
Citation: Long-xing Qi, Yanwu Tang, Shou-jing Tian. Parameter estimation of modeling schistosomiasis transmission for four provinces in China[J]. Mathematical Biosciences and Engineering, 2019, 16(2): 1005-1020. doi: 10.3934/mbe.2019047
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Schistosomiasis is one of the major parasitic diseases in China, which has caused serious damage in our country. Although the founding of new China made great achievements for the investigation and prevention work of the schistosomiasis epidemiology, schistosomiasis is still a serious public health problem in parts of China at present. Anhui, Jiangxi, Hubei and Jiangsu, as the focus endemic provinces of schistosomiasis in China, have reached the criterion of basic elimination of schistosomiasis after long-term prevention. However, due to the society, natural environment and other factors, schistosomiasis in those provinces has some recovery and rebound.
Anhui province is located in the downstream of Yangtze and Huaihe River in North China, and schistosomiasis epidemic is more serious. The schistosomiasis endemic areas are mainly distributed on both sides of the Yangtze River, in the mountain areas of South Anhui province and beside the Lake Gaoyou ([22]).
In Jiangxi province, after years' effort of prevention and treatment, the epidemic situation is still serious, and schistosomiasis control task is still arduous. The reasons are that the screw area of Poyang Lake region is vast, the epidemic factors are complex, and the sources of infection have not been well controlled ([4]). Schistosomiasis in Hubei province has been prevalent for at least 2100 years, and has been effectively controlled after many years of large-scale prevention and control ([3]).
In Jiangsu province, the epidemic situation of schistosomiasis has been effectively controlled because of the large-scale prevention carried on since the fifties of the 20th century. However, Jiangsu province is located in the lower reaches of the Yangtze River, the flood and other natural factors have caused rebound of schistosomiasis endemic in the whole province ([20]).
At present, the prevention and control work in the four provinces are at different stages, and the measures of the implementation of prevention and control work in different provinces should be adapted to local conditions to achieve different objectives. The Epidemic situations of schistosomiasis in the four provinces are affected by varying natural environmental factors. For example, the influence of lake and marshland along the Yangtze River on prevention and control work is stronger than the influence of the surround area and the lower reaches. Hence, the reversal of schistosomiasis endemic should not be ignored. In summary, it requires a rather long period to completely reach the goal of eliminating schistosomiasis Yangtze River beach areas in China.
The prevalence rate of humans, the infection rate of snails, the changes of snail density of different monitoring sites in the four provinces from 2005 to 2010 are shown as follows (Figure 1-3).
The green, red, black, and blue lines in Figure 1-3 represent the change trajectories of some relevant factors in Anhui, Jiangxi, Hubei, Jiangsu province, respectively. Figure 1-3 indicate the trajectories of the prevalence rate of humans, the infection rate of snails and the snail density of monitoring sites in four provinces in 2005-2010, respectively.
The main purpose of this paper is combining monitoring data with mathematical model to estimate some transmission rates and then to discuss these differences on the dynamic behavior of schistosomiasis in different four provinces.
Mathematical model can describe the actual transmission process of schistosomiasis, and has been regarded as a powerful tool to explore the complex relationship in the process of the transmission of schistosomiasis for a long time. In spite that the values of the parameters in mathematical model change with place and times, their meaning in physiology, biology and society behalf are always the same. Macdonald had improved the famous Ross malaria model and proposed the first schistosomiasis deterministic differential equation model, namely Macdonald model in the 1950s ([11]). The model laid the foundation for the subsequent mathematical model of schistosomiasis transmission dynamics, and put forward the concept of "basic reproduction number", which is still widely used today for a wide variety of diseases. An advantage of Macdonald model is that it can make the direct reflection of the influence of the average worm burden on snail infection rate, and even on the whole transmission process. However, the average worm burden is not easy to investigate and estimate in practice. In 1966, based on Macdonald's model, Barbour replaced the change rate of worm burden with the change rate that reflects the prevalence rate of definitive host ([1]). The advantage of this model is that as long as the prevalence rate of local human host, the inflected snail prevalence, the density of human host and snails are known, we can estimate the related factors of schistosomiasis and the values of related parameters through the model, and therefore manage to do some further analysis and computation of prevalence rate ([9]).
Using Barbour's model and the concept of the basic reproduction number R0, Wu revealed clearly the characteristics and the inherent spread rules of schistosomiasis ([19]), predicted and evaluated the effect of various prevention and control measures of schistosomiasis. The main parameters in this model, a and b are difficult to quantify, as it's also difficult to investigate and collect them and be directly used to calculate the basic reproduction number nowadays. The two parameters could only be estimated indirectly through the equilibrium prevalence rate or the equilibrium state of the disease spread. This shows that some design of parameters in this model still need to be further improved. Furthermore, the prediction and evaluation in theory must be combined with practice, tested and corrected by practice. Gao had studied the characteristics of schistosomiasis transmission in Xingzi County, Jiujiang City Liao Nan Xiang, Jiangxi Province using Barbour's model to calculate the basic reproduction number ([7]). This research is carried out in a closed village, but villages are always connected with each other in actual situation, and human host and snails will move between the neighboring villages.
Here, motivated by the Gao's paper we study the transmission of schistosomiasis by monitoring data and Barbour's model in four provinces. Because variables in Barbour's model can be monitored in practice, and the previous work has confirmed that it is consistent with the dynamic behavior of schistosomiasis transmission, we choose Barbour's model. In 1965, Barbour established two differential equations based on Ross malaria model, reflecting the change rates of prevalence rate of human host and the infection rate of snails, respectively, and designed the related parameters. The corresponding model is as following ([19]):
{dPdt=aΔy(1−P)−gP,dydt=b(ΣΔ)P(1−y)−μy. | (2.1) |
The parameters are described as follows:
a -the incidence rate of people at unit density of infected snails
Δ -the density of snails
y -the proportion of infected snails
b -the rate at which an infected people causes snail infections
P -the prevalence rate of infection in people population
g -the recovery rate for people infections
Σ -the density of population
μ -per capita death rate of infected snails
Both human host and snails are divided into infected (P and y) and uninfected (1−P and 1−y) in (2.1). The population and snail populations were assumed to be constant closed systems, in which the birth and death rates are equal. The mortality rate of human host is very small and is negligible in the system, and the dead are compensated by the same amount of newborn snails at any time so that the death of uninfected snails is also omitted in the equation. In addition, it is easy to see from the equations that, the difference of P, y, Δ and Σ will result in different values of a, b.
Based on its biological meanings the basic reproduction number can be defined by
R0=abΣgμ. |
In the above formula, infectious definitive hosts with density Σ can cause bΣ snail infections in their lifetimes 1g. These snails can infect abΣgμ definitive hosts in their lifetimes 1μ. This formula gives the total number of second offspring of infectious human infected by infectious snails during their lifetimes in susceptible human populations.
In our previous work, the stability analysis of the system (2.1) has been completed ([12]). The results show that schistosomiasis transmission will gradually disappear if R0<1. When R0>1, the spread of disease will continue until to a certain level of balance. That means the ultimate goal of disease control is to make the basic reproduction number less than 1 through the influence of the relevant parameters, and then to make the transmission disappear finally. In [12], numerical simulation did not performed because there was no data at that time. In the paper, based on monitoring data parameter estimation and simulation will be carried out.
From the formula, we can see parameters a and b are key to calculate the basic reproduction number R0. However, to obtain the values of a and b is not easy. Ross had used R′0 instead of R0.
R′0=1(1−¯y)(1−¯P). |
When the spread develops to a certain stage, the local epidemic can be seen as steady state. At this time, the prevalence of infection in humans and snails can be think as the equilibrium values in the system (2.1). Hence, the prevalence rate of humans (¯P) and the infection rate of snails (¯y) are as following
¯P=(abΣ−μg)ΔbΣ(g+aΔ),¯y=abΣ−μga(bΣ+μΔ). |
The values of these two prevalence can obtained from the monitoring data. Then R′0 can be calculated by ¯P and ¯y.
Remark: In fact, from the formula of R′0, it is obvious that R′0 is certainly greater than 1. It's impossible to make R′0 smaller than 1 because the prevalence rate of humans and snails ¯P and ¯y are both positive number. This result does not conform with the actual situation. The existence of patients does not necessarily mean that schistosomiasis will continue. Especially in the situation of no-mass transmission, the basic reproduction number R′0 may not explain the actual phenomenon quite well.
According to the calculation method in the reference ([19]), the basic reproduction number R′0 and the key parameters a and b can be obtained. From the national monitoring sites in Anhui, Jiangxi, Hubei, Jiangsu provinces ([2,4,20,22]), the values of ¯P, ¯y and Δ can be obtained. In order to obtain the values of the combined parameters a and b, we get the data of the population density (Σ) of in Anhui, Jiangxi, Hubei, Jiangsu provinces from related references, which are, respectively, 4.35 people /m2, 0.1 people /m2, 127 people /m2, 1.09 people /m2 ([3,8,10,18,20]). The average infection duration of humans is 4 years (g=11460=0.00068) and that of snails is of 6 months (μ=0.0055) ([14,19]). Then the basic reproduction number and values of a and b are listed in the following Table 1, 2, 3, 4.
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0074 | 0.0018 | 14.9 | 1.0093 | 0.00019 | 0.004591 |
2006 | 0.0070 | 0.0023 | 22.1 | 1.0094 | 0.00009 | 0.040026 |
2007 | 0.0061 | 0.0025 | 6.7 | 1.0087 | 0.00025 | 0.003481 |
2008 | 0.0054 | 0.0016 | 7.7 | 1.0070 | 0.00030 | 0.002890 |
2009 | 0.0051 | 0.0014 | 12.2 | 1.0065 | 0.00020 | 0.004240 |
2010 | 0.0048 | 0.0023 | 12.7 | 1.0071 | 0.00011 | 0.007712 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0503 | 0.0025 | 14.4 | 1.0556 | 0.00100 | 0.039472 |
2006 | 0.0309 | 0.0033 | 8.1 | 1.0353 | 0.00089 | 0.047748 |
2007 | 0.0158 | 0.0010 | 7.1 | 1.0171 | 0.00153 | 0.024869 |
2008 | 0.0115 | 0.0047 | 3.2 | 1.0164 | 0.00052 | 0.073124 |
2009 | 0.0053 | 0.0026 | 2.5 | 1.0079 | 0.00056 | 0.067487 |
2010 | 0.0068 | 0.0009 | 1.8 | 1.0078 | 0.00295 | 0.0127782 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0171 | 0.0030 | 7.7 | 1.0204 | 0.000514 | 0.005754 |
2006 | 0.0191 | 0.0017 | 6.1 | 1.0212 | 0.001277 | 0.002356 |
2007 | 0.0145 | 0.0018 | 4.0 | 1.0165 | 0.001395 | 0.002147 |
2008 | 0.0110 | 0.0027 | 2.5 | 1.0134 | 0.001333 | 0.002238 |
2009 | 0.0103 | 0.0014 | 2.7 | 1.0118 | 0.001914 | 0.001556 |
2010 | 0.0090 | 0.0060 | 3.0 | 1.0097 | 0.003548 | 0.000838 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0022 | 0.0026 | 5.7 | 1.0048 | 0.000101 | 0.034199 |
2006 | 0.0014 | 0.0067 | 5.5 | 1.0082 | 0.000026 | 0.134183 |
2007 | 0.0009 | 0.0036 | 6.1 | 1.0045 | 0.001038 | 0.123566 |
2008 | 0.0010 | 0.0013 | 3.2 | 1.0023 | 0.000017 | 0.020756 |
2009 | 0.0001 | 0.0010 | 4.0 | 1.0011 | 0.000017 | 0.200016 |
2010 | 0.0020 | 0.0000 | 4.5 | 1.0020 | – | 0.00000 |
Through the calculation and analysis of the transmission dynamics, the epidemic characteristics of schistosomiasis and the epidemic characteristics of different endemic areas are revealed. The basic reproduction numbers of the monitoring sites in the four provinces are relatively low and are between 1 to 1.1. This means that one patient in the whole transmission process can spread and produce one or more new patients. In the four provinces schistosomiasis will continue to spread and may develop into local disease. In additional, from the four tables, we can see that the basic reproduction numbers of Jiangxi and Hubei are greater than that of Anhui and Jiangsu. In summary, the continuous monitoring results of six years show that schistosomiasis has been effectively controlled in those provinces through the implementation of effective prevention strategies and measures. However, it still need to strengthen the monitoring of external infection sources and comprehensive management to further reduce schistosomiasis endemic level.
Note that in the first method the basic reproduction number R′0 is calculated firstly, and then the value of a and b is calculated by R′0. If we want to obtain the value of the basic reproduction number R0, we need to get the values of parameters a and b firstly. Using the method of noise measurement and data smoothing in [15], the follows are to estimate new values of parameter a and b based on the mathematical model (2.1) and monitoring data in four provinces. Then the basic reproduction number R0 are obtained from the new values of a and b. Summarize the results in Table 5.
Province | a | b | R0 |
Anhui | 0.000098 | 0.005524 | 0.6307 |
Jiangxi | 0.000369 | 0.037184 | 0.3667 |
Hubei | 0.0018036 | 0.000337 | 0.2046 |
Jiangsu | 0.0000103 | 0.059264 | 0.1781 |
In the following four figures (Figure 4, 5, 6, 7), the blue points represent the real data, the green trajectories represent the paths of P and y with the values of a and b obtained by the first method in 2005, and the red trajectories represent the paths of P and y by parameter estimation method.
It's clear to see that the curves by parameter estimation method fit the monitoring data in four provinces better than that by the first method. We also found an interesting phenomenon. That is all the values of the basic reproduction number R0 in the four provinces are smaller than 1. This is in contradiction with the results by the first method, where the basic reproduction number R′0 is always greater than 1. This is because R′0 is calculated by the prevalence rate of humans (¯P) and infection rate of snails (¯y). Furthermore, the prevalence rate of humans and the infection rate of snails are between the 0.1%-10.0% in the actual situation. Thus the value of R′0 is in the range of 1.0−1.1.
In order to predict the future trend of schistosomiasis transmission in those four provinces after 2010, we carry out some numerical simulations about prevalence of humans and snails by using the new values of a and b in the above section.
From Figure 8, 9, 10, 11, we can see all the prevalence of human and snails in four provinces eventually tend to be 0. It may indicate that schistosomiasis in the four provinces will eventually be eliminated, but the premise is that the current standards of prevention and control must be maintained or improved. In addition, from these figures, we can see that the four provinces to eliminate schistosomiasis probably take a different time. For Anhui and Jiangxi province, it takes about 50 and 30 years to eradicate schistosomiasis patients and infectious snails, respectively. For Hubei province, no patients need to take about 25 years and no infectious snails need to take about 15 years. For Jiangsu province, it needs about 25 and 10 years to have no patients and infectious snails, respectively.
In fact, based on the new data from Anhui Provincial Institute of Schistosomiasis Control in 2011-2016 ([4,5,6]), we can find the control effect of schistosomiasis is better than expected due to the strengthening of local control policies (Figure 12).
Comparison of the two methods, the reasons for different results may have two aspects. Firstly, in some areas the spread of schistosomiasis has been significantly inhibited due to the implementation of control measures. At present, there are some patients and disease snails. This does not mean that schistosomiasis will continue to go on. Hence, we cannot say the basic reproduction number must be greater than 1. Secondly, it is also possible that, there are other new thresholds for schistosomiasis transmission expect for the threshold condition R0=1. For example, some backward bifurcations occur in many disease transmission. In one of our work, a backward bifurcation can happen in a schistosomiasis model with multiple infection ([13]). When R0<1, the disease is still in the spread. In this case, to control the spread of schistosomiasis the value of R0 must be less than a new threshold.
In addition, from the figures above, it can be seen that there is a little gap between the simulation of the infection rate of snails and the data, and the prevalence rate of humans is in good agreement. This is mainly because the infection rate of snails is affected by natural factors (such as floods and climate), biological factors (snails diffusion), human factors (the artificial transplanting of reed and poplar) and other factors. For example, in the flood year of Anhui Province, the annual average increase of the recovery areas of snails and the areas of snails are as much as 2.56 times and 2.16 times of that in a normal year ([21]). Hence, more careful consideration of these factors in the model is the direction of our work in the future.
The authors are very grateful to anonymous referees for their valuable comments and suggestions which lead to an improvement of their original manuscript. This research is supported by National Natural Science Foundation of China (11401002, 11771001), Natural Science Fund for Colleges and Universities in Anhui Province (KJ2018A0029) and Teaching Research Project of Anhui University (ZLTS2016065).
The authors declared that they have no conflicts of interest to this work.
[1] | A. D. Barbour, Modelling the transmission of schistosomiasis: an introductory view, Am. J. Trop. Med. Hyg., 55 (1996), 135–143. |
[2] | Y. Y. Chen, S. X. Cai, J. B. Liu, X. B. Huang, Z. M. Su, Z. W. Tu, X. W. Shan, G. Li, Assessment of schistosomiasis endemic situation in national monitoring sites in Hubei Province from 2005 to 2010 (in Chinese), Chin. J. Schisto. Control, 26 (2014), 260–264. |
[3] | Y. Y. Chen, Spatial endemic situation and forecast for schistosomiasis in Hubei Province (in Chinese), Ph.D thesis Huadong University in China, 2014. |
[4] | Z. Chen, X. N. Gu, S. B. LV, Y. F. Li, W. S. Jiang, C. Q. Hang, J. Ge, D. D. Lin, Endemic situation of schistosomiasis in the national monitoring sites in Jiangxi Province from 2005 to 2014 (in Chinese). J. Trop. Dis. Parasitol. 13 (2015), 193–196. |
[5] | F. H. Gao, S. Q. Zhang, T. P. Wang, J. C. He, X. J. Xu, T. T. Li, G. H. Zhang, H. Wang, Endemic status of schistosomiasis in Anhui Province in 2015(in Chinese), J. Trop. Dis. Parasitol., 14 (2016), 137–140. |
[6] | F. H. Gao, S. Q. Zhang, T. P. Wang, J. C. He, X. J. Xu, T. T. Li, G. H. Zhang, H. Wang, Endemic status of schistosomiasis in Anhui Province in 2016(in Chinese), J. Trop. Dis. Parasitol., 15 (2017), 125–130. |
[7] | S. J. Gao, Y. Y. He, Y. J. Liu, G. J. Yang, X. N. Zhou, Field transmission intensity of Schistosoma japonicum measured by basic reproduction ratio from modified Barbour's model, Parasites Vector, 6 (2013), 141–151. |
[8] | X. N. Gu, C. Q. Hang, H. G. Chen, S. B. Lv, Z. Chen, J. Sun, The analysis of national monitoring results of schistosomiasis in Jiangxi in 2005 (in Chinese), J. Trop. Dis. Parasitology, 4 (2006), 202–204. |
[9] | Y. P. Li, Y. B. Zhou, Q. W. Jiang, Progress of research on mathematical model for transmission of schistosomiasis (in Chinese), Chin. J. Schisto. Control, 21 (2009), 568–571. |
[10] | D. D. Lin, X. N. Gu, Z. Chen, X. J. Zeng, H. Y. Liu, Z. J. Li, W. S. Jiang, S. B. Lv, Z. L. Gao, H. G, Chen, Assessment and analysis of risks of realizing schistosomiasis transmission control in Jiangxi Province (in Chinese), Chin. J. Schisto. Control, 25 (2013), 348–366. |
[11] | G. Macdonald, The dynamics of helminth infections, with special reference to schistosomes, Trans. R. Soc. Trop. Med. Hyg, 59 (1965), 489–506. |
[12] | L. X. Qi, J. A. Cui, Qualitative analysis for Barbour's schistosomiasis model with diffusion, J. Biomath., 27 (2012), 54–64. |
[13] | L. X. Qi, S. J. Tian, J. A. Cui, T. P. Wang, Multiple infection leads to backward bifurcation for a schistosomiasis model, Math. Biosci. Eng., in press. |
[14] | L. X. Qi, M. Xue, J. A. Cui, Q. Z. Wang, T. P. Wang, Schistosomiasis transmission model and its control in Anhui province, B. Math. Biol., 80 (2018), 2435–2451. |
[15] | J. O. Ramsay, G. Hooker, D. Campbell, J. Cao, Parameter estimation for differential equations: a generalized smoothing approach, J. R. Statist. Soc. B, 69 (2007), 741–796. |
[16] | L. D. Wang, The key to the control of schistosomiasis in China is good management of livestock manure (in Chinese), Chin. J. Epidemiol., 26 (2005), 929–930. |
[17] | L. D.Wang, H. G. Chen, J. G. Guo, X. J. Zeng, X. L. Hong, J. J. Xiong, X. H.Wu, X. H.Wang, L. Y.Wang, G. Xia, Y. Hao, D. P. Chin, X. N. Zhou, A strategy to control transmission of Schistosoma japonicum in China, N. Engl. J. Med., 360 (2009), 121–128. |
[18] | T. P.Wang, F. Zhao, S. Q. Zhang, Z. J. Zhang, F. H. Gao, Y. B. Zhou, J. C. He, Q.W. Jiang, Spatial temporal clustering analysis of schistosomiasis in Anhui from 2000 to 2008 (in Chinese), J. Trop. Dis. Parasitol., 9 (2011), 127–130. |
[19] | K. C. Wu, Mathematical model and transmission dynamics of schistosomiasis and its application (in Chinese), China Trop. Med., 5 (2005), 837–843. |
[20] | K. Yang, G. J. Yang, Q. B. Hong, Y. X. Huang, L. P. Sun, Y. Gao, Y. Gao, L. H. Zhang, J. B. Yang, H. R. Zhu, Y. S. Liang, Monitoring of schistosomiasis in Jiangsu Province, China, 2005-2010 (in Chinese), Chin. J. Schisto. Control, 24 (2012), 527–532. |
[21] | S. Q. Zhang, T. P.Wang, J. H. Ge, C. G. Tao, G. H. Zhang, D. B. Lv, W. Z.Wu, Q. Z.Wang, Influence on the diffusion of snail by flooding in Anhui province (in Chinese), J. Trop. Dis. Parasitol., 2 (2004), 90–93. |
[22] | S. Q. Zhang, F. H. Gao, J. C. He, G. H. Zhang, H. Wang, T. P. Wang, Trend analysis of schistosomiasis endemic situation in Anhui Province from 2004 to 2014 (in Chinese), Chin. J. Schisto. Control, 27 (2015), 235–240. |
1. | Ursula Panzner, Transmission Modelling for Human Non-Zoonotic Schistosomiasis Incorporating Vaccination: Guiding Decision- and Policymaking, 2024, 4, 2673-6772, 101, 10.3390/parasitologia4020010 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0074 | 0.0018 | 14.9 | 1.0093 | 0.00019 | 0.004591 |
2006 | 0.0070 | 0.0023 | 22.1 | 1.0094 | 0.00009 | 0.040026 |
2007 | 0.0061 | 0.0025 | 6.7 | 1.0087 | 0.00025 | 0.003481 |
2008 | 0.0054 | 0.0016 | 7.7 | 1.0070 | 0.00030 | 0.002890 |
2009 | 0.0051 | 0.0014 | 12.2 | 1.0065 | 0.00020 | 0.004240 |
2010 | 0.0048 | 0.0023 | 12.7 | 1.0071 | 0.00011 | 0.007712 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0503 | 0.0025 | 14.4 | 1.0556 | 0.00100 | 0.039472 |
2006 | 0.0309 | 0.0033 | 8.1 | 1.0353 | 0.00089 | 0.047748 |
2007 | 0.0158 | 0.0010 | 7.1 | 1.0171 | 0.00153 | 0.024869 |
2008 | 0.0115 | 0.0047 | 3.2 | 1.0164 | 0.00052 | 0.073124 |
2009 | 0.0053 | 0.0026 | 2.5 | 1.0079 | 0.00056 | 0.067487 |
2010 | 0.0068 | 0.0009 | 1.8 | 1.0078 | 0.00295 | 0.0127782 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0171 | 0.0030 | 7.7 | 1.0204 | 0.000514 | 0.005754 |
2006 | 0.0191 | 0.0017 | 6.1 | 1.0212 | 0.001277 | 0.002356 |
2007 | 0.0145 | 0.0018 | 4.0 | 1.0165 | 0.001395 | 0.002147 |
2008 | 0.0110 | 0.0027 | 2.5 | 1.0134 | 0.001333 | 0.002238 |
2009 | 0.0103 | 0.0014 | 2.7 | 1.0118 | 0.001914 | 0.001556 |
2010 | 0.0090 | 0.0060 | 3.0 | 1.0097 | 0.003548 | 0.000838 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0022 | 0.0026 | 5.7 | 1.0048 | 0.000101 | 0.034199 |
2006 | 0.0014 | 0.0067 | 5.5 | 1.0082 | 0.000026 | 0.134183 |
2007 | 0.0009 | 0.0036 | 6.1 | 1.0045 | 0.001038 | 0.123566 |
2008 | 0.0010 | 0.0013 | 3.2 | 1.0023 | 0.000017 | 0.020756 |
2009 | 0.0001 | 0.0010 | 4.0 | 1.0011 | 0.000017 | 0.200016 |
2010 | 0.0020 | 0.0000 | 4.5 | 1.0020 | – | 0.00000 |
Province | a | b | R0 |
Anhui | 0.000098 | 0.005524 | 0.6307 |
Jiangxi | 0.000369 | 0.037184 | 0.3667 |
Hubei | 0.0018036 | 0.000337 | 0.2046 |
Jiangsu | 0.0000103 | 0.059264 | 0.1781 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0074 | 0.0018 | 14.9 | 1.0093 | 0.00019 | 0.004591 |
2006 | 0.0070 | 0.0023 | 22.1 | 1.0094 | 0.00009 | 0.040026 |
2007 | 0.0061 | 0.0025 | 6.7 | 1.0087 | 0.00025 | 0.003481 |
2008 | 0.0054 | 0.0016 | 7.7 | 1.0070 | 0.00030 | 0.002890 |
2009 | 0.0051 | 0.0014 | 12.2 | 1.0065 | 0.00020 | 0.004240 |
2010 | 0.0048 | 0.0023 | 12.7 | 1.0071 | 0.00011 | 0.007712 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0503 | 0.0025 | 14.4 | 1.0556 | 0.00100 | 0.039472 |
2006 | 0.0309 | 0.0033 | 8.1 | 1.0353 | 0.00089 | 0.047748 |
2007 | 0.0158 | 0.0010 | 7.1 | 1.0171 | 0.00153 | 0.024869 |
2008 | 0.0115 | 0.0047 | 3.2 | 1.0164 | 0.00052 | 0.073124 |
2009 | 0.0053 | 0.0026 | 2.5 | 1.0079 | 0.00056 | 0.067487 |
2010 | 0.0068 | 0.0009 | 1.8 | 1.0078 | 0.00295 | 0.0127782 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0171 | 0.0030 | 7.7 | 1.0204 | 0.000514 | 0.005754 |
2006 | 0.0191 | 0.0017 | 6.1 | 1.0212 | 0.001277 | 0.002356 |
2007 | 0.0145 | 0.0018 | 4.0 | 1.0165 | 0.001395 | 0.002147 |
2008 | 0.0110 | 0.0027 | 2.5 | 1.0134 | 0.001333 | 0.002238 |
2009 | 0.0103 | 0.0014 | 2.7 | 1.0118 | 0.001914 | 0.001556 |
2010 | 0.0090 | 0.0060 | 3.0 | 1.0097 | 0.003548 | 0.000838 |
Year | ¯P | ¯y | Δ | R′0 | a | b |
2005 | 0.0022 | 0.0026 | 5.7 | 1.0048 | 0.000101 | 0.034199 |
2006 | 0.0014 | 0.0067 | 5.5 | 1.0082 | 0.000026 | 0.134183 |
2007 | 0.0009 | 0.0036 | 6.1 | 1.0045 | 0.001038 | 0.123566 |
2008 | 0.0010 | 0.0013 | 3.2 | 1.0023 | 0.000017 | 0.020756 |
2009 | 0.0001 | 0.0010 | 4.0 | 1.0011 | 0.000017 | 0.200016 |
2010 | 0.0020 | 0.0000 | 4.5 | 1.0020 | – | 0.00000 |
Province | a | b | R0 |
Anhui | 0.000098 | 0.005524 | 0.6307 |
Jiangxi | 0.000369 | 0.037184 | 0.3667 |
Hubei | 0.0018036 | 0.000337 | 0.2046 |
Jiangsu | 0.0000103 | 0.059264 | 0.1781 |