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2018 <p>This dataset includes Statistics Canada table 46-10-0029-01, titled “Property use of residential properties, by property type and residency ownership”.</p> <p>The table has been edited to include only geographies from British Columbia and to have the unique ID numbers added to the Census Subdivisions and Census Metropolitan Areas. The table is available in CSV and Excel Workbook format. Definitions and notes are included at the bottom of the spreadsheet.</p> <p>This data set was collected as part of the Canadian Housing Statistics Program by Statistics Canada.</p> <p>Geographies:<br /> British Columbia, Abbotsford-Mission, census metropolitan area, Abbotsford, Mission, Kelowna, census metropolitan area, Central Okanagan, Central Okanagan J, Kelowna, Lake Country, Peachland, West Kelowna, Vancouver, census metropolitan area, Anmore, Belcarra, Bowen Island, Burnaby, Coquitlam, Delta, Langley, city, Langley, municipal district, Lions Bay, Maple Ridge, Metro Vancouver A, New Westminster, North Vancouver, city, North Vancouver, municipal district, Pitt Meadows, Port Coquitlam, Port Moody, Richmond, Surrey, Vancouver, West Vancouver, White Rock, Victoria, census metropolitan area, Central Saanich, Colwood, Esquimalt, Highlands, Juan de Fuca (Part 1), Langford, Metchosin, North Saanich, Oak Bay, Saanich, Sidney, Sooke, Victoria, View Royal, British Columbia, outside of census metropolitan areas, Alberni-Clayoquot A, Alberni-Clayoquot B, Alberni-Clayoquot C, Alberni-Clayoquot D, Alberni-Clayoquot E, Alberni-Clayoquot F, Alert Bay, Armstrong, Ashcroft, Barriere, Bulkley-Nechako A, Bulkley-Nechako B, Bulkley-Nechako C, Bulkley-Nechako D, Bulkley-Nechako E, Bulkley-Nechako F, Bulkley-Nechako G, Burns Lake, Cache Creek, Campbell River, Canal Flats, Cariboo A, Cariboo B, Cariboo C, Cariboo D, Cariboo E, Cariboo F, Cariboo G, Cariboo H, Cariboo I, Cariboo J, Cariboo K, Cariboo L, Castlegar, Central Coast A, Central Coast C, Central Coast D, Central Coast E, Central Kootenay A, Central Kootenay B, Central Kootenay C, Central Kootenay D, Central Kootenay E, Central Kootenay F, Central Kootenay G, Central Kootenay H, Central Kootenay I, Central Kootenay J, Central Kootenay K, Chase, Chetwynd, Chilliwack, Clearwater, Clinton, Coldstream, Columbia-Shuswap A, Columbia-Shuswap B, Columbia-Shuswap C, Columbia-Shuswap D, Columbia-Shuswap E, Columbia-Shuswap F, Comox, Comox Valley A, Comox Valley B (Lazo North), Comox Valley C (Puntledge - Black Creek), Courtenay, Cowichan Valley A, Cowichan Valley B, Cowichan Valley C, Cowichan Valley D, Cowichan Valley E, Cowichan Valley F, Cowichan Valley G, Cowichan Valley H, Cowichan Valley I, Cranbrook, Creston, Cumberland, Dawson Creek, Duncan, East Kootenay A, East Kootenay B, East Kootenay C, East Kootenay E, East Kootenay F, East Kootenay G, Elkford, Enderby, Fernie, Fort St. James, Fort St. John, Fraser Lake, Fraser Valley A, Fraser Valley B, Fraser Valley C, Fraser Valley D, Fraser Valley E, Fraser Valley F, Fraser Valley G, Fraser Valley H, Fraser-Fort George A, Fraser-Fort George C, Fraser-Fort George D, Fraser-Fort George E, Fraser-Fort George F, Fraser-Fort George G, Fraser-Fort George H, Fruitvale, Gibsons, Gold River, Golden, Grand Forks, Granisle, Greenwood, Harrison Hot Springs, Hazelton, Hope, Houston, Hudson's Hope, Invermere, Juan de Fuca (Part 2), Kamloops, Kaslo, Kent, Keremeos, Kimberley, Kitimat, Kitimat-Stikine A, Kitimat-Stikine B, Kitimat-Stikine C (Part 1), Kitimat-Stikine C (Part 2), Kitimat-Stikine D, Kitimat-Stikine E, Kitimat-Stikine F, Kootenay Boundary A, Kootenay Boundary B / Lower Columbia-Old-Glory, Kootenay Boundary C / Christina Lake, Kootenay Boundary D / Rural Grand Forks, Kootenay Boundary E / West Boundary, Ladysmith, Lake Cowichan, Lantzville, Lillooet, Logan Lake, Lumby, Lytton, Mackenzie, Masset, McBride, Merritt, Midway, Montrose, Mount Waddington A, Mount Waddington B, Mount Waddington C, Mount Waddington D, Nakusp, Nanaimo, Nanaimo A, Nanaimo B, Nanaimo C, Nanaimo E, Nanaimo F, Nanaimo G, Nanaimo H, Nelson, New Denver, New Hazelton, North Coast A, North Coast C, North Coast D, North Coast E, North Cowichan, North Okanagan B, North Okanagan C, North Okanagan D, North Okanagan E, North Okanagan F, Northern Rockies, Okanagan-Similkameen A, Okanagan-Similkameen B, Okanagan-Similkameen C, Okanagan-Similkameen D, Okanagan-Similkameen E, Okanagan-Similkameen F, Okanagan-Similkameen G, Okanagan-Similkameen H, Oliver, One Hundred Mile House, Osoyoos, Parksville, Peace River B, Peace River C, Peace River D, Peace River E, Pemberton, Penticton, Port Alberni, Port Alice, Port Clements, Port Edward, Port Hardy, Port McNeill, Pouce Coupe, Powell River, Powell River A, Powell River B, Powell River C, Powell River D, Powell River E, Prince George, Prince Rupert, Princeton, Qualicum Beach, Queen Charlotte, Quesnel, Radium Hot Springs, Revelstoke, Rossland, Salmo, Salmon Arm, Saltspring Island, Sayward, Sechelt, Sicamous, Silverton, Slocan, Smithers, Southern Gulf Islands, Spallumcheen, Sparwood, Squamish, Squamish-Lillooet A, Squamish-Lillooet B, Squamish-Lillooet C, Squamish-Lillooet D, Stewart, Stikine Region, Strathcona A, Strathcona B, Strathcona C, Strathcona D (Oyster Bay - Buttle Lake), Summerland, Sun Peaks Mountain, Sunshine Coast A, Sunshine Coast B, Sunshine Coast D, Sunshine Coast E, Sunshine Coast F, Tahsis, Taylor, Telkwa, Terrace, Thompson-Nicola A (Wells Gray Country), Thompson-Nicola B (Thompson Headwaters), Thompson-Nicola E (Bonaparte Plateau), Thompson-Nicola I (Blue Sky Country), Thompson-Nicola J (Copper Desert Country), Thompson-Nicola L (Grasslands), Thompson-Nicola M (Beautiful Nicola Valley - North), Thompson-Nicola N (Beautiful Nicola Valley - South), Thompson-Nicola O (Lower North Thompson), Thompson-Nicola P (Rivers and the Peaks), Tofino, Trail, Tumbler Ridge, Ucluelet, Valemount, Vanderhoof, Vernon, Warfield, Wells, Whistler, Williams Lake, Zeballos</p>
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2021-04-23 <p>Background: The legacy of war in Northern Uganda continues to impact people’s health and wellbeing in the Acholi region. Despite increasing attention to Hepatitis B Virus (HBV) in Uganda and globally, concerns remain that unique drivers of infection, and barriers to screening, and treatment, persist among those affected by conflict.</p> <p>Methods: Cango Lyec (Healing the Elephant) cohort survey involved conflict-affected adults aged 13-49 in three mid-Northern Uganda districts (Gulu, Amuru and Nwoya). Baseline (2011-2012) samples were tested for HBV surface antigen (HBsAg), HBV e-antigen (HBeAg), antibodies to HBV surface antigen (HBsAb), antibodies to HBV e-antigen (HBeAb), and antibodies to HBV core antigen (HBcAb). All HBsAg positive samples were tested for IgM antibodies to HBV B core antigen (HBc-IgM) and where available, &gt;6-month follow-up samples were tested for HBeAg and HBV DNA. Data were analyzed using STATA 15 software. Logistic regression accounted for variance due to complex two-stage sampling that included stratification, unequal selection probabilities and community clustering. Odds ratios measured effect potential risk factors associated with chronic HBV infection.</p> <p>Results: Among 2,421 participants, 45.7% were still susceptible to HBV infection. HBsAg seropositivity was 11.9% (10.9-13.0), chronic HBV was 11.6% (10.4-12.8), acquired immunity resulting from vaccination was 10.9%, and prior natural infection was 31.5%. Older age (OR:0.570; 95%CI:0.368-0.883) and higher education (OR:0.598; 95%CI:0.412-0.868) were associated with reduced odds of chronic HBV infection. Being male (OR:1.639; 95%CI:1.007-2.669) and having been abducted (OR:1.461; 95%CI:1.055-2.023) were associated with increased odds of infection. Among women, having 1 or 2 pregnancies (compared to none or &gt;2) was associated with increased odds of infection (OR:1.764; 95%CI:1.009-3.084).</p> <p>Conclusion: Chronic HBV is endemic in Gulu, Amuru and Nwoya districts. Recommended strategies to reduce post-conflict prevalence include establishment of Northern Uganda Liver Wellness Centres, integration of screening and treatment into antenatal care, and roll out of birth-dose vaccination.</p>
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2022-05-04 Standing dead trees (snags) are crucial habitats for fauna in mature and diverse forests along the Interior Douglas-fir Zone of British Columbia. The objective of this study is to evaluate whether snag density and snag metrics differ between three categories of at-risk and irreplaceable Old Growth Priority Deferral Areas (ancient, big-treed and remnant) and their neighbouring areas with no deferral status. Using airborne LiDAR data, we detect snags using 1) area-based forest metrics paired with random forest modelling, and 2) an individual snag detection algorithm.
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2020-04-20 This study investigates the relationship between waste rock weathering, processes controlling mineral reactivity or solute mobility, and drainage chemistry in field barrel kinetic tests or within the full-scale waste-rock pile. This thesis is divided into 3 research chapters (Chapters 2 to 4) describing the application of automated mineralogical characterizations of waste rock linked to the hydrological regime and/or the leaching behaviour of waste rock after weathering at two scales: field barrels (Chapters 2 and 3) and full-scale waste-rock pile (Chapter 4). Overall, this thesis is facilitating the interpretation of waste-rock reactivity using waste-rock quantitative mineralogical evaluations; providing mineralogical perspectives on geochemical and hydrological processes; expanding the identification of mechanisms affecting metal mobility from waste-rock drainage; and, providing information to achieve more accurate drainage prediction models.
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2022-04-19 Upslope treeline advancement has been occurring globally over the last several decades, leading to displacement and fragmentation of alpine habitats and declines in species richness. Examining past and current treeline migration can provide insight into potential future conditions and can be used to improve ecosystem management. There is no long-term data on treeline advancement in Central British Columbia (B.C.) and the response to climate change is poorly understood. To address this, we explored treeline advancement in the Cariboo Natural Resource Region over a 35-year period (1985-2020) using Landsat imagery. Changes to the rate of advancement within the Engelmann-Spruce Subalpine Fir (ESSF) Biogeoclimatic Zone (BEC) were investigated in five-year increments using a common greenness index and the effects of slope and aspect were analysed. The most significant increase in advancement was observed between 2005 to 2015, with 190 km2 more advancement occurring in the 2010-2015 period compared to the 2005-2010 period. This large increase could be a result of temperature warming in the region beginning in the 1990s. Unexpectedly, we found steep sloped regions (> 30 degrees) exhibited greater treeline advancement throughout the study period, compared to gentle slopes (< 30 degrees). One possible reason for this is that steep slopes are less prone to cold sinks and trees favour warm temperatures for establishment. Aspect had no effect on treeline advancement, likely due to greater moisture on north-facing slopes but warmer temperatures on south-facing slopes. Additionally, significant variability throughout the study region was found, illustrating the complexity of treeline advancement and the challenges that exist when examining large geographic regions, as well as the importance of local ecosystem knowledge for future treeline modelling.
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2022-04-19 Urban trees play an essential role in alleviating the local effects of global warming by sequestering atmospheric carbon dioxide, regulating temperature and reducing air pollution in urban areas. There have been studies estimating carbon sequestration of urban trees using Light Detection and Ranging (LiDAR). Yet, neither of the studies made comparison between species nor extended the discussion towards ecosystem services. Therefore, this study compared the attributes between native and cultivated trees in the Asian Garden of the University of British Columbia (UBC) Botanical Garden, estimated their level of above-ground carbon sequestration, and thus examined respective implications in terms of ecosystem services. A canopy height model was first generated from LiDAR point cloud data for individual tree segmentation based on Dalponte algorithm. There were 803 derived trees matched successfully with the field-measured trees in ArcGIS with an accuracy of 69.5%. The level of above-ground carbon sequestration of each tree was estimated from tree height and canopy area using a non-linear regression model. Results showed that the average carbon sequestration level of native trees was higher than cultivated trees by 1102 kg (p = 3.045 x 10-7), which facilitated more effective soil formation. The average canopy areas of both trees were approximately 63 m2 (p = 0.696), which gives rise to their similar contribution in temperature cooling and air purification. In general, the garden provides a high level of biodiversity and education value thanks to its high species diversity. Regarding future directions in garden management, the removal of native trees and the planting location of cultivated trees in the garden should be carefully evaluated since they have higher level of ecosystem services and higher crown area to height ratio respectively.
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2022-06-02 <br /><strong>NOTE for restricted files:</strong> If you are not yet a CoLab member, please complete our <a href = "https://rc.bcchr.ca/redcap/surveys/?s=EDCYL7AC79">membership application survey</a> to gain access to restricted files within 2 business days. <br />Some files may remain restricted to CoLab members. These files are deemed more sensitive by the file owner and are meant to be shared on a case-by-case basis. Please contact the CoLab coordinator on <a href = "https://www.bcchr.ca/pediatric-sepsis-data-colab">this page</a> under "collaborate with the pediatric sepsis colab." <strong>Objective(s):</strong> Smart Discharges is a digital health program that uses individual-level risk prediction and intervention to increase effective health seeking behavior, improve health outcomes, and reduce mortality during the post-discharge period. Health workers aim to mitigate risk by educating caregivers on post-discharge care and by scheduling follow-up visits for at-risk children in their communities. <br /><strong>Data Description:</strong> This dataset includes an introductory video and caregiver discharge counselling videos on: 1) Hygiene; 2) Nutrition; 3) Breastfeeding; 4) Care Seeking; 5) Mosquito Net Use; 6) Medications; 7) Immunizations. Videos are available in English and local Ugandan languages of Acholi, Luganda, Lusoga, and Runyankole. This dataset contains the <strong> Acholi</strong> version. <br /><strong>Limitations:</strong> Videos were designed for the Ugandan context and may not be generalizable to other settings. <br /><strong>Abbreviations:</strong> Village Health Teams (VHT) (i.e. local term for Community Health Worker (CHW)) <br /><strong>Ethics Declaration:</strong> NA <br /><strong>Funding Source(s):</strong> BC Children's Hospital Foundation; Grand Challenges Canada; Mining4Life; Thrasher Research Fund;
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2021-08-19 Data from G-cubed paper "Thallium isotopic compositions in Hawaiian lavas: evidence for recycled materials on the Kea side of the Hawaiian mantle plume". These are supporting information data tables that contain all data generated from this study as well as literature data compiled and used in the publication. Table S1 contains the data collected during this study and includes sample information as well as reference materials and standards. Table S2 contains literature data used and includes radiogenic isotopes and major elements. Table S3 contains a compilation of literature O, Ce, He, and W isotopic data for shield-stage Hawaiian samples.
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2020-02-14 Flow activities (e.g. sports and gaming) have been associated with positive affect and prolonged engagement. In the gambling field, modern electronic gaming machines (EGMs, including modern slot machines) have drawn concern as a potentially flow inducing activity that may be associated with gambling-related harms. Current research has heavily relied on self-reported flow, and further insights may be afforded by physiological methods. We present data from three separate experiments in which self reported gambling flow and cardiac pre-ejection period (PEP; a measure of sympathetic nervous system arousal) were examined. Male undergraduate participants gambled on a genuine EGM in a laboratory setting for a period of at least 15 min, and completed the Flow subscale of the game experience questionnaire (GEQ). Aggregated data were analyzed using multilevel regression. Although EGM gambling was not associated with significant changes in PEP across participants, we found that self-reported flow states were associated with significant decreases in PEP during the first five minutes of EGM use. Thus, participants who experienced flow showed a greater sympathetic nervous system response to the onset of gambling. Though these effects were consistent in experiments 1 and 2, in experiment 3 the effect was inverted during the same time window. We conclude that flow during EGM gambling appears to be associated with early changes in sympathetic nervous system activity, but stress that more research is needed to characterize boundary conditions and moderating factors.
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2021-10-01 The data included here are useful in the application of the Ellipse Approximation method, which allows for the estimation of sweeping and advection velocities. This dataset is a collection of case studies selected from two weeks of data collected during a field campaign investigating turbulent exchange within and above a sloped vineyard in the Okanagan Valley, British Columbia. These case studies were selected because the predominate wind direction at all five measurement heights was aligned in the upslope direction (parallel to the vineyard rows; towards the east), and all of the deployed instruments were working properly.
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2019-12-04 Full analytical data in support of the manuscript "Progressive development of E-W extension across the Tibetan plateau: A case study of the Thakkhola graben, west-central Nepal", submitted to International Geology Review The Thakkhola graben is a large-scale N-S striking, E-W extensional structure located in west-central Nepal that previous work has shown was actively developing ~ 17 Myr ago. New multi-system geochronological data from the immediate footwall of the Dangardzong fault, the main graben-forming structure in the Thakkhola, outline decelerating cooling paths. The average cooling rate in the footwall of the Dangardzong fault changes from 55 ± 5 ˚C/Ma in the early Miocene (~ 22-13) defined by monazite U-Th/Pb pluton crystallization ages, mica <sup>40</sup>Ar/<sup>39</sup>Ar cooling ages and zircon U-Th/He ages, to 18 ± 7 ˚C/Ma in the middle to late Miocene (~13-8 Ma) between zircon and apatite U-Th/He ages, and finally to 6 ± 3 ˚C/Ma from the late Miocene to present day (cooling post apatite U-Th/He closure). The changing cooling rate is interpreted to reflect the widespread development of graben in the Tibetan plateau beginning in the middle Miocene and the progressive partitioning of strain away from the Thakkhola.
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2016 <p>This dataset includes three tables which were custom ordered from Statistics Canada. There is a table each for Vancouver CMA, Montreal CMA, and Toronto CMA, and the tables contain variables regarding dwelling characteristics, tenure, and shelter cost. </p> <p>The dataset is in Beyond 20/20 (.ivt) format. The Beyond 20/20 browser is required in order to open it. This software can be freely downloaded from the Statistics Canada website: https://www.statcan.gc.ca/eng/public/beyond20-20 (Windows only). <br /> For information on how to use Beyond 20/20, please see:<br /> http://odesi2.scholarsportal.info/documentation/Beyond2020/beyond20-quickstart.pdf <br /> https://wiki.ubc.ca/Library:Beyond_20/20_Guide </p> <p><b>Custom order from Statistics Canada includes the following dimensions and variables:</b></p> <p>Geography: Montreal CMA, Vancouver CMA, Toronto CMA to the census tract level</p> <p>Total Shelter Cost: Under $500 to over $3000 in $500 intervals</p> <p>Shelter Cost to-Income Ratio: Spending less than 15%, 15-30%, 30-50%, 50% or more</p> <p>Tenure: Owner (including presence of mortgage), renter, subsidized housing, not subsidized housing</p> <p>Condominium Status: Condominium, not a condominium</p> <p>Household Size: 1 person, 2 persons, 3 or more people </p> <p>Number of Bedrooms: No bedroom or 1 bedroom, 2 or more bedrooms</p> <p>Structural Type: <br /> -Single detached house<br /> -Apartment with 5 or more stories<br /> -Semi-detached house, row house or other single detached house<br /> -Apartment or flat in a duplex<br /> -Apartment, building with fewer than 5 stories</p> <p>Household Income: Median income and average income only</p> <p>Original file names:<br /> EO3091_Table1_Montreal.ivt<br /> EO3091_Table1_Toronto.ivt<br /> EO3091_Table1_Vancouver.ivt</p>
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2021-06-24 <br /><strong>NOTE for restricted files:</strong> If you are not yet a CoLab member, please complete our <a href = "https://rc.bcchr.ca/redcap/surveys/?s=EDCYL7AC79">membership application survey</a> to gain access to restricted files within 2 business days. <br />Some files may remain restricted to CoLab members. These files are deemed more sensitive by the file owner and are meant to be shared on a case-by-case basis. Please contact the CoLab coordinator on <a href = "https://www.bcchr.ca/pediatric-sepsis-data-colab">this page</a> under "collaborate with the pediatric sepsis colab." The purpose of this environmental scan is to support health facilities in identifying and assessing quality improvement (QI) priorities and initiatives to treat children with sepsis. This dataset contains training materials for project setup and data collection.
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2013 BC Transit routes for Victoria, Whistler, Pemberton Local and Commuter, Squamish Commuter, Kelowna and Kamloops. The routes were created from the Google transit feed (GTFS) and ArcGIS Network Analyst. As no route shape information was available from the feed, the shape of the route was extrapolated from the road network and layout of transit stops. The transit routes were not verified as no maps are available. Although routes were calculated as carefully as possible, this data set carries no guarantee of accuracy beyond the information included in the Google transit feed. http://hdl.handle.net/11272/ICSCO <p><p> Info:Misc:<br> GTFS feed coordinate system: WGS 84<br> Projection: NAD_1983_BC_Environment_Albers<br> Route and arrival data used in this product or service is provided by permission of BC Transit. BC Transit assumes no responsibility for the accuracy or currency of the Data used in this product or service. <p> Info:Migration:<br> UBC Library Data Services repository software migration from DSPACE to DATAVERSE. Dataset 10573/42762 was migrated on 2013/10/03.<br> The former URI for this resource (<a href="http://hdl.handle.net/10573/42762">http://hdl.handle.net/10573/42762</a>) is deprecated. <p> Resource access is PUBLIC.<p> <h2 id="toc_0">Terms of Use for BC Transit data</h2> <p>These Terms of Use set out the terms and conditions (the “Terms&quot;) that govern your use of BC Transit&#39;s General Transit Feed Specification (GTFS) Data (the &quot;Data&quot;).</p> <p><strong>In consideration of BC Transit providing you with a copy of the Data, you agree to comply with all obligations and conditions contained in these Terms. These Terms are designed to protect BC Transit and promote the publication of its Data.</strong></p> <ol> <li><p>BC Transit retains all rights, title, and interest in the Data, and any intellectual property rights embodied in the Data, including any copyright, and any and all improvements or modifications to the Data that BC Transit may provide and that you acquire no such proprietary rights from the use or distribution of the Data, and that you will not attempt to restrict, limit or prevent BC Transit&#39;s use of the Data or BC Transit&#39;s trade-marks or official marks in association with the Data.</p></li> <li><p>BC Transit grants you a limited, revocable and non-exclusive license to use, reproduce, and redistribute the Data in accordance with these Terms.</p></li> <li><p>You must, unless otherwise agreed to by BC Transit in writing, indicate that BC Transit is the source of the Data you are using. You are not authorized and are prohibited from, making use of BC Transit&#39;s domain name or any trade-marks or official marks, which are owned by BC Transit or any confusingly similar variation of the domain name or those marks. At BC Transit&#39;s request, you will be required to withdraw such indication when its use is deemed illegitimate or contrary to the public&#39;s interest.</p></li> <li><p>The Data is provided to you on &quot;as is&quot; and &quot;as available&quot; basis, without any express or implied warranty of any kind, including without limitation, the implied warranties of merchantability, fitness for a particular purpose, accuracy and non-infringement. Under no circumstances will BC Transit be liable for any direct or indirect damages, even if BC Transit is aware of the possibility of such damages, including without limitation damages, loss of profits or for any other special, economic loss, consequential, exemplary or incidental damages, however caused, whether based upon contract, including negligence, strict liability in tort, warranty or contractual claims, or any other legal theory, arising out of or related to your use of the Data. You agree with BC Transit that this limitation should apply even if the Data, is faulty or inaccurate or otherwise fails. You agree that the use of the Data is at your own risk, and you assume the risk that the Data may provide incorrect information to you or your users, as well as the risk that the Data may cause loss of data or damage to your computer system.</p></li> <li><p>You agree to indemnify, defend and hold harmless BC Transit and its officers, directors, employees, and agents from and against all demands, claims, causes of action, suits, actions or proceedings, or liabilities of any kind or of any nature arising out of or in connection with your use or distribution of the Data to any end user.</p></li> <li><p>These Terms sets forth the entire agreement between you and BC Transit and supersedes all previous discussions, representations and agreements between you and BC Transit, whether written or oral, and may be amended only with the written consent of BC Transit.</p></li> <li><p>BC Transit reserves the right to modify these Terms at any time, without notice.</p></li> </ol>
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2020-04-23 Dataset of physical limnological observations from Quesnel Lake, British Columbia, Canada produced during research conducted into the impact of the 4 August 2014 Mount Polley mine tailings dam spill. Included are conductivity-temperature-depth (CTD) profiles from 2006-2017, and mooring timeseries from 2014-2017.
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2022-02-10 Climatic suitability of 10 tree species in 1237 restoration sites in Northwest Ecuador under baseline climatic conditions (1960-1990) and two climate scenarios (RCP 4.5 and 8.5) in the 2030s, 2050s, and 2070s. We built bioclimatic niche models to obtain the climatic suitability values for the species at each restoration site. The suitability values ranged from 0 (unsuitable) to 1 (suitable). Suitability thresholds (i.e., MaxSS, MTP, 10% TP) per species are provided to categorize species as "suitable" or "unsuitable" at the restoration sites. We used this dataset on species climatic suitability in restoration sites to assess the species climatic viability (i.e., persistance over time). Obtain further detail on this dataset's content in the file "AA_README.txt" in English, or "AA_README_Español.txt" in Spanish. Geographical data on the restoration sites location is not publicly available due to privacy restrictions from the government of Ecuador under the permit (MAE-SG-2018-6447-E). We submited the manuscript related to this dataset to a scientific journal. We hope to add the publication link to this metadata as soon as it is published and available online.
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2020-01-28 MESSENGER orbit activity indices Column 1 contains the MESSENGER orbit number, column 2 contains the activity index (the heliocentric-distance-normalized, ranked index, R_D, see Anderson et al. (2013) for details).
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2022-02-14 In this study we conducted an online survey of Canadian and European laboratory animal professionals and researchers (n 592) to assess their attitudes towards the use of CO2 and alternative methods for rodent euthanasia using quantitative 7-point scale (from 1 (  strongly oppose) to 7 (  strongly favour) and qualitative (open-ended text) responses. CO2 was identified as the most common method used to kill rodents, and attitudes towards this method were variable and on average ambivalent (mean SD score on our 7-point scale was 4.4 1.46). Qualitative analysis revealed four themes relating to participant attitude: (a) the animal’s experience during gas exposure; (b) practical considerations for humans; (c) compromise between the animal’s experience and practical considerations; and (d) technical description of the procedure or policies. Many participants (51%) felt that there were alternatives available that could be considered an improvement over CO2, but perceived barriers to implementing these refinements. Qualitative analysis of these responses revealed five themes: (a) financial constraints; (b) institutional culture; (c) regulatory constraints; (d) research constraints; and (e) safety concerns. In conclusion, concerns regarding the use of CO2 often focused on the animal’s experience, but barriers to alternatives related to operational limitations. New research is now required on to how best to overcome these barriers.
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2003 http://hdl.handle.net/11272/10564 <p>MOTIVATION:<br> We examine the effect of replication on the detection of apparently differentially expressed genes in gene expression microarray experiments. Our analysis is based on a random sampling approach using real data sets from 16 published studies. We consider both the ability to find genes that meet particular statistical criteria as well as the stability of the results in the face of changing levels of replication.<p> <p>RESULTS:<br> While dependent on the data source, our findings suggest that stable results are typically not obtained until at least five biological replicates have been used. Conversely, for most studies, 10-15 replicates yield results that are quite stable, and there is less improvement in stability as the number of replicates is further increased. Our methods will be of use in evaluating existing data sets and in helping to design new studies.<p>

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