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Forests Sourcebook - HCV Resource Network

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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 />

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