International Conference on Habitat Fragmentation Due to Transportation Infrastructure and Presentation of COST Action 341 Products
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Landscape Connectivity Science and Practice: Ways Forward for Large Ranging Species and Their Landscapes
LANDSCAPE CONNECTIVITY SCIENCE AND PRACTICE: WAYS FORWARD FOR LARGE RANGING SPECIES AND THEIR LANDSCAPES 1 Acknowledgements: This report was developed following the Landscape Connectivity Workshop held at and hosted by WWF India, Delhi in May 2018. We are grateful to the following people who provided valuable input, facilitation and compilation of notes throughout and following the workshop: Hamsini Bijlani, Dipankar Ghose (WWF India), Nilanga Jayasinghe (WWF US), Nitin Seker (WWF India), Indira Akoijam (WWF India), Thu Ba Huynh (WWF Tigers Alive). Suggested citation: WWF Tigers Alive (2020). Landscape Connectivity Science and Practice: Ways forward for large ranging species and their landscapes. Workshop Report, WWF Tigers Alive, WWF International. Workshop report editors: Ashley Brooks (WWF Tigers Alive), Hamsini Bijlani. Case study report researcher and author: Kyle Lukas Report prepared by: WWF Tigers Alive Published in: 2020 by WWF – World Wide Fund for Nature (Formerly World Wildlife Fund), Gland, Switzerland. Any reproduction in full or in part must mention the title and credit the above- mentioned publisher as the copyright owner. For more information please contact: Ashley Brooks. [email protected] WWF Tigers Alive is an initiative of WWF that supports tiger range countries achieve their commitments under the Global Tiger Recovery Program to double the number of tigers by 2022. WWF is one of the world’s largest and most experienced independent conservation organizations, with over 5 million supporters and a global network active in more than 100 countries. WWF’s mission is to stop the degradation of the planet’s natural environment and to build a future in which humans live in harmony with nature, by: conserving the world’s biological diversity, ensuring that the use of renewable natural resources is sustainable, and promoting the reduction of pollution and wasteful consumption. -
Road Ecology Studies for Mexico: a Review
Oecologia Australis 17(1): 175-190, Março 2013 http://dx.doi.org/10.4257/oeco.2013.1701.14 ROAD ECOLOGY STUDIES FOR MEXICO: A REVIEW Alberto González Gallina1,* & Griselda Benítez Badillo1 1Instituto de Ecología, AC, Carretera Antigua a Coatepec, No. 351, El Haya, Xalapa 91070, Veracruz, México. E-mail: [email protected], [email protected] ABSTRACT The main goal of this study is to perform review of road ecology issue in Mexico. More specifically we addressed: 1) a general overview of road construction from pre-Colonial times to the present; 2) a description of the historical background context for understanding modern Mexico´s highway system; 3) a review of the main results of the road ecology studies in Mexico and 4) the Mexican policy on mitigation actions. Finally, we discuss the key points of future research and road policies. There is already some research, mainly in road mortality, which gives us a glimpse of the impact of roads on Mexican wildlife. Mexico has wide diversity of habitats and ecosystems. So, to gain knowledge on the impact of roads on wildlife so that efficient corrective and preventive actions can be planned much more study is required. Unfortunately, most of the studies carried out in Latin America, and specifically in Mexico, were done only over Environmental Impact studies for large scale infrastructure projects. There is still a long way to go in Mexico for roadways to become environmentally friendly, but little by little the issue is gaining importance and hopefully more and more academics, policy makers and people in general will become interested and get involved, so that this goal can be achieved. -
MAPPING the SPIDER FAUNA (ARANEAE) of FINLAND Seppo Koponen
Advances in Arachnology and Developmental Biology. UDC 595.4(480):591.9(480) Papers dedicated to Prof. Dr. Božidar Ćurčić. S. E. Makarov & R. N. Dimitrijević (Eds.) 2008. Inst. Zool., Belgrade; BAS, Sofia; Fac. Life Sci., Vienna; SASA, Belgrade & UNESCO MAB Serbia. Vienna — Belgrade — Sofia, Monographs, 12, 349-354. MAPPING THE SPIDER FAUNA (ARANEAE) OF FINLAND Seppo Koponen Zoological Museum, University of Turku, FI-20014 Turku, Finland Abstract — The history of research on the spider fauna of Finland is briefly dealt with. The first list of spiders from Finland was published by Nordmann in 1863 and included 140 species; the well-known list of Palmgren (1977) included 595 species and the present (internet) checklist contains ca. 640 species. A recent study project on Finnish spiders and their distribution patterns (“The Spider Fauna of Finland”) is also discussed. Key words: Araneae, spiders, fauna, distribution, research history, threatened species, Finland INTRODUCTION The area of Finland is about 338000 km2, and the country is situated between 60° and 70° N latitude. Most of Finland belongs to the boreal coniferous forest (taiga) zone, the southwestern corner to the hemiboreal zone, and the northernmost parts to the sub-arctic zone. About 80% of Finland can be classified as lowland, lying below 200 m. The highest point of the country is situated in Lapland: Halti, 1328 m a.s.l., in the northwesternmost corner of Finland. The known spider fauna of Finland consists of about 640 species (Koponen, 2007). For comparison, the number of spiders reported from neighboring coun- tries, Sweden (Almquist, 2006) and Norway (Artsdatabanken, 2006), is 716 and 562, respectively. -
Toward Understanding the Ecological Impact of Transportation Corridors
United States Department of Agriculture Toward Understanding Forest Service the Ecological Impact of Pacific Northwest Research Station Transportation Corridors General Technical Report PNW-GTR-846 Victoria J. Bennett, Winston P. Smith, and July 2011 Matthew G. Betts D E E P R A U R T LT MENT OF AGRICU The Forest Service of the U.S. Department of Agriculture is dedicated to the principle of multiple use management of the Nation’s forest resources for sustained yields of wood, water, forage, wildlife, and recreation. Through forestry research, cooperation with the States and private forest owners, and management of the National Forests and National Grasslands, it strives—as directed by Congress—to provide increasingly greater service to a growing Nation. The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or part of an individual’s income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA’s TARGET Center at (202) 720-2600 (voice and TDD). To file a complaint of discrimination, write USDA, Director, Office of Civil Rights, 1400 Independence Avenue, SW, Washington, DC 20250-9410 or call (800) 795-3272 (voice) or (202) 720-6382 (TDD). USDA is an equal opportunity provider and employer. Authors Victoria J. -
Helsinki 1987 © Figures
English summary of the report of the Committee for the Conservation of Threatened Ädimals and Plants in Finland Edited by Pertti Rass1 and Rauno Väisänen Helsinki 1987 Threatened animais and plants in Finland English summary of the report of the Committee for the Conservation of Threatened Animais and Plants in Finland Edited by Pertti Rassi and Rauno Väisänen Helsinki 1987 © Figures Markku Bussman Dick Forssman Marja Koistinen Katriina Metsänheimo Maija Mustonen Tuomo Niemelä Antti Rönkä Päivö Somerma Cover: Etiomys quercinus (left) Asptenium adutterinum (above right) Morchetta semilibera (below right) ISSN 0356-9470 ISBN 951-46-7961-X Helsinki 1987. Valtion painatuskeskus Julkaisija KUVAILULEHTI YMPÄRSTöMINISTERIö Julkaisun päivämäärä 22.8.1986 Tekijät (toimielimestä: toimielimen nimi, puheenjohtaja, sihteeri) Julkaisun laji Uhanalaisten eläinten ja kasvien suojelutoimikunta Komiteanmietintö, englanninkielinen yhteenveto Puheenjohtaja Pertti Rassi Toimeksiantaja Sihteerit Aulikki Alanen, Eija Kemppainen, Maa- ja metsätalousministeriö Markku Vickholm, Rauno Väisänen Toimielimen asettamispvm Yhteenvedon toimittajat P. Rassi & R. Väisänen 17.3.1983 Julkaisun nimi (myös ruotsinkielinen) Threatened animals and plants in Finland English summary of the report of the Committee for the Conservation of Threatened Animals and Plants in Finland Julkaisun osat Tiivistelmä Englanninkielinen yhteenveto uhanalaisten eläinten ja kasvien suojelutoimikunnanmietinnöstä (1985:43) osat 1—111. Yhteenvedossa on aluksi katsaus luonnonsuojeluun Suomessa. Siinä -
L. VAN AARTSEN Van Rijksstraatweg 134, Naar Bergkampweg 4, Wamsveld. Mej. AG VAN ARK Van Haarlem Naar Heemsteedse Dr
PERSONALIA Benoemd: tot reserve-eerste-luitenant-tandarts de vaandrigs-tandarts M. C. J. KLERK, J. W. VAN . HILVOORDE, A. A. KEUZER en H. J. MEIJERING. Gevestigd: A. VAN ALPHEN, Akeleilaan (praktijk), Fr. Vogelstr. 126 (privé), Zwijndrecht. N. Bos, Schiedamseweg 175, Vlaardingen. Hr. en Mw. B. P. HAZENBERG—ELSLO, v. Zuylen v. Nijeveltstraat 108, Wassenaar. J. F. SCHIECK, van Brakelstraat 14, Oud-Beyerland. Mw. E. V. R. M. J. HRISTOV-SUGAR, Burg. Meineszlaan 33a, Rotterdam. A. H. W. P. THEUNISSEN, Rijksweg 202, Rijen. Verhuisd: L. VAN AARTSEN van Rijksstraatweg 134, naar Bergkampweg 4, Wamsveld. Mej. A. G. VAN ARK van Haarlem naar Heemsteedse Dreef 190, Heemstede. J. H. BELIE van Dirksland naar Hooigracht 34A, Leiden. G. BOEKING van Groningen naar Noorddijkerweg 15, Noorddijk (Gr.). A. VAN BRUGGEN van Delfzijl naar Garenkokerskade 92, Haarlem. L. J. CLAESSEN van Gebrs. Hoeksstraat 13 naar Nieuwstraat 61, Eersel (N.Br.). S. T. DANTUMA van Leeuwarden naar Overwinningsplein 90, Groningen. R. A. A. FOEKENS, Nassaulaan 1 (praktijk), Sportlaan 998 (privé), Den Haag. C. B. KLAASSEN van Utrecht naar Randweg 80 (praktijk en privé), Rotterdam. J. P. VAN DER KLEI van Utrecht naar Emmalaan 21, Bergen (N.H.). J. DE KooMEN van Rotterdam naar Vuurdoomlaan 12, Pijnacker. G. D. Kos van Nunspeet naar Burg. de Visserlaan 60A (praktijk), Graaf Willem de Oudelaan 24, (privé), Naarden. K. J. G. VAN DER LAAN van Crabethstraat 51 naar Crabethpark 25, Gouda. D. L. DE Moor van Amsterdam naar Woudenbergseweg 104, Maarssen. A. M. MERTENS, Paul Gabriëlstraat 175, Den Haag. J. H. C. RIDDERING, „Lochleigh", Opper Mountainroad, Somerset C.P., Z. -
Improving Habitat and Connectivity Model Predictions with Multi-Scale Resource Selection Functions from Two Geographic Areas
Landscape Ecol (2019) 34:503–519 https://doi.org/10.1007/s10980-019-00788-w (0123456789().,-volV)(0123456789().,-volV) RESEARCH ARTICLE Improving habitat and connectivity model predictions with multi-scale resource selection functions from two geographic areas Ho Yi Wan . Samuel A. Cushman . Joseph L. Ganey Received: 22 May 2018 / Accepted: 18 February 2019 / Published online: 4 March 2019 Ó This is a U.S. government work and its text is not subject to copyright protection in the United States; however, its text may be subject to foreign copyright protection 2019 Abstract converted the models into landscape resistance sur- Context Habitat loss and fragmentation are the most faces and used simulations to model connectivity pressing threats to biodiversity, yet assessing their corridors for the species, and created composite impacts across broad landscapes is challenging. habitat and connectivity models by averaging the Information on habitat suitability is sometimes avail- local and non-local models. able in the form of a resource selection function model Results While the local and the non-local models developed from a different geographical area, but its both performed well, the local model performed best applicability is unknown until tested. in the part of the study area where it was built, but Objectives We used the Mexican spotted owl as a performed worse in areas that are beyond the extent of case study to demonstrate how models developed from the data used to train it. The composite habitat model different geographic areas affect our predictions for improved performances over both models in most habitat suitability, landscape resistance, and connec- cases. -
Guidelines for Wildlife and Traffic in the Carpathians
Wildlife and Traffic in the Carpathians Guidelines how to minimize the impact of transport infrastructure development on nature in the Carpathian countries Wildlife and Traffic in the Carpathians Guidelines how to minimize the impact of transport infrastructure development on nature in the Carpathian countries Part of Output 3.2 Planning Toolkit TRANSGREEN Project “Integrated Transport and Green Infrastructure Planning in the Danube-Carpathian Region for the Benefit of People and Nature” Danube Transnational Programme, DTP1-187-3.1 April 2019 Project co-funded by the European Regional Development Fund (ERDF) www.interreg-danube.eu/transgreen Authors Václav Hlaváč (Nature Conservation Agency of the Czech Republic, Member of the Carpathian Convention Work- ing Group for Sustainable Transport, co-author of “COST 341 Habitat Fragmentation due to Trans- portation Infrastructure, Wildlife and Traffic, A European Handbook for Identifying Conflicts and Designing Solutions” and “On the permeability of roads for wildlife: a handbook, 2002”) Petr Anděl (Consultant, EVERNIA s.r.o. Liberec, Czech Republic, co-author of “On the permeability of roads for wildlife: a handbook, 2002”) Jitka Matoušová (Nature Conservation Agency of the Czech Republic) Ivo Dostál (Transport Research Centre, Czech Republic) Martin Strnad (Nature Conservation Agency of the Czech Republic, specialist in ecological connectivity) Contributors Andriy-Taras Bashta (Biologist, Institute of Ecology of the Carpathians, National Academy of Science in Ukraine) Katarína Gáliková (National -
Roadside Ecology
Michael Brereton NRS 534 Final White Paper Roadside Ecology There are very few species in the recent history of our planet Earth that have made such a lasting impact on the surface of the world as us. Human activity has left the landscape of our planet forever changed as we continue to expand our territory to fit our exponentially growing population. One of the signs of a rapidly growing civilization is the road. Whether paved or dirt, roads are used by humans to transport ourselves great distances at the cost of our natural surroundings. Roads are a major driver of habitat fragmentation, a term used in ecology to describe the fracturing or dividing of a natural landscape type by an impassible barrier. The creation of roads clears large areas of land and reduces forest cover, furthering an ever-growing loss of habitat for arboreal species to human growth. The constant mowing of roadsides allow invasive exotic species to colonize. Roads can reduce the range for foraging and hunting animals, and those who dare to cross risk death by vehicle. Roads can also change the physical aspect of an environment, causing greater risk to pollution and flooding. In order to continue living in harmony with the flora and fauna of our natural surroundings, we must employ new ideas and technologies to our roads. The study of road ecology will provide the answers we need to have safer roads for both ourselves and our natural world. Road ecology sits at the crossroads between many different scientific fields, including invasion ecology, hydrology, stream ecology, soil science, and many more. -
Green Infrastructure Design for Transport Projects: a Road Map To
GREEN INFRASTRUCTURE DESIGN FOR TRANSPORT PROJECTS A ROAD MAP TO PROTECTING ASIA’S WILDLIFE BIODIVERSITY DECEMBER 2019 ASIAN DEVELOPMENT BANK GREEN INFRASTRUCTURE DESIGN FOR TRANSPORT PROJECTS A ROAD MAP TO PROTECTING ASIA’S WILDLIFE BIODIVERSITY DECEMBER 2019 ASIAN DEVELOPMENT BANK Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) © 2019 Asian Development Bank 6 ADB Avenue, Mandaluyong City, 1550 Metro Manila, Philippines Tel +63 2 8632 4444; Fax +63 2 8636 2444 www.adb.org Some rights reserved. Published in 2019. ISBN 978-92-9261-991-6 (print), 978-92-9261-992-3 (electronic) Publication Stock No. TCS189222 DOI: http://dx.doi.org/10.22617/TCS189222 The views expressed in this publication are those of the authors and do not necessarily reflect the views and policies of the Asian Development Bank (ADB) or its Board of Governors or the governments they represent. ADB does not guarantee the accuracy of the data included in this publication and accepts no responsibility for any consequence of their use. The mention of specific companies or products of manufacturers does not imply that they are endorsed or recommended by ADB in preference to others of a similar nature that are not mentioned. By making any designation of or reference to a particular territory or geographic area, or by using the term “country” in this document, ADB does not intend to make any judgments as to the legal or other status of any territory or area. This work is available under the Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) https://creativecommons.org/licenses/by/3.0/igo/. -
For Rent Rijksstraatweg 7, Nieuwersluis PROJECT INFORMATION Rijksstraatweg 7, Nieuwersluis
For Rent Rijksstraatweg 7, Nieuwersluis PROJECT INFORMATION Rijksstraatweg 7, Nieuwersluis On the Rijksstraatweg in Nieuwersluis, this beautiful monumental farmhouse is available for rent. The farm complex is embedded in an old monumental 10-hectare landscape park with 5,000 meters of hiking trails and a beautiful 6,000 m2 pond. The farm complex is part of a historic country estate, in the Vecht region of Utrecht. The oldest part is from 1750. The family that bought it in 1815 is still the owner. The extensive restoration was completed at the beginning of 2019. The restoration principles were restoring old looks and introducing modern comfort. A coach house, horse stable and haystack are available next to the farm. The haystack is open and has a hard floor. General - Farmhouse: approx. 285 m2 - Coach house: approx. 73 m2 - Horse stable: approx. 81 m2 - Haystack (open with hard floor) approx. 65 m2 - Northern Barn (2019/2020) approx. 88 m2 The buildings are not fully measured in accordance with NEN-2580. Square meters are a good indication. Floor surfaces with a sloping roof are from 150 cm. headroom calculated. Hofstede Sterreschans is a national monument in a unique location. For more information about the history, present and future of Hofstede Sterreschans visit the website: hofstedesterreschans.nl (still only in Dutch). Parking There are 29 parking places available on the backyard of the farm. Construction of an electric charging point for a car is prepared by means of casing in the ground. Next to the main-driveway, another 22 grass-paved parking spaces are available. -
How Should We Measure Landscape Connectivity?
Landscape Ecology 15: 633–641, 2000. 633 © 2000 Kluwer Academic Publishers. Printed in the Netherlands. How should we measure landscape connectivity? Lutz Tischendorf∗ & Lenore Fahrig Ottawa-Carleton Institute of Biology, Carleton University, 1125 Colonel By Drive, Ottawa, Canada K1S 5B6 (∗Current address: Busestrasse 76, 28213 Bremen, Germany; E-mail: [email protected]) Received 9 April 1999; Revised 27 December 1999; Accepted 7 February 2000 Abstract The methods for measuring landscape connectivity have never been compared or tested for their responses to habitat fragmentation. We simulated movement, mortality and boundary reactions across a wide range of land- scape structures to analyze the response of landscape connectivity measures to habitat fragmentation. Landscape connectivity was measured as either dispersal success or search time, based on immigration into all habitat patches in the landscape. Both measures indicated higher connectivity in more fragmented landscapes, a potential for problematic conclusions for conservation plans. We introduce cell immigration as a new measure for landscape connectivity. Cell immigration is the rate of immigration into equal-sized habitat cells in the landscape. It includes both within- and between-patch movement, and shows a negative response to habitat fragmentation. This complies with intuition and existing theoretical work. This method for measuring connectivity is highly robust to reductions in sample size (i.e., number of habitat cells included in the estimate), and we hypothesize that it therefore should be amenable to use in empirical studies. The connectivity measures were weakly correlated to each other and are therefore generally not comparable. We also tested immigration into a single patch as an index of connectivity by comparing it to cell immigration over the landscape.