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| ABSTRACT |
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| INTRODUCTION |
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If use of ITNs is beneficial to near neighbors lacking ITNs, new questions arise. How strong is the community effect of ITNs relative to their individual protective effect? To what extent does the strength of the effect depend upon the proportion of homes having ITNs? Answers to these questions have important implications for policymakers trying to choose among various models for ITN distribution in African communities.
In the context of a large-scale, group-randomized, controlled trial of ITNs in western Kenya, Gimnig and others4 have shown that mosquito abundance was reduced in compounds lacking ITNs but located close to compounds with ITNs. In the present analysis, we determine whether a beneficial community effect on the mosquito population extends to malaria-related morbidity and all-cause mortality in young children, who are profoundly affected by malaria in this area. We show how the strength of the effect varies spatially, both within villages lacking nets and in villages with ITNs. We also describe how the strength of the community effect in individual houses lacking nets varies with the proportion of neighboring houses that have nets. We show that failing to control for the community effect in standard statistical analysis of ITN efficacy results in a systematic underestimate of the true efficacy of ITNs. Finally, we discuss implications of our results for mechanisms of ITN action.
| MATERIALS AND METHODS |
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The landscape consists of rolling hills cut by numerous seasonal rivers that flow into the lake. Underground springs bubble to the surface in parts of the area, providing water for human use, and larval habitat for mosquitoes. Rainfall follows a bimodal annual pattern, with some rain usually falling in every month. Malaria transmission intensity mirrors the rainfall pattern, with a lag of several weeks. The annual number of infective bites sustained per person varies by year, and is highly dependent upon which field and laboratory methods are used to collect and process mosquitoes, but generally ranges from 60 to 300 infective bites per person per year (Hawley WA and others, unpublished data). Except in cases of extreme and atypical drought, some transmission occurs in every month.
Approximately 90% of the malaria infections are due to Plasmodium falciparum; infection with P. malariae makes up most of the balance, along with an occasional P. ovale infection. Three mosquito species transmit nearly all of the malaria here, with Anopheles gambiae and An. funestus responsible for more than 90% of the transmission and An. arabiensis responsible for most of the rest. Both An. gambiae and An. funestus bite primarily indoors late at night; their biting is thus diminished by use of ITNs.
Mapping of the study area and distance calculations. The Global Positioning System (GPS) was used to map the approximate center of all study compounds, clinics, boreholes, roads, rivers, schools, churches, market centers, the shore of Lake Victoria, and obvious mosquito larval habitat. A base station unit established at the Kenya Medical Research Institute in Kisian allowed correlation of readings from field GPS units. This differential processing allowed us to obtain measurements of latitude, longitude, and elevation for each point to an accuracy of less than one meter.12,13 Positions were read into ArcView GIS14 software for production of maps and distance calculations.
Figure 1B
illustrates the method used to calculate the three geographic exposure variables used in this analysis: distance from control compounds to the nearest ITN compound, distance from ITN compounds to the nearest control compound, and proportion of compounds with ITNs within 300 meters of control compounds. Distances were calculated using an accepted standard formula.15 The 300-meter interval for the main exposure variables was based upon the observation that this distance range divides the number of compounds of each type into approximately equal quartiles (Table 1
). All distance calculations were done on the basis of intent to treat; all compounds in ITN villages were assumed to have ITNs and all compounds in control villages were assumed to lack ITNs. Other distance variables mapped and used as covariates in some analyses included distance to the shore of Lake Victoria, distance to the nearest clinic, and distance to the nearest borehole.
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Data analysis. We analyzed the effect of proximity to compounds with ITNs on six outcome measures. With the exception of mortality, all outcomes were examined in children less than three years of age. The six outcome measures were 1) mortality of children 159 months old; 2) moderate anemia defined as a hemoglobin level <9 g/dL; this level was chosen since cut-off values reflecting more severe anemia yielded insufficient statistical power; 3) hemoglobin level as a continuous variable (in g/dL); 4) high density of P. falciparum infection defined as a parasitemia >5,000 parasites/mm3; 5) clinical malaria defined as any level of parasitemia plus fever; and 6) any helminth infection, included as an internal control.
The mortality analysis was done using methods described by Phillips-Howard and others.17 Briefly, the following covariates were incorporated in the model: year of study (year 1 or year 2), age of child, rainfall (during the previous month), and temperature (during the previous week). Weather variables were included to control for seasonality of malaria transmission while the study year variable is intended to control for temporal variation in the efficacy of the ITN intervention itself. We used survival analysis (Procedure PHREG of SAS, version 8.1)18 and controlled for clustering by village.
For the morbidity analysis, which was based on cross-sectional data,16 the following covariates were included in all models as categorical variables: age, sex, weight for age, cross-sectional number, and distance to the nearest clinic. In initial models, various socioeconomic indices were included as independent variables, but these were later excluded because of collinearity with the childs nutritional status. By similar logic, indices of rainfall likely duplicated the effect of controlling for survey number, so these were also excluded. Other variables examined were elevation, distance to the nearest borehole, and distance to the shore of Lake Victoria, but these were found to be neither significant nor confounding relationships of interest, so were excluded from final models.
All models controlled for clustering by village with an exchangeable correlation structure assumed for residents within a village. Dichotomous health outcomes were modeled using a logistic regression. Continuous health outcomes (hemoglobin level) were modeled using an identity link function and a normal distribution. All models were created using Procedure Genmod, a procedure within SAS, version 8.1.
The first set of models describe the relationship between health outcomes and the location of a compound within ITN and control villages relative to the distance to the nearest compound with a different intervention status. Compounds in control villages that are
900 meters from the nearest ITN village served as the comparison group for these analyses. A total of seven dichotomous variables were created that contained all other compounds. For control villages, we created three variables for compounds that were 0299, 300599, or 600899 meters from the nearest ITN compound. For ITN villages, we created four variables for compounds 0299, 300599, 600899, and
900 meters from the nearest control compound. The intent of this analysis was to allow us to illustrate spatial patterns of effect in a straightforward way; however, the cost of this approach was some loss in statistical power. These distance categories approximate compound distribution by quartiles as shown in Table 1
. Additional tests of trend were performed using the same reference group and control compound distance categories, but combining ITN compounds into a separate variable; thus trends were evaluated only in control compounds.
Since the strongest community effect was observed in control areas within 300 meters of ITN villages, we constructed models to describe the relationship between health outcomes and the percentage of homes within 300 meters of compounds in this area. In this way, we were able to model coverage, here defined as the proportion of homes within 300 meters with ITNs, in the region of our study area where coverage varied most widely. The effect of increasing percentage coverage was modeled both categorically and by trend test.
Ethical clearance. The bed net trial was reviewed and approved by the institutional review boards of the Kenya Medical Research Institute (Nairobi, Kenya) and the Centers for Disease Control and Prevention (Atlanta, GA). Informed consent was obtained from all caregivers after the study was explained in the local language.
| RESULTS |
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Results of tests of trend reflect the patterns visible in Figure 2
for clinical malaria (odds ratio [OR] = 0.92, 95% confidence interval [CI] = 0.75, 1.12, P = 0.38), high-density parasitemia (OR = 0.89, 95% CI = 0.78, 1.01, P = 0.08), moderate anemia (OR = 0.78, 95% CI = 0.69, 0.89, P = 0.0001), hemoglobin level regression coefficient (OR = 0.18, 95% CI = 0.06, 0.31, P = 0.0048), and child mortality (hazard ratio = 0.94, 95% CI = 0.90, 0.98, P = 0.002). For all of these malaria-related outcomes, trends are in the direction indicating greater protection in compounds closer to intervention villages, with strongly significant trends seen for mortality, anemia, and hemoglobin level. For geohelminth infection, no trend was observed (OR = 1.09, P = 0.47).
The relationship between coverage and the community effect are shown in Figure 3
. Within the 300-meter band of control compounds nearest to ITN compounds, the strength of this community effect is dependent upon the proportion of compounds with ITNs. For high parasitemia and anemia, significant protective effects are observed only when coverage exceeds 50%. For hemoglobin level, maximal effect is seen when coverage is greater than 50%. No effect was observed for any outcome when coverage was less than 25%; no pattern was observed for helminth infection. Results of trend tests show significantly increasing protection with increasing coverage for clinical malaria (P = 0.027), high-density parasitemia (P = 0.049), anemia (P = 0.0024), and hemoglobin level (P = 0.0016), but not for helminth infection (P = 0.31). Results for clinical malaria (for the analysis illustrated in Figure 3
) and mortality are not presented since models did not converge due to low frequency of these end points.
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| DISCUSSION |
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These results are consistent with the analysis of child morbidity and mortality data from two other large-scale ITN trials in Africa. In Ghana, Binka and others8 showed that mortality rates of children living in control compounds increased with increasing distance from the nearest ITN compound. Similarly, rates of severe clinical malaria in coastal Kenya were lower in children living in houses lacking ITNs but living in villages where most families had nets.7 A community effect for important health measures therefore appears to be commonly associated with use of ITNs. In our study, 23% of the population of the control villages lived within 300 meters of ITN villages. Residents of these villages received as much protection from ITNs as those living in villages within the intervention zone.
The clarity of the community effect we observed, with strongly significant trends seen for mortality, moderate anemia, and hemoglobin level, coupled with the observation that the strength of this effect is strongly correlated with coverage, lead us to consider two different models of ITN action. The prevalent view at present is that ITNs are a barrier to biting of mosquitoes, and that most of the effect of ITNs is at the level of the individual net user. Although no data support this view, it is a logical and obvious one. An alternative view is that the community effect is exceptionally strong, at least in the context of an efficacy trial with high coverage, and that most of the effect of nets stems from area-wide effects on mosquito populations. The fact that the efficacy of nets in reducing mortality and four separate measures of malaria morbidity is approximately the same in control compounds proximate to netted areas supports this conclusion. The degree to which protection of non-netted houses occurs varies in a clear dose-response, and the proportion of nearby compounds having ITNs is also consistent with this hypothesis. Low levels of coverage are associated with a weak community effect; high levels of coverage (greater than 50% of the compounds) are associated with a strong community effect.
These data support the existence of a strong community effect, but they tell us nothing directly about the relative strength of the individual barrier and community effects. To do so, we must infer a plausible mechanism of ITN action that incorporates information on the roles of three interrelated factors: the net as a barrier preventing mosquito feeding on individual net users; community coverage of nets, with effects on mosquito populations; and the insecticide. However, some level of inference is possible, based upon our data and those of other workers. Nets, when properly deployed, clearly act as a barrier to feeding, but, on a community level, sufficient reduction in mosquito feeding to cause a decrease in sporozoite rates in mosquitoes or malaria parasitemia in humans required a relatively high level of coverage in Papua New Guinea villages even when all nets were untreated.5,6 Remarkably, effects on parasitemia in humans were more dependent upon coverage than upon individual use of nets. These investigators hypothesize that the coverage-dependent area-wide effects observed in their study were due to reduced longevity of anthropophilic vectors forced to expend extra energy in a search for blood. In our study, which found marked effects of coverage on malaria morbidity using ITNs (Figure 3
), difficulties in obtaining blood are compounded by the poisonous effects of insecticide. That child mortality increased in our study with increasing time since re-treatment with insecticide drives home the importance of the insecticide.17 The exhaustive review of Lengeler19 comparing effects of treated nets when controls are either no nets or untreated nets further supports the beneficial impact of insecticide. Data showing possible efficacy of untreated nets, recently reviewed by Guyatt and Snow,20 fail to take into account coverage effects and thus may overestimate efficacy of untreated nets in areas of low coverage. It is important to note that there are no field data showing efficacy of nets, either treated or untreated, when coverage is low. Field trials of nets have usually been in the context of high coverage. If not, the extent of coverage has typically been unmeasured or not included as a covariate in estimation of the effect of nets.
We note that the relative importance of individual and community effects may depend upon an interaction of many factors including anthropophily of vectors, availability of alternative hosts, absolute distances among households, density and distribution of larval habitats in relation to blood meal sources, and the type of insecticide used.
All of the heretofore measured impact of ITNs is due to two primary factors: insecticide and coverage. If the individual protective effect of nets is relatively small, then the gap between efficacy of ITNs, as estimated through randomized controlled trials where every effort is made to ensure high coverage with properly treated nets, and effectiveness of ITN intervention programs is likely to be very large unless programs recognize and act upon the knowledge that it is the community effect of insecticide associated with large and dense population of ITNs, not the individual nets themselves, that underlies a large part of the potency of this intervention.
The conclusion that a strong community effect is associated with an ITN intervention programs helps clarify the mechanism by which this intervention works. However, it is not grounds for foolish optimism; low levels of coverage with treated nets or, worse, untreated or poorly treated nets, may do little but fritter away scarce resources. In contrast, high coverage with ITNs will do more for public health in Africa than previously imagined.
Acknowledgments: The authors thank the residents of Asembo for their participation in this study. Many people assisted with field activities and data management; special thanks are due to George Olang and Erik Schoute for their assistance. We also thank all of those at the Centers for Disease Control and Prevention (Atlanta, GA) who supported our efforts to apply GPS mapping technology and spatial analytic techniques to the ITN project. This paper is published with the permission of the Director of the Kenya Medical Research Institute.
Financial support: The ITN project was funded by the United States Agency for International Development.
Disclaimer: The opinions or assertions contained in this manuscript are the private ones of the authors and are not to be construed as official or reflecting the views of the U.S. Public Health Service or Department of Health and Human Services. Use of trade names is for identification only and does not imply endorsement by the U.S. Public Health Service or Department of Health and Human Services.
Authors addresses: William A. Hawley, Penelope A. Phillips-Howard, Feiko O. ter Kuile, Dianne J. Terlouw, John E. Gimnig, Margarette S. Kolczak, and Allen W. Hightower, Division of Parasitic Diseases, National Center for Infectious Diseases, Centers for Disease Control and Prevention, Mailstop F-22, 4770 Buford Highway, Atlanta, GA 30341. John M. Vulule, Maurice Ombok, and Simon K. Kariuki, Centre for Vector Biology and Control Research, Kenya Medical Research Institute, PO Box 1578, Kisumu, Kenya. Bernard L. Nahlen, Roll Back Malaria, World Health Organization, Avenue Appia 20, 1211 Geneva 27, Switzerland.
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W. A. HAWLEY, F. O. TER KUILE, R. S. STEKETEE, B. L. NAHLEN, D. J. TERLOUW, J. E. GIMNIG, Y. P. SHI, J. M. VULULE, J. A. ALAII, A. W. HIGHTOWER, et al. IMPLICATIONS OF THE WESTERN KENYA PERMETHRIN-TREATED BED NET STUDY FOR POLICY, PROGRAM IMPLEMENTATION, AND FUTURE RESEARCH Am J Trop Med Hyg, April 1, 2003; 68(90040): 168 - 173. [Abstract] [Full Text] [PDF] |
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