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Nevada Greenhouse Gas Inventory and Reference Case Projections

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FINAL <strong>Nevada</strong> GHG <strong>Inventory</strong> <strong>and</strong> <strong>Reference</strong> <strong>Case</strong> Projection<br />

CCS, July 2007<br />

associated forest carbon pools <strong>and</strong> the estimated flux). The sum of carbon stock changes for all<br />

forest carbon pools yields a total net CO 2 flux for forest ecosystems.<br />

In preparing these data, USFS estimates the amount of forest carbon in different forest types as<br />

well as different carbon pools. The different forests include those in the national forest system<br />

<strong>and</strong> those that are not federally-owned (private <strong>and</strong> other public forests). USFS also provides<br />

information on forests categorized as being either woodl<strong>and</strong>s (forests not used for timber<br />

harvesting) <strong>and</strong> non-woodl<strong>and</strong>s (such as timberl<strong>and</strong>s).<br />

The data shown in Table H1 are a summary of the FIA data used to derive the carbon pool <strong>and</strong><br />

flux estimates that are shown in Table H2. The previous inventory data came from either a<br />

previous FIA cycle or data from the Resources Planning Act Assessment (RPA). The Resources<br />

Planning Act requires the USFS to report on the state of US forest resources on a regular basis;<br />

the USFS publishes the RPA assessment every five years. FIA is a key contributor to RPA. RPA<br />

data, which are generally lower in resolution, are sometimes used in place of FIA cycles. The<br />

FIA has transitioned from a periodic to annual sampling design, which has created some data sets<br />

that are not comparable over time, in which case the RPA data are better suited for estimating<br />

carbon densities. 100 As shown in Table H1, the current forest carbon pool estimates are derived<br />

from 2005 FIA data. The previous inventory data came from a previous FIA cycle or RPA data.<br />

Table H1. Forest <strong>Inventory</strong> Data Used to Estimate Forest CO 2 Flux<br />

Current <strong>Inventory</strong><br />

Data Source<br />

Past <strong>Inventory</strong> Data<br />

Source<br />

Avg.<br />

Year a<br />

Interval b<br />

(yr)<br />

Current<br />

Forest<br />

Area (10 3<br />

hectares)<br />

Previous<br />

Forest<br />

Area (10 3<br />

hectares)<br />

Forest<br />

National Forest -<br />

Timberl<strong>and</strong>/Reserved/Low<br />

Productivity FISDB21_NV_02_2005 FISDB21_NV_01_1989 2005.1 8.5 290 251<br />

National Forest -Woodl<strong>and</strong>s FISDB21_NV_02_2005 FISDB21_NV_01_1989 2005.1 8.5 1,126 1,041<br />

Other Public/Private Forest –<br />

Timberl<strong>and</strong>/ Reserved/Low<br />

Productivity FISDB21_NV_02_2005 RPAdata_NV____1997 2005.2 19.8 480 212<br />

Other Public/Private Forest -<br />

Woodl<strong>and</strong>s FISDB21_NV_02_2005 FISDB21_NV_01_1989 2005.2 24.7 2,912 2,637<br />

Totals 4,807 4,140<br />

a Average year for the measurements that make up the current FIA inventory data (early 2005 for all forest types).<br />

b The number of years between the current inventory source <strong>and</strong> the past inventory source.<br />

The data in Table H1 show an increase of 667 kilo-hectares (1.6 million acres) in forested area<br />

during the period of analysis (1993-2003). Over 40% of this increase occurred in woodl<strong>and</strong><br />

forests (as mentioned under key uncertainties below, some of this difference is likely driven by<br />

methodological differences in survey methods between the two FIA cycles).<br />

100 Jim Smith, USFS, personal communication with K. Bickel, CCS, November 7, 2006.<br />

<strong>Nevada</strong> Division of 68 Center for Climate Strategies<br />

Environmental Protection<br />

www.climatestrategies.us

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