ have negative real parts for 0<τ<τ, and (2) there exists at least one λ with positive real part for τ>τ.

    Condition (1)

    By Theorem 1, the condition (1) is equivalent to that when w=0, we have

    Theorem 1(b):A0+B<0 and A0B0;

    or

    Theorem 1(c):A0+B<0A0B
     and 0τ<(B2A20)1/2cos1(A0/B),

    where A0=(FX1+2a0FX2)(1a0)GF and B=GXa0.

    Since B is always negative, we have A0B>A0+B and |B|=B so

    A0B0 implies A0+B<0

    and

    A0+B<0 and A0B>0 if and only if |A0|<|B|.

    So the two situations for satisfying the condition (1) can be simplified as the following two cases:

    Case (1a):A0B0

    or

    Case (1b):|A0|<|B| and 0τ<(B2A20)1/2cos1(A0/B).

    From Cases (1a) and (1b), we can see that if the time delay τ is large and A0B>0, the homogeneous steady state is not stable for a homogeneous perturbation. Under this situation, the steady state does not satisfy the condition (1) of Turing instability. For studying this situation, we consider the spatial homogeneous system from the model (2.1):

    dˉadt=konk1+k2ˉa21+k1+k2ˉa2(1ˉa)(g1+g2ˉa(tτ))ˉa.

    It is easy to show that the solution ˉa is bounded between 0 and 1 with ˉa(0)(0,1). If all steady states of ˉa are not stable for a large time delay τ, the solution is under oscillation around some homogeneous steady states. Hence, for the original system (2.1), the instability for some positive wave number w>0 may still contribute to achieve inhomogeneous pattern when the condition (2) is satisfied and the solution is close to the homogeneous steady state. Our simulation results shown in the later section will demonstrate that, with a large time delay, a cluster of signaling molecules can be formed from a homogeneous steady state with a small inhomogeneous perturbation even though all homogeneous steady state is not stable for w=0.

    Condition (2) By Theorem 1, the condition (2) is equivalent to the situation that for some positive integers w>0, we have

    Theorem 1(a):Aw+B>0;

    or

    Theorem 1(c):Aw+B<0,AwB>0 and τ>(B2A2w)1/2cos1(Aw/B),

    where Aw=σwDm+FX1(1a0)G and B is defined above.

    Since Aw is decreasing with respect to w for w1, the two cases can be simplified to the situation only for w=1:

    Case (2a):A1+B>0

    or

    Case (2b):|A1|<|B| and τ>(B2A21)1/2cos1(A1/B).

    where A1=σ1Dm+FX1(1a0)G.

    To obtain Turing instability, at least one of Cases (2a) and (2b) has to be satisfied. The following two propositions provide the necessary conditions for obtaining at least one of Cases (2a) and (2b).

    Proposition 2. For the system (2.1) with the feedback forms (2.3) and (2.4), Case (2a) is satisfied only if

    konk2>g2. (3.6)

    Proof. Case (2a) can be written as

    A1+B=kon2k2a01+k1+k2a20(1a0)(g1+2g2a0)σ1Dm>0. (3.7)

    Since

    kon2k2a01+k1+k2a20(1a0)(g1+2g2a0)σ1Dm<2(konk2g2)a0,

    Case (2a) implies konk2>g2.

    Proposition 3. For the system (2.1) with the feedback forms (2.3) and (2.4), Case (2a) or Case (2b) is satisfied only if

    konk2>12(g1+σ1Dm). (3.8)

    Proof. If Case (2a) or Case (2b) is true, we have A1B>0 which can be written as

    A1B=kon2k2a01+k1+k2a20(1a0)g1σ1Dm>0. (3.9)

    Since

    kon2k2a01+k1+k2a20(1a0)g1σ1Dm<2konk2g1σ1Dm,

    the inequality (3.9) implies konk2>12(g1+σ1Dm).

    The two propositions show that konk2 has to be large enough for achieving Turing instability. Other than the necessary conditions, the following theorem provides a sufficient condition for determining a range of parameters in which Case (2a) is satisfied:

    Theorem 4. Assume that σ1Dm<konk1. For the system (2.1) with the feedback forms (2.3) and (2.4), Case (2a) is satisfied if

    112kon(g2k2+g22k22+(g1+σ1Dm)2k1k2)>0 (3.10)

    and

    k1g2k2+k21g22k22+(g1+σ1Dm)2k1k2<(g1σ1Dm)[(kon+g1)24g22+kong2(112kon(g2k2+g22k22+(g1+σ1Dm)2k1k2))kon+g12g2]. (3.11)

    The proof of Theorem 4 is based on the method used in [14] and the detailed proof is presented in A.2. It is worth noting that the necessary and sufficient conditions can be obtained by the formula for the roots of quadratic equation but the formula is too complicated and not applicable for parameter estimation.

    The conditions obtained in Theorem 4 provide a good insight on the range of parameters for achieving Case (2a). For example, Theorem 4 implies that there exist a constant k>0 such that Case (2a) is satisfied if kon>k. Figure 2 displays the numerical results for determining how close between the conditions in Theorem 4 and the exact range for achieving Case (2a). In the figure, we consider 1000 sets of different (k2,g2) generated uniformly within [1,100]×[1,10], and choose the remaining parameters within the ranges: σ1Dm=[0.025,0.225]/min, kon[1,5]/min, k1=1, g1=1/min, which are based on some previous works [22,27].

    Figure 2.  The stability diagrams for the system (2.1) with the feedback forms (2.3) and (2.4) with different kon and σ1Dm. A) The ranges of the parameters that satisfy the conditions provided in Theorem 4. Brown region represents the ranges that satisfy the conditions; Green region represents the ranges that do not satisfy the conditions. B) The ranges of the parameters that satisfy Case (2a). Brown region represents the ranges that satisfy Case (2a); Green region represents the ranges that do not satisfy Case (2a). C) The difference between the ranges obtained in (A) and (B). Brown region represents the ranges that the results in (A) and (B) are not consistent; Green region represents the ranges that the results in (A) and (B) are consistent.

    Although the conditions in Theorem 4 (the brown regions in Figure 2A) are just sufficient conditions for Case (2a), they still have a good agreement with the exact range for Case (2a) (the brown regions in Figure 2B) and the difference appears only in a few sets of parameters (Figure 2C). The numerical results in Figure 2 show that the difference between the conditions in Theorem 4 and the exact region for Case (2a) can be minimized by reducing the membrane-bound diffusion coefficient Dm which is usually small (<0.5μm2/min) in budding yeast system [22,27].

    Linear stability analysis only focuses on the local behavior near the homogeneous steady state. Here we apply numerical simulations to study the long-term behavior of the system under different stability conditions studied in the previous section.

    First, we use a computational simulation for one-dimensional model to study the ranges of the parameters for satisfying the two stability conditions (1) and (2). 10,000 sets of different (k2,g2) are uniformly generated within the region [1,100]×[1,100]. Other parameters are set as follows: Dm=0.1μm2/min, kon[1,5]/min, k1=1, g1=1/min, τ[0.1,1]min. Here Dm was obtained by the smallest value of σ1Dm (σ1Dm=0.025/min and σ1=1/R2) in Figure 2 which has given the conclusion that smaller Dm can reduce the difference between conditions in Theorem 4 and the exact region for Case (2a). Figure 3 displays the stability diagrams for kon=1/min,3/min and 5/min and τ=0.1min,0.5min and 1min. Figure 3A shows the ranges of the parameters that satisfy the condition (1) (the stability condition for homogeneous perturbation with w=0); Figure 3B shows the ranges of the parameters that satisfy the condition (2) (the stability condition for inhomogeneous perturbation with w=1).

    Figure 3.  The stability diagrams for the system (2.1) with the feedback forms (2.3) and (2.4) with different kon values and τ values. A) The ranges of parameters that satisfy the condition (1). B) The ranges of parameters that satisfy the condition (2). Brown region represents the ranges that satisfy the condition; Green region represents the ranges that do not satisfy the condition.

    According to the results in Figure 3, different combinations of parameters are chosen under different stability conditions. Here we fix the parameters Dm=0.1μm2/min, kon=3/min, k1=1 and g1=1/min [22,27]. For other parameters, we choose within the ranges k2[1,100], g2[1,100]/min and τ[0.1,1]min. Under this parameter setting, the system has a unique homogeneous steady state solution a0. In all the simulations throughout this paper, the initial conditions are the homogeneous steady states with spatial perturbation (±10% perturbation):

    a(t,x)=a0(1+0.1η(x)), for τt0,

    where η(x) is a function of uniformly distributed random number between -1 and 1. If the perturbation is large, the initial condition may be larger than 1. Within the ranges of the parameters we tested, we have verified that 1.1a0<1. In some cases, larger perturbation (±20%) is also considered for further study and the results are consistent with what we observed here. We apply the second-order central difference approximation for the diffusion term, periodic boundary conditions for two end sides, Riemann sum for the definite integrals and the built-in function dde23 in the MATLAB for the temporal simulation with the constant time delay τ. For the spatial discretization, the number of spatial points is 300 with uniform distribution and the radius of the circle is R=2μm.

    Figure 4 demonstrates the simulations for g2=5/min which represents the cases that the magnitude of negative feedback is low. When τ=0.1min (short time delay) and k2=20 (weak positive feedback), the system does not satisfy the condition (2) and the numerical simulation in Figure 4A shows that the concentration of a rapidly returns back to the homogeneous steady state. When the magnitude of positive feedback (k2) increases to 50 or higher, the system satisfies the two conditions (1) and (2) and inhomogeneous patterns can be always observed in the simulation (Figure 4A). Figure 4B shows that when τ is increased to be 0.5min, a cluster of signaling molecules does not exist if the condition (2) is not satisfied, such as k2=20 (weak positive feedback). When k2 increases to 50 or higher, a cluster of signaling molecules appears but is not stable at a certain location. In this case, the signaling cluster is traveling with constant speed and keeps moving until the end.

    Figure 4.  The simulations for the one-dimensional model with weak negative feedback, g2=5/min. In the simulations, we set Dm=0.1μm2/min, kon=3/min, k1=1, g1=1/min, k2[20,100], τ=0.1min (in A), 0.5min (in B). The horizontal axis represents time evolution and the vertical axis represents membrane position (shown in the left panel).

    For stronger negative feedback (g2=50/min or 100/min) with large enough time delay and positive feedback, a cluster of signaling molecules can appear but may not be stable at a certain location. Figure 5A demonstrates that when τ=0.1min and the system does not satisfy the condition (2), the concentration of a rapidly returns back to the homogeneous steady state even under a strong positive feedback.

    Figure 5.  The simulations for the one-dimensional model with strong negative feedback, g2=50/min (in A-C) and g2=100/min (in D). In the simulations, we set Dm=0.1μm2/min, kon=3/min, k1=1, g1=1/min, k2[15,100], τ=0.1min (in A), 0.5min (in B), 1min (in C-D). The horizontal axis represents time evolution and the vertical axis represents membrane position (as in Figure 4).

    Figures 5B-D show that how the dynamics of the signaling clusters change when the magnitude of the positive feedback increases from 5 to 50. Interestingly, when k215, Case (2b) is satisfied and an inhomogeneous pattern is observed: for k2=15, the concentration of a signaling cluster is oscillating during the process; when k2 increases to 50, a traveling signaling cluster appears. In Figure 5D, when k2=50, both Case (1a) and Case (1b) are not satisfied so the homogeneous steady state is unstable for a homogeneous perturbation w=0. The simulation shows that a signaling cluster can be obtained in this case even though the homogeneous steady state is not stable when w=0. But this situation is usually with larger time delay constant so the signaling cluster may not be stable at a certain location.

    Figure 6 summarizes the simulation results for studying how the long-term behavior of the system depends on the values of k2 and τ with two different levels of negative feedback, g2=5/min,50/min. The results are consistent with our previous stability analysis. From this result, we observe that suitable ranges of the magnitude of positive feedback and time delay are important for achieving an oscillation of signaling cluster, observed in experiments [22]. It is worth noting that although the numerical results obtained here only focused on a simplified domain (the one-dimensional domain for the cross section of the cell), we can apply the results onto the the two-dimensional spherical surface. Figure 7 displays three examples of the simulations on the two-dimensional spherical surface. For the spatial discretization, the number of spatial points is 4098 with uniform distribution and the radius of the circle is R=2μm. These three simulations are corresponding to the one-dimensional simulations shown in Fig 4A and Figures 5B and C. In Figure 7A, a stable cluster is formed until the end; in Figures 7B, C, the concentration of the signaling cluster is oscillating during the process. The results in these three cases are consistent with what observed in the one-dimensional simulations.

    Figure 6.  The long-term behavior of the system with different values of k2, τ and g2. A) Weak negative feedback, g2=5/min. Blue region: no cluster is formed; green region: a traveling signaling cluster is observed; yellow region: a stable signaling cluster is formed. B) Strong negative feedback, g2=50/min. For the simulations, 100 sets of different (k2,τ) are uniformly generated within the region [1,50]×[0.1,0.5]. Blue region: no cluster is formed; green region: a traveling signaling cluster is observed; yellow region: an oscillating cluster is observed.
    Figure 7.  Time-dependent solutions of a for the two-dimensional model. In the simulations, Dm=0.1μm2/min; kon=3/min; k1=1; k2=50 (in A), 15 (in B, C); g1=1/min; g2=5/min (in A), 50/min (in B, C); τ=0.1min (in A), 0.5min (in B), 1min (in C).

    Recent experimental studies demonstrated that delayed negative feedback regulation may play an important role in robustness of Cdc42 localization and the oscillating behavior of Cdc42 cluster during cell polarization [22]. However, detailed mathematical analysis is not well studied for this system.

    In this paper, we have built a simple model of reaction-diffusion equation for cell polarization system which is regulated by positive and delayed negative feedback together. Our model involves general forms of positive and negative feedbacks. We have applied Turing stability analysis to analyze the conditions that can give rise to spontaneous cell polarization. Moreover, our numerical studies reveal that Cdc42 cluster can form but may not be spatially stable when the time delay τ is large. Also, our numerical results support that the oscillating behavior of Cdc42 cluster can be achieved by controlling the length of time delay and the magnitude of positive feedback.

    The results in this paper provide parameter conditions for the existence of polarized solutions in the cell polarization system with delayed negative feedback. Furthermore, the analysis of the feedback can be easily extended to higher dimensional domain and provides insights to understand other similar biological systems in which cell polarity is established. Also, like the study in [22], our results can be used to study how the spatial cue level and the time delay affect the oscillating behavior by involving a spatial cue function kcue in the positive feedback term:

    F(x,a,^a2)=kcue(x)+konk1+k2a21+k1+k2^a2, (5.1)

    where

    kcue(x)={C0if x[π0.25,π+0.25],0otherwise.

    In the future work, our model can be combined with a moving boundary system for cell shape change during budding, then we can extend our study of Cdc42 localization to cell morphogenesis.

    WCL was partially supported by a CityU Strategic Research Grant (Project No. 7004697) and a grant from the Research Grants Council of the Hong Kong Special Administrative Region, China (Project No. CityU 11303117).

    All authors declare no conflicts of interest in this paper.

    We assume that the feedback molecules, as shown in Figure 1B, are initially uniformly distributed in the cytoplasm and then the active signaling molecules will recruit them to the cell membrane. On the other hand, the activation rate of the signaling molecules is proportional to the density of the membrane-bound feedback molecules. Therefore, we obtain the following equation for c:

    ct=(h1+h2a2)(1ˆc)hoffc, (A.1)

    where (h1+h2a2) and hoff are the recruitment rate and the dissociation rate of the feedback molecules, respectively; (1ˆc) is the fraction of the cytoplasmic feedback molecules (ˆc is the average value of c over the membrane).

    We know that the dynamics of the feedback molecules is much faster than that of the signaling molecules [18,27], the variable c can be approximated by the solution of the quasi steady state equation of Eq. (A.1):

    (h1+h2an)(1ˆc)hoffc=0.

    By integrating the above equation over the membrane, we can obtain the value of ˆc. After substituting ˆc back into the equation, we have

    c=k1+k2an1+k1+k2^an,

    where k1 and k2 equal to h1/hoff and h2/hoff, respectively. We assume that the feedback strength is linearly proportional to the value of c, then we obtain the feedback function (2.3).

    Here we will state two lemmas, which will be used in Section A.2.2 for the proofs of Theorems 4. First, we define a function fy(a) used in the lemmas:

    fy(a)=(γ1+γ2a2)(1γ3yγ4y2)γ5aγ6a2D(ay). (A.2)

    where γ1,γ2,γ4,γ5,γ6>0, γ31 and 0D<γ1γ3.

    Lemma 5. Assume that γ2>γ6 and y[0,y] where γ2(1γ3yγ4y2)γ6=0. The function fy in (A.2) has the following properties:

    1. mina0fy(a) equals to

    γ1(γ1γ3D)yγ1γ4y2(γ5+D)24(γ2(1γ3yγ4y2)γ6),

    which is strictly decreasing with respect to y for y(0,y).

    2. For each y, there exist at most two solutions in {a|a0} satisfying fy(a)=0.

    3. There exists a number ym in [0,y) such that two smooth functions a1(y), a2(y) can be well defined in the domain [ym,y) and the following properties hold:

    (a) mina0fy(a)0 for any y[ym,y);

    (b) fy(a1(y))=fy(a2(y))=0 for any y[ym,y);

    (c) a1(y)>a2(y)0 for any y(ym,y);

    (d) a1(y)>0 and a2(y)<0 for any y(ym,y);

    (e) limyya1(y)= and limyya2(y)=0;

    (f) dfyda|a=a1(y)>0 and dfyda|a=a2(y)<0 for any y(ym,</italic><italic>y);

    (g) if there is at least one solution in a0 for f0(a)=0, then ym=0;

    (h) if there is no solution in a0 for f0(a)=0, then a1(ym)=a2(ym), dfymda|a=a1(ym)=dfymda|a=a2(ym)=0 and mina0fym(a)=0.

    Proof. 1. First we consider the first and second derivatives of fy,

    dfy(a)da=2γ2a(1γ3yγ4y2)γ52γ6aD, (A.3)
    d2fy(a)da2=2γ2(1γ3yγ4y2)2γ6. (A.4)

    By Eq. (A.4), we show that d2fy(a)da2>0 for y[0,y) and the minimum point in {a|a0} is at

    a=γ5+D2γ2(1γ3yγ4y2)2γ6

    with

    mina0fy(a)=γ1(γ1γ3D)yγ1γ4y2(γ5+D)24(γ2(1γ3yγ4y2)γ6).

    By the given condition D<γ1γ3, we can show that mina0fy(a) is strictly decreasing with respect to y.

    2. Suppose that y is a fixed number. If mina0fy(a)>0, there is no solution a0 satisfying fy(a)=0.

    If mina0fy(a)=0, the minimum point

    ˉa=γ5+D2γ2(1γ3yγ4y2)2γ6

    is one of the roots for fy(a). As dfy(a)da>0 for a>ˉa and dfy(a)da<0 for 0a<ˉa, fy(a)>fy(ˉa) for any aˉa, and therefore ˉa is the only solution of fy(a)=0.

    If mina0fy(a)<0, by the fact that fy(0)>0, limafy(a)>0 and the intermediate value theorem, we can show that there are at least two solutions satisfying fy(a)=0. As dfy(a)da>0 for a>ˉa and dfy(a)da<0 for 0a<ˉa, fy(a)>fy(ˉa) for any aˉa. So there are only two roots of fy(a): one is in [0,ˉa), and the other is in (ˉa,).

    3. By the result of part 1, mina0fy(a) tends to as y is close to y. If mina0fy(a)>0 for y=0, according to the intermediate value theorem, we can find ym such that mina0fym(a) equals zero; if mina0fy(a)0 for y=0, we define ym=0.

    Since mina0fy(a) is strictly decreasing with respect to y, and according to the results of part 2, fy(a)=0 has two solutions a for any y(ym,y), so we can define two functions a1(y) and a2(y) that satisfy fy(a1(y))=fy(a2(y))=0 and a1(y)>a2(y) for any y(ym,y), that is,

    a1(y)=max{a0|fy(a)=0},a2(y)=min{a0|fy(a)=0}.

    The derivative of fy(a) with respect to y is (γ1+γ2a2)(γ3+2γ4y)+D, which is always negative due to γ1γ3>D, and fy(a) is a smooth function with respect to y and a, and therefore we can apply the inverse function theorem to show that a1(y) and a2(y) are smooth functions. By the definitions and the proof of part 2, it is easy to verify the properties (a, b, c, f, g, h).

    By property (b), we have fy(a1(y))=0 and fy(a2(y))=0. By differentiating these two equations with respect to y on both sides, we have (γ1+γ2a1(y)2)(γ3+2γ4y)+D+dfyda(a1(y))a1(y)=0 and (γ1+γ2a2(y)2)(γ3+2γ4y)+D+dfyda(a2(y))a2(y)=0. Hence we obtain

    a1(y)=(γ1+γ2a1(y)2)(γ3+2γ4y)+Ddfyda(a1(y)),a2(y)=(γ1+γ2a2(y)2)(γ3+2γ4y)+Ddfyda(a2(y)).

    By property (f) and γ1γ3>D, we proved that a1(y)>0 and a2(y)<0, which completes the proof of property (d).

    From the proof of part 2, we have a2[0,ˉa) and a1(ˉa,). So we know that a1(y) tends to infinity as y goes to y. Since a=0 is the solution for fy(a)=0, we have limyya2(y)=0, which completes the proof of property (e).

    Lemma 6. Let Ω be a solution of

    (γ5+D)24(γ2(1γ3Ωγ4Ω2)γ6)+γ1(1γ3Ωγ4Ω2)=0, (A.5)

    and assume that Ω>0 and γ2>γ6. If

    2γ1(1γ3Ωγ4Ω2)+(Dγ5)Ω<0 (A.6)

    is satisfied, then dfa0da|a=a0>0 holds for any solution a0 satisfying fa0(a0)=0.

    For the proofs of Lemmas 6, we define two functions S1, S2 in the domain [ym,1/γ3):

    S1(y)=a1(y)y,S2(y)=a2(y)y,

    where a1, a2 and ym are defined in Lemma 5.

    Proof. There are two parts in the proof:

    1. Prove that if S1(ym)<0, dfa0da|a=a0>0 holds for any solution a00 satisfying fa0(a0)=0.

    2. Prove that condition (A.6) implies S1(ym)<0.

    By combining these two results, we can prove that if the condition (A.6) is satisfied, then dfa0da|a=a0>0 holds for any solution a00 satisfying fa0(a0)=0.

    Proof of part 1: Suppose that S1(ym)<0. Since a1(y)a2(y), we get S2(ym)S1(ym)<0. By a2(y)<0 (Lemma 5(3c)), we have S2<0, which means that S2 is a decreasing function. Since S2(ym)<0 and S2 is a decreasing function, S2(y)<0 for all y[ym,y), and there is no solution to S2(y)=0.

    According to Lemma 5 and the definitions of S1 and S2, all solutions a00 for fa0(a0)=0 have to satisfy S1(a0)=0 or S2(a0)=0. Since S1(ym)<0 implies that there is no solution satisfying S2(y)=0, all solutions a00 for fa0(a0) have to satisfy S1(a0)=0 and therefore dfa0da|a=a0>0 according to Lemma 5(3f).

    Proof of part 2: Suppose that condition (A.6) is satisfied, by Lemma 5(1), we have

    mina0fy(a)=γ1(γ1γ3D)yγ1γ4y2(γ5+D)24(γ2(1γ3yγ4y2)γ6).

    If 0<y<Ω, we have

    (γ5+D)24(γ2(1γ3yγ4y2)γ6)+γ1(1γ3yγ4y2)>0(γ5+D)24(γ2(1γ3yγ4y2)γ6)+γ1(1γ3yγ4y2)+Dy>0mina0fy(a)>0. (A.7)

    Lemma 5(3a) implies that mina0fym(a)>0 so ym is larger than Ω>0. Then we apply Lemma 5(3h) to show that there is no solution with a0 such that f0(a)=0.

    By Lemma 5(3b, h), we know that (ym,a1(ym)) satisfies the following two equations:

    fym(am)=(γ1+γ2a2m)(1γ3ymγ4y2m)γ5amγ6a2mD(amym)=0, (A.8)
    dfymda|a=am=2γ2am(1γ3ymγ4y2m)γ52γ6amD=0, (A.9)

    where am=a1(ym).

    After multiplying (A.8) and (A.9) by n and am, respectively, we have

    2(γ1+γ2a2m)(1γ3ymy4y2m)2γ5am2γ6a2m2D(amym)=0, (A.10)
    2γ2a2m(1γ3ymγ4y2m)γ5am2γ6a2mDam=0. (A.11)

    Subtracting (A.10) by (A.11), we obtain

    2γ1(1γ3ymγ4y2m)γ5am+2DymDam=0,

    which leads to

    am=2γ5+D(γ1(1γ3ymγ4y2m)+Dym). (A.12)

    By substituting (A.12) into S1(ym), we obtain

    S1(ym)=amym=1γ5+D(2γ1(1γ3ymγ4y2m)+(Dγ5)ym). (A.13)

    By applying ym>Ω>0, D<γ1γ3 and condition (A.6),

    2γ1(1γ3ymγ4y2m)+(Dγ5)ym<0

    which, coupled with (A.13), implies that S1(ym)<0.

    Proof. First, we set γ1=konk1, γ2=konk2, γ3=kon+g1kon>1, γ4=g2kon, γ5=g1, γ6=g2 and D=σ1Dm used in the lemmas.

    Solving (A.5) in Lemma 6, we obtain

    Ω=((kon+g1)24g22+kong2(112kon(g2k2+g22k22+(g1+σ1Dm)2k1k2))kon+g12g2)

    By the condition (3.10) of Theorem 4

    112kon(g2k2+g22k22+(g1+σ1Dm)2k1k2)>0

    we have Ω>0 and γ2=konk2>γ6=g2. Also the other condition (3.11) of Theorem 4

    k1g2k2+k21g22k22+(g1+σ1Dm)2k1k2<(g1σ1Dm)((kon+g1)24g22+kong2(112kon(g2k2+g22k22+(g1+σ1Dm)2k1k2))kon+g12g2)

    implies the condition (A.6). By Lemma 6, we have

    2konk2a0(1kon+g1kona0g2kona20)(g1+2g2a0)σ1Dm>0 (A.14)

    holds for any a0 satisfying

    kon(k1+k2a20)(1kon+g1kona0g2kona20)(g1+g2a0)a0=0. (A.15)

    Eq. (A.15) implies that

    kon(k1+k2a20)(1a0)(1+k1+k2a20)(g1+g2a0)a0=0konk1+k2a201+k1+k2a20(1a0)(g1+g2a0)a0=0 (A.16)

    Now we get that a0 is a homogeneous steady state solution for a in system (2.1) with the feedback forms (2.3) and (2.4) if and only if a0 satisfies (A.15).

    Also, (A.16) and (A.15) imply that

    11+k1+k2a20(1a0)=1kon+g1kona0g2kona20

    and then combining (A.14), we have

    kon2k2a01+k1+k2a20(1a0)(g1+2g2a0)σ1Dm>0

    which is equivalent to Case (2a).



    Conflict of interest



    The authors confirm that they have no competing interests. They are solely responsible for the writing and content of this paper.

    [1] Coccia M, Bellitto M (2018) Human progress and its socioeconomic effects in society. JEST 5: 160-178.
    [2] Coccia M (2019) Comparative Institutional Changes. Global Encyclopedia of Public Administration, Public Policy, and Governance . Springer Nature. https://doi.org/10.1007/978-3-319-31816-5_1277-1
    [3] Coccia M (2018) An introduction to the theories of national and regional economic development. TER 5: 350-358. https://doi.org/10.2139/ssrn.3857165
    [4] Coccia M (2021) Effects of human progress driven by technological change on physical and mental health. Studi Sociol 2: 113-132.
    [5] Coccia M (2015) The Nexus between technological performances of countries and incidence of cancers in society. Technol Soc 42: 61-70. https://doi.org/10.1016/j.techsoc.2015.02.003
    [6] Irigaray P, Newby JA, Clapp R, et al. (2007) Lifestyle-related factors and environmental agents causing cancer: an overview. Biomed Pharmacother 61: 640-658. https://doi.org/10.1016/j.biopha.2007.10.006
    [7] Coccia M (2013) The effect of country wealth on incidence of breast cancer. Breast Cancer Res Treat 141: 225-229. https://doi.org/10.1007/s10549-013-2683-y
    [8] Coccia M (2020) Factors determining the diffusion of COVID-19 and suggested strategy to prevent future accelerated viral infectivity similar to COVID. Sci Total Environ 729: 138474. https://doi.org/10.1016/j.scitotenv.2020.138474
    [9] Núñez-Delgado A, Bontempi E, Coccia M, et al. (2021) SARS-CoV-2 and other pathogenic microorganisms in the environment. Environ Res 201: 111606. https://doi.org/10.1016/j.envres.2021.111606
    [10] Chang LW, Magos L, Suzuki T (1996) Toxicology of Metals. Boca Raton, FL, USA: CRC Press.
    [11] Prabhakaran KP, Cottenie A (1971) Parent material - soil relationship in trace elements - a quantitative estimation. Geoderma 5: 81-97. https://doi.org/10.1016/0016-7061(71)90014-0
    [12] Khan S, Cao Q, Zheng YM, et al. (2008) Health risks of heavy metals in contaminated soils and food crops irrigated with wastewater in Beijing, China. Environ Poll 152: 686-692. https://doi.org/10.1016/j.envpol.2007.06.056
    [13] Wuana RA, Okieimen FE (2011) Heavy metals in contaminated soils: a review of sources, chemistry, risks and best available strategies for remediation. International Scholarly Research Network ISRN Ecology . https://doi.org/10.5402/2011/402647
    [14] Li G, Sun GX, Ren Y, et al. (2018) Urban soil and human health: a review. Eur J Soil Sci 69: 196-215. https://doi.org/10.1111/ejss.12518
    [15] Nieder R, Benbi DK, Reichl FX (2018) Soil Components and Human Health. Dordrecht: Springer. https://doi.org/10.1007/978-94-024-1222-2
    [16] Rinklebe J, Antoniadis V, Shaheen SM, et al. (2019) Health risk assessmant of potentially oxic elements in soils along the Elbe River, Germany. Environ Int 126: 76-88. https://doi.org/10.1016/j.envint.2019.02.011
    [17] Pohl WL (2020) Economic Geology. Principles and Practice. Stuttgart: Schweizerbart Science Publishers.
    [18] GWRTACRemediation of metals-contaminated soils and groundwater, Tech Rep TE-97-01, GWRTAC, Pittsburgh, Pa, USA, 1997, GWRTAC-E Series (1997).
    [19] Aslanidis PSC, Golia EE (2022) Urban Sustainability at Risk Due to Soil Pollution by Heavy Metals—Case Study: Volos, Greece. Land 11: 1016. https://doi.org/10.3390/land11071016
    [20] Golia EE, Papadimou SG, Cavalaris C, et al. (2021) Level of Contamination Assessment of Potentially Toxic Elements in the Urban Soils of Volos City (Central Greece). Sustainability 13: 2029. https://doi.org/10.3390/su13042029
    [21] Serrani D, Ajmone-Marsan F, Corti G, et al. (2022) Heavy metal load and effects on biochemical properties in urban soils of a medium-sized city, Ancona, Italy. Environ Geochem Health 44: 3425-3449. https://doi.org/10.1007/s10653-021-01105-8
    [22] Ndoli A, Naramabuye F, Diogo RV, et al. (2013) Greenhouse experiments on soybean (Glycine max) growth on Technosol substrates from tantalum mining in Rwanda. Int J Agric Sci 2: 144-152.
    [23] Nieder R, Weber TKD, Paulmann I, et al. (2014) The geochemical signature of rare-metal pegmatites in the Central Africa Region: Soils, plants, water and stream sediments in the Gatumba tin-tantalum mining district, Rwanda. J Geochem Explor 144: 539-551. https://doi.org/10.1016/j.gexplo.2014.01.025
    [24] Reetsch A, Naramabuye F, Pohl W, et al. (2008) Properties and quality of soils in the open-cast mining district of Gatumba, Rwanda. Etudes Rwandaises 16: 51-79.
    [25] Rossiter, DG (2007) Classification of Urban and Industrial Soils in the World Reference Base for Soil Resources. J Soils Sediments 7: 96-100. https://doi.org/10.1065/jss2007.02.208
    [26] Guo G, Li K, Lei M (2022) Accumulation, environmental risk characteristics and associated driving mechanisms of potential toxicity elements in roadside soils across China. Sci Total Environ 835: 155342. https://doi.org/10.1016/j.scitotenv.2022.155342
    [27] Antoniadis V, Levizou E, Shaheen SM, et al. (2017) Trace elements in the soil-plant interface: phytoavailability, translocation, and phytoremediation – a review. Earth Sci Rev 171: 621-645. https://doi.org/10.1016/j.earscirev.2017.06.005
    [28] US EPA (Environmental Protection Agency)Reducing mercury pollution from gold mining (2011). Available from: http://www.epa.gov/oia/toxics/asgm.html.
    [29] Pelfrêne A, Waterlot C, Mazzuca M, et al. (2012) Bioaccessibility of trace elements as affected by soil parameters in smelter-contaminated agricultural soils: A statistical modeling approach. Environ Pollut 160: 130-138. https://doi.org/10.1016/j.envpol.2011.09.008
    [30] Bolan N, Kunhikrishnan A, Thangarajan R, et al. (2014) Remediation of heavy metal(loid) contaminated soils – to mobilize or not to mobilize?. J Hazar Mater 266: 141-166. https://doi.org/10.1016/j.jhazmat.2013.12.018
    [31] Tong S, von Schirnding YE, Prapamontol T (2000) Environmental lead exposure: a public health problem of global dimensions. Bulletin of the World Health Organization 78: 1068-1077.
    [32] Järup L, Hellström L, Alfvén T, et al. (2000) Low level exposure to cadmium and early kidney damage: the OSCAR study. Occup Environ Med 57: 668-672. https://doi.org/10.1136/oem.57.10.668
    [33] Thomas LDK, Hodgson S, Nieuwenhuijsen M, et al. (2009) Early kidney damage in a population exposed to cadmium and other heavy metals. Environ Health Perspect 117: 181-184. https://doi.org/10.1289/ehp.11641
    [34] Putila JJ, Guo NL (2011) Association of arsenic exposure with lung cancer incidence rates in the United States. PLOS ONE 6: e25886. https://doi.org/10.1371/journal.pone.0025886
    [35] WHO (World Health Organization)News Release, Geneva (2016). Available from: http://www.who.int/news-room/detail/15-03-2016-an-estimated-12-6-million-deaths-each-year-are-attributable-to-unhealthy-environments.
    [36] Liu P, Zhang Y, Feng N, et al. (2020) Potentially toxic element (PTE) levels in maize, soil, and irrigation water and health risks through maize consumption in northern Ningxia, China. BMC Public Health 20: 1729. https://doi.org/10.1186/s12889-020-09845-5
    [37] Mazumder D (2008) Chronic arsenic toxicity and human health. Indian J Med Res 128: 436-47.
    [38] Bires J, Dianovsky J, Bartko P, et al. (1995) Effects on enzymes and the genetic apparatus of sheep after administration of samples from industrial emissions. Biol Met 8: 53-58. https://doi.org/10.1007/BF00156158
    [39] Bolan S, Kunhikrishnan A, Seshadri B, et al. (2017) Sources, distribution, bioavailability, toxicity, and risk assessment of heavy metal(loid)s in complementary medicines. Environ Int 108: 103-118. https://doi.org/10.1016/j.envint.2017.08.005
    [40] Rajkumar V, Gupta V (2022) Heavy Metal Toxicity. Treasure Island (FL): StatPearls Publishing 2022. Available from: https://www.ncbi.nlm.nih.gov/books/NBK560920/.
    [41] (2000) ATSDR (Agency for Toxic Substances and Disease Registry)Toxicological Profile for Arsenic. Georgia: Center for Disease Control, Atlanta.
    [42] Tchounwou PB, Yedjou CG, Patlolla AK, et al. (2012) Heavy metal toxicity and the environment. Exp Suppl 101: 133-164. https://doi.org/10.1007/978-3-7643-8340-4_6
    [43] (2001) WHO (World Health Organization)Arsenic and Arsenic Compounds. Environmental Health Criteria 224 . Geneva: . Available from: http://www.inchem.org/documents/ehc/ehc/ehc224.htm
    [44] Ravenscroft P, Brammer H, Richards K (2009) Arsenic Pollution: A Global Synthesis. West Sussex, UK: John Wiley and Sons. https://doi.org/10.1002/9781444308785
    [45] Shakoor MB, Niazi NK, Bibi I, et al. (2019) Exploring the arsenic removal potential of various biosorbents from water. Environ Int 123: 567-579. https://doi.org/10.1016/j.envint.2018.12.049
    [46] Shresther RR, Upadhyay NP, Pradhan R, et al. (2003) Groundwater arsenic contamination, its health impact and mitigation program in Nepal. J Environ Sci Health A38: 185-200. https://doi.org/10.1081/ESE-120016888
    [47] Berg M, Trans HC, Nguyeu TC, et al. (2001) Arsenic contamination of groundwater and drinking water in Vietnam: a human health threat. Environ Sci Technol 35: 2621-2626. https://doi.org/10.1021/es010027y
    [48] Morton WE, Dunnette DA (1994) Health effects of environmental arsenic. Arsenic in the Environment Part II: Human Health and Ecosystem Effects . New York: John Wiley & Sons 17-34.
    [49] Zhao KL, Liu XM, Xu JM, et al. (2010) Heavy metal contaminations in a soil–rice system: Identification of spatial dependence in relation to soil properties of paddy fields. J Hazard Mater 181: 778-787. https://doi.org/10.1016/j.jhazmat.2010.05.081
    [50] Williams PN, Islam MR, Adomako EE, et al. (2006) Increase in rice grain arsenic for regions of Bangladesh irrigating paddies with elevated arsenic in ground waters. Environ Sci Technol 40: 4903-4908. https://doi.org/10.1021/es060222i
    [51] Tchounwou PB, Centeno JA, Patlolla AK (2004) Arsenic toxicity, mutagenesis and carcinogenesis - a health risk assessment and management approach. Mol Cell Biochem 255: 47-55.
    [52] Concha G, Vogler G, Nermell B, et al. (1998) Low-level arsenic excretion inbreast milk of native Andean women exposed to high levels of arsenic in the drinking water. Int Arch Occup Environ Health 71: 42-46.
    [53] Dakeishi M, Murata K, Grandjean P (2006) Long-term consequences of arsenic poisoning during infancy due to contaminated milk powder. Environ Health 5: 31.
    [54] Järup L, Åkesson A (2009) Current status of cadmium as an environmental healthproblem. Toxicol Appl Pharm 238: 201-208.
    [55] Inaba T, Kobayashi E, Suwazono Y, et al. (2005) Estimation of cumulative cadmium intake causing Itai-itai disease. Toxicol Lett 159: 192-201.
    [56] Skinner HCW (2007) The earth, source of health and hazards: An introduction to Medical Geology. Annu Rev Earth Planet Sci 35: 177-213.
    [57] Nakagawa H, Tabata M, Moikawa Y, et al. (1990) High mortality and shortened life-span in patients with itai-itai disease and subjects with suspected disease. Arch Environ Health 45: 283-287.
    [58] Horiguchi H, Oguma E, Sasaki S, et al. (2004) Comprehensive study of the effects of age, iron deficiency, diabetes mellitus and cadmium burden on dietary cadmium absorption in cadmium-exposed female Japanese farmers. Toxicol Appl Pharmacol 196: 114-123.
    [59] Diamond GL, Thayer WC, Choudhury H (2003) Pharmacokinetic/pharmacodynamics (PK/PD) modeling of risks of kidney toxicity from exposure to cadmium: estimates of dietary risks in the U.S. population. J Toxicol Environ Health 66: 2141-2164.
    [60] Dayan AD, Paine AJ (2001) Mechanisms of chromium toxicity, carcinogenicity and allergenicity: Review of the literature from 1985 to 2000. Hum Exp Toxicol 20: 439-451.
    [61] Coetzee JJ, Bansal N, Evans M N, et al. (2020) Chromium in environment, its toxic effect from chromite-mining and ferrochrome industries, and its possible bioremediation. Expos Health 12: 51-62. https://doi.org/10.1007/s12403-018-0284-z
    [62] Holmes AL, Wise SS, Wise JP (2008) Carcinogenicity of hexavalent chromium. Indian J Med Res 128: 353-357.
    [63] IARC (International Agency for Research on Cancer).Chromium, Nickel and Welding. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans (1990) 49: 249-256.
    [64] Zhang JD, Li XL (1987) Chromium pollution of soil and water in Jinzhou. Zhonghua Yu Fang Yi Xue Za Zhi 21: 262-264.
    [65] Barregard L, Sallsten G, Conradi N (1999) Tissue levels of mercury determined in a deceased worker after occupational exposure. Int Arch Occup Environ Health 72: 169-173. https://doi.org/10.1007/s004200050356
    [66] Ralston NVC, Raymond LJ (2018) Mercury's neurotoxicity is characterized by its disruption of selenium biochemistry. Biochim Biophys Acta Gen Subj 1862: 2405-2416. https://doi.org/10.1016/j.bbagen.2018.05.009
    [67] Sall ML, Diaw AKD, Gningue-Sall D, et al. (2020) Toxic heavy metals: impact on the environment and human health, and treatment with conducting organic polymers, a review. Environ Sci Pollut Res 27: 29927-29942. https://doi.org/10.1007/s11356-020-09354-3
    [68] Ekino S, Susa M, Ninomiya T, et al. (2007) Minamata disease revisited: An update on the acute and chronic manifestations of methyl mercury poisoning. J Neurol Sci 262: 131-144. https://doi.org/10.1016/j.jns.2007.06.036
    [69] Eto K (2000) Minamata disease. Neuropathol 20: S14-S19. https://doi.org/10.1046/j.1440-1789.2000.00295.x
    [70] Babut M, Sekyi R (2003) Improving the environmental management of small-scale gold mining in Ghana: a case study of Dumasi. J Cleaner Prod 11: 215-221. https://doi.org/10.1016/S0959-6526(02)00042-2
    [71] Taylor H, Appleton JD, Lister R, et al. (2004) Environmental assessment of mercury contamination from the Rwamagasa artisanal gold mining centre, Geita District, Tanzania. Sci Total Environ 343: 111-133. https://doi.org/10.1016/j.scitotenv.2004.09.042
    [72] WHO (World Health Organization)Lead poisoning and health (2018). Available from: https://www.who.int/news-room/fact-sheets/detail/lead-poisoning-and-health
    [73] O'Connor D, Hou D, Ye J, et al. (2018) Lead-based paint remains a major public health concern: a critical review of global production, trade, use, exposure, health risk, and implications. Environ Int 121: 85-101. https://doi.org/10.1016/j.envint.2018.08.052
    [74] Järup L (2003) Hazards of heavy metal contamination. Brit Med Bull 68: 67-182. https://doi.org/10.1093/bmb/ldg032
    [75] Shifaw E (2018) Review of Heavy Metals Pollution in China in Agricultural and Urban Soils. J Health Pollut 8: 180607. https://doi.org/10.5696/2156-9614-8.18.180607
    [76] Wang W, Xu X, Zhou Z, et al. (2022) A joint method to assess pollution status and source-specific human health risks of potential toxic elements in soils. Environ Monit Assess 194: 685. https://doi.org/10.1007/s10661-022-10353-9
    [77] Lei M, Li K, Guo G, et al. (2022) Source-specific health risks apportionment of soil potential toxicity elements combining multiple receptor models with Monte Carlo simulation. Sci Total Environ 817: 152899. https://doi.org/10.1016/j.scitotenv.2021.152899
    [78] Xue S, Korna R, Fan J, et al. (2023) Spatial distribution, environmental risks, and sources of potentially toxic elements in soils from a typical abandoned antimony smelting site. J Environ Sci 127: 780-790. https://doi.org/10.1016/j.jes.2022.07.009
    [79] Mohammadpour A, Emadi Z, Keshtkar M, et al. (2022) Assessment of potentially toxic elements (PTEs) in fruits from Iranian market (Shiraz): A health risk assessment study. J Food Compost Anal 114: 104826. https://doi.org/10.1016/j.jfca.2022.104826
    [80] Vejvodová K, Ash C, Dajčl J, et al. (2022) Assessment of potential exposure to As, Cd, Pb and Zn in vegetable garden soils and vegetables in a mining region. Sci Rep 12: 13495. https://doi.org/10.1038/s41598-022-17461-z
    [81] Natasha N, Shahid M, Murtaza B, et al. (2022) Accumulation pattern and risk assessment of potentially toxic elements in selected wastewater-irrigated soils and plants in Vehari, Pakistan. Environ Res 214: 114033. https://doi.org/10.1016/j.envres.2022.114033
    [82] Ghane ET, Khanverdiluo S, Mehri F (2022) The concentration and health risk of potentially toxic elements (PTEs) in the breast milk of mothers: a systematic review and meta-analysis. J Trace Elem Med Biol 73: 126998. https://doi.org/10.1016/j.jtemb.2022.126998
    [83] DeForest DK, Brix KV, Adams WJ (2007) Assessing metal bioaccumulation in aquatic environments: the inverse relationship between bioaccumulation factors, trophic transfer factors and exposure concentration. Aquat Toxicol 84: 236-246. https://doi.org/10.1016/j.aquatox.2007.02.022
    [84] Wang S, Shi X (2001) Molecular mechanisms of metal toxicity and carcinogenesis. Mol Cell Biochem 222: 3-9. https://doi.org/10.1023/A:1017918013293
    [85] Ercal N, Gurer-Orhan H, Aykin-Burns N (2001) Toxic metals and oxidative stress Part I: mechanisms involved in metal-induced oxidative damage. Curr Top Med Chem 1: 529-539. https://doi.org/10.2174/1568026013394831
    [86] Wilk A, Kalisinska E, Kosik-Bogacka DI, et al. (2017) Cadmium, lead and mercury concentrations in pathologically altered human kidneys. Environ Geochem Health 39: 889-899. https://doi.org/10.1007/s10653-016-9860-y
    [87] Ebrahimpour M, Mosavisefat M, Mohabatti R (2010) Acute toxicity bioassay of mercuric chloride: an alien fish from a river. Toxicol Environ Chem 92: 169-173. https://doi.org/10.1080/02772240902794977
    [88] Brown SE, Welton WC (2008) Heavy metal pollution. New York: Nova Science publishers, Inc..
    [89] Iyengar V, Nair P (2000) Global outlook on nutrition and the environment meeting the challenges of the next millennium. Sci Tot Environ 249: 331-346. https://doi.org/10.1016/S0048-9697(99)00529-X
    [90] Turkdogan MK, Kulicel F, Kara K, et al. (2003) Heavy metals in soils, vegetable and fruit in the endermic upper gastro intestinal cancer region of Turkey. Environ Toxicol Pharmacol 13: 175-179. https://doi.org/10.1016/S1382-6689(02)00156-4
    [91] Hindmarsh JT, Abernethy CO, Peters GR, et al. (2002) Environmental Aspects of Arsenic Toxicity. Heavy Metals in the Environment . New York: Marcel Dekker 217-229. https://doi.org/10.1201/9780203909300.ch7
    [92] Apostoli P, Catalani S (2011) Metal ions affecting reproduction and development. Met Ions Life Sci 8: 263-303. https://doi.org/10.1039/9781849732116-00263
    [93] Rattan S, Zhou C, Chiang C, et al. (2017) Exposure to endocrine disruptors during adulthood: Consequences for female fertility. J Endocrinol 233: R109-R129. https://doi.org/10.1530/JOE-17-0023
    [94] Bradl HB (2005) Heavy metals in the environment: origin, interaction and remediation. London: Elsevier.
    [95] Davydova S (2005) Heavy metals as toxicants in big cities. Microchem J 79: 133-136. https://doi.org/10.1016/j.microc.2004.06.010
    [96] Fergusson JE (1990) The heavy elements: Chemistry, environmental impact and health effects. Oxford: Pergamon Press.
    [97] Pierzynsky GM, Sims JT, Vance GF (2005) Soils and environmental quality. New York: CRC Press. https://doi.org/10.1201/b12786
    [98] Wang LK, Chen JP, Hung Y, et al. (2009) Heavy metals in the environment. Boca Raton: CRC Press. https://doi.org/10.1201/9781420073195
    [99] Sharma S, Kaur I, Kaur Nagpal A (2021) Contamination of rice crop with potentially toxic elements and associated human health risks—a review. Environ Sci Pollut Res 28: 12282-12299. https://doi.org/10.1007/s11356-020-11696-x
    [100] Shankar S, Shanker U, Shikha (2014) Arsenic contamination of groundwater: a review of sources, prevalence, health risks, and strategies for mitigation. Sci World J 2014: 304524. https://doi.org/10.1155/2014/304524
    [101] Reichl FX, Ritter L (2011) Illustrated Handbook of Toxicology. New York: Thieme, Stuttgart. https://doi.org/10.1055/b-005-148918
    [102] (2001) NRC (National Research Council)Arsenic in drinking water-2001 update. Washington DC: National Academy Press.
    [103] Lauwerys RR, Hoet P (2001) Industrial Chemical Exposure. Guidelines for Biological Monitoring . Boca Raton: Lewis Publishers. https://doi.org/10.1201/9781482293838
    [104] Hughes MF (2002) Arsenic toxicity and potential mechanisms of action. Toxicol Lett 11: 1-16. https://doi.org/10.1016/S0378-4274(02)00084-X
    [105] Kumagai Y, Sumi D (2007) Arsenic: signal transduction, transcription factor, and biotransformation involved in cellular response and toxicity. Annu Rev Pharmacol Toxicol 47: 243-262. https://doi.org/10.1146/annurev.pharmtox.47.120505.105144
    [106] Huang HW, Lee CH, Yu HS (2019) Arsenic-induced carcinogenesis and immune dysregulation. Int J Environ Res Public Health 16: 2746. https://doi.org/10.3390/ijerph16152746
    [107] Kapaj S, Peterson H, Liber K, et al. (2006) Human health effects from chronic arsenic poisoning – a review. J Environ Sci Health Part A 41: 2399-2428. https://doi.org/10.1080/10934520600873571
    [108] Garza-Lombó C, Pappa A, Panayiotidis MI, et al. (2019) Arsenic-induced neurotoxicity: a mechanistic appraisal. J Biol Inorg Chem 24: 1305-1316. https://doi.org/10.1007/s00775-019-01740-8
    [109] Mitra S, Chakraborty AJ, Tareq AM, et al. (2022) Impact of heavy metals on the environment and human health: Novel therapeutic insights to counter the toxicity. Science 34: 101865. https://doi.org/10.1016/j.jksus.2022.101865
    [110] Kim YJ, Kim JM (2015) Arsenic toxicity in male reproduction and development. Dev Reprod 19: 167-180. https://doi.org/10.12717/DR.2015.19.4.167
    [111] Salnikow K, Zhitkovich A (2008) Genetic and epigenetic mechanisms in metal carcinogenesis and cocarcinogenesis: Nickel, arsenic, and chromium. Chem Res Toxicol 21: 28-44. https://doi.org/10.1021/tx700198a
    [112] Milton A, Hussain S, Akter S, et al. (2017) A review of the effects of chronic arsenic exposure on adverse pregnancy outcomes. Int J Environ Res Public Health 14: 556. https://doi.org/10.3390/ijerph14060556
    [113] Roy J, Chatterjee D, Das N, et al. (2018) Substantial evidences indicate that inorganic arsenic is a genotoxic carcinogen: A review. Toxicol Res 34: 311-324. https://doi.org/10.5487/TR.2018.34.4.311
    [114] Pierce BL, Kibriya MG, Tong L, et al. (2012) Genome-wide association study identifies chromosome 10q24.32 variants associated with arsenic metabolism and toxicity phenotypes in Bangladesh. PLoS Genet 8: e1002522. https://doi.org/10.1371/journal.pgen.1002522
    [115] Yin Y, Meng F, Sui C, et al. (2019) Arsenic enhances cell death and DNA damage induced by ultraviolet B exposure in mouse epidermal cells through the production of reactive oxygen species. Clin Exp Dermatol 44: 512-519. https://doi.org/10.1111/ced.13834
    [116] Schwartz GG, Il'yasova D, Ivanova A (2003) Urinary cadmium, impaired fasting glucose, and diabetes in the NHANES III. Diabetes Care 26: 468-470. https://doi.org/10.2337/diacare.26.2.468
    [117] Messner B, Knoflach M, Seubert A, et al. (2009) Cadmium is a novel and independent risk factor for early atherosclerosis mechanisms and in vivo relevance. Arterioscler Thromb Vasc Biol 29: 1392-1398. https://doi.org/10.1161/ATVBAHA.109.190082
    [118] Navas-Acien A, Selvin E, Sharrett AR, et al. (2004) Lead, cadmium, smoking, and increased risk of peripheral arterial disease. Circulation 109: 3196-3201. https://doi.org/10.1161/01.CIR.0000130848.18636.B2
    [119] Hellström L, Elinder CG, Dahlberg B, et al. (2001) Cadmium exposure and end-stage renal disease. Am J Kidney Dis 38: 1001-1008. https://doi.org/10.1053/ajkd.2001.28589
    [120] Everett CJ, Frithsen IL (2008) Association of urinary cadmium and myocardial infarction. Environ Res 106: 284-286. https://doi.org/10.1016/j.envres.2007.10.009
    [121] Tellez-Plaza M, Navas-Acien A, Crainiceanu CM, et al. (2008) Cadmium exposure and hypertension in the 1999–2004 National Health and Nutrition Examination Survey (NHANES). Environ Health Perspect 116: 51-56. https://doi.org/10.1289/ehp.10764
    [122] Peters JL, Perlstein TS, Perry MJ, et al. (2010) Cadmium exposure in association with history of stroke and heart failure. Environ Res 110: 199-206. https://doi.org/10.1016/j.envres.2009.12.004
    [123] Tellez-Plaza M, Guallar E, Howard BV, et al. (2013) Cadmium exposure and incident cardiovascular disease. Epidemiology 24: 421-429. https://doi.org/10.1097/EDE.0b013e31828b0631
    [124] Branca JJV, Morucci G, Pacini A (2018) Cadmium-induced neurotoxicity: Still much to do. Neural Regen Res 13: 1879-1882. https://doi.org/10.4103/1673-5374.239434
    [125] Marchetti C (2014) Interaction of metal ions with neurotransmitter receptors and potential role in neurodiseases. Biometals 27: 1097-1113. https://doi.org/10.1007/s10534-014-9791-y
    [126] Wang BO, Du Y (2013) Cadmium and its neurotoxic effects. Oxid Med Cell Longevity 2013: 1-12. https://doi.org/10.1155/2013/898034
    [127] Nordberg GF, Nordberg M (2001) Biological monitoring of cadmium. Biological monitoring of toxic metals . New York: Plenum Press 151-168. https://doi.org/10.1007/978-1-4613-0961-1_6
    [128] Roels HA, Hoet P, Lison D (1999) Usefulness of biomarkers of exposure to inorganic mercury, lead, or cadmium in controlling occupational and environmental risks of nephrotoxicity. Ren Fail 21: 251-262. https://doi.org/10.3109/08860229909085087
    [129] Alfven T, Jarup L, Elinder CG (2002) Cadmium and lead in blood in relation to low bone mineral density and tubular proteinuria. Environ Health Perspect 110: 699-702. https://doi.org/10.1289/ehp.02110699
    [130] Olsson IM, Bensryd I, Lundh T, et al. (2002) Cadmium in blood and urine – impact of sex, age, dietary intake, iron status, and former smoking – association of renal effects. Environ Health Perspect 110: 1185-1190. https://doi.org/10.1289/ehp.021101185
    [131] Zalups RK (2000) Evidence for basolateral uptake of cadmium in the kidneys of rats. Toxicol Appl Pharmacol 164: 15-23. https://doi.org/10.1006/taap.1999.8854
    [132] Hyder O, Chung M, Cosgrove D, et al. (2013) Cadmium exposure and liver disease among US adults. J Gastrointest Surg 17: 1265-1273. https://doi.org/10.1007/s11605-013-2210-9
    [133] Jin T, Nordberg G, Ye T, et al. (2004) Osteoporosis and renal dysfunction in a general population exposed to cadmium in China. Environ Res 96: 353-359. https://doi.org/10.1016/j.envres.2004.02.012
    [134] Fernandez MA, Sanz P, Palomar M, et al. (1996) Fatal chemical pneumonitis due to cadmium fumes. Occup Med 46: 372-374. https://doi.org/10.1093/occmed/46.5.372
    [135] Davidson AG, Fayers PM, Newman Taylor AJ, et al. (1988) Cadmium fume inhalation and emphysema. Lancet 1: 663-667. https://doi.org/10.1016/S0140-6736(88)91474-2
    [136] Mascagni P, Consonni D, Bregante G, et al. (2003) Olfactory function in workers exposed to moderate airborne cadmium levels. Neurotoxicol 24: 717-724. https://doi.org/10.1016/S0161-813X(03)00024-X
    [137] Nishijo M, Nakagawa H, Honda R, et al. (2002) Effects of maternal exposure to cadmium on pregnancy outcome and breast milk. Occup Environ Med 59: 394-397. https://doi.org/10.1136/oem.59.6.394
    [138] Othumpamgat S, Kashon M, Joseph P (2005) Eukaryotic translation initiation factor 4E is a cellular target for toxicity and death due to exposure to cadmium chloride. J Biol Chem 280: 25162-25169. https://doi.org/10.1074/jbc.M414303200
    [139] (1990) WHO (World Health Organisation)Chromium. Environmental Health Criteria 61. Geneva: International Programme on Chemical Safety.
    [140] Aaseth J, Alexander J, Norseth T (1982) Uptake of 51Cr chromate by human erythrocytes - a role of glutathione. Acta Pharmacol Toxicol 50: 310-315. https://doi.org/10.1111/j.1600-0773.1982.tb00979.x
    [141] Mertz W (1969) Chromium occurrence and function in biological systems. Physiol Rev 49: 163-239. https://doi.org/10.1152/physrev.1969.49.2.163
    [142] Sharma BK, Singhal PC, Chugh KS (1978) Intravascular haemolysis and acute renal failure following potassium dichromate poisoning. Postgrad Med J 54: 414-415. https://doi.org/10.1136/pgmj.54.632.414
    [143] Glaser U, Hochrainer D, Kloppel H, et al. (1985) Low level chromium (VI) inhalation effects on alveolar macrophages and immune functions in Wistar rats. Arch Toxicol 57: 250-256. https://doi.org/10.1007/BF00324787
    [144] Thompson CM, Fedorov Y, Brown DD, et al. (2012) Assessment of Cr(VI)-induced cytotoxicity and genotoxicity using high content analysis. PLoS ONE 7: e42720. https://doi.org/10.1371/journal.pone.0042720
    [145] Fang Z, Zhao M, Zhen H, et al. (2014) Genotoxicity of tri- and hexavalent chromium compounds in vivo and their modes of action on DNA damage in vitro. PLoS ONE 9: e103194. https://doi.org/10.1371/journal.pone.0103194
    [146] Sánchez-Sicilia L, Seto DS, Nakamoto S, et al. (1963) Acute mercury intoxication treated by hemodialysis. Ann Intern Med 59: 692-706. https://doi.org/10.7326/0003-4819-59-5-692
    [147] Hong YS, Kim YM, Lee KE (2012) Methylmercury Exposure and Health Effects. J Prev Med Public Health 45: 353-363. https://doi.org/10.3961/jpmph.2012.45.6.353
    [148] Cernichiari E, Brewer R, Myers GJ, et al. (1995) Monitoring methylmercury during pregnancy: maternal hari predicts fetal brain exposure. Neurotoxicol 16: 705-710.
    [149] Barregard L, Sallsten G, Schutz A, et al. (1992) Kinetics of mercury in blood and urine after brief occupational exposure. Arch Environ Health 7: 176-184. https://doi.org/10.1080/00039896.1992.9938347
    [150] Rahola T, Hattula T, Korolainen A, et al. (1973) Elimination of free and protein-bound ionic mercury (203Hg2+) in man. Ann Clin Res 5: 214-219.
    [151] (2000) NRC (National Research Council)Toxicological effects of methylmercury. Washington DC: National Academy Press.
    [152] Oskarsson A, Schultz A, Skerfving S, et al. (1996) Total and inorganic mercury in breast milk and blood in relation to fish consumption and amalgam fillings in lactating women. Arch Environ Health 51: 234-241. https://doi.org/10.1080/00039896.1996.9936021
    [153] Horowitz Y, Greenberg D, Ling G, et al. (2002) Acrodynia: a case report of two siblings. Arch Dis Child 86: 453. https://doi.org/10.1136/adc.86.6.453
    [154] Boyd AS, Seger D, Vannucci S, et al. (2000) Mercury exposure and cutaneous disease. J Am Acad Dermatol 43: 81-90. https://doi.org/10.1067/mjd.2000.106360
    [155] Smith RG, Vorwald AJ, Pantil LS, et al. (1970) Effects of exposure to mercury in the manufacture of chlorine. Am Ind Hyg Assoc J 31: 687-700. https://doi.org/10.1080/0002889708506315
    [156] Smith PJ, Langolf GD, Goldberg J (1983) Effects of occupational exposure to elemental mercury on short term memory. Br J Ind Med 40: 413-419. https://doi.org/10.1136/oem.40.4.413
    [157] Tan SW, Meiller JC, Mahaffey KR (2009) The endocrine effects of mercury in humans and wildlife. Crit Rev Toxicol 39: 228-269. https://doi.org/10.1080/10408440802233259
    [158] Vupputuri S, Longnecker MP, Daniels JL, et al. (2005) Blood mercury level and blood pressure accrocc US women: results from the National Health and Nutrition Examination Survey 1999-2000. Environ Res 97: 195-200. https://doi.org/10.1016/j.envres.2004.05.001
    [159] Yoshizawa K, Rimm EB, Morris JS, et al. (2002) Mercury and the risk of coronary heart disease in men. N Engl J Med 347: 1755-1760. https://doi.org/10.1056/NEJMoa021437
    [160] Salonen JT, Malin R, Tuomainen TP, et al. (1999) Polymorphism in high density lipoprotein paraoxonase gene and risk of acute myocardial infarction in men: Prospective nested case-control study. Br Med J 319: 487-488. https://doi.org/10.1136/bmj.319.7208.487
    [161] Kulka M (2016) A review of paraoxonase 1 properties and diagnostic applications. Pol J Vet Sci 19: 225-232. https://doi.org/10.1515/pjvs-2016-0028
    [162] Zefferino R, Piccoli C, Ricciard N, et al. (2017) Possible mechanisms of mercury toxicity and cancer promotion: involvement of gap junction intercellular communications and inflammatory cytokines. Oxid Med Cell Longev 2017: 1-6. https://doi.org/10.1155/2017/7028583
    [163] Smith DR, Osterlod JD, Flegal AR (1996) Use of endogenous, stable lead isotopes to determine release of lead from the skeleton. Environ Health Perspect 104: 60-66. https://doi.org/10.1289/ehp.9610460
    [164] Ettinger AS, Téllez-Rojo MM, Amarasiriwardena C, et al. (2004) Effect of Breast Milk Lead on Infant Blood Lead Levels at 1 Month of Age. Environ Health Perspect 112: 245-275. https://doi.org/10.1289/ehp.6616
    [165] Leggett RW (1993) Age-specific kinetic model of lead metal in humans. Environ Health Perspect 101: 598-616. https://doi.org/10.1289/ehp.93101598
    [166] (2007) ATSDR (Agency for Toxic Substance and Disease Registry)Toxicological profile for lead. Georgia: Center for Disease Control, Atlanta.
    [167] Muntner P, Vupputyuri S, Coresh J, et al. (2003) Blood lead and chronic kidney disease in the general United States population: results from NHANES III. Kidney Int 63: 1044-1050. https://doi.org/10.1046/j.1523-1755.2003.00812.x
    [168] Hegazy AMS, Fouad UA (2014) Evaluation of lead hepatotoxicity; histological, histochemical and ultrastructural study. Forensic Med Anat Res 02: 70-79. https://doi.org/10.4236/fmar.2014.23013
    [169] Hsiao CL, Wu KH, Wan KS (2011) Effects of environmental lead exposure on T-helper cell-specific cytokines in children. J Immunotoxicol 8: 284-287. https://doi.org/10.3109/1547691X.2011.592162
    [170] Silbergeld EK, Waalkes M, Rice JM (2000) Lead as a carcinogen: Experimental evidence and mechanisms of action. Am J Ind Med 38: 316-323. https://doi.org/10.1002/1097-0274(200009)38:3<316::AID-AJIM11>3.0.CO;2-P
    [171] Rousseau MC, Parent ME, Nadon L, et al. (2007) Occupational exposure to lead compounds and risk of cancer among men: A population-based case-control study. Am J Epidemiol 166: 1005-1014. https://doi.org/10.1093/aje/kwm183
    [172] Pueschel SM, Linakis JG, Anderson AC (1996) Lead poisoning in childhood. Baltimore: Paul Brooks.
    [173] Ling C, Ching Y, Hung-Chang L, et al. (2006) Effect of mother's consumption of traditional Chinese herbs on estimated infant daily intake of lead from breast milk. Sci Tot Environ 354: 120-126. https://doi.org/10.1016/j.scitotenv.2005.01.033
    [174] Carton JA (1988) Saturnismo. Med Clin 91: 538-540. https://doi.org/10.1177/0040571X8809100630
    [175] Larkin M (1997) Lead in mothers' milk could lead to dental caries in children. Sci Med 35: 789. https://doi.org/10.1016/S0140-6736(05)62579-2
    [176] Canfield RL, Henderson CR, Cory-Slechta DA, et al. (2003) Intellectual impairment in children with blood lead concentrations below 10 µg dL−1. N Engl J Med 348: 1517-1526. https://doi.org/10.1056/NEJMoa022848
    [177] Schwartz BS, Lee BK, Lee GS, et al. (2001) Associations of blood lead, dimercaptosuccinic acid-chelatable lead, and tibia lead with neurobehavioral test scores in South Korean lead workers. Am J Epidemiol 153: 453-464. https://doi.org/10.1093/aje/153.5.453
    [178] Vaziri ND (2008) Mechanisms of lead-induced hypertension and cardiovascular disease. Am J Physiol 295: H454-H465. https://doi.org/10.1152/ajpheart.00158.2008
    [179] Bellinger D (2005) Teratogen update: lead and pregnancy. Birth Defects Research 73: 409-420. https://doi.org/10.1002/bdra.20127
    [180] Borja-Aburto VH, Hertz-Picciotto I, Rojas LM, et al. (1999) Blood lead levels measured prospectively and risk of spontaneous abortion. Am J Epidemiol 150: 590-597. https://doi.org/10.1093/oxfordjournals.aje.a010057
    [181] Telisman S, Cvitkovic P, Jurasovic J, et al. (2000) Semen quality and reproductive endocrine function in relation to biomarkers of lead, cadmium, zinc and copper in men. Environ Health Perspect 108: 45-53. https://doi.org/10.1289/ehp.0010845
    [182] Kim JJ, Kim YS, Kumar V (2019) Heavy metal toxicity: An update of chelating therapeutic strategies. J Trace Elem Med Biol 54: 226-231. https://doi.org/10.1016/j.jtemb.2019.05.003
    [183] Sears ME (2013) Chelation: harnessing and enhancing heavy metal detoxification - a review. Sci World J 2013: 219840. https://doi.org/10.1155/2013/219840
    [184] Amadi CN, Offor SJ, Frazzoli C, et al. (2019) Natural antidotes and management of metal toxicity. Environ Sci Pollut Res 26: 18032-18052. https://doi.org/10.1007/s11356-019-05104-2
    [185] Rafati Rahimzadeh M, Rafati Rahimzadeh M, Kazemi S, et al. (2017) Cadmium toxicity and treatment: An update. Caspian J Intern Med 8: 135-145.
    [186] Singh KP, Bhattacharya S, Sharma P (2014) Assessment of heavy metal contents of some Indian medicinal plants. Am Eurasian J Agric Environ Sci 14: 1125-1129.
    [187] Bhattacharya S (2018) Medicinal plants and natural products can play a significant role in mitigation of mercury toxicity. Interdiscip Toxicol 11: 247-254. https://doi.org/10.2478/intox-2018-0024
    [188] Bhattacharya S, Haldar PK (2012) Trichosanthes dioica root possesses stimulant laxative activity in mice. Nat Prod Res 26: 952-957. https://doi.org/10.1080/14786419.2010.535161
    [189] Bhattacharya S, Haldar PK (2012) Protective role of the triterpenoid-enriched extract of Trichosanthes dioica root against experimentally induced pain and inflammation in rodents. Nat Prod Res 26: 2348-2352. https://doi.org/10.1080/14786419.2012.656111
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