Eastern Mediterranean Health Journal

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Volume 13 No. 1  January - February , 2007

 

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Climatic variables and transmission of falciparum malaria in New Halfa, eastern Sudan

Y.E. Himeidan,1 E.E. Hamid,1 L. Thalib,2 M.I. Elbashir3 and I. Adam4

المتغيِّرات المناخية وسراية الملاريا المنجلية في حلفا الجديدة، بشرق السودان

يوسف الصافي حميدان، إخلاص الحاج حامد، لقمان طالب، مصطفى إدريس البشير، إسحق آدم


الخلاصـة: درس الباحثون دور المتغيِّرات المناخية والزراعة الـمَرْويَّة في السراية الموسمية للملاريا في حلفا الجديدة، بشرق السودان. وأُجري تحليل متسلسل زمنياً بالاعتماد على المتغيرات المناخية الشهرية، والمياه المتوافرة شهرياً لِرَىِّ المحاصيل، ومعدل الشرائح الإيجابية الشهرية للملاريا، في ما بين عامَيْ 1986 و2002. وقد تم التبليغ عن حالات الملاريا شهرياً على مدار العام بمتوسط 13.0/100 شخص/الشهر (11.9 – 14.2) وبنَمَط سنوي ثنائي الدارج في فصلَيْ الشتاء والخريف. وقد وجد أن سقوط الأمطار هو المتغير المناخي الأساسي في سراية المرض، إذْ يؤدي الهطول الغزير للأمطار إلى بدء ظهور الأوبئة. أما الحرارة، والرطوبة النسبية والري فلم تكن من العوامل التي يُعتدُّ بها.

ABSTRACT: The study investigated the role of climatic variables and irrigated agricultural on the seasonality of malaria transmission in New Halfa, eastern Sudan. A time-series analysis was performed using monthly climatic variables, monthly water available for irrigation of crops and monthly slide positive rate of malaria during the period 1986–2002. Cases of malaria were reported every month of the year with a mean of 13.0/100 persons/month (95% CI: 11.9–14.2), and bimodal annual pattern in autumn and winter seasons. Rainfall was the significant climatic variable in the transmission of the disease, whereas heavy rainfall was found to initiate epidemics. Temperature, relative humidity and irrigation water were not significant factors.

Variables climatiques et transmission du paludisme à P. falciparum à New Halfa au Soudan oriental

RÉSUMÉ: Cette étude a évalué le rôle des variables climatiques et de l’agriculture irriguée sur la saisonnalité de la transmission du paludisme à New Halfa au Soudan oriental. Il a été procédé à une analyse de séries chronobiologiques s’appuyant sur les variables climatiques mensuelles, les volumes mensuels d’eau disponibles pour l’irrigation des cultures et le taux de positivité des lames mensuel pour la période 1986-2002. Des cas de paludisme ont été rapportés tout au long de l’année, avec une moyenne de 13,0/100 sujets/mois (IC 95 % : 11,9 - 14,2) et un profil bimodal retrouvé chaque année en automne et en hiver. La pluie s’est avérée être la variable climatique significative quant à la transmission de la maladie, les fortes chutes de pluie apparaissant comme le facteur déclenchant d’une épidémie. La température, l’humidité relative et les eaux d’irrigation n’étaient pas des facteurs importants.


1University of Kassala, Faculty of Agriculture and Natural Resources, New Halfa, Sudan (Correspondence to I. Adam: ishagadam@hotmail.com).

 2University of Kuwait, Faculty of Medicine, Kuwait.
 3University of Khartoum, Faculty of Medicine, Khartoum, Sudan.

 4New Halfa Teaching Hospital, New Halfa, Sudan Received: 13/12/04; accepted: 23/05/05

 

Introduction

Malaria remains one of the major public health concerns in most tropical countries. Despite continuous efforts to curb malaria transmission, the incidence in some parts of the world is reported to be increasing. The costs, morbidity and mortality associated with malaria are huge.

It has been suggested that both global climate and local environment changes may be affecting the pattern of malaria. The predictive models of the effects of global warming show a widespread expansion in the distribution of stable malaria in Africa during the next few decades [1,2]. Changes in the pattern of tropical weather conditions, particularly rainfall and temperature, are reported to have an important role in the increase of malaria risk [3–5]. Other factors such as changes in land use pattern and construction of water control systems have also been shown to have considerable effects on malaria transmission [6,7].

Although global warming might affect regions above 1500 m, it will probably have little influence on the stability and pattern of malaria in areas below 1500 m, where the majority of the tropical African population lives. More serious in the short and medium term are the effects of deforestation in the hill areas. Also important is the temperature governing sporogony. The duration of sporogony is rising again above the optimum (26 °C for Plasmodium falciparum) [8]. In areas with unstable malaria transmission, minor changes in the transmission parameters such as mosquito population density and longevity could have a sustainable impact on human morbidity and mortality [8,9]. Therefore, it is important to identify the forces that drive the proliferation of malaria transmission as a result of these changes. Although such studies on the dynamics and distribution of malaria transmission have been upgraded to the continental scale, few studies have been made on a temporal scale.

The aim of this study was to plot the transmission dynamics of falciparum malaria in relation to climatic variables and irrigation water available for agriculture in the New Halfa area of eastern Sudan, based on empirical data for the period 1986–2002. This may be important for forecasting and planning of the malaria control programme in the area.

Methods

Study area

The study was carried out in the New Halfa area (located at 15° 18'–15° 21' N & 35° 33’–35° 37' E). This is 500 km from Khartoum in the middle of the second largest irrigated agricultural scheme in Sudan. Cotton and wheat are the main crops cultivated during the winter season. The region is the semi-arid dry savannah belt of Sudan. During the period of the study the mean monthly temperature was 29.4 °C (range 14.1–42.7 °C), the mean monthly relative humidity was 49.2% (range 19.0%–78.2%) and average annual rainfall was 238.7 mm (range 68.7–543.8 mm). The area is characterized by a high level of drug resistance to falciparum malaria; Anopheles arabiensis is the principle vector [10–12].

Data collection

As the New Halfa irrigated scheme is a relatively recent construction, data were only available from 1986 onwards. The slide positive rate (SPR) of malaria was the number of parasitologically confirmed clinical cases of malaria/100 persons attending/month. Results were calculated monthly from the routine reports of the health authority that collected data from patients attending 8 malaria referral laboratories in the area.

The climatic variables collected were: monthly mean maximum and minimum temperature (°C), relative humidity (%) and total rainfall (mm), as well as monthly amounts of irrigation water available for agriculture (m3/month). The seasons were classified as: cool dry winter (November to February), hot dry summer (March to June) and autumn (July to October). Meteorological data were retrieved from the New Halfa meteorology station. The data about irrigation water were collected from the irrigation station in New Halfa town and was only available for the period 1997–2002. This data measured the monthly amount of water available for crop irrigation in the New Halfa agriculture scheme. The amount of water fluctuates depending on the yearly amount of water available in Khashm El-Girba dam reservoir and on the actual monthly amount of water released from the dam to irrigate the crops cultivated in a specific time and area.

Data analysis

Data were analysed using SPSS, version 12. The monthly SPR of malaria was regarded as the dependent variable, while climatic variables were independent variables. Spearman correlation analysis was conducted to examine the relationship between the independent variables and the SPR of malaria. Autoregressive integrated moving average (ARIMA) analyses were performed to account for possible auto-correlation in the time-series data. Therefore a model was developed after the effect of auto-correlation had been removed and then regression analyses were used to assess the independent effect of each independent variable. P < 0.05 was considered significant.

Results

Malaria cases were reported every month of the year, with a mean SPR of 13.0/100 persons/month (95% CI: 11.9–14.2/100 persons/month). The general pattern was a bimodal annual increase in SPR during the end of the autumn (September/ October) and the cool dry season (January/February) (Figure 1).  This figure shows the 2 peaks of SPR by clustering the months of the main peak (right) and minor peak (left) and months with low level of SPR (in between).

Rainfall was the only climatic variable that was significantly correlated with malaria SPR in the area over 1986–2002 (P = 0.006) (Table 1).

This is illustrated in Figure 2, showing the relationship between heavy rainfall and the malaria epidemics that were reported in 1992 and 1998. The monthly average total rainfall was 205% higher in 1992 (95% CI: 9.1–33.0 mm) and 183% higher in 1998 (95% CI: 11.3–80.3 mm), compared with the previous 3 years (1989–91 and 1995–97) respectively. Similarly, the malaria SPR increased by 263% in 1992 in comparison with the previous 3 years [7.3/100 persons/month (95% CI: 5.4–9.1/100 persons/month)] and by 133% in 1998 in comparison with the monthly mean SPR during 1995–97 [17.3/100 persons/month (95% CI: 15.5–19.2/100 persons/month)]. The inverse relationship observed reflected the opposite position between rainfall and malaria SPR; when there was no rainfall (dry years), the highest number of cases of malaria were recorded during the cool dry season. The correlation analyses conducted for the data of these 2 epidemic years revealed a high positive relationship between SPR and monthly total rainfall (r = 0.79, P = 0.001). However, the negative association between rainfall and SPR observed during the whole period of study reflected only the pattern of malaria incidence under a control programme, when mosquitoes were intensively sprayed. The highest number of malaria cases occurred during the cool dry season (irrigation season), i.e. years 1993 and 1999 (Figure 2). In fact this was also the case of some drought years, i.e. year 1987 (Figure 2).

Temperature, relative humidity and irrigation water showed no significant correlation with malaria SPR over 1986–2002 (Table 1). Cross-correlations conducted among the independent variables revealed a significant correlation between monthly mean relative humidity and both minimum and maximum temperature (P > 0.001). Also a significant correlation was found between minimum and maximum temperature (P > 0.000). Due to these high coefficient correlations among the independent variables, each variable was analysed with rainfall in a separate regression model to reduce this multicollinearity. The best combination was found between rainfall and minimum temperature in comparison with other combinations of monthly maximum temperature and humidity. The effect of these factors was more pronounced during the dry years 1990 and 1991, and also the lowest SPR was reported in July (the beginning of the rainy season), following the harsh environment conditions of the hot dry season (Figure 1).

Significant differences were found between the SPR in the hot dry season and both the cool dry and the autumn seasons, but there were no significant differences between the autumn and the cool dry seasons (Table 2). However, “year” was not significant in the regression model, reflecting the stability in the number of cases during most years of the study period, especially 1992–99 (Figure 2).

Discussion

This was the first study reporting the association between climatic variables and malaria SPR in an irrigated area in eastern Sudan. There were significant differences in the SPR of malaria between the 3 seasons. Cases of malaria were reported almost every month of the year, with a general pattern of a bimodal annual increase in SPR in the autumn and cool dry season. Clearly, the pattern of malaria transmission was completely different from that in the other parts of eastern Sudan, where transmission of the disease was restricted to the rainy season [13]. Despite the non-significant correlation between irrigation water and malaria SPR, perhaps due to the use of limiting data, the bimodal annual rate of malaria transmission could be explained by the presence of the agriculture schemes.

Previous entomological surveys in the same area reported a continuous breeding activity of A. arabiensis in the leakages of the irrigation system and therefore a minor peak of larvae density was investigated during the cool dry season. However, the larvae numbers of A. arabiensis were correlated significantly with the irrigation water [12]. Nevertheless, irrigated agriculture has influenced malaria incidence in this area and extended the transmission season beyond the rainy season [14]. The introduction of irrigated schemes in areas with seasonal rainfall has been reported to increase the incidence of malaria significantly [15,16].

Our findings showed a significant positive association between malaria SPR and rainfall, and epidemic malaria was associated with heavy rains. Previously, it was documented that the transmission of malaria was governed by rainfall and fluctuated considerably from year to year according to the rainfall, and heavy rains were associated with malaria epidemics [4,5,17–19]. The results of the present study support the model of Lindsay et al. [3], who found that temperature and rainfall were driving forces of the spatial distribution of the malaria vector A. gambiae s.l. Koenraadt et al. [20] showed that the numbers of the larval and adult population of A. gambiae s.s. and A. arabiensis are closely linked with rainfall, while Craig et al. [21] observed a direct and predictable relation between rainfall and malaria transmission. Although excessive rainfall flushes the aquatic stages of A. arabiensis away, leaving them stranded on the dry ground, it does not eliminate them. Thus very high rainfall is still relevant for malaria vectors, as dispersed water collections that are suitable for breeding can be created [21–23].

The study showed that malaria SPR was not significantly correlated with temperature. Although temperature governs mosquito survival only to a limited extent, it has a significant impact on the transmission dynamics mainly due to the specific effect on sporogenic duration [8,24]. However, during March to June, hot dry weather has a significant correlation with SPR (Table 2). This could be attributed to the rise in maximum temperature and decrease in relative humidity that reduces significantly the breeding activity of A. arabiensis [12]. Earlier investigations in the Sudan and elsewhere in Africa have demonstrated that relative humidity is the main determinant of the lifespan of A. arabiensis [25]. Since the evidence for the effect of climate change for expanding the areas of suitable malaria transmission is derived largely from temperature [3], it is likely that malaria infections in the New Halfa area will increase in response to the rise of temperature during the cool dry season.

Our findings have important implications for malaria control in areas with similar geographic, climate and environmental conditions to those of New Halfa. Both the duration and timing of malaria transmission are important factors to consider when directing efforts in malaria control.

References

  1. Tanser FC, Sharp B, le Sueur D. Potential effect of climate change on malaria transmission in Africa. Lancet, 2003, 362:1792–8.

  2. Thomas CJ, Davies G, Dunn CE. Mixed picture for changes in stable malaria distribution with future climate in Africa. Trends in parasitology, 2004, 20:216–20.

  3. Lindsay SW, Martens WJM. Malaria in the African highlands: past, present and future. Bulletin of the World Health Organization, 1998, 76:33–45.

  4. Lindblade SW Maretnes, WJ. Highland malaria in Uganda: prospective analysis of an epidemic associated with El Nino. Transactions of the Royal Society of Tropical Medicine and Hygiene, 1999, 93:480–7.

  5. Kilian AH et al. Rainfall pattern, Elnino and malaria in Uganda. Transactions of the Royal Society of Tropical Medicine and Hygiene, 1999, 93:22–3.

  6. Hay SI et al. Climate change and the resurgence of malaria in the East African highlands. Nature, 2002, 415:905–9.

  7. Githeko AK et al. Climate change and vector-borne diseases: a regional analysis. Bulletin of the World Health Organization, 2000, 78:1136–47.

  8. Onori E, Grab B. Indicators for the forecasting of malaria epidemics. Bulletin of the World Health Organization, 1980, 58:91–8.

  9. Epidemiology of malaria. In: Gilles HM, Warrell DA, eds. Bruce-Chwatt’s essential malariology, 3rd ed. London, Arnold, 1993:124–63.

  10. Adam I et al. In the Sudan: chloroquine resistance is worsening and quinine resistance is emerging. Sudan medical journal, 2001, 39:5–11.

  11. Himeidan YE et al. Anopheles arabiensis: abundance and insecticide resistance in irrigated area of eastern Sudan. Eastern Mediterranean health journal, 2004, 10:167–74.

  12. Himeidan YE, Rayah E. Role of some environmental factors on the breeding activity of Anopheles arabiensis in new Halfa town, eastern Sudan. Eastern Mediterranean health journal [in press].

  13. Hamad AA et al. A marked seasonality of malaria transmission in two rural sites in eastern Sudan. Acta tropica, 2002, 83:71–82.

  14. Himeidan YE et al. Epidemiology of malaria in an irrigated area in the eastern Sudan. Eastern Mediterranean health journal, 2005, 11:499–504.

  15. Robert V et al. Mosquito and malaria transmission in irrigated rice-field in the Benoue valley in northern Cameroon. Acta tropica, 1992, 52:201–4.

  16. Ghebreyesus TA et al. Incidence of malaria among children living near dams in northern Ethiopia: community based incidence survey. British medical journal, 1999, 319: 663–6.

  17. Van der Hoek W et al. Correlation between rainfall and malaria in the dry zone of Sri Lanka. Annals of tropical medicine and parasitology, 1997, 91:945–9.

  18. Loevinsohn ME et al. Climate warming and increased malaria incidence in Rwanda. Lancet, 1994, 343:714–8.

  19. Bi P et al. Climatic variables and transmission of malaria: a 12-year data analysis in Shuchen County, China. Public health reports, 2003, 118:65–71.

  20. Koenraadt CJ, Githeko AK, Takken W. The effects of rainfall and evapotranspiration on the temporal dynamics of Anopheles gambiae s.s. and Anopheles arabiensis in a Kenyan village. Acta tropica, 2004, 90:141–53.

  21. Craig MH, Snow RW, le Sueur D. A climate-based distribution model of malaria transmission in sub-Saharan Africa. Parasitology today, 1999, 15:105–11.

  22. Jepson WF, Moutia A, Courtois C. The malaria problem in Mauritius: the bionomics of Mauritian anophelines. Bulletin of entomological research, 1947, 38:177–208.

  23. Robert V et al. Rainfall is not a direct mortality factor for Anopheline larvae. Parasite, 1999, 6:195–6.

  24. MacDonald G. The epidemiology and control of malaria. London, Oxford University Press, 1957.

  25. Molineaux L et al. The epidemiology of malaria and its measurement. In: Wernsdorfer WH, McGregor I, eds. Malaria: principles and practice of malariology. London, Churchill Livingstone, 1988:999–1090.

 

Guidelines for the treatment of malaria
Guidelines for the treatment of malaria aims to provide comprehensible, global, evidence-based guidelines to help formulate policies and protocols for the treatment of malaria. Information is presented on the treatment of uncomplicated malaria, including disease in special groups (young children, pregnant women, people who are HIV positive, travellers from non-malaria endemic regions) and in complex emergency situations and severe malaria. The guidelines do not deal with preventive uses of antimalarials, such as intermittent preventive treatment or chemoprophylaxis.
The guidelines are aimed primarily at policy-makers in ministries of health. Public health and policy specialists working in hospitals, ministries, nongovernmental organizations and primary health care services as well as health professionals (doctors, nurses and paramedical officers) should also find them useful.
 

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