Emerald ash borer (Agrilus planipennis Fairmaire) (EAB) is an invasive, wood-boring beetle (Coleoptera: Buprestidae) introduced unintentionally to the United States from East Asia that infests and eventually kills native ash trees (Fraxinus spp.). First detected near Detroit, Michigan in 2002, EAB had spread to fifteen U.S. states by 2011, killing an estimated 50 million ash trees along the way. EAB was first discovered in Virginia in 2003 and re-infested the state in 2008, raising concerns over impacts that the invasive pest might have on municipal urban forests and street trees. Despite these concerns, little is known about native ash abundance in Virginia's urban forests; as a result, potential EAB impacts have been difficult to project. In this study, street tree assessments were conducted in fourteen Virginia municipalities using i-Tree Streets®, which is a software program developed by the U.S. Forest Service that uses field inventory data to estimate street tree abundance and composition along with the quantity and monetary worth of functional benefits provided by these street trees. In addition to estimating potential losses of functional benefits provided by native ash street trees, information obtained from Virginia Dept. of Transportation was used to estimate the potential cost of removing these trees from the street side. The assessment indicated that there are about 4,600 native ash street trees in the fourteen studied localities and that native ash species comprise about 2% of municipal street tree populations on average. The highest relative abundance of native ash was found in Winchester City (5.8% of all street trees) whereas Richmond City had the greatest number of native ash street trees (estimated at 1,417). In terms of species importance (which accounts for both the relative abundance and relative size of trees in the population), only two localities (City of Roanoke and Town of Abingdon) had a native Fraxinus species among the top-five most important street tree species in the locality. In contrast, every municipality had at least one Acer species among the top-five, and eight of fourteen localities had at least one top-five Quercus species. Native ash street trees in the studied localities were estimated to provide functional benefits (energy conservation, stormwater mitigation, air pollution abatement, carbon sequestration, and aesthetic contributions) valued at over $535,000 annually, or roughly $38,000 per locality. In addition, carbon stored in these trees (about 17 million kilograms) was valued at nearly $277 thousand. The total estimated cost of removing lost ash trees was estimated at nearly $1.75 million, averaging about $124,000 for each municipality, and replacing the canopy cover and basal area provided by existing native ash street trees would exceed $17 million. In total, the studied localities would incur a gross financial impact of about $20.26 million due to losses of functional benefits and structural assets provided by native ash street trees. / Master of Science

Gamla träd i kulturmiljöer uppmärksammas alltmer inom naturvården på grund av sina höga naturvärden och är viktiga som värdar för fortlevnaden av hotade och sällsynta växt- och djurarter. Studiens syfte var att undersöka om Sörenssons AHA-metod (framtagen för vedlevande insekter) fungerar också på mossor och lavar, samt att jämföra två kulturmiljöer med gamla träd. Inventeringen utfördes i Kristianstad och omfattade totalt 443 träd; 230 i Tivoliparken och 213 på Östra begravningsplatsen. Träden bedömdes utifrån olika karaktärer: förekomst av håligheter, barklösa partier, grenhål, savflöde samt svamppåväxt. Förekomsten av dessa användes sedan för att dela in träden i fem olika klasser av varierande värde för naturvården. Även kryptogamer inventerades; dels förutbestämda lavar och mossor som signalerar höga naturvärden, dels en enkel bedömning av det totala antalet triviala arter på varje träd. Träden i Tivoliparken hade större spridning mellan AHA-klasserna. Här hamnade 56 träd i de högsta värdeklasserna (klass I och II-träd), 114 i värdeklass III och 60 som resursträd. På Östra begravningsplatsen hamnade hälften av träden i de högsta värdeklasserna och 93 i värdeklass III. De resterade träden klassades som resursträd. Totalt gjordes 89fynd av 6 signalarter på de inventerade träden, samt en vedsvamp. Dessa fynd gjordes både på träd med höga och låga värden enligt AHA-metoden. AHA-klasser med högre naturvärde hade lägre artrikedom för samtliga träd sammanslagna, men inget samband för enbart trädslagen bok och lind. Endast hälften av träden med signalarter fick hög AHA-klassning. Resultatet antyder att AHA-metoden inte fungerar på kryptogamer som den gör för vedlevande insekter. / Old trees in cultural environments are receiving increasing attention in nature conservation due to their high conservation values and provide important habitat for endangered plant and animal species. The purposes of the study were to investigate whether Sörensson's AHA-method is applicable also to mosses and lichens, as well as to compare two environments with old trees. 443 trees were inventoried in Kristianstad, of which 230 in Tivoliparken and 213 in Östra begravningsplatsen. The trees were assessed based on the occurrence of: cavities, barkless areas, and so on. These findings were used to assign each tree to the five AHA classes of varying conservation value. Trees were also searched for predetermined lichens and mosses signalling high conservation value, and a simple count was made of the total number of trivial cryptogam species on each tree. Tivoliparken had a wider scatter of trees among the AHA classes; 56 in the highest value classes (class I and II), 114 in class III, and 60 as resource trees. At Östra begravningsplatsen, half of the oldest trees were in the two highest value classes and 93 in class III. The remaining trees ended up as resource trees. In total, 89 records of 6 signal species were made, and one wood fungus. There was a significant association between AHA class and richness of trivial species when trees of all species were pooled, but no association when beech and linden were assessed separately. These results suggest that the AHA method does not work on cryptogams.