uid=AND,o=lter,dc=ecoinformatics,dc=org all public read WE008 Joan C. Hagar Brenda C McComb

Dean, OSU Graduate School Corvallis OR USA

brenda.mccomb@oregonstate.edu Tom Manning

Dept of Forest Ecosystems & Society, 321 Richardson Hall, Oregon State University Corvallis OR 97370 USA

541-737-0946 tom.manning@oregonstate.edu Steven L. Garman

USA

SLGarman@usgs.gov Former Investigator Joan C. Hagar Principal Investigator Joan C. Hagar Creator Matthew G. Hunter

2205 NW 13th St. Corvallis OR 97330 USA

541-752-4604 matt.hunter@comcast.net Former Investigator Brenda C McComb

Dean, OSU Graduate School Corvallis OR USA

brenda.mccomb@oregonstate.edu Creator Tom Manning

Dept of Forest Ecosystems & Society, 321 Richardson Hall, Oregon State University Corvallis OR 97370 USA

541-737-0946 tom.manning@oregonstate.edu Other Researcher Tom Manning

Dept of Forest Ecosystems & Society, 321 Richardson Hall, Oregon State University Corvallis OR 97370 USA

541-737-0946 tom.manning@oregonstate.edu Abstractor 2011-10-07 The US Forest Service (USFS), Pacific Northwest Research Station (PNW), and Oregon State University (OSU) established the Young Stand Thinning and Diversity Study (YSTDS) in 1990 to demonstrate and test options for young stand management in western Oregon. The YSTDS is designed to determine if different thinning, underplanting, and snag creation treatments can accelerate the development of late-seral conditions in 35-50 year-old plantations. The study was implemented on 4 replicate blocks, each consisting of an untreated Control stand and 1 each of the following stand-level thinning treatments: (1) a Light Thin treatment, approximating the timber industry standard, with about 260 residual trees per hectare (tph; 100/acre); (2) a Heavy Thin treatment leaving approximately 130 tph (50/acre) and underplanted with native conifer seedlings; and (3) a Light Thin with Gaps (hereafter simply “Gaps”) treatment, again with 260 tph plus an additional 20% of the stand area harvested to leave 0.2 ha (0.5-acre) openings underplanted with native conifer seedlings. Pre-thinning baseline data (documenting vegetation, fungi, wildlife, and photopoints) were gathered in 1992-1994, and the thinning treatments were implemented through timber sale contracts from late 1994 through early 1997, with most logging occurring during 1995-96. During the thinning harvests, detailed analyses were carried out to examine pre-sale planning and layout costs, comparative productivity and costs of various harvesting alternatives, residual stand damage, and soil disturbance and compaction. A considerable body of publications on these operational aspects of the YSTDS constitutes one of the largest portions of the study’s results so far. Much science has been accomplished in the 15 years since the YSTDS thinning treatments were installed. Vegetative response to the thinning has been measured at frequent intervals, in 1996, 1999, 2001, and 2006. Changes in volumes of coarse woody debris and the responses of fungi, arthropods, amphibians, birds, and small mammals have also been assessed, and are intended to continue into the future. Five years after thinning (2001), snag densities in the YSTDS were artificially increased by topping trees and inoculating some with fungal mycelia, in an effort to increase the abundance of dead trees for cavity-nesting birds and mammals; long-term monitoring of these artificial snags is underway. The study also included a social science component exploring the public’s response to visual changes in the forest from the thinning operations. population dynamics biodiversity thinning animals fauna amphibians birds mammals canopy gaps LTER controlled vocabulary young forests squirrels Andrews Experimental Forest site thesaurus Manning, T., J. Hagar, B. McComb. 2012. Thinning of young Douglas-fir forests decreases density of northern flying squirrels in the Oregon Cascades. Forest Ecology and Management 264:115-124. Results of the first year of post-treatment sampling suggests that thinning treatments had a limited effect on ground-dwelling vertebrates. Compared to control plots, capture rates tended to be higher in the thinned stands for the deer mouse, chipmunk, and Ensatina, and lower for shrew species. However, only the deer mouse exhibited a statistically significant (P less than 0.05) response to thinning treatments. Mean capture rates of the deer mouse were about three times as high in thinned stands as in the control plots. A numeric response of the deer mouse to more open conditions would be expected given its preference for shrub and herbaceous vegetation. Although mean capture rate of this species did increase with thinning intensity, rates were statistically similar (P greater than 0.05) among thinning treatments. Based on the 1998 results, it appears that removing at least one-half of the initial stem density is sufficient for a numerical increase in the deer mouse, but additional overstory thinning does little to enhance habitat conditions for this species. Analyses of mean weights and recapture rates suggest that the numerical response (or lack of a statistically significant response) of individual species to thinning treatments was not confounded by sink/source habitat or differential dispersal effects. For all species for which samples sizes were sufficient for analysis, mean weights and recapture rates were statistically similar (P greater than 0.05) among treatments. - Steve Garman Matthew Hunter, Joan Hagar, Steve Garman, Tom Manning.Related PublicationsHagar, Joan. 1996. Pre-treatment analysis of wildlife - habitat relationships in young managed stands in the Oregon Cascade Range: young stand thinning and diversity monitoring project, wildlife pretreatment report. Corvallis, OR: Cascade Center for Ecosystem Management. 35 p.Garman, Steven L. 1999. Assessing potential development of snags - young stand thinning and diversity study. Corvallis, OR: Department of Forest Science, Oregon State University; final report. 34 p.Garman, Steven L. 2000. Response of ground-dwelling vertebrates to thinning young stands: the Young Stand Thinning and Diversity Study. Corvallis, OR: Oregon State University, Department of Forest Science; final report. 34 p.Garman, Steven L. 1998. Young stand thinning and diversity study: post-treatment assessment of ground-dwelling vertebrates. Corvallis, OR: Oregon State University, Department of Forest Science; Interim report. 13 p.Hagar, Joan C. 1992. Bird communities in commercially thinned and unthinned Douglas-fir stands of western Oregon. Corvallis, OR: Oregon State University. 110 p. M.S. thesis.Garman, Steven L. 2001. Response of ground-dwelling vertebrates to experimental levels of downed woody debris - Long-Term Ecosystem Productivity Study, Willamette National Forest. Corvallis, OR: Oregon State University, Department of Forest Science; final report. 26 p.Hagar, Joan; Howlin, Shay; Ganio, Lisa. 2004. Short-term response of songbirds to experimental thinning of young Douglas-fir forests in the Oregon Cascades. Forest Ecology and Management. 199: 333-347. Data Use Agreement: The re-use of scientific data has the potential to greatly increase communication, collaboration and synthesis within and among disciplines, and thus is fostered, supported and encouraged. This Data Set is released to the public domain under the Creative Commons license CC0 1.0 "No Rights Reserved" (see: https://creativecommons.org/publicdomain/zero/1.0/). Creative Commons license CC0 1.0 - No Rights Reserved states that data are placed in the public domain, so that others may freely build upon, enhance and reuse the works for any purposes without restriction under copyright or database law. It is considered professional conduct and an ethical obligation to acknowledge the work of other scientists. The Data User is asked to provide attribution of the original work if this data package is shared in whole or by individual parts or used in the derivation of other products. A recommended citation is provided for each Data Set in the Andrews LTER data catalog (see: http://andlter.forestry.oregonstate.edu/data/catalog/datacatalog.aspx). A generic citation is also provided for this Data Set on the website https://portal.edirepository.org in the summary metadata page. Data Users are thus strongly encouraged to consider consultation, collaboration and/or co-authorship with the Data Set Creator. While substantial efforts are made to ensure the accuracy of data and associated documentation, complete accuracy of data sets cannot be guaranteed and all data are made available "as is." The Data User should be aware, however, that data are updated periodically and it is the responsibility of the Data User to check for new versions of the data. The data authors and the repository where these data were obtained shall not be liable for damages resulting from any use or misinterpretation of the data. General acknowledgement: Data were provided by the HJ Andrews Experimental Forest research program, funded by the National Science Foundation: Long-Term Ecological Research Program (DEB 1440409), US Forest Service Pacific Northwest Research Station, and Oregon State University. http://andlter.forestry.oregonstate.edu/data/abstract.aspx?dbcode=WE008 Central Cascades Adaptive Management Area, on the McKenzie River Ranger District and Middle Fork Ranger District of the Willamette National Forest. -122.37542000 -122.18637000 44.20598000 43.87573000 1991-10-15 2012-05-05 All Organisms All Organisms Highest common category (ca. kingdom) Animalia Class Mammalia Genus Tamias Species Tamias townsendii Genus Tamiasciurus Species Tamiasciurus douglasii Genus Spermophilus Species Spermophilus beecheyi Genus Sorex Species Sorex trowbridgii Species Sorex bendirii Species Sorex vagrans Genus Peromyscus Species Peromyscus maniculatus Genus Neurotrichus Species Neurotrichus gibbsii Genus Mustela Species Mustela erminea Genus Lepus Species Lepus americanus Genus Clethrionomys Species Clethrionomys californicus Genus Glaucomys Species Glaucomys sabrinus Genus Microtus Species Microtus oregoni Species Microtus longicaudus Species Microtus richardsoni Genus Neotoma Species Neotoma cinerea Genus Ochotona Species Ochotona princeps Genus Scapanus Species Scapanus orarius Genus Spilogale Species Spilogale putorius Genus Ursus Species Ursus americanus Class Amphibia Genus Taricha Species Taricha granulosa Genus Plethodon Species Plethodon dunni Order Urodela Family Dicamptodontidae Genus Dicamptodon Species Dicamptodon tenebrosus Genus Ascaphus Species Ascaphus truei Genus Ambystoma Species Ambystoma gracile Genus Aneides Species Aneides ferreus Genus Bufo Species Bufo boreas Genus Ensatina Species Ensatina eschscholtzii Genus Rana Species Rana aurora Class Aves Species Parus gambeli Species Seiurus aurocapillus Order Coraciiformes Family Alcedinidae Genus Ceryle Species Ceryle alcyon Order Strigiformes Family Tytonidae Genus Tyto Species Tyto alba Family Strigidae Genus Asio Species Asio otus Genus Glaucidium Species Glaucidium gnoma Genus Otus Species Otus kennicottii Species Otus flammeolus Genus Bubo Species Bubo virginianus Genus Strix Species Strix varia Species Strix occidentalis Species Strix nebulosa Order Columbiformes Family Columbidae Genus Columba Species Columba fasciata Genus Zenaida Species Zenaida macroura Order Charadriiformes Family Scolopacidae Genus Actitis Species Actitis macularia Family Alcidae Genus Brachyramphus Species Brachyramphus marmoratus Order Galliformes Family Odontophoridae Genus Oreortyx Species Oreortyx pictus Genus Callipepla Species Callipepla californica Family Phasianidae Genus Dendragapus Species Dendragapus obscurus Genus Bonasa Species Bonasa umbellus Genus Falcipennis Species Falcipennis canadensis Genus Meleagris Species Meleagris gallopavo Order Falconiformes Family Accipitridae Genus Aquila Species Aquila chrysaetos Genus Accipiter Species Accipiter gentilis Species Accipiter striatus Species Accipiter cooperii Genus Pandion Species Pandion haliaetus Genus Haliaeetus Species Haliaeetus leucocephalus Genus Buteo Species Buteo jamaicensis Family Cathartidae Genus Cathartes Species Cathartes aura Family Falconidae Genus Falco Species Falco peregrinus Species Falco sparverius Species Falco mexicanus Order Ciconiiformes Family Ardeidae Genus Ardea Species Ardea herodias Order Anseriformes Family Anatidae Genus Lophodytes Species Lophodytes cucullatus Genus Aix Species Aix sponsa Genus Branta Species Branta canadensis Genus Anas Species Anas platyrhynchos Genus Mergus Species Mergus merganser Order Caprimulgiformes Family Caprimulgidae Genus Caprimulgus Species Caprimulgus vociferus Genus Chordeiles Species Chordeiles minor Order Apodiformes Family Apodidae Genus Chaetura Species Chaetura vauxi Genus Cypseloides Species Cypseloides niger Family Trochilidae Genus Stellula Species Stellula calliope Genus Calypte Species Calypte anna Genus Selasphorus Species Selasphorus rufus Order Piciformes Family Picidae Genus Dryocopus Species Dryocopus pileatus Genus Picoides Species Picoides arcticus Species Picoides pubescens Species Picoides villosus Genus Sphyrapicus Species Sphyrapicus nuchalis Species Sphyrapicus ruber Genus Melanerpes Species Melanerpes lewis Genus Colaptes Species Colaptes auratus Order Passeriformes Family Fringillidae Genus Coccothraustes Species Coccothraustes vespertinus Genus Carpodacus Species Carpodacus mexicanus Species Carpodacus purpureus Species Carpodacus cassinii Genus Loxia Species Loxia leucoptera Species Loxia curvirostra Genus Carduelis Species Carduelis psaltria Species Carduelis pinus Species Carduelis tristis Family Icteridae Genus Euphagus Species Euphagus cyanocephalus Genus Agelaius Species Agelaius phoeniceus Genus Sturnella Species Sturnella neglecta Genus Molothrus Species Molothrus ater Genus Icterus Species Icterus galbula Family Cardinalidae Genus Pheucticus Species Pheucticus melanocephalus Genus Passerina Species Passerina amoena Family Emberizidae Genus Passerella Species Passerella iliaca Genus Pooecetes Species Pooecetes gramineus Genus Spizella Species Spizella passerina Species Spizella breweri Genus Pipilo Species Pipilo chlorurus Species Pipilo maculatus Genus Passerculus Species Passerculus sandwichensis Genus Melospiza Species Melospiza lincolnii Species Melospiza melodia Genus Zonotrichia Species Zonotrichia atricapilla Species Zonotrichia leucophrys Genus Junco Species Junco hyemalis Family Parulidae Genus Wilsonia Species Wilsonia pusilla Genus Oporornis Species Oporornis tolmiei Genus Dendroica Species Dendroica townsendi Species Dendroica coronata Species Dendroica petechia Species Dendroica nigrescens Species Dendroica occidentalis Genus Vermivora Species Vermivora celata Species Vermivora ruficapilla Genus Geothlypis Species Geothlypis trichas Family Motacillidae Genus Anthus Species Anthus rubescens Family Timaliidae Genus Chamaea Species Chamaea fasciata Family Cinclidae Genus Cinclus Species Cinclus mexicanus Family Troglodytidae Genus Troglodytes Species Troglodytes aedon Species Troglodytes troglodytes Genus Salpinctes Species Salpinctes obsoletus Genus Thryomanes Species Thryomanes bewickii Family Aegithalidae Genus Psaltriparus Species Psaltriparus minimus Family Paridae Genus Poecile Species Poecile gambeli Species Poecile atricapillus Species Poecile gambeli Species Poecile rufescens Family Vireonidae Genus Vireo Species Vireo gilvus Species Vireo cassinii Species Vireo huttoni Family Tyrannidae Genus Contopus Species Contopus sordidulus Species Contopus cooperi Genus Empidonax Species Empidonax difficilis Species Empidonax wrightii Species Empidonax traillii Species Empidonax alnorum Species Empidonax hammondii Species Empidonax oberholseri Genus Tyrannus Species Tyrannus verticalis Family Corvidae Genus Aphelocoma Species Aphelocoma coerulescens Genus Cyanocitta Species Cyanocitta stelleri Genus Perisoreus Species Perisoreus canadensis Genus Corvus Species Corvus corax Species Corvus brachyrhynchos Family Hirundinidae Genus Petrochelidon Species Petrochelidon pyrrhonota Genus Tachycineta Species Tachycineta bicolor Genus Progne Species Progne subis Genus Stelgidopteryx Species Stelgidopteryx serripennis Genus Hirundo Species Hirundo rustica Species Hirundo pyrrhonota Family Sittidae Genus Sitta Species Sitta carolinensis Species Sitta canadensis Family Certhiidae Genus Certhia Species Certhia americana Family Regulidae Genus Regulus Species Regulus calendula Species Regulus satrapa Family Turdidae Genus Turdus Species Turdus migratorius Genus Catharus Species Catharus ustulatus Species Catharus guttatus Genus Sialia Species Sialia currucoides Species Sialia mexicana Genus Myadestes Species Myadestes townsendi Genus Ixoreus Species Ixoreus naevius Family Sturnidae Genus Sturnus Species Sturnus vulgaris Family Bombycillidae Genus Bombycilla Species Bombycilla cedrorum Family Thraupidae Genus Piranga Species Piranga ludoviciana Family Passeridae Genus Passer Species Passer domesticus Species Parus atricapillus Understanding how to maintain the ecological diversity of young managed stands is a topical issue in forest management in the Pacific Northwest region. To begin to understand the effects of different thinning treatments on ecological diversity, the Willamette National Forest initiated the Young Stand Thinning and Diversity study (YSS). This study compares relative populations of small mammals, amphibians, and birds under different thinning treatments. Tree growth and vegetation development are also examined.

An update history is logged and maintained with each new version of every dataset.

irregular Original metadata creation. Version1 1999-06-07 This data set was updated for post treatment sampling of ground-dwelling vertebrates in June, 1999. Post-treatment sampling will continue in Fall, 1999. Format 1 was entirely reworked in this process and Formats 5 and 6 were added. (Steve Garman, Don Henshaw) Version2 1999-09-01 Metadata restructured and moved into SQLServer metadata database LTERMETA. Data moved into SQLServer database FSDBDATA. Version3 2002-05-29 Metadata restructured and moved into SQLServer metadata database LTERMETA. Data moved into SQLServer database FSDBDATA. Version4 2002-07-01 Data has become unrestricted per Steve Garman. Data is now available via web online. Version5 2007-07-10 Updated entity 1 with 2007 and 2008 data. Added entities 11 and 12. Still working on adding entity 13 (snags). Version6 2010-08-03 Updated entity 3 to pass metacat harvest. See entity_update_history for details. Version9 2011-10-07 Information Manager

Andrews Forest LTER Program US Forest Service Pacific Northwest Research Station 3200 SW Jefferson Way Corvallis OR 97331

hjaweb@fsl.orst.edu http://andrewsforest.oregonstate.edu/ Tom Manning

Dept of Forest Ecosystems & Society, 321 Richardson Hall, Oregon State University Corvallis OR 97370 USA

541-737-0946 tom.manning@oregonstate.edu Andrews Forest LTER Site

Forest Ecosystems and Society Department in Forestry Oregon State University 201K Richardson Hall Corvallis OR 97331-5752

(541) 737-8480 lterweb@fsl.orst.edu http://andrewsforest.oregonstate.edu/ Field Methods - WE008: Snags To date, there has been no standard sampling design for assessing the created snag component of the YSTDS, but several small-scale field efforts have been launched to evaluate the project. In 2007, about 5.5 years after topping and inoculating, the created snags were surveyed to assess general condition (living, dead, or fallen), extent of decay (presence of insects and fungus, decay class), and presence of foraging and nesting cavities. Snags showing evidence of nesting activity were re-visited twice between 7 June and 5 July 2007. At each of these return visits, each snag was observed for 20 minutes to determine whether nest cavities were in current use. The same snags were re-visited in 2008, again to document nesting activity. In all, 77 created snags were identified as having nest cavities in 2007; among these, 2 active nests were confirmed in 2007 and 2 others were confirmed in 2008. In addition to these nests in created snags, an additional 5 nests were found in natural snags and stumps. Conclusions from this monitoring were that: the created snags were used for foraging and nesting; inoculation of snags with heart-rot fungi increased the frequency of bark beetle and pouch fungus, and foraging use by birds was greater than for snags created by topping alone; and that the usefulness of snags less than 50 cm dbh for nesting is likely marginal, as demonstrated by the low detection rate of active nests. In 2009, a brief pilot project was fielded to try to find evidence that mammals were using the created snags. In particular, there was interest in whether northern flying squirrels were using the snags as summer or maternity dens. All snags were examined visually for cavities, and those with cavities large enough were probed with a Tree-Top Peeper, essentially a video camera on a telescoping pole. No mammals were detected using the Peeper. In fact, only a few cavities were large enough to insert the camera; small cavities such as these are not likely to be used by flying squirrels, but may have been used by smaller mammals such as mice or shrews. As a corollary to this work, the condition (live, dead, or fallen) and location of all snags was updated and added to the Forest Science Data Base, and several missing tree tags were replaced. In 2010, another round of nest activity monitoring was accomplished. In this assessment, all YSTDS stands were systematically surveyed for the presence of cavity-nesting birds between May 15 and July 15, and detected birds were followed in an attempt to locate nest cavities. The protocol combined passive listening and periodic playbacks of 9 cavity-nesting bird species and covered all areas of each stand. Each morning that weather permitted, 2 stands were surveyed for 3 hours each, and each stand was surveyed twice during the season. Actual search time per survey varied from 2.6 to 2.8 hours because a portion of each 3-hour survey was spent following birds to nests and recording data, so results were standardized as nests found per unit of time actively searching. In all, 20 active cavity nests were found. These 20 nests were rechecked every few days to assess nesting success as well as possible; however, most nests were already far advanced when first discovered, and nestlings were gone from most before they were revisited; thus, conclusions about nest success could not be made. Analysis-of-variance provided weak statistical evidence of differences among thinning treatments in terms of numbers of active nests (P = 0.0982). More active nests were found in thinned treatments than in unthinned control stands. Field Methods - WE008 SMALL MAMMALS Methods for sampling the mammal fauna on the YSTDS changed over the course of the study. In the 1990’s, pre-treatment and immediate post-treatment sampling was focused on sampling of forest floor vertebrates using Sherman live-traps and pitfall traps. In later years, efforts to measure densities of northern flying squirrels (Glaucomys sabrinus) were gradually increased, because of the squirrel’s importance as prey for spotted owls and its larger role as an indicator of forest health generally. Before thinning, in Oct-Nov of 1991 and 1992, the mammal fauna on the YSS sites was sampled for 8 consecutive nights annually in each stand using conventional square grids of Sherman live-traps (10x10 with 20 m inter-trap spacing) and pitfall traps (5x5 with 20 m spacing; Garman 2001). This effort sampled only a small portion of each YSTDS stand. The YSTDS sites were trapped again for several years soon after thinning, in 1998, 1999, and 2001 (Garman 2001). To better sample the spatial variability in these post-treatment stands, square trapping grids were replaced by variable-length transects that covered more of each stand. Number of transects per stand varied from 4 to 11 depending on stand shape, but each stand included a total of 100 trapping stations. Distance between traps on each transect was 30 m. Transects were spaced 30 m apart and >50 m from a stand edge. In 1998-99, 1 Sherman live-trap (Model LFATDG) was placed at each station (total of 100 traps per stand), and 1 pitfall trap was installed at every 2nd station (total of 50 pitfalls per stand). In 2001, Tomahawk live-traps (Model 201) were added to the design to specifically target flying squirrels; in each treatment stand, 1 Tomahawk trap was placed on the ground at every 2nd station on alternating transects, so that traps were evenly distributed through the treatment unit (total of 25 Tomahawk traps per stand). In each year of the 1998-2001 sampling effort, all 4 stands within a block were trapped simultaneously for 6-8 consecutive nights during late September to mid-November. It should be noted that these early efforts (1991-2001) also sampled forest floor amphibians, though captures were sparse. More recently, efforts to quantify abundance and diversity of amphibians have been made separately from mammal sampling, and are covered in a separate section of this report. In 2007-08 (11-13 years after thinning), all stands were resampled, using the same variable-length transects established in 1998 (Manning et al., in review). Trapping occurred for 4 consecutive nights in each stand between late September and late November. Two stands in each block were sampled simultaneously and the other 2 stands in the same block were sampled in the following week. The order for sampling stands within blocks was randomized, and blocks were sampled sequentially. Considerations for the order of sampling among blocks included elevation, seasonal road closures, and proximity to other blocks. One trap was placed at each station. In this phase of the study, we increased efforts to capture flying squirrels by doubling the number of Tomahawk traps deployed. In each stand, Sherman traps alternated with Tomahawk traps along each transect, so that 50 of each were evenly distributed throughout the 100 stations in each stand. Half of the Tomahawk traps were attached to the boles of trees (approx. 1.5 m high), and the rest were placed on the ground; tree and ground placements of Tomahawk traps alternated along transects. To increase capture rates, all traps were locked open and pre-baited once 10 days before the trap session began. During the trapping session, traps were checked twice daily to minimize mortality of trap-prone diurnal species (e.g., chipmunks). Traps were set in the afternoon on the 1st day of each trap session, checked twice each day for 3 days, then checked and closed on the morning of the 5th day; thus, each trap session included 4 nights and 7 capture occasions. In all years, traps were baited with a mixture of peanut butter, oats, and sunflower seeds. Polyester or cotton fiber insulation was placed in each trap, and traps were placed within weather-resistant covers. Pitfall traps (not used after 2001) were provided with a small shelter, insulation, and food, and were operated as live-traps. All traps were checked daily (twice daily in 2007-2008). Captured rodents were identified to species, weighed, sexed, marked with individually-numbered eartags, and immediately released at the point of capture. Trap mortalities were frozen for later necropsy to confirm species and sex. After trapping was completed, pitfall traps were made inoperable and box traps were removed. All procedures were conducted under protocols approved by the Institutional Animal Care and Use Committee at Oregon State University. Field Methods - WE008 (1) BIRDS Standard point count methodology was used to sample breeding birds at 3-5 point count stations in each of the 16 YSTDS stands. Stations were separated by at least 150 m, and were greater than 75 m from stand edges, road buffers, or riparian buffers. All surveys were conducted between 0.5 h before and 6 h after sunrise. Surveys were not conducted during periods of heavy rain or strong wind. Pre-harvest bird counts (1992-93) were conducted by a single observer 5 times each year from early May to late June. The pre-harvest observer waited 2 min at each station before recording the species and estimated distance to each bird detected during an 8-min count period. Post-harvest bird counts (1997–1999, 2001, 2006-07) were conducted by 4 observers. Each station was sampled in 3 visits from late May to late June in 1997-98, and during 4 visits from late May to early July thereafter. Observers recorded the species and estimated distance to each bird detected during a 10-min count period at each station for all post-harvest surveys. Field Methods - WE008 (2) AMHIBIANS During pre-treatment sampling (1991-1992), pitfall trapping was used to sample both small mammals and amphibians. A 5x5 grid of pitfall traps, with 20-m spacing between traps, was deployed for 8 nights in each of the 16 YSTDS experimental stands. This design yielded a total of 53 individuals of 6 species of salamanders and no frogs or toads (Garman 2001). This amounts to a capture rate of 0.8 salamanders per 100 trap-nights. During an initial bout of post-treatment sampling (1998-2001), the number of pitfalls was doubled and more evenly distributed throughout each YSTDS stand. This yielded 151 captures of 5 species of salamanders (2.7 captures/100 trapnights), as well as 4 individual frogs and a single toad (Garman 2001). At the beginning of a second period (2007-2009) of post-treatment sampling, we attempted to continue pitfall sampling using the same design as in 1998-2001. After 3 days of simultaneous mammal and amphibian sampling in Oct 2007, it became clear that we had underestimated the resources required to do the work. Since the capture rate of salamanders was very low (0.67 captures per 100 trap nights), pitfall trapping was halted to concentrate on mammal live-trapping. In lieu of pitfalls for sampling amphibians, time-constrained searches (TCS) were attempted. In each stand, 3 strip plots measuring 50 m by 4 m were laid out. Each plot was searched intensively for one person-hour, by turning over logs, bark, and other debris to expose salamanders. After sampling 12 of these plots, and capturing only 4 salamanders, this work was discontinued because 3 person-hours per salamander was not considered an efficient use of human resources. Another attempt was made by Joan Hagar and Brenda McComb to implement the same TCS design in June 2008, again with disappointing results (2 salamanders in a day of work for 2 people). It was after this setback that the idea of using artificial cover objects (ACOs) was advanced. ACOs provide a standardized method for sampling of terrestrial salamanders. The board design used is detailed in: Davis, T.M. 1997. Non-disruptive monitoring of terrestrial salamanders with artificial cover objects on southern Vancouver Island, British Columbia. In Amphibians in decline: Canadian studies of a global problem, D.M. Green, editor. Society for Study of Amphibians and Reptiles, Salt Lake City, UT. The ACOs were constructed of freshly milled Douglas-fir without any sort of anti-fungal treatment. The thickness of the baseboard was about 5 cm, and the top boards were about 3 cm thick. Three of these devices were deployed within each YSTDS stand in October of 2008 at randomly chosen locations within the mammal trapping transect arrays. Each location was marked with bright orange flagging, and GPS coordinates were recorded and stored. Sampling from ACOs involves removing the top boards one at a time, and examining any salamanders thus exposed. Next the main (bottom) board is lifted and the ground underneath examined for salamanders. Each salamander is placed in a small plastic bag for weighing and measuring. Weight is measured with a 50-g Pesola spring scale to the nearest 0.5 gram. Snout-vent length (SVL) is measured to the nearest millimeter with a small plastic ruler. These data, along with location, species, and sex (when it can be determined) are recorded on a field sheet printed on water resistant paper. During the November 2009 checks, salamanders were photographed in order to attempt to later determine sex, but this was not successful. In practice, few salamanders captured on the YSTDS stands have been sexed, other than larger Ensatina which are relatively easy to sex based on lip and vent morphology, and the occasional appearance of visible ova within the females’ abdomens. After handling, each salamander is carefully placed back into the re-assembled ACO in approximately the position it was found, through the side openings created by the lengths of lath attached to the main board. 1 WE00801 Small vertebrate captures: WE00801.csv 1556254 ab6d8c958e7db7084d6a70ea6648add8 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00801_v1.csv 1991-10-16 2008-11-21 DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 1.0000 1.0000 SAMPLEDATE Date of capture or sample datetime YYYY-MM-DD hh:mm:ss 10/16/1991 12:00:00 AM 11/21/2008 12:00:00 AM YEAR Year of sampling numeric(4,0) number 1.000000 natural 1991.0000 2008.0000 JULIAN Julian day numeric(3,0) number 1.000000 natural 264.0000 326.0000 TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 BLOCK Block code char(1) 1 Cougar resevoir, blue river district 2 Mill creek, mckenzie bridge district 3 Christy flats, oakridge district 4 Sidewalk creek, oakridge district TREATMENT Treatment code char(1) 1 Control; no harvest 2 Heavy thin 3 Light thin 4 Light thin with gaps TRANSECT Transect number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 whole 1.0000 11.0000 STATION Trap station number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 natural 1.0000 37.0000 TRST Transect/station code (1991 and 1992 measurement years) char(3) Transect/station code (1991 and 1992 measurement years) TRAPTYPE Trap type char(2) P Pitfall trap S Sherman live trap T Tree Tomahawk G Ground Tomahawk TCHECK Designates whether the check was in the morning or afternoon. char(2) AM Morning Check PM Afternoon Check   Time of check not specified SPECIES Ground-dwelling vertebrate species char(4) STJA Stellaria jamesiana AMGR Ambystoma gracile ANFE Aneides ferreus ASTR Ascaphus truei BAWR Batrachoseps wrighti BUBO Bufo boreas DITE Dicamptodon tenebrosus ENES Ensatina eschscholtzii PLDU Plethodon dunni RAAU Rana aurora TAGR Taricha granulosa CLCA Clethrionomys californicus GLSA Glaucomys sabrinus LEAM Lepus americanus MILO Microtus longicaudus MIOR Microtus oregoni MIRI Microtus richardsoni MUER Mustela erminea NECI Neotoma cinerea NEGI Neurotrichus gibbsii PEMA Peromyscus maniculatus SCOR Scapanus orarius SOSP Sorex SOBE Sorex bendirii SOTR Sorex trowbridgii SOVA Sorex vagrans SPBE Spermophilus beecheyi TADO Tamiasciurus douglasii ZATR Zapus trinotatus TATO Tamias townsendii PHLO Phenacomys longicaudus SOBA Sorex bairdi SOSO Sorex sonoma DIMA Didelphis marsupialis SOPA Sorex pacificus SPGR Spilogale gracilis SYBA Sylvilagus bachmani UNKN Unknown Mammal Species VOLE unknown vole CAPSTAT Capture status char(2) E Escaped / capture status unknown N New capture NE New capture / escaped prior to tagging/toe-clipping P Torn ear(s) indicative of tag loss R Recapture RE Recapture / escaped prior to recording tag/toe number RT Retagged due to problems with existing ear tag U Unknown TAG1 Tag #1 (0 indicates no tag) numeric(4,0) number 1.000000 whole 1.0000 8000.0000 EAR1 Ear for tag #1 char(2) 0 Ear not tagged L Left ear tagged R Right ear tagged TAG2 Tag #2 (0 indicates no tag) numeric(4,0) number 1.000000 whole 1.0000 7000.0000 EAR2 Ear for tag #2 char(2) 0 Ear not tagged L Left ear tagged R Right ear tagged TOENUM1 Toe number assigned in field (0 indicates no toe clipped) numeric(4,0) number 1.000000 whole 1.0000 99.0000 TOENUM2 Re-assigned toe number (1991-1992 only) (0 indicates no toe clipped) numeric(4,0) number 1.000000 whole 1.0000 927.0000 BODYL Body length numeric(5,1) centimeters 0.100000 real 1.0000 30.0000 TAILL Tail length numeric(5,1) centimeters 0.100000 real 1.0000 20.0000 WEIGHT Weight numeric(5,1) grams 0.100000 real 0.7000 900.0000 SEX Gender char(2) F Female M Male U Unknown F? Likely a female, but not positive M? Likely a male, but not positive REPROSTAT Reproductive status char(3) L Lactating NL Not lactating P Pregnant TD Testes descended TR Testes recessed U Unknown LIVE Live status char(1) 0 Alive 1 Dead DEADNUM Bag number of dead specimen numeric(4,0) number 1 whole 1.0000 1616.0000 NOTES Comments varchar(45) Comments NOTNULL WE00801.BLOCK WE00801.DATACODE WE00801.FORMAT WE00801.JULIAN WE00801.SPECIES WE00801.TAC WE00801.TRAPTYPE WE00801.TREATMENT WE00801.YEAR 11146 2 WE00802 Standing snags and down woody debris: WE00802.csv 78117 43fd88c6dbe9d51f5ca74bca247b5574 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00802_v1.csv 1991-10-16 1991-10-16 DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 2.0000 2.0000 PLOT Plot numeric(2,0) number 1.000000 natural 1.0000 66.0000 YEAR Year of sampling numeric(4,0) number 1.000000 natural 1991.0000 1991.0000 DISTR District char(3) BLR Blue river MKB Mckenzie bridge OAK Oakridge STAND Stand char(1) C Conifer? M Mixed? S Softwood? SCLASS Size class char(2) L Large M Medium S Small XL Extra large LENGTH Length numeric(5,1) feet 0.100000 real 0.9000 145.0000 DCLASS Diameter class numeric(1,0) number 1.000000 natural 1.0000 8.0000 NOTNULL WE00802.DATACODE WE00802.DCLASS WE00802.DISTR WE00802.FORMAT WE00802.LENGTH WE00802.PLOT WE00802.SCLASS WE00802.STAND WE00802.YEAR 2449 3 WE00803 Subplot-level habitat data: WE00803.csv 513868 36611fe3c89d08dbbf0422a7e082a0aa 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00803_v2.csv DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 3.0000 3.0000 YEAR Year of sampling numeric(4,0) number 1.000000 natural 1911.0000 1988.0000 SITE Site number numeric(2,0) number 1.000000 natural 1.0000 58.0000 SUBPLOT Cardinal direction from station to subplot char(1) E East N North S South W West OBS Observer code char(2) DS D. shields DV D. vesely GD G. downing GM G. mcatee JF J. fairchild JH J. hagar LB L. brown MC Mccomb MH M.hunter RP R. pastor SH Sharon hope? TW Tom w UN Iunknown observer TF Tim Fox TM Tom Manning JULIAN Julian day numeric(3,0) number 1.000000 natural 231.0000 260.0000 LITTER Litterfall depth to mineral soil numeric(3,1) millimeters 0.100000 real 10.0000 95.0000 COVER Moosehorn measure of canopy cover at subplot center numeric(2,0) percent 1.000000 whole 0.0000 25.0000 WATER Percent subplot cover by water (line intercept basis) numeric(3,0) percent 1.000000 whole 0.0000 5.0000 SOIL Percent subplot cover by soil (line intercept basis) numeric(3,0) percent 1.000000 whole 0.0000 5.0000 ROCK Percent subplot cover by rock (line intercept basis) numeric(3,0) percent 1.000000 whole 0.0000 40.0000 PLANT Percent subplot cover by plants (line intercept basis) numeric(3,0) percent 1.000000 natural 60.0000 100.0000 ZONE Vegetation layer code char(1) H Herb layer S Shrub layer T Tree layer ZONENR Consecutive number of vegetation layers described by following variables numeric(1,0) number 1.000000 natural 1.0000 9.0000 LHGT Lower limit of layer height numeric(4,1) meters 0.100000 real 0.0000 34.0000 UHGT Upper limit of layer height numeric(4,1) meters 0.100000 real 0.0000 40.0000 CUBES Percent of 1 foot cubes in layer containing live foliage numeric(2,0) percent 1.000000 whole 0.0000 98.0000 SPEC Taxonomic Species char(6) ABGR Abies grandis ACCI Acer circinatum ACMA Acer macrophyllum ACMI Achillea millefolium ALRU Alnus rubra AMAL Amelanchier alnifolia ARME Arbutus menziesii ARCO Arnica cordifolia BENE Berberis nervosa CASH Carex sheldonii CONU Cornus nuttallii COCO Cotula coronopifolia CYSC Cytisus scoparius FRLA Fritillaria lanceolata GASH Gaultheria shallon HODI Holodiscus discolor LIBO Listera borealis OECE Oemleria cerasiformis POTR Populus tremuloides PREM Prunus emarginata PSME Pseudotsuga menziesii RHPU Rhamnus purshiana RHMA Rhododendron macrophyllum RIBES Ribes RIBR Ribes bracteosum ROGY Rosa gymnocarpa RUDI Rubus discolor RULE Rubus leucodermis RUNI Rubus nivalis RUPA Rubus parviflorus RUUR Rubus ursinus SALI Salix ligulifolia SACE Sambucus cerulea SYAL Symphoricarpos albus TABR Taxus brevifolia THPL Thuja plicata TSHE Tsuga heterophylla VAPA Vaccinium parvifolium CACH Castanopsis chrysophylla LIDE2 Libocedrus decurrens OSCE Osmaronia cerasiformis UNKN Unknown Mammal Species HERB Herb GRASS Grass FERN Fern RELPCT Relative percent of species or type occupying cubes numeric(3,0) percent 1.000000 whole 0.0000 100.0000 PRIMARY WE00803.JULIAN WE00803.SITE WE00803.SUBPLOT WE00803.YEAR WE00803.ZONE WE00803.ZONENR NOTNULL WE00803.COVER WE00803.DATACODE WE00803.FORMAT WE00803.JULIAN WE00803.LHGT WE00803.LITTER WE00803.OBS WE00803.PLANT WE00803.ROCK WE00803.SITE WE00803.SOIL WE00803.SUBPLOT WE00803.WATER WE00803.YEAR WE00803.ZONE WE00803.ZONENR 7515 4 WE00804 VCP bird detections: WE00804.csv 946354 1077f5fb7b7c353912c35af64d130bde 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00804_v1.csv DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 4.0000 4.0000 YEAR Year of sampling numeric(4,0) number 1.000000 natural 1992.0000 2001.0000 MONTH Month of sampling numeric(2,0) month 1.000000 DAY Day of sampling numeric(2,0) day 1.000000 TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 DISTR District char(3) BLR Blue river MKB Mckenzie bridge OAK Oakridge BLOCK Block code char(1) 1 Cougar resevoir, blue river district 2 Mill creek, mckenzie bridge district 3 Christy flats, oakridge district 4 Sidewalk creek, oakridge district TREATMENT Treatment code char(1) 1 Control; no harvest 2 Heavy thin 3 Light thin 4 Light thin with gaps OBS Observer code char(2) DS D. shields DV D. vesely GD G. downing GM G. mcatee JF J. fairchild JH J. hagar LB L. brown MC Mccomb MH M.hunter RP R. pastor SH Sharon hope? TW Tom w UN Iunknown observer TF Tim Fox TM Tom Manning VNR Visit number numeric(1,0) number 1.000000 natural 1.0000 4.0000 STN Bird station number numeric(2,0) number 1.000000 natural 1.0000 58.0000 CLD Cloud cover numeric(3,0) percent 1.000000 whole 0.0000 100.0000 PR Precipitation code char(1) 0 None 1 Drizzle 2 Light rain 3 Heavy rain   Not recorded WD Wind acitvity code char(1) 0 No wind 1 Light breeze 2 Breezy 3 Windy   Not recorded MTIME Time of observation (hhmm) numeric(4,0) HHMM 1.000000 REF Reference number numeric(3,0) number 1.000000 natural 1.0000 38.0000 BIRDSPEC Species code char(4) GBHE Ardea herodias TUVU Cathartes aura CAGO Branta canadensis OSPR Pandion haliaetus COHA Accipiter cooperii RTHA Buteo jamaicensis RUGR Bonasa umbellus BGSE Dendragapus obscurus MOQU Oreortyx pictus BTPI Columba fasciata NOPO Glaucidium gnoma CONI Chordeiles minor VASW Chaetura vauxi RUHU Selasphorus rufus RBSA Sphyrapicus ruber HAWO Picoides villosus NOFL Colaptes auratus PIWO Dryocopus pileatus OSFL Contopus cooperi WEWP Contopus sordidulus WIFL Empidonax traillii HAFL Empidonax hammondii DUFL Empidonax oberholseri PSFL Empidonax difficilis CAVI Vireo cassinii HUVI Vireo huttoni WAVI Vireo gilvus GRJA Perisoreus canadensis STJA Cyanocitta stelleri AMCR Corvus brachyrhynchos CORA Corvus corax VGSW Tachycineta thalassina BCCH Poecile atricapillus CBCH Poecile rufescens RBNU Sitta canadensis BRCR Certhia americana HOWR Troglodytes aedon WIWR Troglodytes troglodytes GCKI Regulus satrapa WEBL Sialia mexicana TOSO Myadestes townsendi SWTH Catharus ustulatus HETH Catharus guttatus AMRO Turdus migratorius VATH Ixoreus naevius CEWA Bombycilla cedrorum OCWA Vermivora celata NAWA Vermivora ruficapilla YEWA Dendroica petechia YRWA Dendroica coronata BTYW Dendroica nigrescens TOWA Dendroica townsendi HEWA Dendroica occidentalis MGWA Oporornis tolmiei COYE Geothlypis trichas WIWA Wilsonia pusilla WETA Piranga ludoviciana SPTO Pipilo maculatus CHSP Spizella passerina SOSP Melospiza melodia WCSP Zonotrichia leucophrys DEJU Junco hyemalis BHGR Pheucticus melanocephalus LAZB Passerina amoena BHCO Molothrus ater NOOR Icterus bullockii PUFI Carpodacus purpureus RECR Loxia curvirostra PISI Carduelis pinus LEGO Carduelis psaltria AMGO Carduelis tristis EVGR Coccothraustes vespertinus TY Type of detection char(1) 1 Singing 2 Calling 3 Visual A Aural B Aural and visual NEW New or repeat individual char(1) N New individual R Repeat individual DISTANCE Distance to animal when first detected numeric(3,0) meters 1.000000 whole 0.0000 999.0000 NDIST Nearest distance to animal numeric(3,0) meters 1.000000 natural 0.0000 999.0000 LOCA Location in or out of site char(1)   Unknown location 0 Out 1 In NOTES Comments varchar(50) Comments NOTNULL WE00804.BLOCK WE00804.DATACODE WE00804.DAY WE00804.DISTR WE00804.FORMAT WE00804.MONTH WE00804.MTIME WE00804.OBS WE00804.STN WE00804.TAC WE00804.TREATMENT WE00804.VNR WE00804.YEAR 14581 5 WE00805 Small vertebrate trap status: WE00805.csv 417246 4faa8eb3ce34ef1ca504bd3c9fbd0ff0 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00805_v1.csv 1991-10-16 2008-11-21 DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 5.0000 5.0000 YEAR Year of sampling numeric(4,0) number 1.000000 natural 1991.0000 2001.0000 MONTH Month of sampling numeric(2,0) month 1.000000 DAY Day of sampling numeric(2,0) day 1.000000 JULIAN Julian day numeric(3,0) number 1.000000 natural 264.0000 325.0000 TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 BLOCK Block code char(1) 1 Cougar resevoir, blue river district 2 Mill creek, mckenzie bridge district 3 Christy flats, oakridge district 4 Sidewalk creek, oakridge district TREATMENT Treatment code char(1) 1 Control; no harvest 2 Heavy thin 3 Light thin 4 Light thin with gaps TRANSECT Transect number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 whole 0.0000 11.0000 STATION Trap station number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 natural 0.0000 37.0000 TRST Transect/station code (1991 and 1992 measurement years) char(3) Transect/station code (1991 and 1992 measurement years) TRAPTYPE Trap type char(2) P Pitfall trap S Sherman live trap T Tree Tomahawk G Ground Tomahawk STATUS Trap status char(10) BROKEN Trap present, but broken MISSING Trap missing NONFUNC Non-functional NOTSET Trap not activated SHREDDED Shredded carton SPRUNG Trap sprung USE Evidence of animal use, but trap functional NOTES Comments varchar(45) Comments NOTNULL WE00805.BLOCK WE00805.DATACODE WE00805.DAY WE00805.FORMAT WE00805.JULIAN WE00805.MONTH WE00805.TRST WE00805.STATUS WE00805.TAC WE00805.TRANSECT WE00805.TRAPTYPE WE00805.TREATMENT WE00805.YEAR 7854 6 WE00806 Small vertebrate capture summary: WE00806.csv 118821 58f5059b573769c429c1d1e383cf9fcf 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00806_v1.csv DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 6.0000 6.0000 YEAR Year of sampling numeric(4,0) number 1.000000 natural 1991.0000 2001.0000 SPECIES Ground-dwelling vertebrate species char(4) STJA Stellaria jamesiana AMGR Ambystoma gracile ANFE Aneides ferreus ASTR Ascaphus truei BAWR Batrachoseps wrighti BUBO Bufo boreas DITE Dicamptodon tenebrosus ENES Ensatina eschscholtzii PLDU Plethodon dunni RAAU Rana aurora TAGR Taricha granulosa CLCA Clethrionomys californicus GLSA Glaucomys sabrinus LEAM Lepus americanus MILO Microtus longicaudus MIOR Microtus oregoni MIRI Microtus richardsoni MUER Mustela erminea NECI Neotoma cinerea NEGI Neurotrichus gibbsii PEMA Peromyscus maniculatus SCOR Scapanus orarius SOSP Sorex SOBE Sorex bendirii SOTR Sorex trowbridgii SOVA Sorex vagrans SPBE Spermophilus beecheyi TADO Tamiasciurus douglasii ZATR Zapus trinotatus TATO Tamias townsendii PHLO Phenacomys longicaudus SOBA Sorex bairdi SOSO Sorex sonoma DIMA Didelphis marsupialis SOPA Sorex pacificus SPGR Spilogale gracilis SYBA Sylvilagus bachmani UNKN Unknown Mammal Species VOLE unknown vole TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 BLOCK Block code char(1) 1 Cougar resevoir, blue river district 2 Mill creek, mckenzie bridge district 3 Christy flats, oakridge district 4 Sidewalk creek, oakridge district TREATMENT Treatment code char(1) 1 Control; no harvest 2 Heavy thin 3 Light thin 4 Light thin with gaps N_SHERM Number of original captures in sherman traps numeric(4,0) number 1.000000 whole 0.0000 110.0000 R_SHERM Number of recaptures in sherman traps numeric(4,0) number 1.000000 whole 0.0000 190.0000 T_SHERM Total number of captures in sherman traps numeric(4,0) number 1.000000 whole 0.0000 209.0000 N_PIT Number of original captures in pitfall traps numeric(4,0) number 1.000000 whole 0.0000 67.0000 R_PIT Number of recaptures in pitfall traps numeric(4,0) number 1.000000 whole 0.0000 7.0000 T_PIT Total number of captures in pitfall traps numeric(4,0) number 1.000000 whole 0.0000 69.0000 N_TOTAL Total number of recorded original captures numeric(4,0) number 1.000000 whole 0.0000 110.0000 R_TOTAL Total number of recorded recaptures numeric(4,0) number 1.000000 whole 0.0000 190.0000 T_TOTAL Total number of recorded captures numeric(4,0) number 1.000000 whole 0.0000 280.0000 NOTNULL WE00806.BLOCK WE00806.DATACODE WE00806.FORMAT WE00806.SPECIES WE00806.TAC WE00806.TREATMENT WE00806.YEAR 2704 7 WE00807 Stations with pitfall traps (1998-99): WE00807.csv 6340 9d247f34f33d94d4480c73fef142447a 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00807_v1.csv TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 TRANSECT Transect number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 whole 0.0000 11.0000 STATION Trap station number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 natural 0.0000 37.0000 NOTNULL WE00807.TAC WE00807.TRANSECT 802 8 WE00808 Number of transects(1998-99): WE00808.csv 104 fb9f22eb640fa1ebab2edb1cefa8676a 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00808_v1.csv TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 TRANSECTS # of transects numeric(2,0) number 1.000000 natural 0.0000 11.0000 NOTNULL WE00808.TAC WE00808.TRANSECTS 16 9 WE00809 Max number of stations per transect (1998-99): WE00809.csv 882 a7438ec9423746561e54f738b911eb14 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00809_v1.csv TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 TRANSECT Transect number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 whole 0.0000 11.0000 STNS Number of trapping stations numeric(2,0) number 1.000000 natural 0.0000 37.0000 NOTNULL WE00809.TAC WE00809.TRANSECT 104 10 WE00810 GPS coordinates of end points of transects on each stand: WE00810.csv 3648 a1883b3b143c9e939a66c2ed7a4ed668 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00810_v1.csv DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 TRANSECT Transect number (all measurement years except 1991 and 1992) numeric(2,0) number 1.000000 whole 1.0000 11.0000 STN Bird station number numeric(2,0) number 1.000000 natural 1.0000 26.0000 UTME Utm east numeric(7,0) meters 1.000000 natural 550380.0000 565050.0000 UTMN Utm west numeric(7,0) meters 1.000000 natural 4858003.0000 4894614.0000 NOTES Comments varchar(20) Comments NOTNULL WE00810.DATACODE WE00810.STN WE00810.TAC WE00810.TRANSECT WE00810.UTME WE00810.UTMN 111 11 WE00811 Locations of Artificial Cover Objects: Locations of 48 ACO's placed Oct 2008 WE00811.csv 2173 bc54a9d42854ed7fc87d0512aa372561 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00811_v1.csv 2008-10-01 2008-10-31 DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 11.0000 11.0000 TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 ACO Code to identify individual Artificial Cover Object (ACO) within each Treatment Area Code (TAC) char(5) T0101 Treatment Area Code 01, Artificial Cover Object 1 T0102 Treatment Area Code 01, Artificial Cover Object 2 T0103 Treatment Area Code 01, Artificial Cover Object 3 T0201 Treatment Area Code 02, Artificial Cover Object 1 T0202 Treatment Area Code 02, Artificial Cover Object 2 T0203 Treatment Area Code 02, Artificial Cover Object 3 T0301 Treatment Area Code 03, Artificial Cover Object 1 T0302 Treatment Area Code 03, Artificial Cover Object 2 T0303 Treatment Area Code 03, Artificial Cover Object 3 T0401 Treatment Area Code 04, Artificial Cover Object 1 T0402 Treatment Area Code 04, Artificial Cover Object 2 T0403 Treatment Area Code 04, Artificial Cover Object 3 T0501 Treatment Area Code 05, Artificial Cover Object 1 T0502 Treatment Area Code 05, Artificial Cover Object 2 T0503 Treatment Area Code 05, Artificial Cover Object 3 T0601 Treatment Area Code 06, Artificial Cover Object 1 T0602 Treatment Area Code 06, Artificial Cover Object 2 T0603 Treatment Area Code 06, Artificial Cover Object 3 T0701 Treatment Area Code 07, Artificial Cover Object 1 T0702 Treatment Area Code 07, Artificial Cover Object 2 T0703 Treatment Area Code 07, Artificial Cover Object 3 T0801 Treatment Area Code 08, Artificial Cover Object 1 T0802 Treatment Area Code 08, Artificial Cover Object 2 T0803 Treatment Area Code 08, Artificial Cover Object 3 T0901 Treatment Area Code 09, Artificial Cover Object 1 T0902 Treatment Area Code 09, Artificial Cover Object 2 T0903 Treatment Area Code 09, Artificial Cover Object 3 T1001 Treatment Area Code 10, Artificial Cover Object 1 T1002 Treatment Area Code 10, Artificial Cover Object 2 T1003 Treatment Area Code 10, Artificial Cover Object 3 T1101 Treatment Area Code 11, Artificial Cover Object 1 T1102 Treatment Area Code 11, Artificial Cover Object 2 T1103 Treatment Area Code 11, Artificial Cover Object 3 T1201 Treatment Area Code 12, Artificial Cover Object 1 T1202 Treatment Area Code 12, Artificial Cover Object 2 T1203 Treatment Area Code 12, Artificial Cover Object 3 T1301 Treatment Area Code 13, Artificial Cover Object 1 T1302 Treatment Area Code 13, Artificial Cover Object 2 T1303 Treatment Area Code 13, Artificial Cover Object 3 T1401 Treatment Area Code 14, Artificial Cover Object 1 T1402 Treatment Area Code 14, Artificial Cover Object 2 T1403 Treatment Area Code 14, Artificial Cover Object 3 T1501 Treatment Area Code 15, Artificial Cover Object 1 T1502 Treatment Area Code 15, Artificial Cover Object 2 T1503 Treatment Area Code 15, Artificial Cover Object 3 T1601 Treatment Area Code 16, Artificial Cover Object 1 T1602 Treatment Area Code 16, Artificial Cover Object 2 T1603 Treatment Area Code 16, Artificial Cover Object 3 PROJECTION Map projection used to obtain Universal Transverse Mercator (UTM) coordinates char(5) NAD83 North American Datum 1983 UTMZONE Geographic zone for the UTM projection char(3) 10T UTM Zone 10, Band T EASTING UTM easting coordinate numeric(6,0) meters 1 natural 550567.0000 564826.0000 NORTHING UTM northing coordinate numeric(7,0) meters 1 whole 4858285.0000 4894733.0000 PRIMARY WE00811.ACO NOTNULL WE00811.DATACODE WE00811.FORMAT WE00811.TAC WE00811.ACO WE00811.PROJECTION WE00811.EASTING WE00811.NORTHING WE00811.UTMZONE 48 12 WE00812 Amphibian Capture Data from Artificial Cover Objects: Semi-annual capture data from ACO's starting June 2009 WE00812.csv 98 0a9b065fc6eeecab4bcfaae95fdc8914 1 \r\n column , " http://andlter.forestry.oregonstate.edu/ltermeta/ltersearch/dataaccess.aspx?docid=WE00812_v1.csv 2009-06-26 2009-11-05 DATACODE FSDB Database code char(5) WE008 FSDB database code WE008 FORMAT Entity number numeric(2,0) number 1.000000 natural 12.0000 12.0000 SAMPLEDATE Date of capture or sample datetime YYYY-MM-DD hh:mm:ss 6/26/2009 12:00:00 AM 5/2/2012 12:00:00 AM YEAR Year of sampling numeric(4,0) number 1.000000 natural 2009.0000 2012.0000 TAC Treatment area code char(2) 1 Cougar reservoir control treatment ; site #12; blue river ranger district 2 Cougar reservoir heavy thin; site #14; blue river ranger district tap thin timber sale unit 1 3 Cougar reservoir light thin; site #11; blue river ranger district tap thin timber sale unit 3 4 Cougar reservoir light thin with gaps; site #13; blue river ranger district tap thin timber sale unit 4 5 Mill creek control treatment; site #72, mckenzie ranger district 6 Mill creek heavy thin; site #71, mckenzie ranger district mill thin 1 timber sale unit 2 7 Mill creek light thin; site #73; mckenzie ranger district mill thin 1 timber sale unit 1 8 Mill creek light thin with gaps; site #74; mckenzie ranger district mill thin 2 timber sale unit 4/5 9 Christy flats control treatment; site #83; oakridge ranger district 10 Christy flats heavy thin; site #81; oakridge ranger district flat thin timber sale unit 81 11 Christy flats light thin; site #84; oakridge ranger district flat thin timber sale unit 84 12 Christy flats light thin with gaps; site #82; oakridge ranger district flat thin timber sale unit 82 13 Sidewalk creek control treatment; site #87; oakridge ranger district 14 Sidewalk creek heavy thin; site #88; oakridge ranger district walk thin timber sale unit 88 15 Sidewalk creek light thin; site #85; oakridge ranger district walk thin timber sale unit 85 16 Sidewalk creek light thin with gaps; site #86; oakridge ranger district walk thin timber sale units 86 & 89 BLOCK Block code char(1) 1 Cougar resevoir, blue river district 2 Mill creek, mckenzie bridge district 3 Christy flats, oakridge district 4 Sidewalk creek, oakridge district TREATMENT Treatment code char(1) 1 Control; no harvest 2 Heavy thin 3 Light thin 4 Light thin with gaps ACO Code to identify individual Artificial Cover Object (ACO) within each Treatment Area Code (TAC) char(5) T0101 Treatment Area Code 01, Artificial Cover Object 1 T0102 Treatment Area Code 01, Artificial Cover Object 2 T0103 Treatment Area Code 01, Artificial Cover Object 3 T0201 Treatment Area Code 02, Artificial Cover Object 1 T0202 Treatment Area Code 02, Artificial Cover Object 2 T0203 Treatment Area Code 02, Artificial Cover Object 3 T0301 Treatment Area Code 03, Artificial Cover Object 1 T0302 Treatment Area Code 03, Artificial Cover Object 2 T0303 Treatment Area Code 03, Artificial Cover Object 3 T0401 Treatment Area Code 04, Artificial Cover Object 1 T0402 Treatment Area Code 04, Artificial Cover Object 2 T0403 Treatment Area Code 04, Artificial Cover Object 3 T0501 Treatment Area Code 05, Artificial Cover Object 1 T0502 Treatment Area Code 05, Artificial Cover Object 2 T0503 Treatment Area Code 05, Artificial Cover Object 3 T0601 Treatment Area Code 06, Artificial Cover Object 1 T0602 Treatment Area Code 06, Artificial Cover Object 2 T0603 Treatment Area Code 06, Artificial Cover Object 3 T0701 Treatment Area Code 07, Artificial Cover Object 1 T0702 Treatment Area Code 07, Artificial Cover Object 2 T0703 Treatment Area Code 07, Artificial Cover Object 3 T0801 Treatment Area Code 08, Artificial Cover Object 1 T0802 Treatment Area Code 08, Artificial Cover Object 2 T0803 Treatment Area Code 08, Artificial Cover Object 3 T0901 Treatment Area Code 09, Artificial Cover Object 1 T0902 Treatment Area Code 09, Artificial Cover Object 2 T0903 Treatment Area Code 09, Artificial Cover Object 3 T1001 Treatment Area Code 10, Artificial Cover Object 1 T1002 Treatment Area Code 10, Artificial Cover Object 2 T1003 Treatment Area Code 10, Artificial Cover Object 3 T1101 Treatment Area Code 11, Artificial Cover Object 1 T1102 Treatment Area Code 11, Artificial Cover Object 2 T1103 Treatment Area Code 11, Artificial Cover Object 3 T1201 Treatment Area Code 12, Artificial Cover Object 1 T1202 Treatment Area Code 12, Artificial Cover Object 2 T1203 Treatment Area Code 12, Artificial Cover Object 3 T1301 Treatment Area Code 13, Artificial Cover Object 1 T1302 Treatment Area Code 13, Artificial Cover Object 2 T1303 Treatment Area Code 13, Artificial Cover Object 3 T1401 Treatment Area Code 14, Artificial Cover Object 1 T1402 Treatment Area Code 14, Artificial Cover Object 2 T1403 Treatment Area Code 14, Artificial Cover Object 3 T1501 Treatment Area Code 15, Artificial Cover Object 1 T1502 Treatment Area Code 15, Artificial Cover Object 2 T1503 Treatment Area Code 15, Artificial Cover Object 3 T1601 Treatment Area Code 16, Artificial Cover Object 1 T1602 Treatment Area Code 16, Artificial Cover Object 2 T1603 Treatment Area Code 16, Artificial Cover Object 3 SPECIES Ground-dwelling vertebrate species char(4) STJA Stellaria jamesiana AMGR Ambystoma gracile ANFE Aneides ferreus ASTR Ascaphus truei BAWR Batrachoseps wrighti BUBO Bufo boreas DITE Dicamptodon tenebrosus ENES Ensatina eschscholtzii PLDU Plethodon dunni RAAU Rana aurora TAGR Taricha granulosa CLCA Clethrionomys californicus GLSA Glaucomys sabrinus LEAM Lepus americanus MILO Microtus longicaudus MIOR Microtus oregoni MIRI Microtus richardsoni MUER Mustela erminea NECI Neotoma cinerea NEGI Neurotrichus gibbsii PEMA Peromyscus maniculatus SCOR Scapanus orarius SOSP Sorex SOBE Sorex bendirii SOTR Sorex trowbridgii SOVA Sorex vagrans SPBE Spermophilus beecheyi TADO Tamiasciurus douglasii ZATR Zapus trinotatus TATO Tamias townsendii PHLO Phenacomys longicaudus SOBA Sorex bairdi SOSO Sorex sonoma DIMA Didelphis marsupialis SOPA Sorex pacificus SPGR Spilogale gracilis SYBA Sylvilagus bachmani UNKN Unknown Mammal Species VOLE unknown vole INDIVNR Individual count per TAC, BLOCK, TREATMENT, YEAR numeric(1,0) number 1 whole 1.0000 15.0000 WEIGHT Weight numeric(5,1) grams 0.100000 real 0.3000 15.0000 SEX Gender char(2) F Female M Male U Unknown F? Likely a female, but not positive M? Likely a male, but not positive SVL Snout-to-vent length numeric(2,0) millimeters 1 whole 19.0000 68.0000 NOTES Comments varchar(50) Comments OBS Observer code char(2) DS D. shields DV D. vesely GD G. downing GM G. mcatee JF J. fairchild JH J. hagar LB L. brown MC Mccomb MH M.hunter RP R. pastor SH Sharon hope? TW Tom w UN Iunknown observer TF Tim Fox TM Tom Manning PRIMARY WE00812.BLOCK WE00812.SPECIES WE00812.TAC WE00812.TREATMENT WE00812.YEAR WE00812.INDIVNR NOTNULL WE00812.BLOCK WE00812.DATACODE WE00812.FORMAT WE00812.OBS WE00812.SPECIES WE00812.TAC WE00812.TREATMENT WE00812.YEAR WE00812.SAMPLEDATE WE00812.ACO WE00812.INDIVNR 13 feet; 12 inches percent; a number grams; 0.001 kilogram millimeters; .001 meters centimeters; .01 meters meter; SI unit of length dimensionless number, i.e., ratio, count