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62 results for “New Hampshire”
FIGURE 5a–h in Aleocharine rove beetles of New Hampshire, USA: new taxa and new records (Coleoptera, Staphylinidae, Aleocharinae)
FIGURE 5a–h. Atheta struyvei Klimaszewski and Chandler sp. n.: (a) habitus in dorsal view; (b) median lobe of aedeagus in lateral view; (c) median lobe of aedeagus in dorsal view; (d) male tergite VIII; (e) male sternite VIII; (f) female tergite VIII; (g) female sternite VIII; (h) spermatheca. Scale bar for habitus = 1mm; remaining scale bars = 0.2mm.
FIGURE 3a–d in Aleocharine rove beetles of New Hampshire, USA: new taxa and new records (Coleoptera, Staphylinidae, Aleocharinae)
FIGURE 3a–d. Atheta (Dimetrota) ellisi Klimaszewski and Chandler, sp. n.: (a) habitus in dorsal view; (b) median lobe of aedeagus in lateral view; (c) male tergite VIII; (d) male sternite VIII. Scale bar for habitus = 1mm; remaining scale bars = 0.2mm.
FIGURE 9a–g in Aleocharine rove beetles of New Hampshire, USA: new taxa and new records (Coleoptera, Staphylinidae, Aleocharinae)
FIGURE 9a–g. Agaricomorpha hampshirensis Klimaszewski and Chandler sp. n.: (a) habitus in dorsal view; (b) median lobe of aedeagus in lateral view; (c) male tergite VIII; (d) male sternite VIII; (e) female tergite VIII; (f) female sternite VIII; (g) spermatheca. Scale bar for habitus = 1mm; remaining scale bars = 0.2mm.
FIGURE 2a–g in Aleocharine rove beetles of New Hampshire, USA: new taxa and new records (Coleoptera, Staphylinidae, Aleocharinae)
FIGURE 2a–g. Images of Aleochara (Echochara) daviesi Klimaszewski and Brunke: (a) habitus in dorsal view; (b) median lobe of aedeagus in lateral view; (c) male tergite VIII; (d) male sternite VIII; (e) female tergite VIII; (f) female sternite VIII; (g) spermatheca. Scale bar for habitus = 1mm; remaining scale bars = 0.2mm.
FIGURE 1 in Aleocharine rove beetles of New Hampshire, USA: new taxa and new records (Coleoptera, Staphylinidae, Aleocharinae)
FIGURE 1. New Hampshire Ecological Regions with Sections and Subsections indicated (ex. Sperduto & Nichols (2004)), with locations of NH sites intensively collected.
Distribution. NE USA,in coastal S Maine, coastal and Merrimack River valley region of S New Hampshire, SE New York, W Massachusetts (including parts of Cape Cod), W & E (E of the Connecticut River) Connecticut, and Rhode Island. in Leporidae
Distribution. NE USA,in coastal S Maine, coastal and Merrimack River valley region of S New Hampshire, SE New York, W Massachusetts (including parts of Cape Cod), W & E (E of the Connecticut River) Connecticut, and Rhode Island.
Distribution. SE Canada (S Ontario and S Quebec) and NE USA (W Maine, New Hampshire, Vermont, New York, Massachusetts, N Connecticut, N Rhode Island, Ohio, Pennsylvania, N New Jersey, West Virginia, NW Maryland, W Virginia, E Kentucky, E Tennessee, W North Carolina, extreme NE Georgia, and extreme NW South Carolina). in Talpidae
Distribution. SE Canada (S Ontario and S Quebec) and NE USA (W Maine, New Hampshire, Vermont, New York, Massachusetts, N Connecticut, N Rhode Island, Ohio, Pennsylvania, N New Jersey, West Virginia, NW Maryland, W Virginia, E Kentucky, E Tennessee, W North Carolina, extreme NE Georgia, and extreme NW South Carolina).
Subspecies and Distribution. S.f.fumeusG.S.Miller,1895—SECanada(SOntarioandSQuebec)andEUSA(NEMinnesota,NewEngland,exceptmostofMaine,NVermont,andNNewHamnsire,SIndiana,Ohio,Pennsylvania,WestVirginia,Maryland,WNewJersey,Kentucky,N&WVirginia,ETennessee,WNorthCarolina,NEGeorgia,andNWSouthCarolina). S. f. umbrosus H. H. T. Jackson, 1917 — SE Canada (SE Quebec, New Brunswick, and Nova Scotia) and NE USA (NE New York, N Vermont, N New Hampshire, and most of Maine). in Soricidae
Subspecies and Distribution. S.f.fumeusG.S.Miller,1895—SECanada(SOntarioandSQuebec)andEUSA(NEMinnesota,NewEngland,exceptmostofMaine,NVermont,andNNewHamnsire,SIndiana,Ohio,Pennsylvania,WestVirginia,Maryland,WNewJersey,Kentucky,N&WVirginia,ETennessee,WNorthCarolina,NEGeorgia,andNWSouthCarolina). S. f. umbrosus H. H. T. Jackson, 1917 — SE Canada (SE Quebec, New Brunswick, and Nova Scotia) and NE USA (NE New York, N Vermont, N New Hampshire, and most of Maine).
New Hampshire Medicaid Wellness Incentive Program
ClinicalTrials.gov study NCT02515981. IPD Sharing: Not stated. Countries: 1. Publications: 3.
New Hampshire, Mirror Lake LTER water chemistry, 1967-2010
The New York State Lake Classification and Inventory (LCI) monitoring program, which is a component of the Statewide Waters Monitoring Program of the New York State Department of Environmental Conservation Division of Water (NYSDEC). Data was originally provided in an excel sheet LCI Master 1982-2010 updated and this is available in dropbox. The LAGOS-appropriate (shortened, some processing) file is LCI Master 1982-2010_shortened.xls. The LCI database is a complement to the CSLAP database. LCI began in the early 1980s an ambient lake monitoring program to evaluate baseline water quality conditions in lakes throughout the state, utilizing a rotating monitoring cycle loosely patterned after the stream monitoring programs conducted by the Department. However, due to staff shortages, this ambient lake monitoring program (the LCI) was suspended in 1990. This left the NY Citizens Statewide Lake Assessment Program (CSLAP), a volunteer lake monitoring program overseen by NYSDEC, as the only statewide ambient lake monitoring program conducted by the NYSDEC. However, the LCI program was re-initiated in the mid-1990s, using a rotating-basin approach to sampling. Note that some of the lakes appear in both data sets. The primary goals of the LCI Monitoring Program component of the New York Statewide Waters Monitoring Program include: 1) water quality screening of as many waters as possible to document “good” waters that support designated uses, and identify waters with possible/potential impairment to uses; 2) Intensive sampling of selected waters to evaluate impairments, causes and sources and to characterize general water quality conditions
New Hampshire Volunteer Lake Assessment Program 1985-2010
The New Hampshire Volunteer Lake Assessment Program was initiated in 1985 in response to an expressed desire of lake associations to be involved in lake protection and watershed management. VLAP is a cooperative program between volunteer monitors and the DES which leads to local awareness of land use and human practices that may be detrimental to lake quality and also empowers communities in their decision-making regarding lake management issues. The purpose of VLAP is to assess the chemical and biological characteristics of the lakes and ponds throughout the state to determine overall health of the system. Environmental results are measured by making comparisons to established means and ranges of water quality for the state of New Hampshire. See NH_STATION_REPORT for geographic and lake information
Bedrock geologic map of Hubbard Brook Experimental Forest and maps of fractures and geology in roadcuts along Interstate-93, Grafton County, New Hampshire.
Bedrock Geologic Map of Hubbard Brook Experimental Forest and maps of fractures and geology in roadcuts along Interstate-93, Grafton County, New Hampshire. Two maps are included in this data set. Interstate I-93 map includes plots summarizing data for fractures shown on map roadcuts. Citation: Barton, C. C., R. H. Camerlo and S. W. Bailey. 1997. Bedrock Geologic Map of Hubbard Brook Experimental Forest and maps of fractures and geology in roadcuts along Interstate-93, Grafton County, New Hampshire. Sheet 1, Scale 1:12,000; Sheet 2, Scale 1:200. U.S. Geological Survey, Miscellaneous Investigations Series, Map I-2562 These data were gathered as part of the Hubbard Brook Ecosystem Study (HBES). The HBES is a collaborative effort at the Hubbard Brook Experimental Forest, which is operated and maintained by the USDA Forest Service, Northern Research Station.
Figure 2 in Assessing high compositional differences of beetle assemblages across vertical woodland strata in the New Forest, Hampshire, England
Figure 2. Species accumulation curves created by rarefaction for each sampling method. Vertical bars = 95% confidence limits around the species richness estimate.
New Hampshire Synthetic Ecosystem
New Hampshire synthetic population dataset consisting of tables for persons, households, schools, and workplaces. This dataset was created by the SPEW program from 2010 ACS SF 5-Year counts; 2010 US TIGER Roads; ACS PUMS 1-Year micro data; 2013 and 2011 NCES schools; and 2009 ESRI workplaces.
TABLE 1 in Aleocharine rove beetles of New Hampshire, USA: new taxa and new records (Coleoptera, Staphylinidae, Aleocharinae)
<p><b>TABLE 1 (Appendix).</b> List of aleocharine species recorded recorded from New Hampshire and a few adjacent states, with their distribution records in Canada and the United States indicated. * Holarctic species, †adventive species, <b>‡</b> species of uncertain distribution status <b>—</b> adventive in North America or Holarctic, A/S <b>—</b> Arctic/Subarctic elements, A/ Sw—widely distributed species occurring in Arctic/Subarctic; species in bold are new to science; NCR—new country rcord, and NSR—new state records and NPR—new provincial records are in bold. Tribes, genera and species are listed in alphabetical order.</p><table><tbody><tr><th>Taxonomic name</th><th>Canadian distribution</th><th>United States distribution</th></tr></tbody><tbody><tr><th>TRIBE ALEOCHARINI FLEMING</th><td></td></tr><tr><th><i>Aleochara bimaculata</i> Gravenhorst (A/Sw)</th><td>AB, BC, LB, MB, NB,</td><td>AL, AZ, CA, CO, DC, FL, GA, IA, ID, IL,</td></tr><tr><th></th><td>NF, NS, NT, ON, QC,</td><td>IN, KS, KY, LA, MA, MD, ME, MI, MN,</td></tr><tr><th></th><td>SK</td><td>MO, MT, NC, ND, NE, NH, NJ, NM, NV,</td></tr><tr><th></th><td></td><td>NY, OK, OR, PA, RI, SC, SD, TN, TX, UT,</td></tr><tr><th></th><td></td><td>VA, VT, WA, WI, WV, WY</td></tr><tr><th><i>Aleochara castaneimarmotae</i> Klimaszewski, Webster and Brunke</th><td>NB, ON</td><td>AR, IL, KY, <b>MA</b> (NSR), MO <b>NH</b> (NSR),</td></tr><tr><td></td><td>TN, VA</td></tr><tr><th><i>Aleochara castaneipennis</i> Mannerheim (A/Sw)</th><td>AB, BC, LB, NB, NF,</td><td>AK, AR, AZ, CO, ME, NH, WA, WY</td></tr><tr><th>NS, NT, ON, QC, YT</th></tr><tr><th><i>Aleochara caviceps</i> (Casey)</th><td>NB, ON, QC</td><td>AZ, IA, ID, IN, MT, <b>NH</b> (NSR), NJ, NV,</td></tr><tr><th></th><td></td><td>NY, PA</td></tr><tr><th><i>Aleochara curtula</i> (Goeze) †</th><td>BC, NB, NF, NS, ON,</td><td><b>CT</b> (NSR), IL, GA, MA, ME, NH, NJ, NY,</td></tr><tr><th></th><td>PE, QC</td><td>OH, PA, RI, VT</td></tr><tr><th><i>Aleochara daviesi</i> Klimaszewski and Brunke</th><td>ON</td><td><b>NH</b> (NCR, NSR)</td></tr><tr><th><i>Aleochara fumata</i> Gravenhorst † (A/Sw)</th><td>AB, BC, MB, NB, NF,</td><td>AL, AR, AZ, CA, GA, MA, MD, ME, MN,</td></tr><tr><th></th><td>NS, ON, PE, QC, YT</td><td>MO, NC, NH, NJ, NM, NY, OK, OR, PA,</td></tr><tr><th></th><td></td><td>TN, VT, WA, WI, WV, WY</td></tr><tr><th><i>Aleochara gracilicornis</i> Bernhauer (A/Sw)</th><td>BC, MB, NB, NF, NS,</td><td>AR, AZ, CO, FL, IL, IN, KS, LA, MA, MD,</td></tr><tr><th></th><td>NT, ON, QC, SK</td><td>ME, MI, MN, MO, MT, NH, NJ, NM, NY,</td></tr><tr><th></th><td></td><td>OH, PA, RI, SD, UT, VA, WI</td></tr><tr><th><i>Aleochara lacertina</i> Sharp</th><td>AB, BC, MB, NB, NF,</td><td>AZ, CA, CO, FL, MA, ME, MN, MT, ND,</td></tr><tr><th></th><td>NS, ON, QC, SK</td><td>NH, NM, NV, NY, OK, OR, PA, RI, TN, TX,</td></tr><tr><th></th><td></td><td>UT, WA, WI</td></tr><tr><th><i>Aleochara lanuginosa</i> Gravenhorst †</th><td>AB, BC, NB, NF, NS,</td><td>CA, CO, ID, MA, MN, NC, NH, NJ, NY,</td></tr><tr><th></th><td>ON, QC</td><td>OR, PA, RI, WA, WI</td></tr><tr><th><i>Aleochara lata</i> Gravenhorst †</th><td>ON, QC</td><td>AL, AR, AZ, CA, CO, CT, DC, FL, GA,</td></tr><tr><th></th><td></td><td>IA, IL, IN, KS, KY, LA, MA, ME, MD, MI,</td></tr><tr><th></th><td></td><td>MN, MO, NC, NE, NH, NJ, NY, OH, OK,</td></tr><tr><th></th><td></td><td>PA, RI, SC, TN, TX, VA, VT, WV, WI</td></tr></tbody></table>
Land Cover and Land Use Classification for the State of New Hampshire, 1996-2001
The New Hampshire Geographically Referenced Analysis and Information Transfer System (GRANIT) land cover data set provides a land cover and land use product at 30-m resolution with 23 individual classes across the state. The classification is based largely on the analysis of 12 Landsat Thematic Mapper (TM and ETM+) images. Over 1,400 new classification training site data points were collected to supplement 1,200 archived sites from previous projects. The classification represents a snapshot in time from 1996 to 2001. This time range spans the dates of the most recent acquisitions of a TM scene for each region of the state and the dates of the most recent field data collection.
Data from: Tradeoffs between three forest ecosystem services across the state of New Hampshire, USA: timber, carbon, and albedo
Forests are more frequently being managed to store and sequester carbon for the purposes of climate change mitigation. Generally, this practice involves long-term conservation of intact mature forests and/or reductions in the frequency and intensity of timber harvests. However, incorporating the influence of forest surface albedo often suggests that long rotation lengths may not always be optimal in mitigating climate change in forests characterized by frequent snowfall. To address this, we investigated tradeoffs between three ecosystem services: carbon storage, albedo-related radiative forcing, and timber provisioning. We calculated optimal rotation length at 498 diverse Forest Inventory and Analysis forest sites in the state of New Hampshire, USA. We found that the average optimal rotation lengths across all sites is 94 years (s = 44), with a large cluster of short optimal rotation lengths that were calculated at high elevations in the White Mountain National Forest. Using a regression tree approach, we found that timber growth, annual storage of carbon, and the difference between annual albedo in mature forest versus a post-harvest landscape were the most important variables that influenced optimal rotation. Additionally we found that the choice of a baseline albedo value for each site significantly altered the optimal rotation lengths across all sites, lowering the mean rotation to 59 years with a high albedo baseline, and increasing the mean rotation to 112 years given a low albedo baseline. Given these results, we suggest that utilizing temperate forests in New Hampshire for climate mitigation purposes through carbon storage and the cessation of harvest is appropriate at a site-dependent level that varies significantly across the state.
c. 1800 Ship-builder's New Hampshire Axe
Modeled from Eric Sloane's [*Museum of Early American Tools*](https://www.amazon.com/Museum-Early-American-Tools-Americana/dp/0486425606/ref=sr_1_1?crid=1MDB8783EQVPS&dchild=1&keywords=museum+of+early+american+tools&qid=1613590281&s=books&sprefix=museum+of+early%2Cstripbooks%2C170&sr=1-1). Textured with [CC0 Textures](https://cc0textures.com) assets. Made with [Blender](https://blender.org). Source: Objaverse 1.0 / Sketchfab
Table-Top Water Pitcher to Reduce Arsenic Exposure Among Well Users in New Hampshire
ClinicalTrials.gov study NCT07103356. IPD Sharing: Not stated. Countries: 0. Publications: 0.
The Impact of SNAP-Ed Among Bhutanese Adults Residing in New Hampshire
ClinicalTrials.gov study NCT06445452. IPD Sharing: NO. Countries: 1. Publications: 0.
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Allen Brain Atlas
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