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. 2015 Nov 6;8:656. doi: 10.1186/s13104-015-1619-5

On the transmission dynamics of Buruli ulcer in Ghana: Insights through a mathematical model

Farai Nyabadza 1, Ebenezer Bonyah 2,
PMCID: PMC4636839  PMID: 26545356

Abstract

Background

Mycobacterium ulcerans is know to cause the Buruli ulcer. The association between the ulcer and environmental exposure has been documented. However, the epidemiology of the ulcer is not well understood. A hypothesised transmission involves humans being bitten by the water bugs that prey on mollusks, snails and young fishes.

Methods

In this paper, a model for the transmission of Mycobacterium ulcerans to humans in the presence of a preventive strategy is proposed and analysed. The model equilibria are determined and conditions for the existence of the equilibria established. The model analysis is carried out in terms of the reproduction number R0. The disease free equilibrium is found to be locally asymptotically stable for R0<1. The model is fitted to data from Ghana.

Results

The model is found to exhibit a backward bifurcation and the endemic equilibrium point is globally stable when R0>1. Sensitivity analysis showed that the Buruli ulcer epidemic is highly influenced by the shedding and clearance rates of Mycobacterium ulcerans in the environment. The model is found to fit reasonably well to data from Ghana and projections on the future of the Buruli ulcer epidemic are also made.

Conclusions

The model reasonably fitted data from Ghana. The fitting process showed data that appeared to have reached a steady state and projections showed that the epidemic levels will remain the same for the projected time. The implications of the results to policy and future management of the disease are discussed.

Keywords: Buruli ulcer, Transmission dynamics, Basic reproduction number, Sensitivity analysis, Stability

Background

Buruli ulcer is caused by pathogenic bacterium where infection often leads to extensive destruction of skin and soft tissue through the formation of large ulcers usually on the legs or arms [28]. It is a devastating disease caused by Mycobacterium ulcerans. The ulcer is fast becoming a debilitating affliction in many countries [3]. It is named after a region called Buruli, near the Nile River in Uganda, where in 1961 the first large number of cases was reported. In Africa, close to 30,000 cases were reported between 2005 and 2010 [29]. Cote d’Ivoire, with the highest incidence, reported 2533 cases in 2010 [27]. This disease has dramatically emerged in several west African countries, such as Ghana, Cote d’Ivoire, Benin, and Togo in recent years [26].

The transmission mode of the ulcer is not well understood, however residence near an aquatic environment has been identified as a risk factor for the ulcer in Africa [6, 16, 25]. Transmission is thus likely to occur through contact with the environment [20]. Recent studies in West Africa have implicated aquatic bugs as transmission vectors for the ulcer [18, 24]. An attractive hypothesis for a possible mode of transmission to humans was proposed by Portaels et al. [22]: water-filtering hosts (fish, mollusks) concentrate the Mycobacterium ulcerans bacteria present in water or mud and discharge them again to this environment, where they are then ingested by aquatic predators such as beetles and water bugs. These insects, in turn, may transmit the disease to humans by biting [18]. Person to person transmission is less likely. Aquatic bugs are insects found throughout temperate and tropical environments with abundant freshwater. They prey, according to their size, on mollusks, snails, young fishes, and the adults and larvae of other insects that they capture with their raptorial front legs and bite with their rostrum. These insects can inflict painful bites on humans as well. In Ghana, where Buruli ulcer is endemic, the water bugs are present in swamps and rivers, where human activities such as farming, fishing, and bathing take place [18].

Research on Buruli ulcer has focused mainly on the socio-cultural aspects of the disease. The research recommends the need for Information, Education and Communication (IEC) intervention strategies, to encourage early case detection and treatment with the assumption that once people gain knowledge they will take the appropriate action to access treatment early [2]. IEC is defined as an approach which attempts to change or reinforce a set of behaviours to a targeted group regarding a problem. The IEC strategy is preventive in that it has a potential of enhancing control of the ulcer [5]. It is also important to note that Buruli ulcer is treatable with antibiotics. A combination of rifampin and streptomycin administered daily for 8 weeks has the potential to eliminate Mycobacterium ulcerans bacilli and promote healing without relapse.

Mathematical models have been used to model the transmission of many diseases globally. Many advances in the management of diseases have been born from mathematical modeling [11, 12, 14, 15]. Mathematical models can evaluate actual or potential control measures in the absence of experiments, see for instance [19]. To the best of our knowledge very few mathematical models have been formulated to analyse the transmission dynamics of Mycobacterium ulcerans. This could be largely due to the elusive epidemiology of the Buruli ulcer. Aidoo and Osei [3] proposed a mathematical model of the SIR-type in an endeavour to explain the transmission of Mycobacterium ulcerans and its dependence on arsenic. In this paper, we propose a model which takes into account the human population, water bugs as vectors and fish as potential reservoirs of Mycobacterium ulcerans following the transmission dynamics described in [8]. In addition we include the preventive control measures in a bid to capture the IEC strategy. Our main aim is to study the dynamics of the Buruli ulcer in the presence of a preventive control strategy, while emphasizing the role of the vector (water bugs) and fish and their interaction with the environment. The model is then validated using data from Ghana. This is crucial in informing policy and suggesting strategies for the control of the disease.

This paper is arranged as follows; in “Methods”, we formulate and establish the basic properties of the model. We also determine the steady states and analysed their stability. The results of this paper are given in “Results”. Parameter estimation, sensitivity analysis and the numerical results on the behavior of the model are also presented in this section. The paper is concluded in “Discussion”.

Methods

Model formulation

We consider a constant human population NH(t), the vector population of water bugs NV(t) and the fish population NF(t) at any time t. The total human population is divided into three epidemiological subclasses of those that are susceptible SH(t), the infected IH(t) and the recovered who are still immune RH(t). Total population of vector (water bug) at any time t is divided into two subclasses to susceptible water bugs SV(t) and those that are infectious and can transmit the Buruli ulcer to humans, IV(t). The total population reservoir of small fish is also divided into two compartments of susceptible fish SF(t) and infected fish IF(t). We also consider the role of the environment by introducing a compartment U,  representing the density of Mycobacterium ulcerans in the environment. We make the following basic assumptions:

  • Mycobacterium ulcerans are transferred only from vector ( water bug) to the humans.

  • There is homogeneity of human, water bug and fish populations’ interactions.

  • Infected humans recover and are temporarily immune, but lose immunity.

  • Fish are preyed on by the water bugs.

  • Unlike some bacterial infections such as leprosy (caused by Mycobacterium leprae) and tuberculosis (caused by Mycobacterium tuberculosis), which are characterized by person-to-person contact transmission, it is hypothesized that Mycobacterium ulcerans is acquired through environmental contact and direct person-to-person transmission is rare [20].

  • Susceptible host (human population) can be infected through biting by an infectious vector (water bug). We represent the effective biting rate that an infectious vector has to susceptible host as βH and the incidence of new infections transmitted by water bugs is expressed by standard incidence rate βHSHIVNH. One can interpret βH as a function of the biting frequency of the infected water bugs on humans, density of infectious water bugs per human, the probability that a bite will result in an infection and the efficacy of the IEC strategy. In particular we can set βH=(1-ϵ)ταβH, where ϵ(0,1) is the efficacy of the IEC strategy, τ the number of water bugs per human host, α the biting frequency (the biting rate of humans by a single water bug) and βH the probability that a bite by an infected vector to a susceptible human will produce an infection.

  • Susceptible water bugs are infected at a rate βVSVIFNV through predation of infected fish and ηvβVSVUK representing other sources in the environment. Here ηV differentiates the infectivity potential of the fish from that of the environment.

  • Assuming fish prey on infected water bugs, susceptible fish are infected at a rate βFSFIVNF through predation of infected fish and ηFβFSFUK representing infection through the environment. Here ηF is a modification parameter that models the relative infectivity of fish from that of the environment.

  • The vector population and the fish populations are assumed to be constant. The growth functions are respectively given by g(NV) and g(NF), where
    g(NV)=μVNVandg(NF)=μFNF.

    It is important to note that other types of functions can be chosen as growth functions. In this work we however assume that the growth functions are linear.

  • There is a proposed hypothesis that environmental mycobacteria in the bottoms of swamps may be mechanically concentrated by small water-filtering organisms such as microphagous fish, snails, mosquito larvae, small crustaceans, and protozoa [8]. We assume that fish increase the environmental concentrations of Mycobacterium ulcerans at a rate σF. Humans are are assumed not to shed any bacteria into the environment.

  • Aquatic bugs release bacteria into the environment at a rate σV.

  • The model does not include a potential route of direct contact with the bacterium in water.

  • The birth rate of the human population is directly proportional to the size of the human population.

  • The recovery of infected individuals is assumed to occur both spontaneously and through treatment. Research has shown that localized lesions may spontaneously heal but, without treatment, most cases of Buruli ulcer result in physical deformities that often lead to physiological abnormalities and stigmas [4].

We now describe briefly, the transmission dynamics of Buruli ulcer:

New susceptibles enter the population at a rate of μHNH. Buruli ulcer sufferers do not recover with permanent immunity, they loose immunity at a rate θ and become susceptible again. Susceptibles and infected through interaction with infected water bugs, with infection driven by water bugs biting susceptible humans. Once infected, individuals are allowed to recover either spontaneously or through antibiotic treatment at a rate γ. In this model, the human population is assumed to be constant over the modeling time with the birth and death rates being equal. The compartment SV tracks the changes in the susceptible water bugs population that are recruited at a rate μVNV. The infection of water bugs is driven by two processes: their interaction infected fish and with the environment. The natural mortality of the water bugs occurs at a rate μV. Similarly, the compartment SF tracks the changes in the susceptible fish population that are recruited at a rate μFNF. The infection of fish is also driven by two processes: their interaction infected water bugs and with the environment. Fish’s natural mortality rate is μF. The growth of Mycobacterium ulcerans in the environment is driven by their shedding by infected water bugs and fish into the environment. They are assumed to die naturally at a rate μE. The possible interrelations between humans, the water bug and fish are represented by the schematic diagram below (Fig. 1).

Fig. 1.

Fig. 1

Proposed transmission dynamics of the Buruli ulcer among humans, fish, water bugs and the environment (U)

The descriptions of the parameters that describe the flow rates between compartments are given in Table 1.

Table 1.

Description of parameters used in the model

Symbol Description
βH The effective contact rate between the vector and susceptible humans
βV The effective contact rate between fish and susceptible vectors
βF The effective contact rate between the susceptible fish and Mycobacterium ulcerans
γ The recovery rate of infected humans
θ The rate of loss of immunity of recovered humans
μH Natural mortality rate/birth rate of the human population
μV Natural mortality rate of the vector population
μF Natural mortality rate of the fish population
rV The growth rate of the vector population
rF The growth rate of the fish population
K The environmental carrying capacity of the bacteria population
σF Rate of shedding of Mycobacterium ulcerans into the environment by fish
σV Rate of shedding of Mycobacterium ulcerans into the environment by the water bugs
μE Rate at which Mycobacterium ulcerans are cleared from the environment

The dynamics of the ulcer can be described by the following set of nonlinear differential equations:

dSHdt=μHNH+θRH-βHSHIVNH-μHSH,dIHdt=βHSHIVNH-(μH+γ)IH,dRHdt=γIH-(μH+θ)RH,dSVdt=μVNV-βVSVIFNV-ηVβVSVUK-μVSV,dIVdt=βVSVIFNV+ηVβVSVUK-μVIV,dSFdt=μFNF-βFSFIVNF-ηFβFSFUK-μFSF,dIFdt=βFSFIVNF+ηFβFSFUK-μFIF,dUdt=σFIF+σVIV-μEU. 1

We assume that all the model parameters are positive and the initial conditions of the model system (1) are given by

SH(0)=SH0>0,IH(0)=IH00,RH(0)=RH0=0,SV(0)=SV0>0,IV(0)=IV00,SF(0)=SF0>0,IF(0)=IF00andU(0)=U0>0.

We arbitrarily scale the time t by the quantity 1μV by letting τ=μVt and introduce the following dimensionless parameters;

τ=μVt,βh=βHμV,μh=μHμV,θh=θμV,γh=γμV,m1=NHNV,m2=NFNV,m3=1m2,m4=NFK,m5=NVK,μf=μFμV,βf=βFμV,σf=σFμV,σv=σVμV,βv=βVμVandμe=μEμV.

can be non dimensionalised bySo, system (1) setting

sh=SHNH,ih=IHNH,rh=RHNH,iv=IVNV,sf=SFNF,if=IFNFandu=UK.

The forces of infection for humans, water bugs and fish are respectively

λH=βhm1iv,λV=βvm2if+ηVβvu,λF=βfm3iv+ηFβfu.

Given that the total number of bites made by the water bugs must equal the number of bites received by the humans, m1 is a constant, see [9]. Similarly m2 is constant and so is m3. We also note that since NF and NV are constants, m4 and m5 are constants.

Given that sh+ih+rh=1,sv+iv=1,sf+if=1 and 0u1, system (1) can be reduced to the following system of equations by conveniently maintaining the capitalised subscripts so that we can still respectively write sh,ih,iv,if and u as SH,IH,IV,IF and U.

dSHdτ=(μh+θh)(1-SH)-θhIH-λHSH,dIHdτ=λHSH-(μh+γh)IH,dIVdτ=λV(1-IV)-μvIV,dIFdτ=λF(1-IF)-μfIF,dUdτ=m4σfIF+m5σvIV-μeU. 2

Basic properties

Feasible region

Note that dUdτ=m4σfIF+m5σvIV-μeUm4σf+m5σv-μeU. Through integration we obtain Um4σf+m5σvμe. The feasible region (the region where the model makes biological sense) for the system (2) is in R+5 and is represented by the set

Ω=(SH,IH,IV,IF,U)R+5|0SH+IH1,0IV1,0IF1,0Um4σf+m5σvμe,

where the basic properties of local existence, uniqueness and continuity of solutions are valid for the Lipschitzian system (2). The populations described in this model are assumed to be constant over the modelling time. The solutions of system (2) starting in Ω remain in Ω for all t>0. Thus , Ω is positively invariant and it is sufficient to consider solutions in Ω.

Positivity of solutions

We desire to show that for any non-negative initial conditions of system (2), say (SH0,IH0,IV0,IF0,U0), the solutions remain non-negative for all τ[0,). We prove that all the state variables remain non-negative and the solutions of the system (2) with positive initial conditions will remain positive for all τ>0. We thus state the following lemma.

Lemma 1

Given that the initial conditions of system (2) are positive, the solutionsSH(τ),IH(τ),IV(τ),IF(τ)andU(τ)are non-negative for allτ>0.

Proof

Assume that

τ^=supτ>0:SH>0,IH>0,IV>0,IF>0,U>0(0,τ].

Thus τ^>0, and it follows directly from the first equation of the system (2) that

dSHdτ-(θh+λH)SH.

We thus have

dSHdtSH0exp-θht+0τλH(ς)dς.

Since the exponential function is always positive and SH0=SH(0)>0, the solution SH(τ) will thus be always positive.

From the second equation of (2),

dIHdτ-(μh+γh)IH,IHIH0e-(μh+γh)τ>0.

Similarly, it can be shown that IV(τ)>0,IF(τ)>0 and U(τ)>0 for all τ>0, and this completes the proof.

Steady states analysis

The disease free equilibrium

In this section, we solve for the equilibrium points by setting the right hand side of system (2) to zero. This direct calculation shows that system (2) always has a disease free equilibrium point

E0=(1,0,0,0,0).

We have the following result on the local stability of the disease free equilibrium.

Theorem 1

The disease free equilibriumE0whenever it exists, is locally asymptotically stable ifR0<1and unstable otherwise.

Proof

The Jacobian matrix of system (2) at the equilibrium point E0 is given by

JE0=-(μh+θh)-θh-m1βh000-(μh+γh)m1βh0000-1m2βvηvβv00m3βf-μfηfβf00m5σvm4σf-μe.

It can be seen that the eigenvalues of JE0 are -(μh+θh),-(μh+γh) and the solution of the characteristic polynomial

P(ϑ)=ϑ3+a2ϑ2+a1ϑ+μeμf(1-R0)=0,

where

a2=1+μe+μf,a1=μe+μf+μeμf-(βfβv+m4ηfσfβf+m5ηvσvβv)andR0=R01+R02+R03,

for

R01=m4ηfσfβfμeμf,R02=m5ηvσvβvμeandR03=βfβvμe+m3m4ηvσf+m2m5ηfσvμeμf.

The solutions of P(ϑ)=0 have negative real parts only if R0<1 following the use of the Routh Hurwitz Criterion. We can thus conclude that the disease free equilibrium is locally asymptotically stable whenever R0<1.

We note that R0 is the model system (2)’s reproduction number and does not depend on the human population size. The model reproduction number is a sum of three terms. The terms R01 and R02 represent the contribution of fish and water bugs respectively to the infection dynamics. The term R03, which is not very common in many epidemiological models, shows the combined contribution of the water bugs, fish and their shedding of Mycobacterium ulcerans into the environment. So, the infection is driven by the water bugs, fish and the density of the bacterium in the environment. The model reproduction number increases linearly with the shedding rates of the Mycobacterium ulcerans into the environment by fish and water bugs and the effective contact rates βf and βv. It decreases with increasing removal rates of the fish and Mycobacterium ulcerans. So the control of the ulcer depends largely on environmental management.

The endemic equilibrium

The endemic equilibrium is much more tedious to obtain. Given that λH=βhm1IV, from the first and second equations of system (2) we have

SH=11+AIVandIH=m1βhIV(μh+γh)(1+AIV),

where A=m1βh(μh+θh+γh)(μh+γh)(μh+θh).

The last equation of system (2) can be written as

U=ϑ1IF+ϑ2IV,whereϑ1=m4σfμeandϑ2=m5σvμe.

We thus have

λF=ϑ3IV+ϑ4IFandλV=ϑ5IV+ϑ6IF,

where ϑ3=βf(m3+ϑ2ηf),ϑ4=ϑ1βfηf,ϑ5=ϑ2ηvβvandϑ6=βv(m2+ϑ1ηv).

From the third and fourth equations of system (2)we have

IF=IV[1-ϑ5(1-IV)]ϑ6(1-IV), 3
IV=IF[μf-ϑ4(1-IF)]ϑ3(1-IF). 4

Substituting (3) into (4) we obtain IV=0 and the cubic equation

f(IV)=a3IV3+a2IV2+a1IV+a0=0, 5

where

a0=βfμfμeμem2+m4ηvσfR0-1,a1=ϑ4ϑ5(1+ϑ6)+ϑ5(ϑ4+ϑ3ϑ6)+ϑ3ϑ5ϑ6-[ϑ3ϑ6(1+ϑ6)+ϑ5(ϑ4ϑ5+μfϑ6)+ϑ4ϑ52],a2=(1+ϑ6)(ϑ4+ϑ3ϑ6)+ϑ5(ϑ4ϑ5+μfϑ6)+ϑ6(ϑ3ϑ6+μfϑ5)-[2ϑ4ϑ5(1+ϑ6)+ϑ6(ϑ3ϑ5+μf)],a3=-m5βfηvσvβv2μe2(μem2+m4ηvσf)m3+m2m5ηfσv<0.

Note that

a0>0ifR0>1<0ifR0<1.

Given that

f(IV)=3a3(IV)2+2a2λ1+a1, 6

the turning points of equation (5) are given by

(IV)1,2=-a2±a22-3a1a33a3. 7

The discriminant of solutions (7) is =a22-3a1a3. We now focus on the sign of the discriminant.

If <0, then f(IV) has no real turning points, which implies that f(IV) is a strictly monotonic function. The sign of f(λ1) is crucial in determining the monotonicity. Through completing the square, equation (6) can be written as

f(IV)=3a3IV+a23a32+19a32(3a1a3-a22). 8

Clearly if <0, then 3a1a3-a22>0. Since a3<0, then f(IV)<0. Thus f(IV) is a strictly monotone decreasing function. Note that limIVf(IV)=±. For f(0)=a0<0, the polynomial f(IV) has no positive real roots for R0<1,. However, if f(0)=a0>0 it has only one positive real root for R0>1, and consequently only one endemic equilibrium.

If =0, then f(IV) has only one real root with multiplicity two. This implies that (IV)1=(IV)2=-a23a3 and that f(IV)<0. Thus the polynomial f(IV) is a decreasing function. Given that f(IV)(-a23a3)=0, the turning point is a point of inflexion for f(IV). The polynomial f(IV) has only one endemic equilibrium.

For >0, we consider two cases; a1<0 and a1>0. If a1<0, then a1a3>0. This means that <a2. Irrespective of the sign of a2, f(IV) has two real positive and distinct roots. This implies that (5) has two positive turning points. If f(0)=a0>0 i.e R0>1 then, f(IV) has at least one positive real root, and hence at least one endemic equilibrium. On the other hand, if f(0)=a0<0 then, f(IV) has at most two positive real roots when R0<1, and hence at most two endemic equilibria.

If a1>0, then a1a3<0, which implies that >a2. For a2>0, f(IV) has two real roots of opposite signs. Since f(0)=a0>0 for R0>1, then, f(IV) has one positive root. For a2<0, f(IV) has two negative real roots. Since f(0)=a0<0 for R0<1, then, f(IV) has no positive real roots, and consequently no endemic equilibria.

Furthermore, we can use the Descartes’ Rule of Signs [7] to explore the existence of endemic equilibrium (or equilibria) for R0<1. We note the possible existence of backward bifurcation. The theorem below summarises the existence of endemic equilibria of the model system (2).

Theorem 2

The model system (2) has

  1. a unique endemic equilibrium point ifR0>1.

  2. has two endemic equilibria forR0c<R0<1whereR0cis the critical threshold below which no endemic equilibrium exists.

Remark The evaluation of R0c depends on the signs of a2 and a1 and the sign of the discriminant. The computations are algebraically involving and long and are not included here. Since the model system (2) possesses two endemic equilibria when R0c<R0<1, the model exhibits backward bifurcation for R0<1.

The consequence of the above remark is that bringing R0 below unity is not sufficient to eradicate the disease. For eradication, R0 must be brought below the critical value R0c.

Global stability of the endemic equilibrium

Theorem 3

The endemic equilibrium pointE1of system (2), is globally asymptotically stable.

Proof

The global stability of the endemic equilibrium, can be determined by constructing a Lyapunov function V(t) such that

V(t)=SH-SH-SHlnSHSH+AIH-IH-IHlnIHIH+BIV-IV-IVlnIVIV+CIF-IF-IFlnIFIF+DU-U-UlnUU. 9

The corresponding time derivative of V(t) is given by

V˙=1-SHSHS˙H+A1-IHIHI˙H+B1-IVIVI˙V+C1-IFIFI˙F+D1-UUU˙. 10

At the endemic equilibrium, we have the following relations

μh+θh=(μh+θh)SH+θhIH+m1βhSHIV,μh+γh=m1βhSHIVIH,1=m2βv1-IVIFIV+ηvβv1-IVUIV,μf=m3βf1-IFIVIF+ηfβf1-IFUIF,μe=m4σfIFU+m5σvIVU. 11

Evaluating the components of the time derivative of the Lyapunov function using the relations (11) we have

V˙=1-SHSH(μh+θh)SH1-SHSH+θhIH1-IHIH+m1βhSHIV1-SHIVSHIV+A1-IHIHm1βhSHIVSHIVSHIV-IHIH+B1-IVIVm2βvIFIFIF-IVIV+m2βvIFIV1-IFIF+ηvβvUUU-IVIV+ηvβvUIV1-UU+C1-IFIFηfβfUUU-IFIF+ηfβfUIF1-UU+m3βfIVIVIV-IFIF+m3βfIVIF1-IVIV+D1-UUm4σfIFIFIF-UU+m5σvIVIVIV-UU. 12

Let

v=SHSH,w=IHIH,x=IVIV,y=IFIFandz=UU. 13

Substituting (13) into (12), we obtain

V˙=-(μh+θh)SH(1-v)2v+H(v,w,x,y,z), 14

where

H=θhIH1-w-1v+wv+m1βhSHIV1-1v+x-xv+Am1βhSHIV1+xv-w-vxw+Bm2βvIF1+y-x-xy+Bm2βvIFIVx+y-xy-1+BηvβvU1+z-x-zx+BηvβvUIVx+z-xz-1+Cm3βfIV1+x-y-xy+Cm3βfIVIFy+x-xy-1+CηfβfU1+z-y-zy+CηfβfUIFy+z-yz-1+Dm4σfIF1+y-z-yz+Dm5σvIV1+x-z-xz. 15

Next, we choose ABC and D so that none of the variable terms of H are positive. It is important to group together the terms in H that involve the same state variable terms, as well as grouping all of the constant terms together. So we can show that H<0 by expanding (15), writing out the constant term and the coefficients of the variable terms such as v,w,x,y,z,1v,wv,xv and so on. The only variable terms that appear with positive coefficients are xy and z. We thus choose the Lyapunov coefficients so as to make the coefficients ofxy and z equal to zero. We have

A=1,B=m1βhSHIVm2βvIV(1-IF)+ηβvU(1-IV).

The coefficients C and D can similarly be evaluated from the coefficients of y and z. Note that expressions such as

m1βhSHIV2-1v-xvw

emanating from the substitution of the coefficients into H, are less than or equal to zero by the arithmetic mean-geometric mean inequality. This implies that H0 with equality only if SHSH=IHIH=IVIV=IFIF=UU=1.

Therefore, V˙0 and by the LaSalle’s Extension [17], it implies that the omega limit set of each solution lies in an invariant set contained in Ω. The only invariant set contained in Ω is the singleton E1. This shows that each solution which intersects R+5 limits to the endemic equilibrium. This completes the proof.

Results

Parameter estimation

The biggest challenge in epidemic modeling is the estimation of parameters in the model validation process. In this section we endeavour to estimate some of the parameter values of system (2). The demographic parameters can be easily estimated from census population data. We begin by estimating the mortality rate μh. We note that the average life expectancy of the human population in Ghana is 60 years [21]. This translates into μh=0.017 per year or equivalently 4.6×10-5 per day. Buruli ulcer is currently regarded as a vector borne disease. Recovery rates modelled by γh, of vector borne diseases range from 1.6×10-5 to 0.5 per day [23]. This translates to an average of between 0.00584 and 183 per year. The rate of loss of immunity θh for vector borne diseases range between 0 and 1.1×10-2 per day[23]. The mortality rate of the water bugs is assumed to be 0.15 per day [3]. The rates per day can easily be transferred to yearly rates.

In this model we shall assume that we have more water bugs than humans so that m1<1. Since the water bugs prey on the fish, a reasonable food chain structure leads to the assumption that we have more fish than water bugs hence m2>1 and consequently 0<m3<1. If the water bug is assumed to interact more with the environment than fish then ηv>1 and 0<ηf<1. The natural mortality of small fish in rivers is not well documented and data on the mortality of river fish in Ghana is not available. For the purpose of our simulations, we shall assume that 3×10-3<μf<7×10-3 per day. Given that KNF,NV we have 0m4,m51. We shall also assume that 0σf,σv1. We summarise the parameters in the following Table 2.

Table 2.

Parameter values used for the simulations and sensitivity analysis

Parameter Value/range Source
μh 4.5×10-5 [21]
γh 1.6×10-5-0.5 [23]
θh 0-1.1×10-2 [23]
m1,m2 m1<1,m2>1 Estimated
m3,m4,m5 (0,1) Estimated
βh,βf,βv (0,1) Estimated
ηv (1,5) Estimated
ηf (0, 1) Estimated
σf,σv (0,1) Estimated
μf 3×10-3-7×10-3 Estimated
μe (0,1) Estimated

Sensitivity analysis

Many of the parameters used in this paper are not determined experimentally. Therefore their accuracy is always in doubt. This can be overcome by observing responses of such parameters and their influence on the model variables through sensitivity and uncertainty analysis. In this subsection we present the sensitivity analysis of the model parameters to ascertain the degree to which the parameters affect the outputs of the model. We use the Partial Correlation Coefficients (PRCCs) analysis to determine the sensitivity of our model to each of the parameters used in the model. Through correlations, the association of the parameters and state variables can be established. In our case, we determine the correlation of our parameters and the state variable U. Alongside the PRCCs are the statistical significance test p-values for each of the parameters. If the magnitude of the PRCC value of a parameter is greater than 0.5 or less than −0.5 and the p-value less than 0.05, then the model is sensitive to the parameter. On the other hand, PRCC values close to +1 or -1 indicate that the parameter strongly influences the state variable output. The sign of a PRCC value indicates the qualitative relationship between the parameter and the output variable. A negative sign indicates that the parameter is inversely proportional to the outcome measure [10]. The parameters with negative PRCCs reduce the severity of Burili ulcer disease while those with positive PRCCs aggravate it. Using Latin Hypercube Sampling (LHS) scheme with 1000 simulations for each run, with U as the outcome variable. Our results show that the variable U is sensitive to the changes in the parameters m3,ηf,μe,μf and βf. The results are shown in Fig. 2.

Fig. 2.

Fig. 2

PRCC plots: The variable U largely depends on m3,ηf,μe,μf and βf. The bars pointing to the left indicate that U has an inverse dependence on the respective parameters. We observe that the parameters m3,ηf and βf aggravate the disease when they are increased while μf and μe reduce its severity when increased

The results from the PRCC analysis are summarized in Table 3. The significant parameters together with their PRCC values and p-values have been encircled.

Table 3.

Outputs from PRCC analysis

graphic file with name 13104_2015_1619_Tab3_HTML.jpg

In Fig. 3 the residuals for the ranked Latin Hypercube Sampling parameter values are plotted against the residuals for the ranked density of Mycobacterium ulcerans.The PRCC plots for parameters βf,μf,μe and ηf show a strong linear correlation. The growth of Mycobacterium ulcerans increases as the number of infected fish that eventually shed bacteria into the environment increases. An increase in the parameters μf and μe leads a decrease in amount of bacteria in the environment.

Fig. 3.

Fig. 3

PRCC plots shows the PRCC plots for the parameters βf, μf, μe, ηf and m3

Data and the fitting process

One of the most important steps in the model building chronology is model validation. We now focus on the data provided by the Ashanti Regional Disease Control Office for Buruli ulcer cases in Ghana per 10,0000 people. The data are given in the Table 4 below for the years 2003–2012.

Table 4.

Data on Buruli ulcer cases in Ghana

Year 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012
Buruli ulcer cases 739 1159 1201 1096 1136 1300 1158 1428 1324 1292

Source [13]

We fit the model system (2) to the data of Buruli ulcer cases expressed as fractions. We use the least squares curve fit routine (lsqcurvefit) in Matlab with optimisation to estimate the parameter values. Many parameters are known to lie within limits. A few parameters such as the demographic parameters are known [13] and it is thus important to estimate the others. The process of estimating the parameters aims at finding the best concordance between computed and observed data. One tedious way to do it is by trial and error or by the use of software programs designed to find parameters that give the best fit. Here, the fitting process involves the use of the least squares-curve fitting method. Matlab code is used where unknown parameter values are given a lower and upper bound from which the set of parameter values that produce the best fit are obtained.

Figure 4 shows how system (2) fits to the available data on the incidence of the BU. The incidence solution curve shows a very reasonable fit to the data.

Fig. 4.

Fig. 4

Model fit to data. Model system (2) fitted to data of Burili ulcer cases in Ghana. The circles indicate the actual data and the solid line indicates the model fit to the data. The parameter values used for the fitting; μh=0.000045,θ=0.1,m1=5,βh=0.1,γ=0.056,m2=10,βv=0.000065,ηv=1.5,ηf=0.6,μV=0.15,βf=0.00005,μf=0.05,σf=0.05,σv=0.006,μe=0.4

In planning for a long term response to the Buruli ulcer epidemic, it is important to have some reasonable projections to the epidemic. The fitting process allows us to envisage the Buruli ulcer epidemic in future. it is important to note that the projections are reasonably good over a short period of time since the current is evolving gradually based on the available data. We chose to project the epidemic beyond 5 years to 2017. Figure 5 show the projected Buruli ulcer epidemic.

Fig. 5.

Fig. 5

Projected model fit. Projection to fit in Fig. 4

Figures 6 and 7 show the changes in the prevalence of infected humans respectively when σf, the shedding rate of Mycobacterium ulcerans in the environment and μe the removal rate of MU from the environment, are varied. Based on the sensitivity analysis, our model is very sensitive to the shedding rate of Mycobacterium ulcerans into the environment. Figure 6 shows that an increase in the shedding rate will lead increased human infections. We can actually quantify the related increases. For instance, if σf is increased from 0.51 to 0.52 on year 15, the percentage increase in the prevalence of human infections is 6 %. Minimising Mycobacterium ulceransin the environment is an important control measure that is, albeit impractical at the moment. We observe through our results that their decrease in the environment can lead to quantifiable changes in the prevalence of infected humans. Increasing μe leads to a decrease in the prevalence of infected humans.

Fig. 6.

Fig. 6

Prevalence of Buruli ulcer infection in humans. Shows prevalence humans when σf is varied

Fig. 7.

Fig. 7

Prevalence of Buruli ulcer in infected humans for different values of μe. Shows prevalence the infected humans when μe is varied

Discussion

In this paper, a deterministic model on the dynamics of the Buruli ulcer in the presence of a preventive intervention strategy is presented. The model’s steady states are determined and their stabilities investigated in terms of the classic threshold R0. In disease transmission modelling, it is well known that a classical necessary condition for disease eradication is that the basic reproductive number R0, must be less than unity. The model has multiple endemic equilibria (in fact it exhibits a backward bifurcation). When a backward bifurcation occurs, endemic equilibria coexist with the disease free equilibrium for R0<1. This means that getting the classic threshold R0 less than 1, might not be sufficient to eliminate the disease. Thus the existence of backward bifurcation has important public health implications. This might explain why the disease has persisted in the human population over time. The endemic equilibrium is found to be globally stable if R0>1.

The sensitivity analysis of model parameters showed some interesting results. These results suggest that efforts to remove Mycobacterium ulcerans and infected fish from the environment will greatly reduce the epidemic although the latter will be impracticable. This is because of the costs involved and the fact that many governments in affected areas operate on lean budgets.

The model is then fitted to data on the Buruli ulcer in Ghana. The model reasonably fits the data. The challenge in the fitting process was that the data appears to indicate that Buruli ulcer has reached a steady state. This then produced some parameter values that appeared unreasonable. Despite these challenges, the fit produced reasonable projections on the future of the ulcer. The model shows that in the near future, the number of cases will not change if everything remains the same. An important consideration that can be added to the model is the inclusion of probable policy shifts and the investigation of different scenarios on the progression of the epidemic as the policies change. Because not much of the disease is understood, parameter estimation was a daunting task. So we had to reasonably estimate some of the parameter using the hypothesis that Buruli ulcer is a vector borne disease. Due to the estimation of essential parameters sensitivity analysis was necessary and very important to determine how these parameters influence the model. The implications of varying some of the important epidemiological parameters such as the shedding rates were investigated. Important results were drawn through Figs. 6 and 7. The main result of this paper is that the management of Buruli ulcer depends mostly on the management of the environment.

Conclusions

This model can be improved by considering social interventions in the human population, modeled as functions and the inclusion of the different forms of treatment available as some individuals opt for traditional methods while others depend on the government health care system [1]. Social interventions include education, awareness, poverty reduction and provision of social services. While the mathematical representations of these interventions are insurmountable, they are vital to the dynamics of the disease and public health policy designs. Finally this model can be used to suggest the type of data that should be collected as research on the Buruli ulcer intensifies. The global burden of the disease and its epidemiology are not well understood, [28]. Clearly, gaps do exist in the nature and type of data available. Reports on the disease are often based on passive presentations of patients at health care facilities. As a result of the difficulties of accessing health care in affected areas, data on the disease is scanty.

Authors’ contributions

FN designed the model and carried out the numerical simulations. EB did the mathematical analysis and writing of the manuscript. Both authors read and approved the final manuscript.

Acknowledgements

The first author acknowledges with gratitude the support from the Stellenbosch University, International office for the research visit that culminated into this manuscript. The second author acknowledge, with thanks, the support of the Department of Mathematics and Statistics, Kumasi Polytechnic.

Competing interests

The authors declare that they have no competing interests.

Contributor Information

Farai Nyabadza, Email: nyabadzaf@sun.ac.za.

Ebenezer Bonyah, Email: ebbonya@yahoo.com.

References

  • 1.Agbenorku P, Donwi IK, Kuadzi P, Saunderson P. Buruli Ulcer: treatment challenges at three centres in Ghana. J Trop Med. 2012 doi: 10.1155/2012/371915. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 2.Ahorlu CK, Koka E, Yeboah-Manu D, Lamptey I, Ampadu E. Enhancing Buruli ulcer control in Ghana through social interventions: a case study from the Obom sub-district. BMC Public Health. 2013;13:59. doi: 10.1186/1471-2458-13-59. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Aidoo AY, OSei B. Prevalence of acquatic insects and arsenic concentration determine the geographical distribution of Mycobacterium ulcerans infection. Comput Math Method Med. 2007;8:235–244. doi: 10.1080/17486700701695167. [DOI] [Google Scholar]
  • 4.Boleira M, Lupi O, Lehman L, Asiedu KB, Kiszewski Ana Elisa. Buruli ulcer. Anais Brasileiros de Dermatologia. 2010;85(3):281–301. doi: 10.1590/S0365-05962010000300002. [DOI] [PubMed] [Google Scholar]
  • 5.Clift E. IEC interventions for health: a 20 year retrospective on dichotomies and directions. Int J Health Commun. 1998;3(4):367–375. doi: 10.1080/108107398127166. [DOI] [PubMed] [Google Scholar]
  • 6.Debacker M, Portaels F, Aguiar J, Steunou C, Zinsou C, Meyers W, et al. Risk factors for Buruli ulcer, Benin. Emerg Infect Dis. 2006;12:1325–1331. doi: 10.3201/eid1209.050598. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Descartes’ Rule of Signs, Available at: http://www.purplemath.com/modules/drofsign.htm, Acessed 2 Sept 2013.
  • 8.Eddyani M, Ofori-Adjei D, Teugels G, De Weirdt D, Boakye D, Meyers WM, Portaels F. Potential role for fish in transmission of Mycobacterium ulcerans disease (Buruli Ulcer): an environmental study. Appl Environ Microbiol. 2004;5679–81. [DOI] [PMC free article] [PubMed]
  • 9.Garba SM, Gumel AB, Abu Bakar MR. Backward bifurcaytion in dengue transmission dynamics. Math Biosci. 2008;215:11–25. doi: 10.1016/j.mbs.2008.05.002. [DOI] [PubMed] [Google Scholar]
  • 10.Gomero B. Latin Hypercube Sampling and Partial Rank Correlation Coefficient analysis applied to an optimal control problem, MSc Thesis, The University of Tennessee. 2012.
  • 11.Grassly NC, Fraser C. Mathematical models of infectious disease transmission. Nat Rev Microbiol. 2008;6:477–487. doi: 10.1038/nrmicro1845. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Grundmann H, Hellriegel B. Mathematical modelling: a tool for hospital infection control. Lancet Infect Dis. 2005;6(1):39–45. doi: 10.1016/S1473-3099(05)70325-X. [DOI] [PubMed] [Google Scholar]
  • 13.Ghana Statistical Service, Available at: http://www.statsghana.gov.gh. Accessed Sept 2013.
  • 14.Houben RM, Dowdy DW, Vassall A, et al. How can mathematical models advance tuberculosis control in high HIV prevalence settings? Int J Tuber Lung Dis. 2014;18(5):509–514. doi: 10.5588/ijtld.13.0773. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Huppert A, Katriel G. Mathematical modelling and prediction in infectious disease epidemiology. Clin Microbiol Infect. 2013;19:999–1005. doi: 10.1111/1469-0691.12308. [DOI] [PubMed] [Google Scholar]
  • 16.Jacobsen KH, Padgett JJ. Risk factors for Mycobacterium ulcerans infection. Int J Infect Dis. 2010;14(8):e677–e681. doi: 10.1016/j.ijid.2009.11.013. [DOI] [PubMed] [Google Scholar]
  • 17.LaSalle JP. The stability of dynamical systems. In: CBMS-NSF Regional Conference Series in Applied Mathematics 25, SIAM: Philadelphia. 1976.
  • 18.Marsollier L, Robert R, Aubry J, Andre JS, Kouakou H, Legras P, Manceau A, Mahaza C, Carbonnelle B. Aquatic insects as a vector for Mycobacterium ulcerans. Appl Environ Microbiol. 2002;68:4623–4628. doi: 10.1128/AEM.68.9.4623-4628.2002. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Marty R, Roze S, Bresse X, Largeron N, Smith-Palmer J. Estimating the clinical benefits of vaccinating boys and girls against HPV-related diseases in Europe. BMC Cancer. 2013 doi: 10.1186/1471-2407-13-10. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Merritt RW, Walker ED, Small PLC, Wallace JR, Johnson PDR, et al. Ecology and transmission of buruli ulcer disease: a systematic review. PLoS Neglect Trop Dis. 2010;4(12):e911. doi: 10.1371/journal.pntd.0000911. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Population and Housing Census National Analytical Report, 2012. http://www.statsghana.gov.gh.
  • 22.Portaels F, Chemlal K, Elsen P, Johnson PD, Hayman JA, Hibble J, Kirkwood R, Meyers WM. Mycobacterium ulcerans in wild animals. Revue Scientifique et Technique. 2001;20:252–264. doi: 10.20506/rst.20.1.1270. [DOI] [PubMed] [Google Scholar]
  • 23.Rascalou G, Pontier D, Menu F, Gourbie‘re S. Emergence and prevalence of human vector-borne diseases in sink vector populations. PLoS One. 2012;7(5):e36858. doi: 10.1371/journal.pone.0036858. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 24.Silva MT, Portaels F, Pedrosa J. Aquatic insects and Mycobacterium ulcerans: an association relevant to buruli ulcer control? PLoS Med. 2007;4(2):e63. doi: 10.1371/journal.pmed.0040063. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Sopoh GE, Barogui YT, Johnson RC, Dossou AD, Makoutode M. Family relationship, water contact and occurrence of Buruli ulcer in Benin. PLoS Neglect Trop Dis. 2010;4(7):e746.. doi: 10.1371/journal.pntd.0000746. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Stienstra Y, van der Graaf WTA, Asamoa K, van der Werf TS. Beliefs and attitudes toward buruli ulcer in Ghana. Am J Trop Med Hyg. 2002;67:207–213. doi: 10.4269/ajtmh.2002.67.207. [DOI] [PubMed] [Google Scholar]
  • 27.Williamson HR, Benbow ME, Campbell LP, Johnson CR, Sopoh G, Barogui Y, Merritt RW, Small PLC. Detection of Mycobacterium ulcerans in the environment predicts prevalence of buruli ulcer in Benin, PLoS Neglect Trop Dis. 2012; e1506. [DOI] [PMC free article] [PubMed]
  • 28.World Health Organization. Buruli ulcer Mycobacterium ulcerans infection, http://www.who.int/buruli/en/.
  • 29.World Health Organization. Buruli ulcer: Number of new cases of Buruli ulcer reported (per year). http://apps.who.int/neglected_diseases/ntddata/buruli/buruli.html.

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