Malaria Research and Treatment
Volume 2017 (2017), Article ID 7820454, 8 pages
https://doi.org/10.1155/2017/7820454

Research Article

A Weather-Based Prediction Model of Malaria Prevalence in Amenfi West District, Ghana

Esther Love Darkoh,¹ John Aseidu Larbi,¹ and Eric Adjei Lawer²

¹Department of Theoretical and Applied Biology, College of Science, Kwame Nkrumah University of Science and Technology, Kumasi, Ghana
²Department of Biodiversity Conservation and Management, Faculty of Natural Resources and Environment, University for Development Studies, Nyankpala Campus, Tamale, Ghana

Correspondence should be addressed to Esther Love Darkoh; amamaamekyedarkoh@gmail.com

Received 14 October 2016; Accepted 15 January 2017; Published 31 January 2017

Academic Editor: Robert Novak

Copyright © 2017 Esther Love Darkoh et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

This study investigated the effects of climatic variables, particularly, rainfall and temperature, on malaria incidence using time series analysis. Our preliminary analysis revealed that malaria incidence in the study area decreased at about 0.35% annually. Also, the month of November recorded approximately 21% more malaria cases than the other months while September had a decreased effect of about 14%. The forecast model developed for this investigation indicated that mean minimum () and maximum () monthly temperatures lagged at three months were significant predictors of malaria incidence while rainfall was not. Diagnostic tests using Ljung-Box and ARCH-LM tests revealed that the model developed was adequate for forecasting. Forecast values for 2016 to 2020 generated by our model suggest a possible future decline in malaria incidence. This goes to suggest that intervention strategies put in place by some nongovernmental and governmental agencies to combat the disease are effective and thus should be encouraged and routinely monitored to yield more desirable outcomes.

1. Introduction

Malaria transmission predominantly occurs in tropical and subtropical areas where Anopheles mosquitoes can survive and multiply. Vectors of the disease are geographically specific. Currently, there are 104 malaria endemic countries and approximately half the world’s population are at risk of infection [1]. Though malaria has been successfully eliminated in temperate regions of the world, the disease is on the rise in Africa [2]. In Ghana, malaria is a principal public health problem which plagues all segments of the society [3]. As a result, the government in line with the Millennium Development Goals implemented a national malaria control program (NMCP) to help reduce malaria morbidity and mortality. It is important to note that malaria vector control interventions using long lasting insecticide treated nets (LLINs) and indoor residual spraying (IRS) have been promoted in the country since 1998 and 2006, respectively. However, due to some challenges encountered with the previous intervention (i.e., 1998-LLIN), the country started a door-to-door distribution and hang up campaign in 2010 (i.e., 05/2010–10/2012) through the NMCP [4]. To maintain universal coverage, it again pioneered a mixed model distribution mechanism using antenatal care, schools, and work places among others in 2013.

Generally, environmental factors have contributed significantly to malaria prevalence and thereby affected its distribution, seasonality, and transmission intensity [5]. Although several other factors account for its occurrence and incidence, the disease seems to have a significant association with climatic variables [6]. Malaria has been identified as the most climate sensitive disease [7]; hence changes in temperature, rainfall, and humidity due to climatic change are expected to influence malaria prevalence directly (modifying the behavior and geographical distribution of malaria vectors as well as changing the length of the cycle of the parasite) and indirectly (changing ecological relationships important to the organisms).

Several studies have attempted to predict epidemics by use of climatic variables that are predictors of malaria transmission potential. In spite of this, little consensus has emerged about the relative importance and predictive value of different factors [8–10]. For instance, Kassa and Beyene [11] found an increase in malaria cases during heavy rainfall while other years with excessive rainfall accounted for reduced malaria incidences. In Ghana, malaria prevalence is affected by flooding and warmer temperatures which cause about seven months of intense malaria transmission beginning in April/May to September [12]. Mbogo et al. [13] also found variation in the relationship between mosquito population and rainfall in different districts of Kenya and attributed these changes to environmental heterogeneity. In addition, Thomson et al. [14] indicated that malaria occurrence was influenced by rainfall and temperature while Ndiaye et al. [15] found a very high correlation between malaria mortality and rainfall but no impact from temperature or humidity.

According to Christiansen-Jucht et al. [16], temperature and precipitation alter vector biting rate, duration of their gonotrophic cycles, fecundity, and development of immature mosquitoes and adults. It has been shown that the development of Anopheles gambiae is strongly impeded at low temperatures and as such its larvae stops development below 16°C and dies at a temperature below 14°C [17]. Thus, for adult mosquitoes, the rate at which they feed on human blood is determined by ambient temperature. Human blood fed on by mosquitoes every 4 days at 17°C consequently speeds up parasite sporogonic development leading to an increased transmission efficacy [16, 17]. Plasmodium species are also sensitive to temperature such that parasites-inhabiting female mosquito is reduced when external temperature is high (above 34°C). In spite of this, the effect of temperature is greatest on transmission at lower (i.e., 17–21°C) temperature [17].

Knowledge of the dynamic structure underlying data collected at regular time intervals (i.e., time series data) can be useful in generating forecasts through modeling. This can be achieved either by self-projecting or cause-effect modeling techniques [18]. Self-projecting approaches produce predictions using only time series data of the activity to be forecasted while the latter relies on relationships between the time series to be forecasted and one or more series that influence it. Several models for forecasting time series data have been developed (e.g., exponential, ARIMA, GARCH, and artificial intelligence) and applied to diverse fields of study including medicine over the past decades [19]. Available literature on malaria forecasting shows that quite a large number of studies rely on the cause-effect approach where covariates such as temperature, vegetation (NDVI), and/or rainfall among others are included in malaria models [20–24]. Nonetheless, forecasts generated using any of these stochastic models (i.e., time series analysis) can play significant roles in disease management or control strategies. Therefore, understanding the impact of climatic variables on malaria prevalence is important for effective policy and management decisions locally and globally. Hence, this study seeks to employ a time series analysis model to predict malaria incidence in the Amenfi West District of Ghana using weather (i.e., rainfall and temperature) as exogenous inputs.

2. Materials and Methods

2.1. Study Area

The study was carried out at Asankrangwa Catholic Hospital in the Amenfi West District of the Western Region, Ghana (Figure 1). It is the largest health facility (district hospital) serving both as the first consultation point and as a referral centre for about 13 health care facilities in the district. This hospital was chosen since most of the 13 health care facilities are community clinics and lack laboratory services as well as past records of confirmed malaria cases from 2002 to 2015. The district’s geographical coordinates are 5°48′18′′N and 2°26′25′′. It is characterized by a bimodal rainfall regime, with the major season occurring from March to July and the minor season from September to mid-December. A dry spell is experienced between late December and February [25].

Figure 1: Map of Ghana showing study area in Amenfi West District.

2.2. Data Collection

Monthly data of confirmed malaria cases as well as rainfall and temperature from 2002 to 2015 were obtained from the district hospital and the meteorological office, respectively. Until 2010, detection of malaria parasites in the study area during the period under consideration was done microscopically on stained thick and thin blood smears. However, for the remainder of the period, detection of malaria in the health facility was done using both Rapid Diagnostic Tests (RDT) and microscopy.

2.3. Data Analysis

A preliminary analysis was first conducted on the dataset to describe and investigate the nature of the trend characterizing the number of malaria cases in the district. In order to determine the trend, linear, quadratic, log-linear, and log-quadratic regression models were fitted and compared. Afterwards, monthly changes in the number of malaria cases were estimated using the selected time trend and a set of seasonal dummy variables (i.e., seasonal categories based on months). The intercept was not included in the model to avoid dummy variable trap. To show differential effects in terms of percentage change, Halvorsen and Palmquist [26] method of interpreting differential coefficients in semilogarithmic equations was used (i.e., , where is the coefficient of the dummy variable). The subsections below provide information on statistical approaches used for subsequent analyses in this research.

2.3.1. Time Series Modeling

In this study, an autoregressive integrated moving average (ARIMA) approach popularly referred to as Box-Jenkins methodology was employed for modeling malaria incidence. The model takes into account past values of the data, prediction errors, and a random term [27]. Specifically, an ARIMAX model which is an extension of ARIMA modeling was employed. This model uses exogenous inputs which consist of external variables (predictors) to help explain the behavior of a dependent variable. Thus, time series of malaria incidence can be explained by predictor variables such as rainfall and/or temperature. Since malaria incidence is influenced by seasonality, monthly number of malaria cases will show periodic or cyclic patterns. Thus, an ARIMA model may be unable to capture such seasonal behavior. Hence, a seasonal ARIMA (SARIMA) model was proposed for use in this study. The general equation of the SARIMAX model denoted by ARIMAX which is an extension of the nonseasonal ARIMA can be written as

where is the observation of a time series at time t; A is a time series of white noise observations; B is the delay operator; that is, ; is the differentiating operator; that is, ; , respectively, represent the mean and parameter vectors of the autoregressive and moving average terms; is the seasonal autoregressive polynomial; is the seasonal moving average polynomial; and are the regressors’ coefficients.

2.3.2. Model Selection, Diagnostics, and Forecast Errors

Diagnostic tests on the developed models were done using Ljung-Box and ARCH-LM tests. The Ljung-Box test was performed to determine whether model residuals were random and independent over time (i.e., no serial correlation) while the ARCH-LM test was employed to check for homoscedasticity of model residuals (i.e., if variances are constant over time). In order to evaluate the performance of the final model, measures of forecast error such as Mean Percent Error (MPE), Mean Absolute Error (MAE), Root Mean Square Error (RMSE), Mean Absolute Percent Error (MAPE), and Mean Absolute Scaled Error (MASE) were computed. For each forecast error estimated lower values are preferred. Mathematical details of the aforementioned statistics and how they are computed are provided elsewhere [28–32]. All analyses were performed using Gretl and R statistical software, specifically “forecast” package. The choice of model (either ARIMAX or SARIMAX) was automatically estimated and selected using information criteria approaches (i.e., Bayesian information criterion—BIC).

3. Results

3.1. Preliminary Analysis

Descriptive statistics of malaria incidence/cases, rainfall, and temperature (minimum, maximum, and average) recorded for the study area are presented in Table 1. Minimum and maximum values of malaria cases observed during the period of investigation were 192.00 and 2112.00, respectively. Rainfall had minimum and maximum values of 0.00 mm and 1022.20 mm while that of average temperature was 23.50°C and 31.00°C, respectively.

Table 1: Descriptive statistics of study variables.

Variable
Mean
Minimum
Maximum
CV (%)

Malaria incidence
809.800
192.000
2112.000
45.730

Rainfall
60.820
0.000
1022.200
181.640

Min. temperature
25.455
20.900
31.000
5.950

Max. temperature
29.549
25.500
32.900
5.660

Avg. temperature
27.507
23.500
31.000
5.090

Min. = minimum, max. = maximum, and avg. = average.

Time series plots of data (malaria, rainfall, and temperature) gathered for the research are shown in Figures 2 and 3. The series plot of rainfall revealed that the amount of rains was constant over time with some heavy downpours observed in late 2007 and early 2008. Interestingly, a cursory examination of Figure 1 showed that high rainfall values within that period did not result in increased malaria incidence instantly. Both rainfall and temperature plots exhibited cyclic/periodic patterns which is an indication of seasonal dependency.

(a)

(b)

Figure 2: Time series plot—malaria cases showing the LLIN intervention in May 2010 (a) and rainfall data (b).

(a)

(b)

(c)

Figure 3: Time series plot of temperature ((a) min.; (b) max.; and (c) avg.).

Figure 4 shows forecasts generated using data before the 2010 LLIN intervention based on an model. From the figure, the preintervention forecast indicates a high malaria incidence rate compared to the actual/observed values after the LLIN intervention in the study area.

Figure 4: Plot of preintervention forecast compared to observed malaria cases.

An investigation of the nature of the trend characterizing malaria incidence was subsequently performed and the results are presented in Table 2. Based on the selection criteria, a log-linear trend model was suitable for malaria incidence, thus confirming the slightly increasing trend observed in the time series plot. In order to investigate the effect of seasonality, the logarithmic transformed malaria incidence was regressed on the linear trend and seasonal dummies. The results indicate that the model is significant at the 5% significance level (-statistic = 3130, value = 0.00; -square = 99.62%; and adjusted -square = 99.95%). To quantify the monthly changes, the transformed malaria incidence data was first differenced and again regressed on the trend and seasonal dummy variables (Table 3). From Table 3, it can be seen that malaria incidence at the study area decreased at about 0.35% per year. Also, the month of November has approximately 21% more malaria cases than the others suggesting that it is the month in which the highest number of malaria cases occurs. The least number of malaria cases occurs in the month of September with a decreased effect of about 14%.

Table 2: Trend analysis of malaria incidence.

Model
AIC
AICC
BIC

Linear
1967.043
2445.953
2455.178

Quadratic
1981.416
2460.326
2469.551

Log-linear
−287.694
191.215
200.441

Log-quadratic
−286.082
192.827
202.053

: means best model based on selection criteria.

Table 3: Estimates of log first differenced series with monthly effects.

Variable
Coefficient
Standard error
Percent effect

January
0.04697
0.10828
4.80884

February
0.11713
0.10439
12.42660

March
−0.00834
0.10437
−0.83026

April
−0.13063
0.10435
−12.24537

May
0.08189
0.10435
8.53359

June
0.00370
0.10434
0.37096

July
−0.00751
0.10434
−0.74837

August
−0.08839
0.10434
−8.45940

September
−0.14806
0.10435
−13.76162

October
0.02261
0.10435
2.28687

November
0.18997
0.10437
20.92168

December
−0.13216
0.10439
−12.37984

Trend
−0.00351
0.00754
−0.35082

Note. Effect of January = .

3.2. Time Series Analysis of Malaria Incidence

Following the time series analysis procedure outlined in the previous section, an ARIMA model was selected for modeling malaria incidence in the study area. The predictors included in the final model were minimum and maximum temperatures lagged at three months since the effect of rainfall () was not significant. Thus, the forecast model includes maximum and minimum temperature in the current month and the two months before that. Parameter estimates of the final model are provided in Table 4. From the table, a unit rise in maximum temperature in a given month will result in an associated increase of malaria cases three months later. On the other hand, a unit rise in minimum temperature will lead to a decline of malaria cases three months later. Figures 5 and 6 show plots of the original time series with the forecasted values based on the developed ARIMAX model. It can be observed that both the in-sample and the out-of-sample forecasts fitted the observed/actual values quite well. Forecast errors of the developed model based on the in-sample and out-of-sample forecasts are given in Table 5.

Table 4: Parameter estimates of the developed model.

Parameter
Estimate
Std. error
-statistic
value

ar1 ()
0.41283
0.15768
2.61820
0.00884

ma1 ()
−0.85977
0.11499
−7.47670
0.00000

Max. temperature
0.07599
0.02579
2.94650
0.00321

Min. temperature
−0.06653
0.02843
−2.34010
0.01928

Table 5: Estimated forecast errors for the developed model.

Variable
ME
MSE
MAPE
RMSE
MAE
Theil’s

Training set
0.00966
0.09953
3.48070
0.31548
0.22677
0.90767

Test set
−0.08955
0.35334
8.09080
0.59442
0.50688
0.91227

Figure 5: Plot of in-sample forecasts compared to training set data.

Figure 6: Plot of out-of-sample forecasts compared to the test set.

The results indicate that all forecast error values estimated were low and that the model was accurate since MAPE values for both training and test sets were less than 10%. Subsequently, the model was diagnosed using the statistics provided in Table 6. The Ljung-Box test yielded a value of 0.7799 indicating that the model was free from serial correlation while the ARCH-LM () test revealed that model residuals were homoscedastic.

Table 6: Diagnostic tests on model residuals.

Method
df
Chi-square
value

Ljung-Box test
24
18.46500
0.77990

ARCH-LM test
24
34.45800
0.07685

A forecast plot generated by the model from 2016 to 2020 is shown in Figure 7. Point forecasts (predicted values) revealed that malaria incidence will fluctuate around 200 patients per month with an upper 95% prediction interval (PI) ranging from 400 to 1400 patients for the forecast period (85% PI: 306–875 patients). Thus, compared to past malaria incidence (2002–2015), both upper PIs (80% and 95%) show a nonincreasing trend in malaria incidence for the forecast period considered (i.e., observed/past min. and max. values were 192.0 and 2112.0 cases, resp.). However, minimum values (i.e., lower PIs) of malaria cases forecasted for the study area were 65 and 105 patients per month based on 95% and 80% PI, respectively.

Figure 7: Forecast of malaria Incidence (i.e., based on back-transformed output) with 80% and 95% prediction intervals (PI).

4. Discussion

According to Jaffar et al. [33], peak in morbidity and mortality of malaria is generally obtained in the rainy season. This rise could be attributed to higher levels of parasitaemia in the rainy season than in the dry season as was reported by Greenwood and Pickering [34]. Similarly, our findings indicated that the highest monthly effect in terms of malaria incidence occurred in the rainy season (i.e., major season, May = ~9%; minor season, November = ~21%). Generally, onset of the two rainy seasons did not result in substantial growths in recorded malaria cases until after the second month specifically, in the third. This is corroborated by Alemu et al. [6] who asserted that climatic factors may not have instantaneous effects on malaria incidence rather they may have lagged effects. This may be because of delayed oviposition by the female mosquito due to heavy or erratic rainfall [35] common to the study area, as moderate rainfall and heat produce suitable habitat for oviposition [36, 37].

Furthermore, the findings of this study which are consistent with others (e.g., [38]) suggest that rainfall (even when lagged) did not significantly influence the predictive ability of the forecast model developed for the study area. Contrarily, other works have revealed a strong positive association between incidence of malaria and rainfall [6, 11, 15]. Unarguably, though rainfall creates breeding sites for mosquitoes [15], we believe that excessive amounts may destroy their breeding grounds, thereby causing reduced numbers of disease vectors as was reported elsewhere [39, 40]. Also, the general lack of consistency in weather variables especially rainfall in predicting malaria incidence could be attributed to complex interactions (i.e., between weather variables and disease transmission) that affect vector recruitment, abundance and survival, and parasite maturation [10]. These interactions as well as lagged effects could possibly explain the high incidence observed in the month of February (~12%) after the end of the minor rainy season in mid-December.

Some studies have reported the importance of temperature in malaria transmission or prediction models [41, 42]. Basically, research has shown that there is a nonlinear relationship between extrinsic incubation period (EIP) and temperature. EIP is very temperature sensitive in that small changes in the latter may result in significantly large effects on malaria transmission. Thus, as temperature increases, mosquitoes become infectious quickly due to a shortened EIP and vice versa [43–46]. Hence, the, respectively, negative and positive association of minimum and maximum temperatures with malaria incidence is somewhat suggestive of the nonlinear relationship between the two variables (i.e., temperature and malaria) as mentioned earlier. Teklehaimanot et al. [10] noted that, at low temperatures, complete development of mosquitoes at larval and pupal stages was delayed. In addition, Beck-Johnson et al. [47] revealed that recruitment dynamics (age structure) of mosquitoes were temperature dependent and thus exhibited a nonlinear behavior. Even though their study revealed that abundance was the largest across the 20–30°C temperature range, it mostly peaked around mid-20°C. Although the decline in abundance was not significantly large, they recorded lower numbers when temperatures were approaching 20°C and lower. Also, they reported a decrease in longevity of mosquitoes at temperatures above 32°C. Essentially, the significance of both minimum and maximum monthly temperatures in our predictive models could be attributed to the consistency of these values falling within the range suitable for a viable sexual cycle of the parasite in the mosquito. We can also safely infer that increased temperature at optimum make mosquitoes feed on blood meal at shorter intervals [46] possibly due to accelerated digestion [17] and biting rates [48], thus influencing malaria transmission.

A number of studies have documented some potential predictors of malaria such as population growth [49], economic hardship [2], and poor environmental sanitation and housing conditions [50]. For instance, high temperatures may cause people to sleep outside or inside their rooms without covering themselves, thereby increasing the risk of mosquito bite at night [39] because of problems attributed to finance or housing conditions. Moreover, due to variation in incubation period among Plasmodium species, it may be possible that species responded differently to the extent of temperature in the study area [51]. Hence, we do not neglect all these probable limitations and the impacts they could have had on our findings. Nonetheless, our forecast of malaria incidence till 2020 suggests a future decline in malaria cases compared to previously reported years. Also, the number of malaria cases following the 2010 intervention decreased compared to the preintervention forecast. Our findings further suggested that malaria incidence in the study area decreased annually at approximately 0.35% over the past years. This is undoubtedly due to the effective intervention strategies put in place by the country’s NMCP to combat the disease over the years [52].

5. Conclusion

The findings of this study present a clear association of temperature and malaria incidence and how malaria cases are likely to reduce in the future based on our forecast model. We, however, cannot ignore the fact that other contributory factors may modulate malaria prevalence in the study district. Hence, it is recommended that future works on malaria incidence in the district should incorporate population size, intervention strategies, and vegetation (NDVI) among others to help improve its predictive accuracy. Also, various ongoing interventions such as sleeping in insecticide treated nets (i.e., LLINs), proper drainage systems, and sanitation practices should be continued/encouraged to help curb the disease.

Competing Interests

The authors declare that there are no competing interests.

Acknowledgments

The authors would like to extend their heartiest appreciation to Asankrangwa Catholic Hospital for providing data on malaria infection and to the Western Regional Meteorological Agency of Ghana for giving them data on weather variables for the study.

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