Butterflies of Montgomeryshire (VC47)
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Vascular Plants at Fort Ross State Historic Park
19005 Coast Highway One, Jenner, CA 95450 ■ 707.847.3437 ■ [email protected] ■ www.fortross.org Title: Vascular Plants at Fort Ross State Historic Park Author(s): Dorothy Scherer Published by: California Native Plant Society i Source: Fort Ross Conservancy Library URL: www.fortross.org Fort Ross Conservancy (FRC) asks that you acknowledge FRC as the source of the content; if you use material from FRC online, we request that you link directly to the URL provided. If you use the content offline, we ask that you credit the source as follows: “Courtesy of Fort Ross Conservancy, www.fortross.org.” Fort Ross Conservancy, a 501(c)(3) and California State Park cooperating association, connects people to the history and beauty of Fort Ross and Salt Point State Parks. © Fort Ross Conservancy, 19005 Coast Highway One, Jenner, CA 95450, 707-847-3437 .~ ) VASCULAR PLANTS of FORT ROSS STATE HISTORIC PARK SONOMA COUNTY A PLANT COMMUNITIES PROJECT DOROTHY KING YOUNG CHAPTER CALIFORNIA NATIVE PLANT SOCIETY DOROTHY SCHERER, CHAIRPERSON DECEMBER 30, 1999 ) Vascular Plants of Fort Ross State Historic Park August 18, 2000 Family Botanical Name Common Name Plant Habitat Listed/ Community Comments Ferns & Fern Allies: Azollaceae/Mosquito Fern Azo/la filiculoides Mosquito Fern wp Blechnaceae/Deer Fern Blechnum spicant Deer Fern RV mp,sp Woodwardia fimbriata Giant Chain Fern RV wp Oennstaedtiaceae/Bracken Fern Pleridium aquilinum var. pubescens Bracken, Brake CG,CC,CF mh T Oryopteridaceae/Wood Fern Athyrium filix-femina var. cyclosorum Western lady Fern RV sp,wp Dryopteris arguta Coastal Wood Fern OS op,st Dryopteris expansa Spreading Wood Fern RV sp,wp Polystichum munitum Western Sword Fern CF mh,mp Equisetaceae/Horsetail Equisetum arvense Common Horsetail RV ds,mp Equisetum hyemale ssp.affine Common Scouring Rush RV mp,sg Equisetum laevigatum Smooth Scouring Rush mp,sg Equisetum telmateia ssp. -
Invasive Plant List
NON-NATIVE INVASIVE PLANTS OF ARLINGTON COUNTY, VIRGINIA While up to 40% of the plants found in a typical urban environment are non-native species, a relatively small number of these “alien” plants are known to represent an ecological threat to the natural environment (parks, woodlands, and backyards). Known as “invasive species”, these non-natives will spread from urban plantings into natural areas, eliminate native species, alter natural plant communities, and degrade the environment. The following plants have been documented as invasive species in Arlington. Known invasive plant species should not be planted as part of any Arlington County sponsored project. This list will be periodically reviewed by the Invasive Plant Coordinator (DPR) and updated by Version (date). Invasive Plant Species List Acer spp.: campestre, tataricum var. ginnala Hedge, Amur maple Threat Acer spp.: palmatum, plantanoides, pseudoplatanus Japanese, Norway, Sycamore maple Invasive Actinidia arguta Hardy kiwi Threat Aegopodium podagraria Goutweed Invasive Agrostis capillaris Colonial bent-grass Invasive Ailanthus altissima Tree of Heaven Invasive Akebia quinata Five-leaved akebia Invasive Albizia julibrissin Mimosa Invasive Aldrovanda vesiculosa* Waterwheel Threat Alliaria petiolata Garlic mustard Invasive Alternanthera philoxeroides Alligator weed Invasive Ampelopsis brevipedunculata Porcelainberry Invasive Aralia elata Japanese angelica tree Invasive Artemisia vulgaris Mugwort Invasive Arthraxon hispidus var. hispidus Hairy jointgrass Invasive Arum italicum -
Dark Green Fritillary Regional Priority Species Factsheet
t e e h s t c a f Da rk Green Frit illary Argynnis aglaja Conservation status Regional priority in several England regions. 2000-4 • 1 sighting • 2-9 max seen • 10+ max seen (827 squares) 1995-9 This large and powerful butterfly is one of our most widespread °+ 1970-82 fritillaries and can be seen flying rapidly in a range of open sunny habitats. The males look similar to the High Brown Fritillary, which is far rarer but sometimes flies with them on Bracken-covered hillsides. The two can be distinguished from the underwing markings, visible when they are feeding on flowers such as thistles. The Dark Green has an olive-green coloration and lacks the row of red-ringed spots of the High Brown. The Dark Green also has rounded, less pointed forewings than the High Brown which has straight or concave outer edges to the forewings. Although the Dark Green Fritillary is still locally abundant in some regions, it has declined in many others, notably central and eastern England. Colony structure Life cycle The adults are highly mobile and the butterflies The Dark Green Fritillary is single-brooded, with adults flying from early June until mid-August. tend to occur at low densities over large areas In warmer and more southerly locations the peak is usually from mid-June to mid-July, but within which there are small pockets of suitable it can be several weeks later at cooler, more northerly sites. The eggs are laid singly either on breeding habitat. On the best sites, with greater the foodplant or more usually on a nearby plant, dead leaves, or dead Bracken. -
Temperate Grass Allergy Season Defined by Spatio-Temporal Shifts in Airborne
bioRxiv preprint doi: https://doi.org/10.1101/410829; this version posted September 19, 2018. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. 1 Title: Temperate grass allergy season defined by spatio-temporal shifts in airborne 2 pollen communities 3 Authors: Georgina L. Brennan1*, Caitlin Potter2, Natasha de Vere2,3, Gareth W. Griffith2, 4 Carsten A. Skjøth4, Nicholas J. Osborne5,6, Benedict W. Wheeler5, Rachel N. McInnes7, 5 Yolanda Clewlow7, Adam Barber7, Helen M. Hanlon7, Matthew Hegarty2, Laura 1,3 4 5 8 6 Jones , Alexander Kurganskiy , Francis M. Rowney , Charlotte Armitage , Beverley Adams- 7 Groom4, Col R. Ford3, Geoff M. Petch4, The PollerGEN Consortium, and Simon Creer1*. 8 9 Consortium Angela Elliot9, Carl A. Frisk4, Roy Neilson10, Stephen Potter11, Abdullah M. Rafiq1, 10 David, B. Roy12, Katherine Selby13, Natascha Steinberg9 11 12 Affiliations: 13 1Molecular Ecology and Fisheries Genetics Laboratory, School of Natural Sciences, Bangor 14 University, Bangor, Gwynedd, Wales, UK 15 2Aberystwyth University, Aberystwyth, Ceredigion, Wales, UK 16 3National Botanic Garden of Wales, Llanarthne, Carmarthenshire, Wales, UK 17 4University of Worcester, Worcester, Worcestershire, UK 18 5University of Exeter, Truro, Cornwall, UK 19 6University of New South Wales, Sydney, New South Wales, Australia 20 7Met Office, Exeter, Devon, UK 21 8The Woodland Trust, Kempton Way, Grantham, Lincolnshire, UK. 22 9College of Life and Environmental Science, University of Exeter, Exeter, UK 1 bioRxiv preprint doi: https://doi.org/10.1101/410829; this version posted September 19, 2018. -
Pollen Morphology of Poaceae (Poales) in the Azores, Portugal
See discussions, stats, and author profiles for this publication at: http://www.researchgate.net/publication/283696832 Pollen morphology of Poaceae (Poales) in the Azores, Portugal ARTICLE in GRANA · OCTOBER 2015 Impact Factor: 1.06 · DOI: 10.1080/00173134.2015.1096301 READS 33 4 AUTHORS, INCLUDING: Vania Gonçalves-Esteves Maria A. Ventura Federal University of Rio de Janeiro University of the Azores 86 PUBLICATIONS 141 CITATIONS 43 PUBLICATIONS 44 CITATIONS SEE PROFILE SEE PROFILE All in-text references underlined in blue are linked to publications on ResearchGate, Available from: Maria A. Ventura letting you access and read them immediately. Retrieved on: 10 December 2015 Grana ISSN: 0017-3134 (Print) 1651-2049 (Online) Journal homepage: http://www.tandfonline.com/loi/sgra20 Pollen morphology of Poaceae (Poales) in the Azores, Portugal Leila Nunes Morgado, Vania Gonçalves-Esteves, Roberto Resendes & Maria Anunciação Mateus Ventura To cite this article: Leila Nunes Morgado, Vania Gonçalves-Esteves, Roberto Resendes & Maria Anunciação Mateus Ventura (2015) Pollen morphology of Poaceae (Poales) in the Azores, Portugal, Grana, 54:4, 282-293, DOI: 10.1080/00173134.2015.1096301 To link to this article: http://dx.doi.org/10.1080/00173134.2015.1096301 Published online: 04 Nov 2015. Submit your article to this journal Article views: 13 View related articles View Crossmark data Full Terms & Conditions of access and use can be found at http://www.tandfonline.com/action/journalInformation?journalCode=sgra20 Download by: [b-on: Biblioteca do conhecimento -
NVC/EUNIS Survey and Management Advice
Scottish Natural Heritage Commissioned Report No. 949 Aith Meadows and Burn of Aith Site of Special Scientific Interest: NVC/EUNIS survey and management advice COMMISSIONED REPORT Commissioned Report No. 949 Aith Meadows and Burn of Aith Site of Special Scientific Interest: NVC/EUNIS survey and management advice For further information on this report please contact: Kirsty North Scottish Natural Heritage Stewart Building Alexandra Wharf LERWICK ZE1 0LL Telephone: 01595 693345 E-mail: [email protected] This report should be quoted as: Crossley, J.E. 2017. Aith Meadows and Burn of Aith Site of Special Scientific Interest: NVC/EUNIS survey and management advice. Scottish Natural Heritage Commissioned Report No. 949. This report, or any part of it, should not be reproduced without the permission of Scottish Natural Heritage. This permission will not be withheld unreasonably. The views expressed by the author(s) of this report should not be taken as the views and policies of Scottish Natural Heritage. © Scottish Natural Heritage 2017. COMMISSIONED REPORT Summary Aith Meadows and Burn of Aith Site of Special Scientific Interest: NVC/EUNIS survey and management advice Commissioned Report No. 949 Project No: 013952 Contractor: J. E. Crossley Year of publication: 2017 Keywords Aith Meadows; SSSI; NVC; EUNIS; lowland neutral grassland; fen meadow. Background Aith Meadows and Burn of Aith SSSI is situated in Cunningsburgh, Shetland. It contains extensive wet meadows, traditionally managed for hay. The notified biological features are lowland neutral grassland and fen meadow. These are classified as in ‘favourable’ but ‘declining’ condition. The declining condition of the meadows is largely attributed to a decrease in active management. -
INVASIVE SPECIES Grass Family (Poaceae) Wild Oats Are Annuals
A PROJECT OF THE SONOMA-MARIN COASTAL PRAIRIE WORKING GROUP INVASIVE SPECIES I NVASIVE A NNUAL P LANTS WILD OATS (AVENA FATUA) AND SLENDER WILD OATS (AVENA BARBATA) - NON-NATIVE Grass Family (Poaceae) Wild oats are annuals. WILD OATS: Are native to Eurasia and North Africa. WILD OAT ECOLOGY Is often dominant or co-dominant in coastal prairie (Ford and Hayes 2007; Sawyer, et al. 2009), Occurs in moist lowland prairies, drier upland prairies and open woodlands (Darris and Gonzalves 2008), Species Interactions: The success of Avena lies in its superior competitive ability: o It has a dense root system. The total root length of a single Avena plant can be from 54.3 miles long (Pavlychenko 1937) to, most likely, twice that long (Dittmer 1937). Wild oats (Avena) in Marin coastal grassland. o It produces allelopathic compounds, Photo by D. (Immel) Jeffery, 2010. chemicals that inhibit the growth of other adjacent plant species. o It has long-lived seeds that can survive for as long as 10 years in the soil (Whitson 2002). Citation: Jeffery (Immel), D., C. Luke, K. Kraft. Last modified February 2020. California’s Coastal Prairie. A project of the Sonoma Marin Coastal Grasslands Working Group, California. Website: www.cnga.org/prairie. Coastal Prairie Described > Species: Invasives: Page 1 of 18 o Pavlychenko (1937) found that, although Avena is a superior competitor when established, it is relatively slow (as compared to cultivated cereal crops wheat, rye and barley) to develop seminal roots in the early growth stages. MORE FUN FACTS ABOUT WILD OATS Avena is Latin for “oat.” The cultivated oat (Avena sativa), also naturalized in California) is thought to be derived from wild oats (Avena fatua) by early humans (Baum and Smith [2011]). -
Pale Dog-Violet Viola Lactea Pale Dog-Violet Is a Member of the Violet Family (Violaceae)
Species fact sheet Pale Dog-violet Viola lactea Pale dog-violet is a member of the violet family (Violaceae). It has sparsely hairy creeping stems originating from a basal rosette of lanceolate leaves with rounded to wedge-shaped or truncate bases. Each stem supports one pale milky-violet to greyish- pink typical violet shaped flower. Distinguishing features between pale dog-violet and similar violets are: the flower colour; the short greenish spurs at the back of the flowers; and the triangular stipules at the base of each upper leaf being equal to or longer than the leaf stalks. This plant does hybridise, particularly with common dog-violet Viola riviniana. © TeunSpaans under Creative Commons BY-SA licence Lifecycle This perennial plant flowers in May and June each year. Buried seed is thought to have good longevity in the soil seed bank; sometimes germinating decades after it was shed from the parent plant. Habitat Pale dog-violet is a species of humid heathland and grass heath (including the culm grasslands), favouring areas with short vegetation and considerable bare ground created by burning, grazing or incidental disturbance such as rutting, turf or gorse cutting, trampling and so on. Distribution A species of humid heathland and grass heath in southern England, largely confined to key heathland districts including the Wealden and Thames Basin heaths, the New Forest and Dorset heaths, and through much of Devon and Cornwall (though seldom ever commonly). This heathland species had already experienced a severe decline prior to 1930, but this has continued and it has disappeared from much of its former range relatively recently, particularly in SE Pale dog-violet distribution across Britain England. -
Original PBF Doc
Pearl Bordered Fritillary (Boloria euphrosyne) History Relatively recent records (from the 1970’s up to 1988 ) seem to suggest that the PBF was most probably an uncommon butterfly on the Welcombe/Marsland Nature Reserve. Data from around this time indicates that there were ‘small numbers on the overgrown rides and glades running throughout the woodland’. Prior to any organized conservation management (and before the woodland became a nature reserve) most of these old ‘access areas’ were covered in scrub,bramble and gorse.The previous 100 years or so had witnessed a considerable amount of cutting and felling in many sections of the woods, mainly by previous owners. Undoubtedly, the PBF would have been a much commoner butterfly in those days perhaps present in very large numbers in the newly coppiced areas. The cessation of this type of management led to a slow decline in the PBF populations but some areas would still have retained small numbers as indicated above. One such area was known as ‘Hard Hills’ – a 15 acre west-facing slope (can be very hot in spring/summer) dominated by gorse and bracken (SS 235176).This area had historically been grazed by sheep/goats but this ‘management’ had ceased some 40 years (before 1981).Some periodical burning of the slopes after the grazing had resulted in a dense bracken layer and yet the herb layer underneath ‘was comparatively diverse’. The first management plan in 1976 suggested that the area ‘be cleared of scrub and the bracken be cut and /or chemically treated’ . Although some minor work had been carried out in the mid 70’s the first real work programme began in 1980.All the work was documented on a card index system: 1 ‘In March of 1980 the whole of the slope was burnt… and the experiments with spraying continued throughout the spring and summer. -
The Habitats and Vegetation (NVC) of Ardersier Port Proposed for Development
The Habitats and Vegetation (NVC) of Ardersier Port proposed for Development [Redacted] , Sept 2018 1 Introduction A National Vegetation Classification (NVC) survey was undertaken of Ardersier covering about 200 ha. The site is situated close to the village of Ardersier in Moray. In parallel to the NVC survey a Phase 1 Habitat survey was undertaken. The purpose of these surveys was to determine the conservation value of the site and to assess the ecological value of the wetland habitat of the site in terms of the Ground Water Dependent Terrestrial Ecosystems (GWDTE) that it contains. Detailed descriptions of each of the habitats and NVC communities is presented below. The NVC classification is based on Rodwell (1991a, 1991b, 1992, 1995 and 2000) and the Phase 1 Habitats on the JNCC (2010). It should be noted that the descriptions in the report are based mainly on the information contained in the Appendices of this report and of the digital map supplied. All the maps in this report have been produced using ArcMap 10.6 and the shape file is available. In view of the proposed development of the area, following the habitat and NVC descriptions, an ecological assessment of the site is presented. The field survey was undertaken over three full days by the author from 6th August to 8th 2018. 1.1 The Appendices This contains much of the compiled data from which the habitat and plant community descriptions have been derived. In Appendix A and in Table 1 a list of all the NVC codes that have been mapped along with the main Phase 1 Habitats associated with this site are presented. -
Holcus Lanatus L
A WEED REPORT from the book Weed Control in Natural Areas in the Western United States This WEED REPORT does not constitute a formal recommendation. When using herbicides always read the label, and when in doubt consult your farm advisor or county agent. This WEED REPORT is an excerpt from the book Weed Control in Natural Areas in the Western United States and is available wholesale through the UC Weed Research & Information Center (wric.ucdavis.edu) or retail through the Western Society of Weed Science (wsweedscience.org) or the California Invasive Species Council (cal-ipc.org). Holcus lanatus L. Common velvetgrass Family: Poaceae Range: Most of the western U.S. except Wyoming and South Dakota. Habitat: Roadsides, disturbed grassland, cultivated fields, and orchards. Often found on soils with low fertility. Some biotypes of common velvetgrass tolerate high salt concentrations. Grows best under moist conditions, but established plants tolerate moderate drought. A facultative wetland indicator species in California and some other western states. It does not survive a period of severe frost. Origin: Native to Europe. Impact: Dense populations of common velvetgrass have been shown to reduce the establishment of native species and the growth of tree seedlings. This species rapidly colonizes disturbed areas, where it out competes native species for soil moisture and nutrients, especially in nutrient-limited substrates. The accumulation of litter can prevent the germination of native grasses and increase risk of fire. In California, common velvetgrass is particularly invasive in coastal grasslands and wetlands in the northern part of the state. Common velvetgrass provides food for game birds, deer, elk, and insects. -
Root Functional Diversity of Native and Non- Native C3 and C4 Grass Species in Hawai'i
Root functional diversity of native and non- native C3 and C4 grass species in Hawai‘i By Courtney L. Angelo* and Stephanie Pau Abstract C3 and C4 plants are often reported to differ in functional traits and resource-use strategies, while non-native plants may differ from native plants in functional traits, leading to different resource- use strategies that facilitate their invasion. In this study, we compared root functional traits of native and non-native C3 and C4 grasses with the prediction that different resource acquisition strategies would be observed among these groups. We examined five root functional traits (mean diameter, specific root length, root tissue density, % fine roots (diameter <0.2 mm), and root length density) among natural communities of C3 and C4 grass species along an elevation gradient in Hawai‘i to classify resource-use strategies. We additionally examined how root functional traits were related to environmental characteristics (mean annual, seasonal, and July soil moisture; mean annual precipitation and temperature; and soil % nitrogen) along this elevation gradient. Root traits broadly corresponded to differences in photosynthetic pathway (C3 vs. C4; P < 0.002). However, significant variation occurred within the C3 functional group (P < 0.05), whereas all C4 species had similar root functional traits. Grass assemblages were associated with differences in seasonal soil moisture, but root traits did not sort consistently along any environmental gradient. Principal component and cluster analyses of root functional traits showed that non-native C3 species tended to be resource acquisitive whereas the native C3 species was resource conservative, similar to native and non-native C4 species.