13.07.2015 Views

Improving Fire Hazard Assessment at the Urban-Wildland Interface ...

Improving Fire Hazard Assessment at the Urban-Wildland Interface ...

Improving Fire Hazard Assessment at the Urban-Wildland Interface ...

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

United St<strong>at</strong>esDepartment ofAgricultureForest ServicePacific SouthwestResearch St<strong>at</strong>ion<strong>Improving</strong> <strong>Fire</strong> <strong>Hazard</strong> <strong>Assessment</strong> <strong>at</strong><strong>the</strong> <strong>Urban</strong>-<strong>Wildland</strong> <strong>Interface</strong>: CaseStudy in South Lake Tahoe, CACenter for <strong>Urban</strong>Forest ResearchInternal Report<strong>Fire</strong>-1Lisa de Jong, Ph. D.AbstractA fire hazard assessment was conductedon priv<strong>at</strong>e, developed lots in South LakeTahoe, a high fire hazard urban-wildlandinterface community in Nor<strong>the</strong>rn California.<strong>Fire</strong> hazard was assessed in terms of <strong>the</strong>minimum standards set forth in <strong>the</strong> N<strong>at</strong>ional<strong>Fire</strong> Protection Associ<strong>at</strong>ion’s (NFPA)Standard 299 and homeowner practicessuch as compliance with <strong>the</strong> fire safety lawPRC 4291, construction m<strong>at</strong>erials of <strong>the</strong>home, and irrig<strong>at</strong>ion. In addition, <strong>the</strong>influence on small parcel fire hazard byneighbors was assessed.Results indic<strong>at</strong>ed th<strong>at</strong> <strong>the</strong> overall firehazard r<strong>at</strong>ing for <strong>the</strong> city was rel<strong>at</strong>ively lowbecause of its good roads, w<strong>at</strong>er, signage,and firefighting resources. However, <strong>the</strong>citywide non-compliance r<strong>at</strong>e for propertymaintenance was 66%, <strong>the</strong> citywide noncompliancer<strong>at</strong>e for defensible space was86% when adjusted for small parcel size,and 57% of <strong>the</strong> parcels were non-compliantfor both defensible space and maintenance.Clearly, homeowners in South LakeTahoe rarely choose for fire safety eventhough <strong>the</strong> city’s infrastructure is good.Fur<strong>the</strong>rmore, results demonstr<strong>at</strong>e th<strong>at</strong>assessing <strong>the</strong> city’s fire hazard using NFPA299 alone will underestim<strong>at</strong>e a parcel’s firehazard. Including an analysis of compliancer<strong>at</strong>es and homeowner practices will providea more accur<strong>at</strong>e estim<strong>at</strong>e of individual firehazard.IntroductionThe m<strong>at</strong>rix of homes and landscaping th<strong>at</strong>make up <strong>the</strong> urban forest of urban-wildlandinterface (UWI) communities is defined as afuel m<strong>at</strong>rix by <strong>the</strong> N<strong>at</strong>ional <strong>Fire</strong> ProtectionLISA DE JONG is a research forester <strong>at</strong> <strong>the</strong>Pacific Southwest Research St<strong>at</strong>ion, Center for<strong>Urban</strong> Forest Research, One Shields Ave.,Rm. 1103, Davis, CA 95616


Associ<strong>at</strong>ion (NFPA 299). In contrast towildland areas, this fuel m<strong>at</strong>rix requiresactive homeowner involvement in firehazard mitig<strong>at</strong>ion. This necessity hasresulted in regul<strong>at</strong>ions governing <strong>the</strong>landscaping practices by priv<strong>at</strong>e landownersin <strong>the</strong> high fire hazard areas of California(CA PRC 4291). Designed with <strong>the</strong>importance of fuels reduction and structuresurvivability in mind (Brown 1994, Cohen1995, Tran 1992, Foote 1991), PRC 4291requires defensible space for <strong>at</strong> least 10meters around <strong>the</strong> home. It limits ahomeowner’s choice of plant species,density, and placement and regul<strong>at</strong>esmaintenance practices such as pruningtrees and removing ladder fuels.Though compliance with PRC 4291 mayincrease fire safety, <strong>the</strong> law does notrecognize (1) <strong>the</strong> variability in <strong>the</strong> individuallandscaping preferences th<strong>at</strong> people have,or (2) <strong>the</strong> impact of neighboring parcels on ahomeowner’s fire hazard. Residents <strong>at</strong> <strong>the</strong>UWI have unique, individual sets of valuesand preferences th<strong>at</strong> are reflected in <strong>the</strong>landscapes <strong>the</strong>y cre<strong>at</strong>e and maintainaround <strong>the</strong>ir homes. These values oftenconflict with <strong>the</strong> principles of fire safety butproperty owners resist fire-safe regul<strong>at</strong>ionsif <strong>the</strong>y detract from wh<strong>at</strong> is valued in <strong>the</strong>landscape (Manfredo 1990, Abt 1991,Bailey 1991, Cortner 1991, Foote 1991,Smith 2001, Hodgson 1993, Winter 2000).In some communities, <strong>the</strong> combin<strong>at</strong>ion of<strong>the</strong>se two problems – small lot size andlandscape preferences – poses a significantbarrier to effective individual and communityfire hazard mitig<strong>at</strong>ion.This report describes a fire hazard analysisconducted on priv<strong>at</strong>e, developed lots inSouth Lake Tahoe, California. South LakeTahoe is a high fire hazard UWI communityin Nor<strong>the</strong>rn California where many of <strong>the</strong>developed lots are noncompliant with PRC4291 even though <strong>the</strong>re is active agencyoutreach and public support of fuelsreduction on undeveloped lots (Garrett,pers. comm., Harcourt, pers. comm.). <strong>Fire</strong>hazard was assessed according to <strong>the</strong>standards in NFPA 299, compliance withPRC 4291, construction m<strong>at</strong>erials of <strong>the</strong>home, irrig<strong>at</strong>ion practices, and <strong>the</strong> influenceon a parcel’s fire hazard by its immedi<strong>at</strong>eneighbors.Results indic<strong>at</strong>ed th<strong>at</strong> <strong>the</strong> overall fire hazardscore for <strong>the</strong> city was rel<strong>at</strong>ively low becauseof infrastructural components such as goodroads, w<strong>at</strong>er availability, signage, andfirefighting resources. Analysis of <strong>the</strong>components th<strong>at</strong> involve homeowner choiceonly (e.g. defensible space, maintenance,irrig<strong>at</strong>ion, and construction m<strong>at</strong>erials)indic<strong>at</strong>ed limited individual, parcel-scale firehazard mitig<strong>at</strong>ion efforts.Study siteSouth Lake Tahoe has approxim<strong>at</strong>ely24,000 inhabitants and is loc<strong>at</strong>ed on <strong>the</strong>south shore of Lake Tahoe, adjacent to <strong>the</strong>Nevada border. The gre<strong>at</strong>er Lake TahoeBasin extends across 88,000 hectares intwo st<strong>at</strong>es (California and Nevada) and fourcounties (El Dorado, Placer, Douglas andNevada). Its elev<strong>at</strong>ion ranges fromapproxim<strong>at</strong>ely 1900 m <strong>at</strong> <strong>the</strong> surface of <strong>the</strong>lake to about 3300 m <strong>at</strong> Freel Peak.Historically, fires in <strong>the</strong> Tahoe Basin wereprobably low and medium intensity surfacefires, occurring every 15 – 25 years andconsuming mostly light surface fuels, rarelybecoming stand-replacing events (Skinnerand Chang 1996). Eighty-five years of firesuppression in <strong>the</strong> basin (Murphy andKnopp 2001) combined with recent,prolonged drought conditions and extensivebug-kill have led to a build up of highlyflammable, hazardous fuel conditionsthroughout <strong>the</strong> area.The dominant conifer species in <strong>the</strong> lowermontane zone is ponderosa pine (Pinusponderosa), with some white fir (Abiesconcolor), incense cedar (Calocedrusdecurrens), and sugar pine (P. lambertiana).The upper montane zone (approx. 2000 –3000 m) is domin<strong>at</strong>ed by Jeffrey pine (P.jeffreyi) and also contains red fir (A.2


magnifica), white fir, western white pine (P.monticola) and some pure stands oflodgepole pine (P. contorta). In <strong>the</strong>subalpine zone (above 3000 m) speciesinclude whitebark pine (P. albicaulis) andmountain hemlock (Tsuga mertensiana)(Manley and Schlesinger 2001).The average January temper<strong>at</strong>ure for <strong>the</strong>basin is slightly below 0° C, <strong>the</strong> averageJuly temper<strong>at</strong>ure is approxim<strong>at</strong>ely 16° C,and <strong>the</strong> average annual precipit<strong>at</strong>ion is 74cm. Average annual snowfall ranges from2.5 m <strong>at</strong> <strong>the</strong> elev<strong>at</strong>ion of <strong>the</strong> lake to almost 9m in <strong>the</strong> mountains. At lake level, <strong>the</strong>re areon average only 70 – 100 frost-free daysper year (U. S. Environmental D<strong>at</strong>a Service2000).Archaeological evidence suggests th<strong>at</strong>human habit<strong>at</strong>ion of <strong>the</strong> Tahoe Basin beganwith <strong>the</strong> ancestors of <strong>the</strong> Washoe N<strong>at</strong>iveAmericans, who entered <strong>the</strong> Basin after <strong>the</strong>Sierran glaciers retre<strong>at</strong>ed 8,000 to 9,000years ago. The first non-N<strong>at</strong>ive settlersarrived in <strong>the</strong> basin after <strong>the</strong> discovery ofgold and silver in nearby Virginia City,Nevada. Early industry included logging,ranching, grazing and fishing. By <strong>the</strong> earlytwentieth century, less than half of <strong>the</strong> presettlementforest in <strong>the</strong> Tahoe Basinremained. While timber harvestingdecreased, grazing and ranching continuedbecause of <strong>the</strong> need for farm products for<strong>the</strong> basin’s expanding popul<strong>at</strong>ion.Management agencies and consortiumswere developed in <strong>the</strong> Lake Tahoe Basin tomitig<strong>at</strong>e <strong>the</strong> neg<strong>at</strong>ive ecological impacts of<strong>the</strong> basin’s growing popul<strong>at</strong>ion. Among <strong>the</strong>most visible are <strong>the</strong> Tahoe RegionalPlanning Agency (TRPA), <strong>the</strong> USDA ForestService’s Lake Tahoe Basin ManagementUnit (LTBMU), and Tahoe Re-Green. TheTRPA is a powerful regul<strong>at</strong>ory organiz<strong>at</strong>ionwhose primary objective is to develop landuse and management standards th<strong>at</strong>maximize environmental health and mitig<strong>at</strong>eneg<strong>at</strong>ive environmental impacts fromdevelopment (Murphy and Knopp, eds.2000). Since <strong>the</strong> early 1970s, TRPA hasprohibited development on environmentallysensitive parcels and has regul<strong>at</strong>ed priv<strong>at</strong>elandowners’ management of <strong>the</strong>ir ownparcels. To compens<strong>at</strong>e landowners, <strong>the</strong>LTBMU and <strong>the</strong> California St<strong>at</strong>e TahoeConservancy have purchased many of<strong>the</strong>se lots. The LTBMU also plays an activerole in fuel management on <strong>the</strong>undeveloped urban lots owned by <strong>the</strong>Forest Service. Tahoe Re-Green is aninteragency consortium th<strong>at</strong> aims to educ<strong>at</strong>eresidents and help <strong>the</strong>m reduce fire hazardby removing fuels on priv<strong>at</strong>ely owned land.MethodsSampling sites were chosen from apopul<strong>at</strong>ion of approxim<strong>at</strong>ely 6,500 singlefamilyresidential parcels. These parcelswere str<strong>at</strong>ified into low, medium, and highcanopy cover and into low, medium, or highdensity residential. A proportional alloc<strong>at</strong>ionmethod was used to determine <strong>the</strong> numberof parcels to be sampled within eachstr<strong>at</strong>um. In total, 102 parcels across <strong>the</strong> citywere sampled. The veget<strong>at</strong>ion andstructural characteristics of each parcelwere measured and mapped.The city was divided into six neighborhoodsbased on observed differences inveget<strong>at</strong>ion, lot, and building characteristics(Fig. 1) (de Jong, in review). The initialocular classific<strong>at</strong>ion was refined throughst<strong>at</strong>istical analysis for homogeneity in eachof <strong>the</strong> defined neighborhoods. Theboundaries of each neighborhoodencompass built areas within city limits andexclude unbuilt areas such as parks andgolf courses. Major roads defined <strong>the</strong>boundaries between adjacentneighborhoods.Neighborhood 1 was <strong>the</strong> Tahoe Keys,characterized by wide streets, canals, large,new homes and planted exotic veget<strong>at</strong>ionand turf grass. There was no significantslope on any of <strong>the</strong> parcels found in thisneighborhood. Neighborhood 2 – 5 weresimilar to one ano<strong>the</strong>r in terms of smallparcel and home size. Their veget<strong>at</strong>ion was3


domin<strong>at</strong>ed by n<strong>at</strong>ive conifer species with asparse assortment of exotic shrubs ando<strong>the</strong>r plants, though <strong>the</strong> speciescomposition and structure differed betweenneighborhoods. Some parcels were slightlysloped. Neighborhood 2 encompassed alarge area surrounding <strong>the</strong> “Y,” or <strong>the</strong>junction of Highways 50 and 89, including<strong>the</strong> tracts of Gardner Mountain, TahoeVista, Tahoe Island, St<strong>at</strong>e Name streets,and <strong>the</strong> area around <strong>the</strong> hospital.Neighborhood 3 was <strong>the</strong> tract consisting of<strong>the</strong> north-central part of <strong>the</strong> city.Neighborhood 4 was <strong>the</strong> Sierra Tract.Neighborhood 5 contained <strong>the</strong> Bijou and AlTahoe tracts. Neighborhood 6 was <strong>the</strong>affluent area of Heavenly Ski Resort andwas characterized by large, new homes,large lots, and dominance of n<strong>at</strong>ive coniferspecies. Slopes in this neighborhood weresignificant.A fire hazard analysis was conducted oneach parcel and <strong>the</strong>n compared qualit<strong>at</strong>ivelyto <strong>the</strong> fire hazard of neighboring parcels.The assessment was based on NFPA 299,which assigns a number score for riskfactors, compliance with PRC 4291,construction m<strong>at</strong>erials, and irrig<strong>at</strong>ion. Higherscores reflect higher fire hazard.Figure 1. -- Neighborhoods and characteristic lots as defined for this study. 1- Tahoe Keys; 2 – The Y; 3-North Central; 4- Sierra; 5- Bijou; 6- Heavenly.Lake Tahoe35 61424


The law (PRC 4291) requires homeownersto prune dead branches, clear needles ando<strong>the</strong>r litter from roofs and gutters, covervents with wire mesh, and clear treebranches for 3 m around chimney outlets.Characteristics known to contribute tostructural ignition potential, such as a woodroof and single-paned windows (Foote1991, White 2000, Quarles 2001, Quarles2002), were also r<strong>at</strong>ed.Compliance with PRC 4291 was analyzed interms of <strong>the</strong> cre<strong>at</strong>ion of defensible spacealone, maintenance alone, and <strong>the</strong>combin<strong>at</strong>ion of defensible space andmaintenance. Parcels demonstr<strong>at</strong>ing little orno defensible space were r<strong>at</strong>ed noncompliant.Parcels th<strong>at</strong> were non-compliantwith one or more of PRC 4291’smaintenance requirements were alsoconsidered non-compliant.Parcels were fur<strong>the</strong>r assessed for presenceof irrig<strong>at</strong>ion, construction m<strong>at</strong>erials, parcelsize, and <strong>the</strong> presence of hazardous decks.Defensible space r<strong>at</strong>ings were adjusted forsmall parcels to account for neighboringveget<strong>at</strong>ion th<strong>at</strong> would influence <strong>the</strong> parcel’sfire hazard. Decks were consideredhazardous if <strong>the</strong>y were made of wood andgre<strong>at</strong>er than 0.5 m high and were openunderne<strong>at</strong>h or had flammable m<strong>at</strong>erialstored underne<strong>at</strong>h <strong>the</strong>m.Parcels were classified as small and under<strong>the</strong> direct influence of <strong>the</strong> fire hazard ofimmedi<strong>at</strong>e neighbors if <strong>the</strong> distancebetween <strong>the</strong> house and <strong>the</strong> side boundariesof <strong>the</strong> parcel was less than 7 m on ei<strong>the</strong>rside, if <strong>the</strong> difference between <strong>the</strong> totalwidth of <strong>the</strong> parcel and <strong>the</strong> total width of <strong>the</strong>house was less than 14 m, or if <strong>the</strong>difference between <strong>the</strong> total length of <strong>the</strong>parcel and <strong>the</strong> total length of <strong>the</strong> house wasless than 14 m. Larger parcels wereconsidered independent of neighboringparcels.The fire hazard r<strong>at</strong>ings of <strong>the</strong> individualsmall parcels were adjusted to include <strong>the</strong>fire hazard of neighboring parcels. Smallparcels with good defensible space and“rel<strong>at</strong>ively better” maintenance were r<strong>at</strong>ed<strong>the</strong> same for defensible space as a mediumor large parcel with moder<strong>at</strong>e defensiblespace. Small parcels with good defensiblespace and “same” rel<strong>at</strong>ive maintenancewere r<strong>at</strong>ed <strong>the</strong> same for defensible spaceas a medium or large parcel with gooddefensible space.Neighborhoods were assigned a mean firehazard r<strong>at</strong>ing based on <strong>the</strong> fire hazards of<strong>the</strong> parcels th<strong>at</strong> were sampled within <strong>the</strong>neighborhoods. The point scoring system isfound in Table 1. The range of possiblescores is 9 – 80 or more, depending on <strong>the</strong>number of decks present.ResultsOverall fire hazard r<strong>at</strong>ingThe mean citywide fire hazard r<strong>at</strong>ing was 30(s.d. 6), due in large part to <strong>the</strong> city’sinfrastructure, including good access (wide,paved roads), <strong>the</strong> availability of w<strong>at</strong>er, and<strong>the</strong> presence of city and agency fire-fightingresources (Table 2). As expected, <strong>the</strong>Tahoe Keys exhibited <strong>the</strong> lowest firehazard, with a mean fire hazard r<strong>at</strong>ing of 24(s.d. 5), and <strong>the</strong> Heavenly Ski Area had <strong>the</strong>highest (38, s.d. 7). The r<strong>at</strong>ing for <strong>the</strong>remaining neighborhoods ranged from 28 to30.Lot sizeThe sampled lots in South Lake Tahoe weresmall. Mean lot size varied from 585 m 2 in<strong>the</strong> Sierra tract to 1211 m 2 in Heavenly. Thedifference in size is explained by <strong>the</strong>vari<strong>at</strong>ion in <strong>the</strong> depth of <strong>the</strong> lots r<strong>at</strong>her than<strong>the</strong>ir width. The mean lot width citywide was22 m (s.d. 8.5 m). The lot size in <strong>the</strong> Sierr<strong>at</strong>ract was significantly smaller than any o<strong>the</strong>rneighborhood in <strong>the</strong> city.5


Table 1. Point scoring system for risk factors.RISK FACTORIngress/egressPrimary road widthAccessibilitySCORING1- two or more primary road3- one road, primary route5- one way in/out1- >6.1m3- 15m3- outside radius 40%Wall m<strong>at</strong>erials+1 – wood sidingWall, eave, roof vents+2 – some present without _ in. mesh coverPredominant number of window panes+1 – predominantly single-panedDeck height +1 – each deck with height > 0.5mOpen space below deck+1 – each deck with open space bene<strong>at</strong>hStorage of flammable m<strong>at</strong>erials under deck +1 – each deck with storage of flammables bene<strong>at</strong>hDeck m<strong>at</strong>erials+1 – each wooden deckParcel sizeAdjustments made for small parcelsRel<strong>at</strong>ive maintenance1- parcel is worse than neighbors3- about <strong>the</strong> same5- neighbors are worse than parcel6


Table 2. <strong>Fire</strong> hazard r<strong>at</strong>ing, non-compliance r<strong>at</strong>es, and risk factors in South Lake Tahoe neighborhoods.Risk FactorCityNeighborhoodTotal(n=102)Keys(n=15)The Y(n=22)N. Central(n=13)Sierra(n=22)Bijou(n=21)Heavenly(n=9)Mean fire hazardr<strong>at</strong>ing (s.d.)30 (6) 24 (5) 30 (4) 30 (6) 30 (6) 28 (5) 38 (7)Maintenance noncompliancer<strong>at</strong>eIndividual def.space noncompliancer<strong>at</strong>eIndividual totalnon-compliancer<strong>at</strong>eIndividual def.space noncompliancer<strong>at</strong>e(adjusted forsmall parcels)Individual totalnon-compliancer<strong>at</strong>e (adjusted forsmall parcels)Irrig<strong>at</strong>ion (% ofparcels with lessthan half irrig<strong>at</strong>ed)Mean slope %(s.d.)Wood exterior (%of homes)Wood roof (% ofhomes)Window hazard(% of homes)Deck hazard (%of homes)66 20 68 69 73 76 8975 47 86 85 77 62 10053 7 59 62 64 48 8986 80 91 92 82 81 10057 20 59 62 64 58 8952 13 45 69 59 58 782 (6) 0 (0) 0 (0) 0 (0) 1 (3) 0 (0) 15 (16)96 87 95 100 100 95 10031 27 18 54 27 29 5629 27 41 23 32 24 2267 60 68 77 73 48 89Compliance with PRC 4291Citywide, <strong>the</strong> majority of parcels hadincreased fire hazard r<strong>at</strong>ings because <strong>the</strong>ywere partially or wholly non-compliant withPRC 4291. Sixty-six percent of <strong>the</strong> sampledparcels were non-compliant with <strong>the</strong> law’srequirements for maintenance and 75%exhibited little or no defensible space. Intotal, 53% of <strong>the</strong> parcels were noncompliantfor both maintenance anddefensible space.When taking small parcel size intoconsider<strong>at</strong>ion, i.e. including <strong>the</strong> veget<strong>at</strong>ionof neighboring parcels in <strong>the</strong> defensiblespace analysis, 86% of <strong>the</strong> parcels werenon-compliant for defensible space and57% were non-compliant for bothmaintenance and defensible space.Adjusting <strong>the</strong> defensible space r<strong>at</strong>ing toaccount for neighboring lots had <strong>the</strong>gre<strong>at</strong>est effect on <strong>the</strong> defensible spacecompliance r<strong>at</strong>es for <strong>the</strong> Keys and for Bijou.Smaller changes were observed for <strong>the</strong> Y,


North Central, and Sierra. It had no effecton <strong>the</strong> 0% defensible space compliance r<strong>at</strong>efor Heavenly.Irrig<strong>at</strong>ionOver half <strong>the</strong> parcels citywide had irrig<strong>at</strong>ionon less than half of <strong>the</strong> veget<strong>at</strong>ion found on<strong>the</strong> parcel. The veget<strong>at</strong>ion in <strong>the</strong> Keys,which was domin<strong>at</strong>ed by turf grass andplanted exotics, was well irrig<strong>at</strong>ed, whileover 75% of <strong>the</strong> parcels in Heavenly, whichwere domin<strong>at</strong>ed by n<strong>at</strong>ive conifer stands,showed little evidence of irrig<strong>at</strong>ion. Lessthan one third of <strong>the</strong> parcels in <strong>the</strong> NorthCentral neighborhood were irrig<strong>at</strong>ed. From41% - 55% of <strong>the</strong> parcels in <strong>the</strong> o<strong>the</strong>rneighborhoods were irrig<strong>at</strong>ed.SlopeMost of <strong>the</strong> parcels th<strong>at</strong> were sampledexisted on little or no slope, with <strong>the</strong>exception of parcels in Heavenly, where <strong>the</strong>mean was 15% and <strong>the</strong> range was from 0%to 53%.Wall m<strong>at</strong>erialThe preferred building m<strong>at</strong>erial for homes inSouth Lake Tahoe was wood. 96% of <strong>the</strong>homes in <strong>the</strong> sample had exterior walls th<strong>at</strong>were shakes, logs, or wood siding. Thirteenpercent of <strong>the</strong> homes in <strong>the</strong> Keys werepredominantly brick, stucco, or stone, butfrom 95 – 100% of <strong>the</strong> homes in <strong>the</strong>remaining neighborhoods had woodexteriors.Roof m<strong>at</strong>erialCitywide, 31% of <strong>the</strong> sampled homes had asignificant increase in susceptibility toignition because of wood roofs.Neighborhoods where more than half <strong>the</strong>homes had wood roofs were North Central(54%) and Heavenly (56%). The fewestnumber were found in <strong>the</strong> neighborhood of<strong>the</strong> Y (18%).Window panesCitywide, 29% of <strong>the</strong> sampled homes hadincreased fire hazard due to <strong>the</strong> presence ofsingle-paned glass in over half <strong>the</strong> windowsof <strong>the</strong> home. The highest percentage ofhomes th<strong>at</strong> had predominantly single-panedwindows was in <strong>the</strong> neighborhood of <strong>the</strong> Y(41%), while <strong>the</strong> lowest was in Heavenly(22%).<strong>Hazard</strong>ous decks<strong>Hazard</strong>ous decks were found on 67% of <strong>the</strong>homes citywide. Deck construction andplacement was particularly problem<strong>at</strong>ic inHeavenly, where slopes were gre<strong>at</strong>est. Inth<strong>at</strong> neighborhood, eight of <strong>the</strong> nine parcelssampled had hazardous decks. In Bijou only48% of <strong>the</strong> homes had hazardous decks,while 60 – 73% of <strong>the</strong> homes in <strong>the</strong>remaining neighborhoods had hazardousdecks.DiscussionThe results of this study clearly indic<strong>at</strong>e th<strong>at</strong>standard city-scale fire hazard r<strong>at</strong>ing inSouth Lake Tahoe will not providemanagers and planners with sufficientlydetailed inform<strong>at</strong>ion to implement aneffective fire hazard mitig<strong>at</strong>ion program.While <strong>the</strong> city’s infrastructure is good,individual homeowners in <strong>the</strong> communityrarely choose for fire safety in terms ofconstruction m<strong>at</strong>erials, propertymaintenance, and landscaping or defensiblespace. The problem of non-compliance isworsened by <strong>the</strong> fact th<strong>at</strong> many of <strong>the</strong> city’slots are so small <strong>the</strong>y are influenced by <strong>the</strong>fire hazard of neighboring lots.Fur<strong>the</strong>rmore, results indic<strong>at</strong>e th<strong>at</strong> firehazard r<strong>at</strong>ing should be improved toaccount for <strong>the</strong> fire hazard cre<strong>at</strong>ed byneighboring veget<strong>at</strong>ion and houses in areasdomin<strong>at</strong>ed by small lots. Also, eachcomponent of a fire hazard r<strong>at</strong>ing systemshould produce results than can be used asdecision support for fire management,including identifying priority areas fortre<strong>at</strong>ment, identifying problem<strong>at</strong>ic areas in8


terms of non-compliance, and identifyingreasons for non-compliance. Each of <strong>the</strong> sixneighborhoods in South Lake Tahoe has aunique profile in terms of <strong>the</strong> suite of factorsth<strong>at</strong> contribute most significantly toneighborhood-scale fire hazard. Theneighborhood profiles can be used to directand focus management and homeownereduc<strong>at</strong>ion efforts. The obvious differencebetween <strong>the</strong> Keys and Heavenly, forexample, provides managers with a clearset of management objectives, but <strong>the</strong>re arealso important, less obvious differencesbetween <strong>the</strong> o<strong>the</strong>r neighborhoods.For example, results indic<strong>at</strong>ed th<strong>at</strong> <strong>the</strong> Yhad an average fire hazard for <strong>the</strong> city, butcompared to <strong>the</strong> rest of <strong>the</strong> city thisneighborhood was characterized by a lowpercentage of wood roofs, better irrig<strong>at</strong>ion,average compliance with PRC 4291, and anaverage hazard cre<strong>at</strong>ed by decks.However, <strong>the</strong> fire hazard r<strong>at</strong>ing was <strong>the</strong>same as <strong>the</strong> citywide average because<strong>the</strong>se positive factors were offset by its 85%non-compliance r<strong>at</strong>e for defensible space.This figure increased to 91% when adjustedfor small lot size. Compared to Sierra, <strong>the</strong> Yhad a lower compliance r<strong>at</strong>e but r<strong>at</strong>ed betterin terms of construction m<strong>at</strong>erials anddecks. Compared to North Central, <strong>the</strong> Yexhibited comparable compliance r<strong>at</strong>es andwas slightly better in terms of deck hazards,but <strong>the</strong> Y r<strong>at</strong>ed far worse in terms of <strong>the</strong>percentage of wood roofs and single-panedwindows. These d<strong>at</strong>a can guidemanagement decisions, including both fuelsreduction programs and outreach andeduc<strong>at</strong>ion th<strong>at</strong> focus on <strong>the</strong> particular needsin each neighborhood.In addition to <strong>the</strong> educ<strong>at</strong>ion efforts th<strong>at</strong>focus on defensible space andmaintenance, <strong>the</strong>re is clearly a need toeduc<strong>at</strong>e residents about o<strong>the</strong>r practicesrel<strong>at</strong>ed to fire hazard. Educ<strong>at</strong>ion is neededin Heavenly and elsewhere about <strong>the</strong>benefits of irrig<strong>at</strong>ion in terms of fuelmoisture content and <strong>the</strong> rel<strong>at</strong>ionshipbetween drought stress, bug kill, and firehazard. Most homes already have doublepanedwindows for better insul<strong>at</strong>ion againstwinter we<strong>at</strong>her, but many residents do notrealize th<strong>at</strong> double-paned windows alsodecrease <strong>the</strong> risk of structural ignition.<strong>Hazard</strong>ous decks are a chronic problem inHeavenly, where most decks hang oversteep slopes covered with continuoussurface fuels. In this community, which ischaracterized by small lots and manyseasonal residents, educ<strong>at</strong>ion on <strong>the</strong>importance of neighborhood-scalecooper<strong>at</strong>ion is critical.In sum, standard fire hazard analysis inSouth Lake Tahoe and similar communitiesis likely to underestim<strong>at</strong>e individual firehazard. First, <strong>the</strong> city’s fire-safeinfrastructure is included in <strong>the</strong> parcel-scaleanalysis, which offsets <strong>the</strong> increasedindividual fire hazard associ<strong>at</strong>ed with a lackof defensible space and maintenancearound <strong>the</strong> home. Compliance with PRC4291 is perhaps <strong>the</strong> most important factor instructure survivability, but <strong>the</strong> influence of<strong>the</strong> city’s good infrastructure on its overallfire hazard r<strong>at</strong>ing obscures <strong>the</strong> fact th<strong>at</strong>three-quarters of <strong>the</strong> parcels citywide arenon-compliant with defensible space codesand two-thirds are non-compliant withmaintenance codes. Second, <strong>the</strong> hazard onsmall lots will be fur<strong>the</strong>r underestim<strong>at</strong>edbecause of <strong>the</strong> influence of <strong>the</strong> fire hazardof neighboring parcels.A more appropri<strong>at</strong>e approach to fire hazardassessment in South Lake Tahoe is toassess parcels for compliance, lot size, and<strong>the</strong> individual choices homeowners make interms of construction m<strong>at</strong>erials andirrig<strong>at</strong>ion. Analysis of compliance r<strong>at</strong>es andhomeowner choices will provide a moreaccur<strong>at</strong>e estim<strong>at</strong>e of individual fire hazard.The analysis can also serve as decisionsupport for focusing outreach and educ<strong>at</strong>ionefforts and for prioritizing areas th<strong>at</strong> aremost in need of homeowner compliance andcooper<strong>at</strong>ion.9


AcknowledgementsThe author would like to thank SteveLennartz, Tommy Mouton, Nancy Strahan,Torry Ingram, Sabrina M<strong>at</strong>his, and StephanStreiling for <strong>the</strong>ir field work. Also, <strong>the</strong> LakeTahoe Basin Management Unit (USDAForest Service) and <strong>the</strong> CaliforniaDepartment of Forestry and <strong>Fire</strong> Protectionwere very helpful with <strong>the</strong>ir insights andsupport. Much appreci<strong>at</strong>ion also goes to Dr.E. Gregory McPherson (Project Leader,USDA Forest Service, Center for <strong>Urban</strong>Forest Research), to Dr. Madalene Ransom(St<strong>at</strong>e Economist, USDA N<strong>at</strong>ural ResourceConserv<strong>at</strong>ion Service), and to Scott Maco(<strong>Urban</strong> Forester, USDA Forest Service,Center for <strong>Urban</strong> Forest Research) forcomments on <strong>the</strong> early drafts of this report.This study was part of a project fundedthrough <strong>the</strong> N<strong>at</strong>ional <strong>Fire</strong> Plan.Liter<strong>at</strong>ure CitedAbt, R. C., M. K. Kupyers and J. B. Whitson.1991. Perception of fire danger andwildland/urban policies after wildfire.USDA Forest Service. GTR SE-69, pp.257-259.Bailey, D. W. 1991. The wildland-urbaninterface: social and politicalimplic<strong>at</strong>ions in <strong>the</strong> 1990’s. <strong>Fire</strong>Management Notes 52(1): 11-18.Cohen, J. 1995. Structure Ignition<strong>Assessment</strong> Model (SIAM).USDAForest Service. PSW-GTR-158.Cortner, H. J. 1991. <strong>Interface</strong> policy offersopportunities and challenges: USDAForest Service str<strong>at</strong>egies andconstraints. Journal of Forestry 89(6):31-34.de Jong, L. 2002 (in review). <strong>Urban</strong>Forestry <strong>at</strong> <strong>the</strong> <strong>Urban</strong> <strong>Wildland</strong><strong>Interface</strong>: Case Study in South LakeTahoe.Foote, E., R. Martin, J. K. Gilless. 1991. Thedefensible space factor study: asurvey instrument for post-firestructure loss analysis. Proceedings,11 th Conference on <strong>Fire</strong> and ForestMeteorology. Society of AmericanForesters. p. 66 – 73.Garrett, Brian. <strong>Urban</strong> Lot Manager, USDAForest Service Lake Tahoe BasinManagement Unit (LTBMU). May 7,2002.Harcourt, Steve. Area Forester, CaliforniaDepartment of Forestry and <strong>Fire</strong>Protection. Telephone convers<strong>at</strong>ion,February 11, 2002.Hodgson, R. W. 1993. Perceptions ofDefensible Space: PerceivedCharacteristics th<strong>at</strong> Influence<strong>Wildland</strong>-<strong>Urban</strong> Intermix Residents toAccept or Reject <strong>Fire</strong> SafeLandscaping. Prepared for <strong>the</strong>California Department of Forestry and<strong>Fire</strong> Protection.Manfredo, M. J., M. Fishbein, G.E. Haasand A.E. W<strong>at</strong>son. 1990. Attitudestoward prescribed fire policies.Journal of Forestry 88(7): 19–23.Manley, P. and M. Schlesinger. 2001. FinalReport for <strong>the</strong> California TahoeConservancy and US Forest Service.April, 2001.Murphy, D.D., C. M. Knopp, eds. 2000.Lake Tahoe w<strong>at</strong>ershed assessment:Volume I. Gen.Tech.Rep. PSW-GTR-175. Albany, CA: Pacific SouthwestResearch St<strong>at</strong>ion, Forest Service, U.S.Department of Agriculture; 736 pp.NFPA. 1997. NFPA-299: Standard forProtection of Life and Property from10


Wildfire. N<strong>at</strong>ional <strong>Fire</strong> ProtectionAssoci<strong>at</strong>ion. 17 pp.Quarles, S. 2001. Testing protocols andfire tests in support of performancebasedcodes. California’s 2001 WildfireConference, Oakland, CA. October 10-12, 2001.Quarles, S. 2002. Conflicting designissues in wood frame construction. 9 thDurability Building M<strong>at</strong>erials Conference,Brisbane, Australia. March 2002.Products. White Sulphur Springs, WV.January 24-27, 2000.Winter, G. and J. S. Fried. 2000.Homeowner Perspectives on <strong>Fire</strong><strong>Hazard</strong>, Responsibility, andManagement Str<strong>at</strong>egies <strong>at</strong> <strong>the</strong><strong>Wildland</strong>-<strong>Urban</strong> <strong>Interface</strong>. Society &N<strong>at</strong>ural Resources, 13: 33-49.Skinner, C., C. Chang 1996. <strong>Fire</strong> regimes,past and present. In: Sierra NevadaEcosystem Project: Final Report toCongress, volume II, chapter 38. Davis,CA, University of California, Centers forW<strong>at</strong>er and <strong>Wildland</strong> Resources.Smith, E. and M. Rebori. 2001. Factorsaffecting property owner decisionsabout defensible space. In: ConferenceProceedings for Forestry Extension:Assisting Forest Owner, Farmer, andStakeholder Decision-Making.Intern<strong>at</strong>ional Union of Forestry ResearchOrganiz<strong>at</strong>ions, Lorne, Australia. October29 -November 2, 2001. p.404-408.Tran, H. C., J. Cohen, R. Chase. 1992.Modeling ignition of structures inwildland/urban interface fires.Proceedings, 1 st Intern<strong>at</strong>ional <strong>Fire</strong> andM<strong>at</strong>erials Conference. Arlington, VA. p.253 – 262.U. S. Environmental D<strong>at</strong>a Service. 2000.Clim<strong>at</strong>ological d<strong>at</strong>a analysis annualsummary: California.White, R. 2000. <strong>Wildland</strong>/urban interfacefire research <strong>at</strong> <strong>the</strong> USDA ForestService, Forest Products Labor<strong>at</strong>ory:past, present and future. In:Proceedings of <strong>the</strong> Thirtieth Intern<strong>at</strong>ionalConference on <strong>Fire</strong> Safety, <strong>the</strong> TwelfthIntern<strong>at</strong>ional Conference on ThermalInsul<strong>at</strong>ion, <strong>the</strong> Fourth Intern<strong>at</strong>ionalConference on Electrical and Electronic11

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!