Recovery Plan for the Northern Spotted Owl - DRAFT
Recovery Plan for the Northern Spotted Owl - DRAFT Recovery Plan for the Northern Spotted Owl - DRAFT
The contrast between the behavior described by sociologists and the behaviordescribed by economists is worth noting. Economic models are based on theassumption that economic behavior is "rational." It is assumed, for example,that people are able to figure out and take the actions that would best improvetheir situations. Displaced workers, in this model, seek new training or moveto new locations with better employment opportunities. Sociologic models, incontrast, recognize that people respond to some traumatic experiences in waysthat prevent such economic adaptation. The resulting individual and communitybehavior patterns may inhibit people's recovery from traumatic changesin their situation.Lee and other sociologists suggested that programs to protect the owl beaccompanied by efforts to draw on the strengths of the people in timber dependentcommunities. Lee recommended, for example, that their entrepreneuriallifestyle and inventiveness be used to develop and implement silviculturalmethods that would promote the growth of owl habitat and increase the valueof timber that can be harvested.Lee's work also points out the difficulties imposed on state and local governmentsby the combined effects of the unemployment and social effects resultingfrom owl habitat conservation and the decline in revenues received bycounties from federal timber sales (Lee 199 lb, and Bray and Lee 1991). Justas the demand for social services increases, the financial resources available tolocal governments will decrease because of the decline in federal timber receiptsin which they share. Counties with a high dependency on federal timberand an above average proportion of protected owl habitat will suffer disproportionately.Studies of this problem concluded that severely affected counties could havedifficulty maintaining essential services and meeting the additional needscaused by economic dislocation. Many counties, particularly in Oregon, havereceived more than 50 percent of their revenues from federal timber receipts(Bray and Lee 1991). Federal receipts have been allocated primarily to schoolsand roads but support other programs as well. Reductions in funds fromfederal timber receipts would force cuts in services that are not mandated bylaw such as preventive health care, social services such as counseling andyouth programs, parks and libraries. The reduction in such services is expectedto heighten the social costs in communities hit by permanent reductionsin employment opportunities and other effects of owl conservationpolicies.C. Indicators of the Timber Dependency of LocalEconomiesOne of the opportunities to reduce the economic and social costs of achievingrecovery for the owl is to reduce the amount of habitat preservation in areaswhere it causes the highest cost. It is useful to identify those communitieswhere people's incomes are most directly tied to timber harvests that might beaffected by owl conservation. A closely related factor is the extent to whichpeople will be able to find employment in other sectors because of the proximityto more diverse urban economies or local opportunities for economicdiversification. Several of the studies reviewed by the Recovery Team includedefforts to measure timber dependency. Instead of developing new indicators,the Recovery Team drew upon these efforts. They are summarized here.The Beuter study included a substantial effort by Douglas C. Olson to assessthe timber dependency of various multicounty regions in the three-state area.550
Table H.2, taken from the Beuter study, summarizes the results of that effort,and shows that the highest dependency on timber occurs in southwest Washingtonand Southwest Oregon. West-central Oregon, the Olympic Peninsula,and western Oregon fall into a second tier of high dependency.The FWS study developed job response coefficients for the 55 counties affectedby owl conservation efforts. These coefficients reflect the flow of logs fromharvest sites to mills and the direct and total employment that results in eachcounty per million board feet of timber harvest. Table H.3 shows the jobresponse coefficients for the 55 counties from the FWS study.The FWS analysis also examined a variety of other economic indicators at thecounty level including unemployment, per capita income, percent of employmentin the timber and wood products industries, the percent of federallyowned land and dependence on federal timber harvest, and the effect of reductionsin timber harvest on county revenues. These statistics are summarizedin Table H.4.Trends in economic development and population growth provide an importantindicator of recent diversification in county economic structure. Counties thathave experienced rapid population and income growth are participating in thegeneral diversification of the economic structure in the Pacific Northwest,primarily through growth in service sectors and light industry. Data onchanges in employment in timber and manufacturing assembled by the FWSfor the 55 counties that may be affected by owl conservation also are includedin Table H.4.The FWS considered these factors in designing a process for deciding whetherto exclude areas from the designation of critical habitat (USDI 1992). It usedthe effects on county budgets and timber based employment to identify 13counties on which to focus exclusion decisions. These counties are:Washington Oregon CaliforniaChelan Curry TrinityClallamDouglasLewisHood RiverSkamaniaJacksonJosephineLaneTillamookWascoThe State of Washington has completed an evaluation of the potential jobs lostdue to efforts to conserve the northern spotted owl. Using ISC recommendationsas a benchmark and recent harvest levels as a base, 8,200 jobs in theforest products industry are considered to be at risk. These are distributed asfollows:Olympic Peninsula 1,161Northwest Washington 1,849Southwest Washington 1,964Central Washington 855Puget Sound 2,234Eastern Washington 136When indirect employment is considered in addition to the direct employmentin the forest products industry, the total potential job loss in Washington is20,800. These estimates reflect the actual harvest in recent years rather thantimber sale plans and include indirect employment impacts for the entire state.551
- Page 516 and 517: Basal area growth continued to incr
- Page 518 and 519: technology probably will allow some
- Page 520 and 521: Stand A. No activities (west side 3
- Page 522 and 523: Stand A. No activities (west side o
- Page 524 and 525: acre, 4 to 12 inches in diameter),
- Page 526 and 527: allow redwood sprout clumps maximum
- Page 528 and 529: KAge 15 years - 511 trees per acre,
- Page 530 and 531: 6Stems per acre100 _ Stand A. Natur
- Page 532 and 533: Basal Area(square feetper acre)50 1
- Page 534 and 535: * Opening the canopy in small patch
- Page 536 and 537: Drew, T.J. and J.W. Flewelling. 197
- Page 538 and 539: Miller, R.E.; D.L. Reukema, and R.L
- Page 540 and 541: Tappeiner, J.C., P.M. McDonald, and
- Page 542 and 543: 526
- Page 544 and 545: 528
- Page 546 and 547: 6. Timber supply curve and economic
- Page 548 and 549: scientifically credible biological
- Page 550 and 551: E. Summary of Preliminary Estimates
- Page 552 and 553: II. General Economic Principles for
- Page 554 and 555: practices may be able to show how s
- Page 556 and 557: Economic patterns show the efficien
- Page 558 and 559: The sustainable yield concept that
- Page 560 and 561: A. Previously Estimated Economic Co
- Page 562 and 563: County receipts were estimated to d
- Page 564 and 565: B. Potential Social Costs of Owl Co
- Page 568 and 569: 0U1 n1nDTable H.2. Economic depende
- Page 570 and 571: cḻlTable H.4. Economic characteri
- Page 572 and 573: An analysis completed by the State
- Page 574 and 575: V. Preliminary Evaluation of the Ec
- Page 576 and 577: 25-° 20/0M 15-a)CLU)0 10-0CL 5 -0)
- Page 578 and 579: 25 -- 20-0co/o 15--Da)a0a)10m~ C) 5
- Page 580 and 581: forestlands. The costs of productio
- Page 582 and 583: In Figure H.8, the equilibrium betw
- Page 584 and 585: foregone and the way they will save
- Page 586 and 587: The income created by the purchase
- Page 588 and 589: Two concepts are useful for underst
- Page 590 and 591: y an estimate of the price that wou
- Page 592 and 593: Table H.10. Comparison of timber em
- Page 594 and 595: of the second year. The same assump
- Page 596 and 597: are generally much lower than for c
- Page 598 and 599: 582
- Page 600 and 601: studies at University of Washington
- Page 602 and 603: 586
- Page 604 and 605: Most significant late successionall
- Page 606 and 607: to evaluate options. Information in
- Page 608 and 609: Q0Table 1.1. Estimated acres and ow
- Page 610 and 611: soTable 1.3. Estimated acres and ow
- Page 612 and 613: 01CDarTable 1.5. Size class distrib
- Page 614 and 615: Table 1.8. Frequency distribution o
The contrast between <strong>the</strong> behavior described by sociologists and <strong>the</strong> behaviordescribed by economists is worth noting. Economic models are based on <strong>the</strong>assumption that economic behavior is "rational." It is assumed, <strong>for</strong> example,that people are able to figure out and take <strong>the</strong> actions that would best improve<strong>the</strong>ir situations. Displaced workers, in this model, seek new training or moveto new locations with better employment opportunities. Sociologic models, incontrast, recognize that people respond to some traumatic experiences in waysthat prevent such economic adaptation. The resulting individual and communitybehavior patterns may inhibit people's recovery from traumatic changesin <strong>the</strong>ir situation.Lee and o<strong>the</strong>r sociologists suggested that programs to protect <strong>the</strong> owl beaccompanied by ef<strong>for</strong>ts to draw on <strong>the</strong> strengths of <strong>the</strong> people in timber dependentcommunities. Lee recommended, <strong>for</strong> example, that <strong>the</strong>ir entrepreneuriallifestyle and inventiveness be used to develop and implement silviculturalmethods that would promote <strong>the</strong> growth of owl habitat and increase <strong>the</strong> valueof timber that can be harvested.Lee's work also points out <strong>the</strong> difficulties imposed on state and local governmentsby <strong>the</strong> combined effects of <strong>the</strong> unemployment and social effects resultingfrom owl habitat conservation and <strong>the</strong> decline in revenues received bycounties from federal timber sales (Lee 199 lb, and Bray and Lee 1991). Justas <strong>the</strong> demand <strong>for</strong> social services increases, <strong>the</strong> financial resources available tolocal governments will decrease because of <strong>the</strong> decline in federal timber receiptsin which <strong>the</strong>y share. Counties with a high dependency on federal timberand an above average proportion of protected owl habitat will suffer disproportionately.Studies of this problem concluded that severely affected counties could havedifficulty maintaining essential services and meeting <strong>the</strong> additional needscaused by economic dislocation. Many counties, particularly in Oregon, havereceived more than 50 percent of <strong>the</strong>ir revenues from federal timber receipts(Bray and Lee 1991). Federal receipts have been allocated primarily to schoolsand roads but support o<strong>the</strong>r programs as well. Reductions in funds fromfederal timber receipts would <strong>for</strong>ce cuts in services that are not mandated bylaw such as preventive health care, social services such as counseling andyouth programs, parks and libraries. The reduction in such services is expectedto heighten <strong>the</strong> social costs in communities hit by permanent reductionsin employment opportunities and o<strong>the</strong>r effects of owl conservationpolicies.C. Indicators of <strong>the</strong> Timber Dependency of LocalEconomiesOne of <strong>the</strong> opportunities to reduce <strong>the</strong> economic and social costs of achievingrecovery <strong>for</strong> <strong>the</strong> owl is to reduce <strong>the</strong> amount of habitat preservation in areaswhere it causes <strong>the</strong> highest cost. It is useful to identify those communitieswhere people's incomes are most directly tied to timber harvests that might beaffected by owl conservation. A closely related factor is <strong>the</strong> extent to whichpeople will be able to find employment in o<strong>the</strong>r sectors because of <strong>the</strong> proximityto more diverse urban economies or local opportunities <strong>for</strong> economicdiversification. Several of <strong>the</strong> studies reviewed by <strong>the</strong> <strong>Recovery</strong> Team includedef<strong>for</strong>ts to measure timber dependency. Instead of developing new indicators,<strong>the</strong> <strong>Recovery</strong> Team drew upon <strong>the</strong>se ef<strong>for</strong>ts. They are summarized here.The Beuter study included a substantial ef<strong>for</strong>t by Douglas C. Olson to assess<strong>the</strong> timber dependency of various multicounty regions in <strong>the</strong> three-state area.550