The Possible Effects of Temperature and Precipitation on Dengue Morbidity in Trinidad and Tobago: A Retrospective Longitudinal Study
Jeny Wegbreit
 
 
 

I. Introduction

General Circulation models have predicted a two degree increase in global temperatures by the end of the next century caused by an expected doubling in atmospheric carbon dioxide (Jetten 1996). If global warming occurs, increased temperatures may have tremendous implications for viral diseases whose vectors are sensitive to climate changes. One disease implicated, which is thought to pose the greatest threat in the case of global warming in North America (Shope, 1991), is dengue fever. Dengue fever is transmitted by Aedes aegypti, a vector whose rates of viral infection vary with climate conditions (Reiter, 1988). It has been predicted that global warming may shift the distribution and frequency of dengue, with dire consequences to public health in the areas affected (Patz et al., 1996). To develop a more accurate prediction of possible future scenarios, this study evaluated retrospectively the relationship between morbidity incidence attributed to dengue fever in Trinidad and Tobago and local variation in temperature and precipitation. This study analyzed weekly dengue morbidity data from the country of Trinidad and Tobago and monthly precipitation and temperature data from the Port of Spain, Trinidad for a nine year period (1982-1990). 

II. Objectives

The main objective of this study was to determine retrospectively, whether there was a temporal pattern of association between weather variables and dengue fever morbidity rates. Because mosquito density, activity, and survival is related to various weather conditions, there may be a correlation between dengue incidence and weather patterns. However, it is uncertain whether temperature or precipitation will be the strongest predictor of dengue incidence, or whether a more predictive relationship exists when both are taken into account. The time lag between weather patterns and possible increases in dengue incidence is also uncertain. The various components of the time lag include the period of embryonic development of the mosquito, hatching time, the adult and sexual development period of the mosquito, the time before the first blood meal, the extrinsic incubation period, the time before the next blood meal in which the mosquito passes the infectious virus, and the time before the appearance of clinical manifestations of dengue fever (Table 1). It has been found that the development of the dengue virus in the mosquito, the extrinsic incubation period (EIP), will range from seven to twelve days depending on ambient temperature (Watts, 1987). It has also been determined that the period between infection and clinical manifestations of disease in humans ranges from four to six days (Pan American Health Organization, 1994). It is therefore assumed that a time lag of at least eleven and perhaps as much as eighteen days will be found. However this may be a very conservative estimate as it does not take into account the life cycle and development of the mosquito which varies according to ambient weather conditions, the availability of food , and larval density in the container in which the mosquito is breeding. Hatching of the mosquito varies dramatically according to precipitation and humidity; a dry period may mean the mosquitoes will delay hatching for more than a year (Pan American Health Organization, 1994). The delayed development could potentially provide a much greater time lag than expected, possibly a time lag of greater than a year. However, because such long dry periods do not occur in Trinidad, a time lag of less than one year is more likely. The goal of this effort was to evaluate whether a temporal association, possibly with a time lag, exists between weather variables and disease incidence. 

 

III. Background

Dengue fever is caused by a virus from the family Flavviviridae; four serotypes are distinguished by serological methods, dengue-1, dengue-2, dengue-3, and dengue-4. All four serotypes have been found in the Americas, however only serotypes 1, 2, and 4 circulated in the period focused on for this study (1982-1990). The virus is transmitted primarily by the Ae. aegypti mosquito to the human host. Ae. aegypti is a highly domesticated mosquito, breeding in freshwater containers stored for drinking and bathing. Because severe frost and cold weather kills adult mosquitoes and eggs, dengue is currently restricted to the region between thirty-five degrees north latitude and thirty-five degrees south latitude. The clinical manifestations of dengue can range from a minor fever, often with flu-like symptoms, to severe Dengue Hemorrhagic Fever (DHF) and Dengue Shock Syndrome (DSS) that may result in death. Between 250,000-500,000 cases of the severe DHF/DSS form occur yearly throughout the world and case fatalities can reach forty to fifty percent if not treated with fluid replacement therapy (Gubler, 1994). The relationship between weather patterns and dengue transmission is multifaceted involving both the mosquito life cycle and viral replication requirements. It has been determined that warmer temperatures reduce larval size of Ae. aegypti which results in a smaller adult size (Rueda, 1990). Smaller adult female mosquitoes have been found to feed more frequently to nourish their developing eggs (Reiter, 1988) which increases the probability of transmission. The positive relationship between biting rates and temperature has been supported in field studies in Bangkok (Pant, 1973). A second consideration in viral transmission is the EIP. A study by Watts et al. (1987) determined that the EIP is heavily contingent upon temperature; the EIP for Ae. aegypti decreased from twelve to seven days when mosquitoes were kept at 32-35 degrees instead of 30 degrees Celsius. These results imply temperature induced variations in the vectorial efficiency of Ae. aegypti may be a significant determinant of the annual pattern of dengue that Watts et. al. found in Bangkok. Research by Koopman et al. (1991) also supports the theory that dengue transmission frequency relies upon climatic conditions. His study concluded that median temperature during the rainy season was the strongest predictor of infection. High temperature was responsible for greater transmission rates by reducing the period of viral replication in mosquitoes. It has been found that increasing precipitation may either increase or decrease dengue incidence rates. It has been proposed that human vector contact may be enhanced during periods of high rainfall (Gubler, 1994) because mosquitoes may become less active. In this scenario they are more likely to stay indoors where their probability of survival is higher and their contact with humans is greater. However, many scientists have found an inverse relationship between incidence rates and rainfall. In his 1938 study, Soper found that low rainfall in Brazil results in more water storage containers in the home and therefore more Ae. aegypti in residential areas. The implications of global warming on dengue transmission has been modeled by Martens et. al. (1997) who found that the transmission potential of dengue may be highly sensitive to climate changes. They predicted that transmission should be particularly sensitive to warming in higher altitudes and in areas which are currently at the periphery of endemic transmission. Jetten and Focks (1996) have also developed a model of the influence of warming on the intensity and distribution of dengue throughout the world. Using a simulation model projection, their results indicate that the current warming prediction of two degrees by 2100 may result in an increase in the latitude and altitude range of dengue. They also concluded that the duration of the transmission season could increase in temperate locations. As yet, there has been no study published of actual case data that seeks a retrospective statistical association between weather variables and dengue incidence. Studies of dengue in the past have not looked at weather factors independently, nor have they looked longitudinally at how these factors may affect morbidity rates. My study is intended to evaluate the relative importance of temperature and precipitation rates to transmission using long-term case data from the islands of Trinidad and Tobago. 

IV. Data

Monthly mean precipitation and temperature data were collected from the Web Page of the National Climatic Data Center (http://www.ncdc.noaa.gov/ghcn/ghcn.html). While Tobago did have its own weather station located at Crown Point Airport, this data was unavailable therefore all weather information came from the Piarco International Airport in Trinidad. The mean temperature and precipitation were used, as opposed to either the minimum or maximum temperature, because it has been found that incidence rates of malaria are most closely related to mean temperature at lower altitudes (Loevinsohn, 1994). Because the disease etiology of malaria is somewhat similar to that of dengue (they are both diseases carried by mosquitoes whose living and breeding conditions are contingent upon the ambient environment) and because Trinidad is at an elevation of twelve meters, I chose the mean temperature and precipitation values. However, it is important to note that malaria and dengue are differentiated by difference species of mosquito vectors, entirely different infectious parasites, and different patterns of breeding and development of the vectors. Therefore, it is possible that minimum and maximum temperatures may be useful in predicting a relationship between weather variables and morbidity rates. The weekly incidence rates of dengue in Trinidad and Tobago were obtained from Dr. Wilson of the University of Michigan Department of Epidemiology. Because data from Trinidad alone was unavailable, I used the coalesced data which included morbidity from both Trinidad and Tobago. The weekly rates were converted to monthly rates, assuming that whatever fraction of the week was ascribed to one of two months, if it was a week split between two months, a similar proportion of incidence was given. 

V. Qualitative Description of the data

The nine year period of monthly temperature data varied less that 4 degrees Celsius. A seasonal distribution of maximum and minimum temperatures exists; annual maximum temperatures were usually observed in the months of May through September, and annual minimum temperatures were found in either December or January (Graph 1). 
 

 
Annual precipitation over the nine years varied considerably (Graph 2). In general, January through April was a period of low precipitation, but the remainder of the year was less consistent with a maximum yearly temperature varying by month each year. Four months had unusually high levels of precipitation, June 1983, July 1984, August 1984, and October 1988, all of which were greater than 30 centimeters, and could be considered outliers. 
 
 
Morbidity data over the nine year period indicated no apparent seasonal distribution (Graph 3) Each year had a different month with a maximum of morbidity cases. Outliers for morbidity are considered months in which the number of cases was greater than 50 and include November 1986, and January, February, March, and July of 1990. 
 
 
There was no visible relationship between morbidity and temperature over time, nor was a temporal relationship taking time lags into account apparent (Graph 4). The periods of high incidence occurred at any point in the year during the nine-year period and did not appear to be associated with either high or low monthly temperatures. 
 
 
There appeared to be no visible relationship between morbidity and temperature during the nine-year period, nor did any time lags between precipitation and monthly morbidity seem apparent (Graph 5). 
 
 

VI. Methods/Approach

To determine the most appropriate model to demonstrate the possible relationship between morbidity due to dengue fever weather variables, several approaches were undertaken (Thesis1-Thesis 3). Thesis 1: Four separate models were tested to determine the most appropriate one: a linear model, an exponential growth model, an autoregressive model with a time lag of one month, and an exponential growth autoregressive model with a time lag of one month. I conjectured that the relationship between the variables may not be linear and thought it best to try both the linear and exponential models with a time lag of one month. To determine the most appropriate model, a regression was run for each of the situations to find the amount of error explained by each model. Also to determine the robustness of the models, the F statistics were calculated, as were their corresponding p-value. Because one of the assumptions of multiple regressions is that errors of the variables are not related to one another, the Durbin Watson statistic was calculated to determine possible serial-correlation. To test the null hypothesis that neither precipitation nor temperature were related to morbidity rates, the t-statistic was calculated with its corresponding p-value. Finally, an equation for the line of each model was determined. Results of Thesis 1: The results of the four models showed no statistical significance for each model, nor were any of the variables alone statistically significant. The Durbin Watson statistic indicated that there was serial correlation between the variables as might be expected between temperature and precipitation which often affect one another. Because a linear relationship with time lags is more likely than an exponential relationship, I chose to retain the linear model for the remainder of the tests. Thesis 1a: To determine whether a better model might be achieved if the outliers were removed, the previous four models were tested after removing monthly records in which either the morbidity was greater that 50 or the precipitation was greater than 30. Because there were no outliers for temperature, no temperature records were removed. Results of Thesis 1a: The results of the four models with the outliers excluded showed no statistical significance for each model, nor were any of the variables alone statistically significant. The Durbin Watson statistic indicated that there was serial correlation between temperature and precipitation. Thesis 2: The linear model was retained because although no statistically significant relationship exists without a time lag or a time lag of only one month, a likely relationship may exist with a time lag of up to one year. To determine if such a relationship is a possibility, the dependent variable was lagged against the two weather variables by each month for up to twenty-four months. Results of Thesis 2: Several statistically significant relationships were found during this test. First, the model with a time lag of six months was statistically significant with an F statistic equal to 3.935, corresponding to a p-value of .0234. To reject the null hypothesis that there was no statistically significant relationship between incidence and the weather variables, the p-value had to be .05 or less. The R-squared value was .0889 which indicates that 8.89 percent of the error is explained by the model. Temperature, with a t-value of 2.64 corresponding to a p-value of .0098, was statistically significant, while precipitation was not a statistically significant parameter. To reject the null hypothesis, that there was no statistically significant relationship between temperature or precipitation and incidence, the t-values for either of the weather variables had to be greater than 1.96 with a corresponding p value of .05 or less. The correlation between temperature and precipitation was positive, with a value of .2504, and the correlation between precipitation and temperature was negative with a correlation value of -.0239. The Durbin Watson statistic indicated that serial-correlation between the two independent variables was occurring and had a value of 1.735 ( a value of 2 indicates that there is no serial correlation). The equation for this model is -142.26 = 5.83 Beta 1 - .196 Beta 2 + error term. The other two statistically significant models were at lags of thirteen and seventeen months, which is too long a period to represent an actual relationship and is likely an artifact of lagging the model for too many months. Because long periods of desiccation do not occur in Trinidad, it is most probable that the existing lag is less than one year. Neither of the models were more statistically significant than the model with the six month lag. At the lag of 6 months the F value was 3.211 with a corresponding p-value of .0459. The R-squared value was .0789 indicating that 7.89 percent of the error is explained by the model. Temperature, the only statistically significant variable for this model, had a t-value of -2.52 with a corresponding p-value of .01. In this model, temperature was negatively correlated with morbidity with a correlation of -.279 and precipitation was positively correlated with morbidity with a correlation of .0197. The equation for this model is 261.81 = -9.963 Beta 1 + .1098 Beta 2 + error term. The other model with a statistically significant relationship which is likely an artifact of lagging for too many moths is found at 17 months. The F value for this model was 4.059 with a corresponding p-value of .02. The R-squared value was .1001 indicating that 10.01 percent of the error is explained by the model. Precipitation, the only statistically significant variable in this model, had a t-value of 2.77 with a corresponding p-value of .007. Precipitation was positively correlated with morbidity with a correlation of .319 and temperature was positively correlated with morbidity with a correlation of .065 in this model. The equation for this model is -39.36 = 1.53 Beta 1 + .76 Beta 2 + error term. Thesis 2a: To test whether temperature as the only independent variable would create a better model, regressions were run of temperature against morbidity lagging the variables up to twenty-four months. Results of Thesis 2a: Two statistically significant relationships were determined. At a lag of six months, the model was statistically significant with an F statistic of 5.887 and a corresponding p-value of .0173. The R-squared value was .0627 which indicates that 6.27 percent of the error is explained by the model. The t-value was 2.426 with a corresponding p-value of .0173, indicating that the variable is statistically significant. A positive correlation between temperature and morbidity was found with a correlation value of .2504. The equation for this model is -96.67 = 4.05 Beta 1 + error term. The second statistically significant relationship was found at a time lag of thirteen months which, as explained previously is too long a period to represent an actual relationship and is likely an artifact of lagging the model for too many months. In this regression, the F statistic was 6.84 with a corresponding p-value of .0106. The R-squared was .0779 indicating that 7.79 percent of the error is explained by the model. The t-statistic was -2.616 with a corresponding p-value of .0106. There was a negative correlation between precipitation and morbidity with a correlation value of -.279. The equation for the line is 257.24 = -9.4 Beta 1 + error term. Thesis 2b: To test whether precipitation as the only independent variable would create a better model, regressions were run of precipitation against morbidity lagging the variables up to twenty-four months. Results of Thesis 2b: There was one statistically significant relationship between precipitation and morbidity at a time lag of seventeen months. However, this is likely an artifact of lagging the variables for too many months. In this regression, the F statistic was 9.047 with a corresponding p-value of .0036. The R-squared was .1016 indicating that 10.16 percent of the error is explained by the model. The t-statistic was 2.008 with a corresponding p-value of .0035. There was a positive correlation between precipitation and morbidity with a correlation value of .318. The equation for the line is .21 = .778 Beta 1 + error term. Thesis 3: Because it is possible that precipitation and temperature have different time lags when affecting morbidity, two models were tested using both independent variables at different time lags. Because the time lags for temperature of six and thirteen months and the time lag for precipitation of seventeen months were statistically significant, the models used first a lag of six months for temperature and seventeen months for precipitation, and then a lag of thirteen months for temperature and seventeen months for precipitation. Results of Thesis 3: Neither the model nor the independent variables were statistically significant for both models tested. The Durbin Watson statistic indicated that serial correlation was occurring between the variables. These results suggest that either the variables are interacting with one another or the time lags chosen are too great to indicate a real relationship. 

VII. Equations for Each Model

Thesis 1: Full dataset

Thesis 1a: Deleting observations where Morbidity > 50 and Precipitation > 30 Thesis 2: Full dataset Thesis 2a: Full dataset Thesis 2b: Full dataset Thesis 3: Full dataset VIII. Discussion

There are two models which show the greatest likely relationship between weather variables and morbidity due to dengue fever. Both of the models at a time lag of six months, with temperature alone and with precipitation and temperature together, were statistically significant and appear to be the best models. The model did not greatly improve when temperature was considered alone, therefore both models are considered appropriate in explaining the association between morbidity and weather. Because the time lag is six months, it suggests a seasonal relationship which may be discerned through further research. As yet, my work has some errors which can be overcome with more data and more time. It is possible that although there were one hundred and eight data points and a minimum of twenty data points is necessary for a statistically significant relationship to be found, more data points are needed. Errors could also have been due to the fact that the weather data was from Trinidad alone while the incidence data was from both Trinidad and Tobago. It is possible that the weather in Trinidad is not reflective of that in Tobago. Also, the method of changing weekly incidence data to monthly incidence data may have induced errors. It is likely that although a certain fraction of a week belongs to one month, the corresponding fraction of incidence does not also belong to that month. For example, there may be an outbreak in one month and not the next, which would mean an unequal division of incidence for a week split between those two months. Lastly, the small amount of serial correlation between temperature and precipitation indicate that these two variables are affecting one another which may reduce the robustness of the model. To correct some of these problems a longer period of time should be analyzed, the data should be given in monthly form for all variables, and all data should be given from one locale. Also, using the minimum and maximum temperatures in place of mean temperature may reveal a more predictive relationship. 

IX. Conclusions

The statistical procedures suggest that there is a statistically significant relationship between temperature and incidence rates given a six month time lag. The results indicate that it takes six months for environmental conditions, as measured by temperature alone, to affect dengue incidence. This may be due to temperature’s influence on the life cycle of a mosquito or viral replication rates. The higher temperatures may reduce the larval size of mosquitoes, which results in smaller adults that need to feed more often. Higher temperatures may also speed up the EIP causing greater rates of transmission. Because the time lag for these to occur is nebulous due to the variable nature to the mosquito life cycle, it difficult to verify how these factors can be ascribed to the six-month time lag found. A small negative correlation of precipitation with incidence was detected, suggesting that precipitation six months prior to reporting dengue may reduce incidence rates. This may be due to a variety of factors. Either high amounts of rain flush out larvae, thereby reducing rates or low amounts of rain requires more water to be stored which will increase incidence rates. In either situation an inverse relationship is observed between precipitation and incidence rates. However, because no statistically significant relationship of precipitation with incidence was found, precipitation did not actually influence incidence, only a negative correlation between the two variables can be alluded to. 

X. Public Health Implications

Because this study indicates that there is a statistically significant relationship between dengue incidence and temperature at a six month time lag, there are both present and future public health implications. The present implications of this study suggest that disease prevention and surveillance measures should focus on the temperature six months prior to determine the risks of increased transmission for the present time. The future implications of this study are more uncertain. Because a positive correlation of temperature with incidence was found, global warming is likely to have an impact on dengue fever, increasing the disease’s range and the number of infected individuals. To mitigate future impacts both disease surveillance and control are necessary. Disease surveillance should include both passive and active surveillance. Passive surveillance would require dengue be a mandated reportable disease that would be recorded in all hospitals and clinics. Active surveillance includes providing a laboratory-based surveillance system which would give public health officials precise information about periods of increased dengue activity. One active surveillance measure suggested is the creation of diagnostic centers in sensitive geographic regions bordering endemic zones (Patz et al., 1996). Such centers would provide early warning of changes in incidence and allow for intervention. Control measures should have an integrated approach combining environmental management, chemical control, and biological methods. Environmental management is any change in the environment that prevents or minimizes vector propagation or man-vector-pathogen contact. These include environmental modification (long-term changes to vector habitat such as improved delivery of potable water), environmental manipulation (short-term changes to vector habitat including proper storage of containers), and changes to human habitation or behavior (including the screening of windows). Chemical control should be used in a limited fashion because of the toxic effects most larvicides have had to humans and aquatic organisms in the past. Present use is restricted to containers that cannot otherwise be eliminated or managed. Biological control is based on the introduction of living organisms that will prey upon, parasitize, compete with or otherwise reduce the abundance of Aedes or anopheline mosquitoes. These interventions have been largely experimental and have included introduction of fish, bacteria, and cylclopoids (‘water fleas") which attempt to reduce mosquito populations. If little is done to prevent global warming, surveillance and control measures will be our last protection against increasing infectious disease transmission. However, preventing warming should be a greater priority to ensure that global dissemination of communicable diseases does not occur. 


References