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Research article

Changes in soft coral Sarcophyton sp. abundance and cytotoxicity at volcanic CO2 seeps in Indonesia

  • Received: 18 January 2016 Accepted: 19 April 2016 Published: 25 April 2016
  • This study presents the relationship between benthic cover of Sarcophyton sp. living on coral reefs and their cytotoxicity (an assumption of soft coral allelochemical levels) along acidification gradients caused by shallow water volcanic vent systems. Stations with moderate acidification (pH 7.87 ± 0.04), low acidification (pH 8.01 ± 0.04), and reference conditions (pH 8.2 ± 0.02) were selected near an Indonesian CO2 seep (Minahasa, Gunung Api Island, and Mahengetang Island). Cover of the dominant soft coral species (Sarcophyton sp.) was assessed and tissue samples were collected at each site. The cytotoxicity tissue extracts were analyzed using the 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolinon bromide (MTT) method. Levels of cytotoxicity were strongly correlated with Sarcophyton sp. cover (p < 0.05; R2 = 0.60 at 30 ppm and 0.56 at 100 ppm), being highest at mean pH 8.01 where the soft corals were most abundant. This finding suggests that Sarcophyton sp. can be expected to survive ocean acidification near Indonesia in the coming decades. How the species might be adversely affected by further ocean acidification later in the century unless CO2 emissions are reduced remains a concern.

    Citation: Hedi Indra Januar, Neviaty Putri Zamani, Dedi Soedarma, Ekowati Chasanah. Changes in soft coral Sarcophyton sp. abundance and cytotoxicity at volcanic CO2 seeps in Indonesia[J]. AIMS Environmental Science, 2016, 3(2): 239-248. doi: 10.3934/environsci.2016.2.239

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  • This study presents the relationship between benthic cover of Sarcophyton sp. living on coral reefs and their cytotoxicity (an assumption of soft coral allelochemical levels) along acidification gradients caused by shallow water volcanic vent systems. Stations with moderate acidification (pH 7.87 ± 0.04), low acidification (pH 8.01 ± 0.04), and reference conditions (pH 8.2 ± 0.02) were selected near an Indonesian CO2 seep (Minahasa, Gunung Api Island, and Mahengetang Island). Cover of the dominant soft coral species (Sarcophyton sp.) was assessed and tissue samples were collected at each site. The cytotoxicity tissue extracts were analyzed using the 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolinon bromide (MTT) method. Levels of cytotoxicity were strongly correlated with Sarcophyton sp. cover (p < 0.05; R2 = 0.60 at 30 ppm and 0.56 at 100 ppm), being highest at mean pH 8.01 where the soft corals were most abundant. This finding suggests that Sarcophyton sp. can be expected to survive ocean acidification near Indonesia in the coming decades. How the species might be adversely affected by further ocean acidification later in the century unless CO2 emissions are reduced remains a concern.


    Due to the difficulty in measuring the biomass of plankton, mathematical models of plankton populations are important methods for understanding the physical and biological processes of plankton. Various phytoplankton-zooplankton models (PZMs) have been studied: An NPZD model [1], a stochastic PZM [2], a plankton-nutrient system [3], a marine phytoplankton-zooplankton ecological model (PZEM) [4], Trophic phytoplankton-zooplankton models (PZM) [5], a bioeconomic PZM with time delays [6], a two-zooplankton one-phytoplankton PZM [7], a phytoplankton and two zooplankton PZM with toxin-producing delay [8], planktonic animal and plant PZM [9], and other PZMs [10, 11, 12]. In [12], Wang et al. investigated the following PZEM:

    $ {dPdt=plant growthrP(1PK)plant losse1PZ1+e1h1P+e2h2A,dZdt=n1e1PZ+n2e2AZ1+e1h1P+e2h2Aanimal gainτZnatural deathσPZh+Panimal death. $ (1.1)

    Fractional-order reaction-diffusion equation can describe the dynamic behavior of real systems more accurately. In recent years, fractional-order models have made remarkable progress in fields such as biomedicine, ecology, and public health. In biomedicine, fractional-order models have been used to study tumor growth [13] and hepatitis B virus (HBV) treatment [14], revealing their advantages in describing the complex dynamic behaviors of biological systems. In ecology, fractional-order models have demonstrated their potential in the study of ecosystem complexity by analyzing the dynamic behaviors of plant-herbivore interactions [15]. In public health, the fractional model has been applied to analyze the transmission of smoking behavior [16] and the correlation between human papilloma virus (HPV) and cervical cancer [17], highlighting their utility in public health research. These studies not only enrich the theoretical application of fractional models but also have made significant progress in numerical analysis, providing new tools and methods for solving complex biomedical and ecological problems [13, 17]. For example, in ecology, fractional PZEMs can more accurately describe the complex dynamics of ecosystems, including population fluctuations and interactions. Li et al. [18] studied an established fractional-order delayed zooplankton-phytoplankton model. Javidi and Ahmad [19] studied dynamic analysis of time fractional-order phytoplankton-toxic PZM. Kumar et al. [20] studied a fractional plankton-oxygen modeling. The proposed fractional-order PZEM extends traditional integer-order models by incorporating memory effects through fractional derivatives, which better capture long-term ecological interactions. This model accounts for toxic substances and additional food transmission, factors critical to understanding algal blooms, and population collapse. Models often neglect cross-diffusion and fractional dynamics, limiting their ability to simulate complex spatiotemporal patterns. Our work bridges this gap, offering insights into chaotic attractors and pattern formation under realistic ecological constraints. In this paper, we investigate the following fractional-order PZEM:

    $ {α1Ptα1=plant growthrP(1PK)plant losse1PZ1+e1h1P+e2h2A+plant diffusiond112P,α2Ztα2=n1e1PZ+n2e2AZ1+e1h1P+e2h2Aanimal gainτZnatural deathσPZh+Panimal death+d212P+d312Zplant and animal diffusion, $ (1.2)

    where $ P $ and $ Z $ represent the population densities of phytoplankton and zooplankton, respectively, at time t. $ \nabla ^2 $ stands for the Laplacian operator of the two-dimensional plane, $ \varOmega $ is a bounded connected region with smooth boundaries $ \partial\varOmega $, and $ d_{11} $ and $ d_{31} $ represent the diffusion coefficients of phytoplankton and zooplankton, respectively. These parameters characterize the stochastic movement of individuals within a population from areas of high concentration to those of lower density. $ d_{21} $ is a cross-diffusion coefficient that indicates the effect of the presence of phytoplankton on the movement of zooplankton populations. $ \alpha_i (i = 1, 2) $ is the fractional-order orders, $ 0 < \alpha_i < 1 $ and $ \frac{\partial^{\alpha_1}P}{\partial t^{\alpha_1}}, \frac{\partial^{\alpha_2}Z}{\partial t^{\alpha_2}} $ are the Grünwald-Letnikov (GL) fractional derivative. $ t $ is the time variable. The meanings of the parameters in the model are shown in Table 1.

    Table 1.  Parameter and biological significance in the model.
    Parameter Ecological Significance
    $ r $ The intrinsic growth rate of phytoplankton
    $ K $ The carrying capacity of the environment for phytoplankton
    $ h_{1} $ The time zooplankton need to process one unit of phytoplankton
    $ h_{2} $ The time zooplankton need to process one unit of supplementary food
    $ e_{1} $ The capacity of zooplankton to prey on phytoplankton
    $ e_{2} $ The capacity of zooplankton to forage for supplementary food
    $ n_{1} $ The nutritional value of phytoplankton
    $ n_{2} $ The nutritional value of supplementary food
    $ A $ The biomass of supplementary food
    $ \tau $ The mortality rate of zooplankton
    $ \sigma $ The proportion of toxins released by phytoplankton
    $ h $ The half-saturation constant

     | Show Table
    DownLoad: CSV

    Several numerical schemes have been used to solve the Fractional-order reaction-diffusion equation, the Galerkin method [21, 22], the Fourier spectral method [23, 24], the finite difference method [25, 26], the operational matrix method [27, 28], and so on [29, 30, 31, 32, 33, 34]. In this paper, we investigate dynamic properties and numerical solutions of the fractional-order PZEM (1.2). The major contributions of this paper are as follows:

    (a) The concept of the phytoplankton-zooplankton ecological model is first extended to fractional-order PZEM that incorporates the effects of toxic substances and additional food transmission in the environment. This model leverages the memory effect of fractional-order derivatives to more effectively capture biological significance compared to traditional integer-order models.

    (b) Stability, Turing instability, Hopf bifurcation, and weakly nonlinear property are analyzed for the PZEM. a new high-precision numerical method is developed for the fractional PZEM without diffusion term, and a discretization method is established for the PZEM with a diffusion term.

    (c) Numerical simulations show some novel chaotic attractor and pattern dynamical behaviors of the PZEM.

    The paper is organized as follows: In Section 2, we give the stability and Hopf bifurcation analysis. In Section 3, we detail weakly nonlinear analysis. In Section 4, we give the numerical algorithm and the numerical simulation results of the system. Finally, in Section 5, we the summarize paper.

    In this section, we investigate the stability of the equilibrium point and the emergence of Hopf bifurcation. Let

    $ ˉu=e1h1P,ˉv=e1rZ,t=rT,κ=e1h1K,α=n1h2n2h1,τ=n1rh1,ζ=n2e2h1n1A,m=τr,μ=τr,G=e1hh1. $

    Equation (1.2) is converted to the following form:

    $ {α1tα1ˉu=ˉu(1ˉuκ)ˉuˉv1+αζ+ˉu+d12ˉu,α2tα2ˉv=τ(ˉu+ζ)ˉv1+αζ+ˉumˉvμˉuˉvG+ˉu+d22ˉu+d32ˉv, $ (2.1)

    where, $ d_1 = e_1h_1d_{11}, d_2 = e_1h_1d_{21}, d_3 = \frac{e_1}{r}d_{31} $.

    We analyze the stability of Eq (2.1) without the diffusion term.

    $ {α1tα1ˉu=ˉu(1ˉuκ)ˉuˉv1+αζ+ˉu,α2tα2ˉv=τ(ˉu+ζ)ˉv1+αζ+ˉumˉvμˉuˉvG+ˉu. $ (2.2)

    Solving the following equation:

    $ {ˉu(1ˉuκ)ˉuˉv1+αζ+ˉu=0,τ(ˉu+ζ)ˉv1+αζ+ˉumˉvμˉuˉvG+ˉu=0. $ (2.3)

    We can get the following equilibrium points of Eq (2.2):

    $ E0=(0,0),E1=(κ,0),E=(ˉu,ˉv), $ (2.4)

    where

    $ ˉv=(1+αζ+ˉu)(1ˉuκ). $

    $ u^{*} $ represents the positive solution to the quadratic equation (2.5)

    $ ˉD1ˉu2+ˉD2ˉu+ˉD3=0, $ (2.5)

    where

    $ ˉD1=τmμ,ˉD3=τζGmGmαζG,ˉD2=τζ+τGmαζmGμαζμm. $

    Solving Eq (2.5), we can get:

    $ {ˉu1,2=(τζ+τHmαζmHμαζμm)2(τmμ)±(τζ+τHmαζmHμαζμm)24(τmμ)(τζHmHmαζH)2(τmμ),ˉv=(1+αζ+ˉu)(1ˉuκ). $ (2.6)

    The Jacobian matrix associated with $ E^{*} = \left(\bar{u}^{*}, \bar{v}^{*}\right) $ is formulated as follows

    $ J=[a11a12a21a22], $ (2.7)

    where

    $ a11=12ˉuκˉv(1+αζ)(1+αζ+ˉu)2, a12=ˉu1+αζ+ˉu,a21=τˉv(1+αζζ)(1+αζ+ˉu)2μˉvG(G+ˉu)2, a22=τ(ˉu+ζ)1+αζ+ˉumμˉuG+ˉu. $

    When $ (\alpha_{1}, \alpha_{2}) = (1, 1) $, the characteristic equation at the equilibrium point is as follows:

    $ λ2+Tr0λ+0=0, $ (2.8)

    where,

    $ Tr0=a11+a22,0=a11a22a21a12. $

    Let $ \alpha = 0.55, \tau = 4.1, \zeta = 0.72, G = 8.43, \mu = 0.79, \kappa = 2.38 $, and $ m = 2.45 $. The system's equilibrium point and its associated eigenvalues are presented in Table 2.

    Table 2.  The calculation results of the equilibrium point, eigenvalue, and argument of the system.
    Equilibrium point Eigenvalues of Jacobian matrix Stability
    0 0 –0.3354 1 Unstability
    2.3800 0 –1 0.7421 Unstability
    0.3131 1.4843 0.0138–0.4838i 0.0138+0.4838i Unstability

     | Show Table
    DownLoad: CSV

    It can be seen from Table 3 that all three equilibrium points are unstable points, and the system may generate chaos. Next, we introduce a high-precision numerical method for numerical simulation.

    Table 3.  Comparison of methods for problem (2.9) when $ \beta = 0.9 $ and $ t \in [0, 1]$.
    Method $ \alpha=0.4 $ $ \alpha=0.7 $ $ \alpha=1 $
    $ h=0.01 $ $ h=0.05 $ $ h=0.01 $ $ h=0.05 $ $ h=0.01 $ $ h=0.05 $
    Closed-from solution [35] 3.2307e-02 5.4302e-02 4.5734e-02 2.5713e-01 2.0716e-01 4.5136e-01
    Present method 8.9463e-05 5.6724e-04 9.1684e-05 7.3524e-04 2.1527e-04 4.5136e-03

     | Show Table
    DownLoad: CSV

    In simulations of this section, let $ \alpha = 1.1, \tau = 4.4, \zeta = 0.8, G = 8, n = 1.75, \kappa = 5.3 $, and $ m = 2.5 $ and initial conditions $ u_0 = 1 $ and $ v_0 = 1 $. We set the time step size $ h = 0.01 $ and the time as $ T = 600 $ for simulation. Figure 1 shows numerical results at $ (\alpha_1, \alpha_2) = (0.895, 0.994) $.

    Figure 1.  Comparative numerical result of the two methods of the model $ \left(\alpha, \tau, \zeta, G, n, \kappa, m\right) = \left(1.1, 4.4, 0.8, 8, 1.75, 5.3, 2.5\right) $, $ \alpha_1 = 0.895 $, and $ \alpha_2 = 0.994 $.

    We consider the following fractional order GL initial value problem

    $ {Dαty(t)=tβ,y(0)=0. $ (2.9)

    Numerical simulations are performed for Eq (2.9). Compared with the closed-from solution, the simulation results of the high-precision numerical method are in good agreement with the simulation results of other methods, and the accuracy is higher. This verifies the effectiveness of the high-precision numerical method.

    We first consider the following GL differential equation:

    $ dαdtαy(t)=f(t,y(t)). $ (2.10)

    According to [36], we can get the high-precision numerical method [36, 37, 38, 39]:

    $ y(tk)=hαf(tk,y(tk1))mi=1ϑ(α,p)jy(tkj), $ (2.11)

    where,

    $ {ϑ(α,p)0=g0,k=0,ϑ(α,p)k=1g0k1i=0(1i1+αk)giϑ(α,p)ki,k=1,2,....,p1,ϑ(α,p)k=1g0pi=0(1i1+αk)giϑ(α,p)ki,k=p,p+1,p+2,.... $ (2.12)
    $ (g0g1g2gp)=(1111123p+112232(p+1)212p3p(p+1)p)1(012p). $ (2.13)

    Where $ m = \left[t_k/h \right] +1 $, $ h $ is the step size. Therefore, a high-precision numerical method for the system (2.2) is the following

    $ {ˉuk=hα1(ˉuk1(1ˉuk1κ)ˉuk1ˉvk11+αζ+ˉuk1)+ˉu0mj=1ϑ(α1,p)jˉukj,ˉvk=hα2(τ(ˉuk+ζ)ˉvk11+αζ+ˉukmˉvk1μˉukˉvk1G+ˉuk)+ˉv0mj=1ϑ(α2,p)jˉvkj. $ (2.14)

    According to [36, 40], the least common order of the system is identified as $ 0.9819 $. Let $ \left(\alpha _1, \alpha _2 \right) = \left(1.05, 0.95 \right), \alpha = 0.55, \tau = 4.1, \zeta = 0.72, G = 8.43, \mu = 0.79, \kappa = 2.38 $, and $ m = 2.45 $, and the characteristic equation of the system is given by

    $ λ401066728823λ212478990071λ19+10396924437077=0, $ (2.15)

    with characteristic roots $ \lambda _{1, 2} = 1.0358\pm 0.0439i $, as $ |arg\left(\lambda _{1, 2} \right) | = 0.0423 < \frac{\pi}{40} $. This indicates that the instability of the system may generate chaos. It can be seen from Figure 2 that the system generates chaos. The chaotic phenomenon of the system gradually disappears over time and tends to a stable state.

    Figure 2.  Numerical simulation of phase diagrams and time series plot of system (2.2) at $ (\alpha_{1}, \alpha_{2}) = (1.05, 0.95). $.

    We set different orders $ \left(\alpha _1, \alpha _2 \right) = \left(1.1, 0.95 \right) $ to observe the influence of the order on the dynamic behavior of the system at parameters $ \alpha = 0.55, \tau = 4.1, \zeta = 0.72, G = 8.43, n = 0.79, \; \kappa = 2.38 $, and $ m = 2.45 $. The characteristic equation of the system is given by

    $ λ411066728823λ222478990071λ19+10396924437077=0, $ (2.16)

    with characteristic roots $ \lambda _{1, 2} = 1.0021\pm 0.2687i $, as $ |arg\left(\lambda _{1, 2} \right) | = 0.2620 < \frac{\pi}{40} $. It indicates that the instability of the system may generate chaos. It can be seen from Figure 3 that the system is in a quasi-periodic state.

    Figure 3.  Numerical simulation of phase diagrams and time series plot of system (2.2) at $ (\alpha_{1}, \alpha_{2}) = (1.1, 0.95). $.

    To gain a clearer view of the system's dynamic behavior, Figure 4 shows the phase diagram of the system under different $ \alpha $ orders.

    Figure 4.  Comparison of the phytoplankton-zooplankton phase diagram of the system (2.2) at different fractional-order derivatives.

    Next, we explore the potential for a Hopf bifurcation at $ E^{*} $. A Hopf bifurcation is critical as it marks a transition in the model's stability and the emergence of periodic solutions. To achieve this, the characteristic roots of system (2.2) must be purely complex.

    The solution to system (2.2) is obtained as follows:

    $ λ1,2=Tr0±Tr204det02. $ (2.17)

    When $ \alpha = 1 $, system (2.2) undergoes a destabilizing Hopf bifurcation under the conditions $ tr_0 = 0 $ and $ det_0 > 0 $. Given that the stability of system (2.2) is influenced by the fractional derivative, this derivative can be considered a parameter in the Hopf bifurcation. We now determine the conditions for the Hopf bifurcation for system (2.2) around parameter $ E_* $, $ \alpha = \alpha_h $:

    (1) At the equilibrium point $ E_* $, the Jacobian matrix possesses a pair of complex conjugate eigenvalues $ \lambda _{1, 2} = a_i+ib_i $, which transition to being purely imaginary at $ \alpha = \alpha_h $;

    (2) $ m\left(\alpha _h \right) = 0 $ where $ m\left(\alpha \right) = \alpha \frac{\pi}{2}-\underset{1\le i\le 2}{\min}|arg\left(\lambda _i \right) | $;

    (3) $ \left. \frac{\partial m\left(\alpha \right)}{\partial \alpha} \right|_{\alpha = \alpha _h}\ne 0 $.

    We now demonstrate that $ E_* $ experiences a Hopf bifurcation as $ \alpha $ crosses the value $ \alpha_h $.

    Proof. Given that $ tr_{0}^{2}-4\det _0 < 0 $ and $ tr_0 > 0 $, the eigenvalues form a complex conjugate pair with a positive real component. Thus,

    $ 0<arg(λ12)=tan1(4det0tr20tr0)<π2, $ (2.18)

    and $ \alpha \frac{\pi}{2} > \Big{|}\tan ^{-1}\left(\frac{\sqrt{4\det _0-tr_{0}^{2}}}{tr_0} \right) \Big{|} $ for some $ \alpha $. Let $ \alpha_h \frac{\pi}{2} = \Big{|}\tan ^{-1}\left(\frac{\sqrt{4\det _0-tr_{0}^{2}}}{tr_0} \right) \Big{|} $, get $ \alpha _h = \frac{2}{\pi}\tan ^{-1}\left(\frac{\sqrt{4\det _0-tr_{0}^{2}}}{tr_0} \right) $. Moreover, $ \left. \frac{\partial m\left(\alpha \right)}{\partial \alpha} \right|_{\alpha = \alpha _h} = \frac{\pi}{2}\ne 0 $. Therefore, all Hopf conditions satisfy.

    Above, we analyze the dynamical behavior of fractional system (2.2). The expression of the solution of system (2.1) involves more complex special functions, such as the Mittag-Leffler function and other hypergeometric functions. Although the form of the solution exists, its expression is very large. Therefore, in this section, we reveal various spatiotemporal behaviors around the Turing bifurcation threshold $ d _2 $ and derive the amplitude equations associated with system (2.1) at $ \alpha_1 = \alpha_2 = 1 $ using multi-scale and weakly nonlinear analysis. The solution of system (2.1) is written in the following form:

    $ (ˉuˉv)=(ˉuˉv)+3j=1(AˉujAˉvj)eiqjr+c.c., $ (3.1)

    where $ \left(A_{j}^{\bar{u}^*}, A_{j}^{\bar{v}^*} \right) ^T $ represents the magnitude of the wave vector $ \boldsymbol{q}_j $, fulfilling the condition that $ \left|\boldsymbol{q}_j \right| = q_T $.

    Adding a perturbation to the equilibrium point $ E^{*}(u^*, v^*) $, such that $ \bar{u} = \bar{u}^*+u $, $ \bar{v} = \bar{v}^*+v $, and substituting them into system (2.1), and performing a Taylor expansion, we can get the following form:

    $ {ut=a11u+a12v+k20u2+k02v2+k11uv+k30u3+k03v3+k21u2v+k12uv2+d12u,vt=a11u+a22v+m20u2+m02v2+m11uv+m30u3+m03v3+m21u2v+m12uv2+d22u+d32v, $ (3.2)

    where

    $ k02=0,k03=0,k12=0,m02=0,m03=0,m12=0,k11=1+αζ(1+αζ+ˉu)2,m11=(1+αζζ)τ(1+αζ+ˉu)2μG(G+ˉu)2,k21=1+αζ(1+αζ+ˉu)3,m21=τ(1+αζζ)(1+αζ+ˉu)3+μG(G+ˉu)3,k30=(1+αζ)(1ˉuκ)(1+αζ+ˉu)3,m30=τ(1ˉuκ)(1+αζζ)(1+αζ+ˉu)3μGˉv(G+ˉu)4,k20=1κ+(1+αζ)(1ˉuκ)(1+αζ+ˉu)2,m20=τ(1+αζζ)(1ˉuκ)(1+αζ+ˉu)2+μGˉv(G+ˉu)3. $

    Let $ U = \left(u, v \right) ^T $ and system (3.2) can be simplified as

    $ Ut=LU+N(U,U), $ (3.3)
    $ L=(a11+d12a12a21+d22a22+d32), $

    where

    $ N=(k20u2+k02v2+k11uv+k30u3+k03v3+k21u2v+k12uv2m20u2+m02v2+m11uc+m30u3+m03v3+m21u2v+m12uv2). $

    Here, $ L $ denotes a linear operator and $ N $ represents a nonlinear operator.

    We expand parameter $ d _2 $ with a sufficiently small parameter $ \varepsilon $, so we can obtain:

    $ dT2=εd(1)2+ε2d(2)2+ε3d(3)2+O(ε3). $ (3.4)

    We develop variable $ U $ and nonlinear term $ N $, respectively, the small parameter $ \varepsilon $:

    $ U=(uv)=ε(u1v1)+ε2(u2v2)+ε3(u3v3)+O(ε3), $ (3.5)
    $ N=ε2N2+ε3N3+O(ε4), $ (3.6)

    where

    $ N2=(k20u21+k11u1v1m20u21+m11u1v1),N3=(2k20u1u2+k11u1v2+k11u2v1+k30u31+k21u21v12m20u1u2+m11u1v2+m11u2v1+m30u31+m21u21v1). $

    We decompose operator $ L $ into the following form:

    $ L=Lc+(d2dT2)M, $ (3.7)

    where

    $ Lc=(d12+a11a12dT22+a21d32+a22),M=(b11b12b21b22). $

    Using the multiple-scale approach, we differentiate the system's time scales into $ T_1 = \varepsilon t, T _2 = \varepsilon ^2t, T_3 = \varepsilon ^3t $, which are mutually independent. Consequently, the time derivative can be articulated as:

    $ t=εT1+ε2T2+ε3T3+O(ε3). $ (3.8)

    Substituting Eqs (3.4)–(3.8) into Eq (3.3), we can obtain the following equation:

    $ ε:Lc(u1v1)=0, $ (3.9)
    $ ε2:Lc(u2v2)=T1(u1v1)d(1)2M(u1v1)N2, $ (3.10)
    $ ε3:Lc(u3v3)=T1(u2v2)+T2(u1v1)d(1)2M(u2v2)d(2)2M(u1v1)N3. $ (3.11)

    The $ 1^{st} $ order of $ (\mathcal{O}\left(\varepsilon \right)) $:

    $ Lc(u1v1)=0. $ (3.12)

    The solution of Eq (3.12) is

    $ (u1v1)=(φ1)3j=1(Wjeiqjr)+c.c., $ (3.13)

    where $ \varphi = \frac{-a_{12}}{a_{11}-{d}_{1}q_{c}^{2}}, \left| \boldsymbol{q}_{_j} \right| = q_c, q_c = q_T\left(d ^{T}_2 \right) $. Additionally, $ W_j $ denotes the amplitude of $ e^{i\boldsymbol{q}_j\cdot r} $.

    The $ 2^{nd} $ order of $ (\mathcal{O}\left(\varepsilon ^2 \right)) $:

    $ Lc(u2v2)=T1(u1v1)d(1)2M(u1v1)N2=(FuFv), $ (3.14)

    $ F_u^j $ and $ F_v^j (j = 1, 2, 3) $ are the coefficients with respect to $ e^{i\boldsymbol{q}_j\cdot r} $ in $ F_u $ and $ F_v $, respectively.

    Using the Fredholm solvability condition for Eq (3.14), the vector function on the right-hand side must be perpendicular to the zero eigenvalue of $ L_{c}^{+} $. The zero eigenvector of $ L_{c} $ is:

    $ (1ψ)eiqjr+c.c., j=1,2,3, $ (3.15)

    with $ \psi = -\frac{a_{11}-{d}_{1}q_{c}^{2}}{a_{21}-{d}^{T}_{2}q_{c}^{2}} $. From the orthogonal condition:

    $ (1,ψ)(FjuFjv)=0,j=1,2,3. $ (3.16)

    Utilizing the Fredholm solvability condition as stated in Eq (3.16), we arrive at the following:

    $ {(φ+ψ)W1T1=d(1)2η0W1+2(η1+ψη2)¯W2¯W3,(φ+ψ)W2T1=d(1)2η0W2+2(η1+ψη2)¯W1¯W3,(φ+ψ)W3T1=d(1)2η0W3+2(η1+ψη2)¯W1¯W2, $ (3.17)

    where

    $ {η0=(φb11+b22)+ψ(φb21+b22),η1=12k20φ2+k11φ,η2=12m20φ2+m11φ. $

    Next, higher-order disturbance terms are introduced:

    $ (u2v2)=(U0V0)+3j=1(UjVj)eiqjr+3j=1(UjjVjj)e2iqjr+(U12V12)ei(q1q2)r+(U23V23)ei(q2q3)r+(U31V31)ei(q3q1)r+c.c.. $ (3.18)

    We substitute formulas (3.13) and (3.18) into formula (3.10). By solving the equations corresponding to different modes, it is known that the coefficients have the following forms:

    $ (U0V0)=(u00v00)(|W1|2+|W2|2+|W3|2), Uj=φYj,(UjjVjj)=(u11v11)W2j,(UijVij)=(ˉuˉv)Wi¯Wj, $

    where

    $ (ˉu00ˉv00)=2a11a22a21a12(a22η1a12η2a11η2a21η1), $ (3.19)
    $ (ˉu11ˉv11)=(a12η2(a224d3q2c)η1(a114d1q2c)(a224d3q2c)(a214dT2q2c)a12(a214dT2q2c)η1(a114d1q2c)η2(a114d1q2c)(a224d3q2c)(a214dT2q2c)a12), $ (3.20)
    $ (ˉuˉv)=2(a12η2(a223d3q2c)η1(a113d1q2c)(a223d3q2c)(a213dT2q2c)a12(a213dT2q2c)η1(a113d1q2c)η2(a113d1q2c)(a223d3q2c)(a213dT2q2c)a12). $ (3.21)

    From the orthogonal condition, we obtain:

    $ {(φ+ψ)(Y1T1+W1T2)=η0(d(2)2W1+d(1)2Y1)[(Q1+ψR1)|W1|2+(Q2+ψR2)(|W2|2+|W3|2)]W1+2(η1+ψη2)(¯W2¯Y3+¯W3¯Y2),(φ+ψ)(Y2T1+W2T2)=η0(d(2)2W2+d(1)2Y2)[(Q1+ψR1)|W2|2+(Q2+ψR2)(|W1|2+|W3|2)]W2+2(η1+ψη2)(¯W1¯Y3+¯W3¯Y1),(φ+ψ)(Y3T1+W3T2)=η0(d(2)2W3+d(1)2Y3)[(Q1+ψR1)|W3|2+(Q2+ψR2)(|W2|2+|W1|2)]W3+2(η1+ψη2)(¯W2¯Y1+¯W1¯Y2), $ (3.22)

    where

    $ Q1=(2φk20+k11)(u00+u11)φk11(v00+v11)3k30φ33k21φ2,Q2=(2φk20+k11)(u00+u)φk11(v00+v)6k30φ36k21φ2,R1=(2φm20+m11)(u00+u11)φm11(v00+v11)3m30φ33m21φ2,R2=(2φm20+m11)(u00+u)φm11(v00+v)6m30φ36m21φ2. $

    The amplitude $ A_{j} $ is the coefficient of $ e^{i\boldsymbol{q}_j\cdot r} $ at each level, so

    $ Aj=εWj+ε2Yj+O(ε3). $ (3.23)

    Substituting Eqs (3.17) and (3.22) into Eq (3.23), we get the following amplitude equations:

    $ {τ0Z1t=ηZ1+χˉZ2ˉZ3[g1|Z1|2+g2(|Z2|2+|Z3|2)]Z1,τ0Z2t=ηZ2+χˉZ1ˉZ3[g1|Z2|2+g2(|Z1|2+|Z3|2)]Z2,τ0Z3t=ηZ3+χˉZ1ˉZ2[g1|Z3|2+g2(|Z1|2+|Z2|2)]Z3, $ (3.24)

    where

    $ η=d2dT2dT2,τ0=φ+ψdT2[(φb11+b12)+ψ(φb21+b22)],χ=k20φ2+2k11φ+m20φ2ψ+2m11φψdT2[(φb11+b12)+ψ(φb21+b22)],g1=Q1+ψR1dT2[(φb11+b12)+ψ(φb21+b22)],g2=Q2+ψR2dT2[(φb11+b12)+ψ(φb21+b22)]. $

    Since each amplitude $ A_j = \omega _je^{i\theta _j}\left(j = 1, 2, 3 \right) $ in Eq (3.24) can be decomposed into mode $ \omega _j = |A_j| $ and phase angle $ \theta_j $, substituting $ A_{j} $ into Eq (3.24) to separate the real and imaginary parts yields the following equation:

    $ {τ0θt=χω21ω22+ω21ω23+ω22ω23ω1ω2ω3sinθ,τ0ω1t=ηω1+χω2ω3cosθ[g1ω31+g2(ω22+ω23)ω1],τ0ω1t=ηω1+χω2ω3cosθ[g1ω31+g2(ω22+ω23)ω1],τ0ω1t=ηω1+χω2ω3cosθ[g1ω31+g2(ω22+ω23)ω1], $ (3.25)

    where, $ \theta = \theta _1+\theta _2+\theta _3 $. From Eq (3.25), it can be deduced that the solution is stable under the conditions $ \chi > 0, \psi = 0 $ and $ \chi < 0, \psi = \pi $. The solutions of Eq (3.25) are shown in Table 4.

    Table 4.  The relationship between pattern shape and steady-state solutions.
    Conditions Solution Pattern shape
    $ \omega_1=\omega_{2}=\omega_3=0 $ Stationary state
    $ \omega_1=\sqrt{\dfrac{\eta}{g_1}}, \omega_2=\omega_3=0 $ Strip pattern
    $ \eta > \eta_1=\dfrac{-\chi^2}{4(g_1+2g_2)} $ $ \omega_1=\omega_{2}=\omega_3=\dfrac{|\chi|\pm\sqrt{\chi^2+4(g_1+2g_2)\eta}}{2(g_1+2g_2)} $ Hexagon pattern
    $ g_2 > g_1, \eta > g_1\omega^2_1 $ $ \omega_1=\dfrac{|\chi|}{g_2-g_1}, \omega_2=\omega_3=\sqrt{\dfrac{\eta-g_1\omega^2_1}{g_1+g_2}} $ Mixed state

     | Show Table
    DownLoad: CSV

    In this section, we conduct numerical simulations to verify the theoretical analysis and observe its pattern dynamic behavior. In order to observe the dynamic behavior, we introduce the numerical method of the PZEM model (2.1). If $ 0 < \alpha_i < 1 (i = 1, 2) $, the time derivative is expressed by formula (2.11), and the space derivative is expressed by the following formula (4.2). If $ \alpha_i = 1(i = 1, 2) $, we employ the Euler discretization approach for conducting numerical simulations in a two-dimensional domain $ \varOmega = \left[0, L_x \right] \times \left[0, L_y \right] $. We select $ L_x = 250, L_y = 250 $, a time increment $ \varDelta t = 0.2 $, and a spatial increment $ \varDelta h = 0.69 $. We denote $ u_{pq}^{n} = u\left(x_p, y_q, n\varDelta t \right) $ and $ v_{pq}^{n} = v\left(x_p, y_q, n\varDelta t \right) $. The model (2.1) is discretized using the Euler method, as outlined below:

    $ {ˉun+1pqˉunpqΔt=ˉunpq(1ˉunpqκ)ˉunpqˉvnpq1+αζ+ˉunpq+d12ˉunpq,ˉvn+1pqˉvnpqΔt=τ(ˉunpq+ζ)ˉvnpq1+αζ+ˉunpqmˉvnpqμˉunpqˉvnpqG+ˉunpq+d22ˉunpq+d32ˉvnpq, $ (4.1)

    where

    $ {2ˉupq=ˉup+1,q+1+ˉup1,q1+ˉup+1,q1+ˉup1,q+1+4(ˉup+1,q+ˉup1,q+ˉup,q+1+ˉup,q1)20ˉupq6h2,2ˉvpq=ˉvp+1,q+1+ˉvp1,q1+ˉvp+1,q1+ˉvp1,q+1+4(ˉvp+1,q+ˉvp1,q+ˉvp,q+1+ˉvp,q1)20ˉvpq6h2. $ (4.2)

    Next, we select the parameters shown in Table 5 and use Eq (4.1) to conduct numerical simulations.

    Table 5.  Parameter values.
    $ \alpha $ $ \tau $ $ \zeta $ $ G $ $ n $ $ \kappa $ $ m $ $ \kappa_{c} $ $ d_{1} $ $ d_{2} $ $ d_{3} $
    $ 0.55 $ $ 4.1 $ $ 0.72 $ $ 8.43 $ $ 0.79 $ $ 2.38 $ $ 2.45 $ $ 1.91 $ $ 0.0036 $ $ 0.00158 $ $ 0.0141 $

     | Show Table
    DownLoad: CSV

    The parameter values are shown in Table 5, and the calculation results are as follows:

    $ E=(0.3131,1.4843),χ=0.4312,η=0.2461,τ0=0.3270,g1=1.2869,g2=1.7464. $

    The initial conditions are specified as follows:

    $ u(x,y,0)=u(1+0.1(rand0.5)),v(x,y,0)=v(1+0.1(rand0.5)). $

    The outcomes of the numerical simulation indicate that speckle and mixed-structure patterns emerge in the graphical representation with this particular set of parameters, as illustrated in Figure 5.

    Figure 5.  Density distribution pattern of system (2.1) at $ \alpha = 0.55, \tau = 4.1, \zeta = 0.72, G = 8.43, n = 0.79, \kappa = 2.38, m = 2.45, d_{1} = 0.0036, d_{2} = 0.00158, d_{3} = 0.0141 $, and $ \alpha_1 = \alpha_2 = 1 $.

    Now, we use the parameters in Table 5 and symmetric initial conditions to perform numerical simulations by changing parameters $ d_{1} $, $ d_{2} $, and $ d_{3} $. Numerical simulation was carried out with other parameters remaining unchanged, and the results showed that there is a symmetric mixed structure solution. The subsequent figure illustrates the intricate pattern evolution of the symmetric mixed pattern across parameters. We select the following symmetric initial conditions:

    $ u(x,y,0)={u,x,y(80,120),u0.001,other,v(x,y,0)={v,x,y(80,120),v0.001,other. $

    Figure 6 shows the spatial distribution patterns of phytoplankton and zooplankton at different diffusion coefficients, $ d_{2} $. The diffusion coefficient $ d $ reflects the influence of phytoplankton on the distribution of zooplankton. When $ d_{2} = 0.003 $, phytoplankton and zooplankton form highly clustered patterns, with zooplankton closely following the prey. When $ d_{2} = 0.005 $, phytoplankton and zooplankton are more dispersed, and the zooplankton pattern is more complex. This indicates that the diffusion ability of phytoplankton affects the hunting efficiency of zooplankton, and zooplankton tend to migrate to areas with a high density of phytoplankton. When $ d_{2} = 0.004 $, the distribution densities of phytoplankton and zooplankton are between the distribution densities of phytoplankton and zooplankton at $ d_{2} = 0.003 $ and $ d_{2} = 0.005 $.

    Figure 6.  Population density distribution pattern of phytoplankton and zootoplankton with with different parameters $ {d}_{1} = 0.002 $ and $ {d}_{3} = 0.018 $.

    Let $ d_{1} = 0.002, d_{2} = 0.004 $, and $ d_{3} = 0.015 $ through the observation of the distribution pattern of plankton population density in Figure 7. At $ t = 6000 $, the system presents an incomplete pattern structure. Phytoplankton begins to form an irregular pattern distribution, while zooplankton shows an aggregation pattern following predation. At $ t = 8000 $, the pattern structure gradually forms a stable state. At $ t = 10000 $, the system reaches a stable state and forms a predator aggregation area that is misaligned with the plant pattern. We find that as time goes by, $ t $, the distribution pattern of plankton population density becomes more complex. This indicates that the system presents a complex competitive process over time. This reflects the process by which the ecosystem reaches a stable state through dynamic adjustment.

    Figure 7.  The distribution patterns of phytoplankton and zooplankton population densities at different time periods.

    Let parameter $ d_{1}=0.002, d_{2}=0.004 $, and $ d_{3}=0.017 $, the patterns of phytoplankton and zooplankton at different times are shown in Figure 8$ a_{1}-a_{4} $ and Figure 8$ c_{1}-c_{4} $. For diffusion coefficients at $ d_{1}=0.002, d_{2}=0.006 $, and $ d_{3}=0.017 $, the patterns of phytoplankton and zooplankton at different times are shown in Figure 8$ b_{1}-b_{4} $ and Figure 8$ d_{1}-d_{4} $. In Figure 8, the density of phytoplankton gradually increases over time. It can be seen from the pattern that the difference between the high-density area and the low-density area significantly increases. The internal structure of the pattern becomes more complex, showing more details and layers. The distribution pattern of zooplankton shows a significantly misaligned predation aggregation area with that of plants, and the density of predation hotspots continues to increase over time. It can be seen from the pattern that the spatial distribution of phytoplankton and zooplankton shows complex dynamic behaviors.

    Figure 8.  Population density distribution patterns of phytoplankton and zootoplankton with parameters $ {d}_{1} = 0.002 $ and $ {d}_{3} = 0.017 $.

    Through the analysis of the patterns of phytoplankton and zooplankton, we see that, as time goes by, the patterns of zooplankton evolve from simple patterns to complex ones, demonstrating the complexity of this ecosystem. The diffusion coefficient is highly sensitive to the generation of patterns. A smaller diffusion coefficient leads to more regular and symmetrical patterns, while a larger diffusion coefficient results in more complex and irregular patterns, significantly affecting the distribution pattern of plankton. The initial conditions and diffusion coefficient significantly impact the long-term ecological behavior of the model. Moreover, initial conditions affect the formation of the pattern, while the parameters affect the distribution structure of the ecosystem.

    We combine theoretical analysis with numerical simulation to deeply explore the dynamic behavioral characteristics of the fractional-order PZEM. In theoretical analysis, we conduct stability, Turing instability, Hopf bifurcation, and nonlinear analysis for the PZEM. In numerical methods, we develop a high-precision numerical method for fractional-order PZEM without diffusion terms and verify the superiority of this method through comparison with other methods. Moreover, an effective discretization method is established for the model with diffusion terms. The numerical simulation results not only verify the correctness of the theoretical analysis, but also demonstrate complex dynamic behaviors at different diffusion coefficients. Moreover, the system presents significantly different spatial pattern evolution characteristics. The results reveal that the diffusion coefficient is crucial to the generation of patterns. A bigger diffusion coefficient will lead to more complex and irregular pattern structures, which directly affects the spatial distribution patterns of plankton populations. Furthermore, the initial conditions and the diffusion coefficient have a decisive influence on the long-term ecological behavior of the model: The initial conditions affect the formation process of the pattern, while the diffusion coefficient affects the dynamic evolution of the pattern structure. In future work, we will explore the response mechanism of the system at the coupling effect of multiple factors, as well as the effect of dynamic behavior for fractional-order.

    Conceptualization, Methodology, Software, Data, Formal analysis and Funding acquisition, Writing-original draft and writing-review and editing: Shuai Zhang, Hao Lu Zhang, Yu Lan Wang and Zhi Yuan Li. All authors have read and agreed to the published version of the manuscript.

    The authors declare they have not used Artificial Intelligence (AI) tools in the creation of this article.

    This paper is supported by Doctoral research start-up Fund of Inner Mongolia University of Technology (DC2300001252) and the Natural Science Foundation of Inner Mongolia (2024LHMS06025).

    The authors declare that there are no conflicts of interest regarding the publication of this article.

    [1] Evenhuis C, Lenton A, Cantin NE, et al. (2015) Modelling coral calcification accounting for the impacts of coral bleaching and ocean acidification. Biogeosci 12: 2607-2630.
    [2] Guinottea JM, Fabry VJ (2008) Ocean Acidification and Its Potential Effects on Marine Ecosystems. Ann NY Acad Sci 1134: 320-342. doi: 10.1196/annals.1439.013
    [3] Cyronak T, Schulz KG, Jokiel PL (2015) The Omega myth: what really drives lower calcification rates in an acidifying ocean. ICES J Mar Sci 73: 558-562.
    [4] Suwa R, Nakamura M, Morita M, et al. (2010) Effects of acidified seawater on early life stages of scleractinian corals (Genus Acropora). Fish Sci 76: 93-99. doi: 10.1007/s12562-009-0189-7
    [5] Hii YS, Ambok Bolong AM, Yang TT, et al. (2009) Effect of elevated carbon dioxide on two Scleractinian corals: Porites cylindrica (Dana, 1846) and Galaxea fascicularis (Linnaeus, 1767). J Mar Biol 2009: 215196.
    [6] Kerrison P, Hall-Spencer JM, Suggett DJ, et al. (2011) Assessment of pH variability at a coastal CO2 vent for ocean acidification studies. Estuar Coast Shelf Sci 94: 129-137. doi: 10.1016/j.ecss.2011.05.025
    [7] Hall-Spencer JM, Rodolfo-Metalpa R, Martin S, et al. (2008) Volcanic carbon dioxide vents show ecosystem effects of ocean acidification. Nature 454: 96-99. doi: 10.1038/nature07051
    [8] Cigliano M, Gambi MC, Rodolfo-Metalpa R, et al. (2010) Effects of ocean acidification on invertebrate settlement at volcanic CO2 vents. Mar Biol 157: 2489-2502. doi: 10.1007/s00227-010-1513-6
    [9] Johnson VR, Brownlee C, Rickaby REM, et al. (2013) Responses of marine benthic microalgae to elevated CO2. Mar Biol 160: 1813-1824.
    [10] Inoue S, Kayanne H, Yamamoto S, et al. (2013) Spatial community shift from hard to soft corals in acidified water. Nat Clim Chang 3: 683-687. doi: 10.1038/nclimate1855
    [11] Gabay Y, Benayahu Y, Fine M (2013) Does elevated pCO2 affect reef octocorals? Ecol Evol 3: 465-473. doi: 10.1002/ece3.351
    [12] Gabay Y, Fine M, Barkay Z (2014) Octocoral Tissue Provides Protection from Declining Oceanic pH. PloS ONE 9: e91553. doi: 10.1371/journal.pone.0091553
    [13] Michalek-Wagner K, Bourne DJ, Bowden BF (2001) The effects of different strains of zooxanthellae on the secondary-metabolite chemistry and development of the soft-coral host Lobophytum compactum. Mar Biol 138: 753-760. doi: 10.1007/s002270000505
    [14] Changyun W, Haiyan L, Changlun S, et al. (2008) Chemical defensive substances of soft corals and gorgonians. Acta Ecol Sin 28: 2320-2328. doi: 10.1016/S1872-2032(08)60048-7
    [15] Sotka E, Forbey J, Horn M, et al. (2009) The emerging role of pharmacology in understanding consumer-prey interactions in marine and freshwater systems. Integr Comp Biol 49: 291-313. doi: 10.1093/icb/icp049
    [16] Lages BG, Fleury BG, Ferreira CE, et al. (2006) Chemical defense of an exotic coral as invasion strategy. J Exp Mar Biol Ecol 328: 127-135.
    [17] Kahng SE, Grigg RW (2005) Impact of an alien octocoral, Carijoa riisei, on black corals in Hawaii. Coral Reefs 24: 556-562. doi: 10.1007/s00338-005-0026-0
    [18] Aceret TL, Sammarco PW, Coll JC (1995) Toxic effects of alcyonacean diterpenes on scleractinian corals. J Exp Mar Biol Ecol 188: 63-78.
    [19] Sammarco PW, Coll JC, Barre SL (1995). Competitive strategies of soft coral (Coelenterata : Octocorallia), II, variable defensive responses and susceptibility to scleractinian corals. J Exp Mar Biol Ecol 91: 199-215.
    [20] Sammarco PW, Coll JC (1990) Lack of predictability in terpenoid function - multiple roles and integration with related adaptations in soft corals. J Chem Ecol 16: 273-289. doi: 10.1007/BF01021284
    [21] Yang B, Liu J, Wang J, et al. (2015) Cytotoxic Cembrane Diterpenoids. InHandbook of Anticancer Drugs from Marine Origin. Springer International Publishing, 649-672.
    [22] Liu X, Zhang J, Liu Q, et al. (2015) Bioactive Cembranoids from the South China Sea Soft Coral Sarcophyton elegans. Molecules 20: 13324-13335. doi: 10.3390/molecules200713324
    [23] Rocha J, Peixe L, Gomes N, et al. (2011) Cnidarians as a source of new marine bioactive compounds—An overview of the last decade and future steps for bioprospecting. Mar Drugs 9: 1860-1886. doi: 10.3390/md9101860
    [24] Fabricius KE, Langdon C, Uthicke S, et al. (2011) Losers and winners in coral reefs acclimatized to elevated carbon dioxide concentrations. Nat Clim Chang 1: 165-169. doi: 10.1038/nclimate1122
    [25] Pierrot DE, Lewis E, Wallace DWR (2006) MS Exel Program Developed for CO2 System Calculations. ORNL/CDIAC-105a. Oak Ridge, Tennessee, USA: Carbon Dioxide Information Analysis Centre, Oak Ridge National Laboratory, US Department of Energy.
    [26] Fabricius KE, Alderslade P (2001) Soft corals and sea fans: a comprehensive guide to the tropical shallow water genera of the central west Pacific, the Indian Ocean and the Red Sea. Australian Institute of Marine Science, 264.
    [27] Zachary I (2003) Determination of cell number, in: Cell proliferation and apoptosis. D. Hughes and H Mehmet (eds), Bios Scientific Publishers, 13-35.
    [28] Kohler KE, Gill SM (2006) Coral Point Count with Excel extensions (CPCe): A visual basic program for the determination of coral and substrate coverage using random point coral methodology,”. Comput Geosci 32: 1259-1269. doi: 10.1016/j.cageo.2005.11.009
    [29] Hammer O, Harper DAT, Ryan PD (2001) Past: Paleontological Statistics Software package for education and data analysis. Palaeontol Electron 4: 9.
    [30] Anthony KR, Kline DI, Diaz-Pulido G (2008) Acidification causes bleaching and productivity loss in coral reef builders. P Natl Acad Sci USA 105: 17442-17446. doi: 10.1073/pnas.0804478105
    [31] Crook ED, Potts D, Rebolledo-Vieyra M (2012) Calcifying coral abundance near low-pH springs: implications for future ocean acidification. Coral Reefs 31: 239-245. doi: 10.1007/s00338-011-0839-y
    [32] Edmunds PJ (2011) Zooplanktivory ameliorates the effects of ocean acidification on the reef coral Porites sp. Limnol Oceanogr 56: 2402-2410. doi: 10.4319/lo.2011.56.6.2402
    [33] Doney SC, Fabry VJ, Feely RA, et al. (2009) Ocean acidification: the other CO2 problem. Ann Rev Mar Sci 1: 169-192. doi: 10.1146/annurev.marine.010908.163834
    [34] Sammarco PJ, Coll JC (1992) Chemical adaptations in the Octocorallia: evolutionary considerations. Mar Ecol Prog Ser 88: 93-93.
    [35] Luter HM, Duckworth AR (2010) Influence of size and spatial competition on the bioactivity of coral reef sponges. Biochem Syst Ecol 38: 146-153.
    [36] Januar HI, Marraskuranto E, Patantis G, et al. (2012) LC-MS Metabolomic Analysis of Environmental Stressors Impacts to the Metabolites Diversity in Nephthea sp.. Chron Young Sci 2: 57-62.
    [37] Januar HI, Pratitis A, Bramandito A (2015) Will the increasing of anthropogenic pressures reduce the biopotential value of sponges? Scientifica 2015: 734385.
    [38] Januar HI, Chasanah E, Tapiolas DM, et al. (2015) Influence of anthropogenic pressures on the bioactivity potential of sponges and soft corals in the coral reef environment. Squallen Bull Mar Fish Postharvest Biotech 10: 51-59.
    [39] Arnold T, Mealey C, Leahey H, et al. (2012) Ocean Acidification and the Loss of Phenolic Substances in Marine Plants. PLoS ONE 7: e35107.
    [40] Suggett DJ, Hall-Spencer J, Rodofo-Metalpa R, et al. (2012) Sea anemones may thrive in a high CO2 world. Global Chang Biol 18: 3015-3025. doi: 10.1111/j.1365-2486.2012.02767.x
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