From: Spatial correlations of mapped malaria rates with environmental factors in Belize, Central America
Area(%) | ||||||
---|---|---|---|---|---|---|
Orange | Stann | |||||
Vegetation type | Corozal (n = 30) | Walk (n = 22) | Belize (n = 25) | Cayo (n = 34) | Creek (n = 16) | Toledo (n = 29) |
Agriculture | 190.0 (74) | 148.2 (61) | 32.6 (11) | 246.2 (70) | 66.7 (42) | 230.9 (71) |
Broadleaf hill forests | 0 | 0 | 4.1 (1) | 44.8 (13) | 7.1 (4) | 51.1 (16) |
Basin mangrove forests | 0 | 0 | 5.7 (2) | 0 | 1.0 (1) | 0 |
Coastal fringe Rhizophora mangle-dominated forests | 4.3 (2) | 0 | 0.2 (<0.5) | 0 | 2.1 (1) | 2.7 (1) |
Dwarf mangrove scrub | 0.2 (<0.5) | 0 | 0.9 (<0.5) | 0 | 0 | 0 |
Disturbed scrub | 0 | 1.3 (1) | 5.5 (2) | 6.2 (2) | 1.9 (1) | 1.6 (<0.5) |
Freshwater swamp forest | 0 | 0 | 0 | 0 | 0 | 0.8 (<0.5) |
Inland well-drained shrubland | 0 | 0 | 0 | 0.8 (<0.5) | 0 | 0 |
Lowland broadleaf moist evergreen seasonal forests | 8.1 (3) | 8.5 (4) | 88.0 (30) | 27.7 (8) | 6.4 (4) | 20.5 (6) |
Lowland broadleaf moist semi-evergreen scrub forest | 1.9 (1) | 0 | 0 | 0 | 8.0 (5) | 0 |
Lowland needle-leaf moist forest | 0 | 12.7 (5) | 54.4 (19) | 2.2 (1) | 7.9 (5) | 1.4 (<0.5) |
Mixed hill forests | 0 | 0 | 0 | 1.7 (<0.5) | 0 | 0 |
Needle-leaf hill forests | 0 | 0 | 0 | 15.4 (4) | 0 | 0 |
Mixed mangrove scrub | 0 | 0 | 0 | 0 | 5.5 (3) | 0 |
Riverine mangrove forests | 17.8 (7) | 29.2 (12) | 5.2 (2) | 0 | 1.1 (1) | 0.2 (<0.5) |
Seasonal swamp forests | 15.4 (6) | 19.1 (8) | 32.5 (11) | 0 | 1.2 (1) | 10.9 (3) |
Seasonally water-logged fire-induced shrubland of the plains | 0 | 6.5 (3) | 20.7 (7) | 1.1 | 41.5 (26) | 3.6 (1) |
Seasonally water-logged scrub | 0 | 5.8 (2) | 6.9 (2) | 6.5 (2) | 0 | 0 |
Tall herb wetland communities | 1.9 (1) | 9.2 (4) | 3.8 (1) | 0 | 0 | 0 |
Urban | 9.5 (4) | 0 | 20.9 (7) | 0.6 (<0.5) | 7.0 (4) | 2.5 (1) |
Water | 8.5 (3) | 2.0 (1) | 9.5 (3) | 0 | 1.7 (1) | 0.1 (<0.5) |