| Literature DB >> 22187553 |
Sophia Giebultowicz1, Mohammad Ali, Mohammad Yunus, Michael Emch.
Abstract
This study uses social network and spatial analytical methods simultaneously to understand cholera transmission in rural Bangladesh. Both have been used separately to incorporate context into health studies, but using them together is a new and recent approach. Data include a spatially referenced longitudinal demographic database consisting of approximately 200,000 people and a database of all laboratory-confirmed cholera cases from 1983 to 2003. A complete kinship-based network linking households is created, and distance matrices are also constructed to model spatial relationships. A spatial error-social effects model tested for cholera clustering in socially linked households while accounting for spatial factors. Results show that there was social clustering in five out of twenty-one years while accounting for both known and unknown environmental variables. This suggests that environmental cholera transmission is significant and social networks also influence transmission, but not as consistently. Simultaneous spatial and social network analysis may improve understanding of disease transmission.Entities:
Year: 2011 PMID: 22187553 PMCID: PMC3236480 DOI: 10.1155/2011/604372
Source DB: PubMed Journal: Interdiscip Perspect Infect Dis ISSN: 1687-708X
Figure 1Matlab study area location within Bangladesh.
Figure 2Total cholera cases in the population of Matlab by month, occurring between the study period of 1983 and 2003.
Figure 3Total cholera cases in the population of Matlab by year.
Figure 4The coefficients representing the effect of social networks and spatial error, or unknown variables not captured in the model, on cholera incidence.
Spatial error and significance, social effect and significance, and environmental variables that affect cholera rate.
| Year | Spatial error | Significance | Social effect | Significance | Environmental control variables |
|---|---|---|---|---|---|
| 1983 | 0.47 | ** | 0.01 | ** | Pond**, tubewell* |
| 1984 | 0.48 | ** | 0.04 | Road* | |
| 1985 | 0.58 | ** | 0.05 | ** | Road*, pond* |
| 1986 | 0.61 | ** | −0.01 | Road** | |
| 1987 | 0.54 | ** | 0.00 | ||
| 1988 | 0.53 | ** | 0.00 | ||
| 1989 | 0.46 | ** | 0.28 | ** | |
| 1990 | 0.34 | ** | 0.00 | ||
| 1991 | 0.42 | ** | −0.01 | ||
| 1992 | 0.52 | ** | −0.01 | Pond*, tubewell* | |
| 1993 | 0.56 | ** | 0.15 | ** | |
| 1994 | 0.53 | ** | −0.01 | ||
| 1995 | 0.34 | ** | −0.01 | ||
| 1996 | 0.45 | ** | 0.00 | Tubewell depth** | |
| 1997 | 0.54 | ** | 0.03 | ||
| 1998 | 0.42 | ** | −0.01 | River*, tubewell depth** | |
| 1999 | 0.57 | ** | −0.01 | ||
| 2000 | 0.54 | ** | 0.14 | ** | |
| 2001 | 0.43 | ** | 0.00 | Road** | |
| 2002 | 0.45 | ** | −0.01 | Tube* | |
| 2003 | 0.51 | ** | −0.01 |
**P ≤ 0.01; *P ≤ 0.05.