Forests Sourcebook - HCV Resource Network
Forests Sourcebook - HCV Resource Network
Forests Sourcebook - HCV Resource Network
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
NOTE 7.3<br />
Spatial Monitoring of <strong>Forests</strong><br />
Remote sensing (RS) has become part of most forest<br />
management strategy implementations. While the<br />
technology for RS has evolved, aerial photography<br />
has been in use for almost a century, and satellites have been<br />
recording forest change for more than 35 years. Landsat,<br />
launched in 1972, was one of the first satellites widely used<br />
for remote sensing. Since then, Landsat has been a workhorse<br />
for scientists interested in measuring changes in the<br />
distribution and condition of forests. Remote sensing (aerial<br />
flights, aerial photography, optical and radar satellite<br />
imagery) and GIS have aided forest mapping and forest<br />
inventories for many years.<br />
Two trends have stimulated the rise of spatial monitoring.<br />
First, technological advances in RS/GIS make these<br />
tools more accessible; human capacity to manipulate this<br />
data has also increased while information has become more<br />
accurate, less expensive, and more freely circulated. In addition,<br />
there is a wider choice of satellites, prices of satellites<br />
have deceased significantly, 1 the Internet is widely used to<br />
share data, and more affordable and more user-friendly<br />
RS/GIS software is now readily available.<br />
Second, in addition to these technical advances, a variety<br />
of needs are increasing demand for forest monitoring. The<br />
impetus to monitor comes from, among other things, the<br />
need to assess national-level compliance with international<br />
conventions, and measure global public goods (for example,<br />
carbon sequestration, area under protection for conservation<br />
purposes, and the like). RS/GIS technology provides<br />
the data and the tools needed for monitoring by enabling<br />
precise overlays between different time periods within specific<br />
boundaries, and by storing and analyzing the data.<br />
However, because inventories and mapping are frequently<br />
time intensive and expensive, they are often carried out only<br />
in specific regions or for specific purposes. To date, only six<br />
attempts to map forests worldwide exist.<br />
Various local, national, and international entities systematically<br />
collect, examine, and disseminate data about<br />
forest resources throughout the world. Nevertheless, efforts<br />
at these different levels to systematically collect, examine,<br />
and disseminate data about forest resources are done independently<br />
of one another, and use different definitions and<br />
measurements. Accordingly, comparison of results is difficult,<br />
major knowledge gaps remain in large areas, and<br />
duplications exist in others. Only a few countries use spatial<br />
information for national forest inventories that are updated<br />
and suitable to address current environmental issues (see<br />
boxes 7.16 and 7.17 for examples).<br />
Spatial monitoring has become increasingly important<br />
in the context of REDD. For REDD, even minimum<br />
requirements to develop national deforestation databases<br />
using typical and internationally agreed on methods will<br />
require using RS data. The data would help assess gross<br />
deforestation, possibly develop a map of national forest<br />
area, and present a visual representation of forest cover<br />
change. Spatial monitoring, in some cases, is already part of<br />
discussions for monitoring land use, land-use change and<br />
forestry (LULUCF) (see box 7.18).<br />
Independent of demand, there are challenges to effective<br />
spatial monitoring of forests:<br />
■<br />
Availability of RS data. Detailed data (that is, certain<br />
satellite sensors and aerial photographs) must be<br />
ordered in advance and may not be available in the short<br />
term. Clouds often hamper monitoring in the tropics<br />
and in mountainous areas, and can become a major<br />
problem, especially for data acquired with less frequency<br />
(for example, it can take more than a year to get a<br />
detailed resolution image with less than 30 percent cloud<br />
cover in Indonesia). Because higher temporal resolution<br />
satellites acquire data more often, they have better opportunities<br />
to acquire imagery with fewer clouds. Another<br />
alternative is the use of radar satellites because radar sensors<br />
“see” through clouds. Nevertheless, radar applications<br />
for forest monitoring are still uncommon.<br />
274