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Tunisia Summary Strategic Environmental and Social
PMIR Summary Strategic Environmental and Social Assessment AFRICAN DEVELOPMENT BANK GROUP PROJECT: ROAD INFRASTRUCTURE MODERNIZATION PROJECT COUNTRY: TUNISIA SUMMARY STRATEGIC ENVIRONMENTAL AND SOCIAL ASSESSMENT (SESA) Project Team: Mr. P. M. FALL, Transport Engineer, OITC.2 Mr. N. SAMB, Consultant Socio-Economist, OITC.2 Mr. A. KIES, Consultant Economist, OITC 2 Mr. M. KINANE, Principal Environmentalist, ONEC.3 Mr. S. BAIOD, Consultant Environmentalist ONEC.3 Project Team Sector Director: Mr. Amadou OUMAROU Regional Director: Mr. Jacob KOLSTER Division Manager: Mr. Abayomi BABALOLA 1 PMIR Summary Strategic Environmental and Social Assessment Project Name : ROAD INFRASTRUCTURE MODERNIZATION PROJECT Country : TUNISIA Project Number : P-TN-DB0-013 Department : OITC Division: OITC.2 1 Introduction This report is a summary of the Strategic Environmental and Social Assessment (SESA) of the Road Project Modernization Project 1 for improvement works in terms of upgrading and construction of road structures and primary roads of the Tunisian classified road network. This summary has been prepared in compliance with the procedures and operational policies of the African Development Bank through its Integrated Safeguards System (ISS) for Category 1 projects. The project description and rationale are first presented, followed by the legal and institutional framework in the Republic of Tunisia. A brief description of the main environmental conditions is presented, and then the road programme components are presented by their typology and by Governorate. The summary is based on the projected activities and information contained in the 60 EIAs already prepared. It identifies the key issues relating to significant impacts and the types of measures to mitigate them. It is consistent with the Environmental and Social Management Framework (ESMF) developed to that end. -
Les Projets D'assainissement Inscrit S Au Plan De Développement
1 Les Projets d’assainissement inscrit au plan de développement (2016-2020) Arrêtés au 31 octobre 2020 1-LES PRINCIPAUX PROJETS EN CONTINUATION 1-1 Projet d'assainissement des petites et moyennes villes (6 villes : Mornaguia, Sers, Makther, Jerissa, Bouarada et Meknassy) : • Assainissement de la ville de Sers : * Station d’épuration : travaux achevés (mise en eau le 12/08/2016); * Réhabilitation et renforcement du réseau et transfert des eaux usées : travaux achevés. - Assainissement de la ville de Bouarada : * Station d’épuration : travaux achevés en 2016. * Réhabilitation et renforcement du réseau et transfert des eaux usées : les travaux sont achevés. - Assainissement de la ville de Meknassy * Station d’épuration : travaux achevés en 2016. * Réhabilitation et renforcement du réseau et transfert des eaux usées : travaux achevés. • Makther: * Station d’épuration : travaux achevés en 2018. * Travaux complémentaires des réseaux d’assainissement : travaux en cours 85% • Jerissa: * Station d’épuration : travaux achevés et réceptionnés le 12/09/2014 ; * Réseaux d’assainissement : travaux achevés (Réception provisoire le 25/09/2017). • Mornaguia : * Station d’épuration : travaux achevés. * Réhabilitation et renforcement du réseau et transfert des eaux usées : travaux achevés Composantes du Reliquat : * Assainissement de la ville de Borj elamri : • Tranche 1 : marché résilié, un nouvel appel d’offres a été lancé, travaux en cours de démarrage. 1 • Tranche2 : les travaux de pose de conduites sont achevés, reste le génie civil de la SP Taoufik et quelques boites de branchement (problème foncier). * Acquisition de 4 centrifugeuses : Fourniture livrée et réceptionnée en date du 19/10/2018 ; * Matériel d’exploitation: Matériel livré et réceptionné ; * Renforcement et réhabilitation du réseau dans la ville de Meknassy : travaux achevés et réceptionnés le 11/02/2019. -
Growth and Population Dynamics of Posidonia Oceanica on the S~Anishmediterranean Coast: Elucidatina Seacrrass Decline
MARINE ECOLOGY PROGRESS SERIES Vol. 137: 203-213, 1996 Published June 27 Mar Ecol Prog Ser Growth and population dynamics of Posidonia oceanica on the S~anishMediterranean coast: elucidatina seacrrass decline Nuria ~arba'l*,Carlos M. ~uarte',Just cebrianl, Margarita E. ~allegos~, Birgit Olesen3, Kaj sand-~ensen~ 'Centre dlEstudis Avanqats de Blanes, C.S.I.C., Cami de Santa Barbara sin, E-17300 Blanes, Girona, Spain 'Departamento de Hidrobiologia, Universidad Autonoma Metropolitana- Iztapalapa, Michocan y Purisima, col. Vicentina, AP 55-535, 09340 Mexico D.F., Mexico 3Department of Plant Ecology, University of Aarhus, Nordlandsvej 68, DK-8240 Risskov. Denmark 'Freshwater Biological Laboratory. University of Copenhagen, 51 Helsingersgade, DK-3400 Hillered. Denmark ABSTRACT: The growth and population dynamics of Posidonia oceanica were examined in 29 mead- ows along 1000 km of the Spanish Mediterranean coast (from 36"46' to 42"22' N). oceanica devel- oped the densest meadows (1141 shoots m-') and the highest aboveground biomass (1400 g DW m") between 38 and 39"N. P. oceanica shoots produced, on average, 1 leaf every 47 d, though leaf forma- tion rates in the populations increased from north to south (range 5 7 to 8.9leaves shoot-' yr-'). P ocean- ica is a long-living seagrass, with shoots able to live for at least 30 yr P, oceanica recruited shoots at low rates (0.02 to 0.5 In units yr-l) which did not balance the mortality rates (0.06 to 0.5 In unlts yr.') found in most (57 %) of the meadows. If the present disturbance and rate of decline are maintained, shoot den- sity is predicted to decline by 50% over the coming 2 to 24 yr. -
Resit Akcakaya
H. Reşit Akçakaya Department of Ecology and Evolution, Stony Brook University, Stony Brook, New York 11794 USA • 1-631-632-8605 • http://life.bio.sunysb.edu/ee/akcakayalab/ EDUCATION 1989 Ph.D. in Ecology and Evolution, State University of New York at Stony Brook Thesis: "Population cycles of mammals: theory and evidence" 1983 B.Sc. (high honors) in Biology, Middle East Technical University, Ankara, Turkey CAREER 2007 to present Professor, Department of Ecology and Evolution, Stony Brook University, New York 2012 to 2015 Director, Graduate Program in Ecology and Evolution, Stony Brook University, New York 1988 to 2007 Senior Scientist, Applied Biomathematics, Setauket, New York 1993 Post-doctoral fellow, Inst. of Animal Ecology, Univ. of Lausanne, Switzerland PROFESSIONAL ACTIVITIES AND MEMBERSHIPS 2016 to present IUCN SSC Task Force on Assessing Conservation Success, which is developing guidelines for a new IUCN Green List of Species to quantify species recovery and conservation impact. 2014 to present Regional Editor (North America), Conservation Biology 2014 to present Coordinating Lead Author, Intergovernmental Platform on Biodiversity and Ecosystem Services (IPBES), deliverable on "Policy support tools and methodologies for scenario analysis and modelling of biodiversity and ecosystem services." 2001 to present Chair, Red List Standards and Petitions Subcommittee, IUCN Species Survival Commission (SSC). 2001 to present IUCN SSC Red List Committee 2012 to present IUCN SSC Climate Change Specialist Group Steering Committee 2014 to -
Global Seagrass Distribution and Diversity: a Bioregional Model ⁎ F
Journal of Experimental Marine Biology and Ecology 350 (2007) 3–20 www.elsevier.com/locate/jembe Global seagrass distribution and diversity: A bioregional model ⁎ F. Short a, , T. Carruthers b, W. Dennison b, M. Waycott c a Department of Natural Resources, University of New Hampshire, Jackson Estuarine Laboratory, Durham, NH 03824, USA b Integration and Application Network, University of Maryland Center for Environmental Science, Cambridge, MD 21613, USA c School of Marine and Tropical Biology, James Cook University, Townsville, 4811 Queensland, Australia Received 1 February 2007; received in revised form 31 May 2007; accepted 4 June 2007 Abstract Seagrasses, marine flowering plants, are widely distributed along temperate and tropical coastlines of the world. Seagrasses have key ecological roles in coastal ecosystems and can form extensive meadows supporting high biodiversity. The global species diversity of seagrasses is low (b60 species), but species can have ranges that extend for thousands of kilometers of coastline. Seagrass bioregions are defined here, based on species assemblages, species distributional ranges, and tropical and temperate influences. Six global bioregions are presented: four temperate and two tropical. The temperate bioregions include the Temperate North Atlantic, the Temperate North Pacific, the Mediterranean, and the Temperate Southern Oceans. The Temperate North Atlantic has low seagrass diversity, the major species being Zostera marina, typically occurring in estuaries and lagoons. The Temperate North Pacific has high seagrass diversity with Zostera spp. in estuaries and lagoons as well as Phyllospadix spp. in the surf zone. The Mediterranean region has clear water with vast meadows of moderate diversity of both temperate and tropical seagrasses, dominated by deep-growing Posidonia oceanica. -
Green Parties and Elections to the European Parliament, 1979–2019 Green Par Elections
Chapter 1 Green Parties and Elections, 1979–2019 Green parties and elections to the European Parliament, 1979–2019 Wolfgang Rüdig Introduction The history of green parties in Europe is closely intertwined with the history of elections to the European Parliament. When the first direct elections to the European Parliament took place in June 1979, the development of green parties in Europe was still in its infancy. Only in Belgium and the UK had green parties been formed that took part in these elections; but ecological lists, which were the pre- decessors of green parties, competed in other countries. Despite not winning representation, the German Greens were particularly influ- enced by the 1979 European elections. Five years later, most partic- ipating countries had seen the formation of national green parties, and the first Green MEPs from Belgium and Germany were elected. Green parties have been represented continuously in the European Parliament since 1984. Subsequent years saw Greens from many other countries joining their Belgian and German colleagues in the Euro- pean Parliament. European elections continued to be important for party formation in new EU member countries. In the 1980s it was the South European countries (Greece, Portugal and Spain), following 4 GREENS FOR A BETTER EUROPE their successful transition to democracies, that became members. Green parties did not have a strong role in their national party systems, and European elections became an important focus for party develop- ment. In the 1990s it was the turn of Austria, Finland and Sweden to join; green parties were already well established in all three nations and provided ongoing support for Greens in the European Parliament. -
Posidonia Paper.Docx
Epiphyte accruel patterns and effects on Posidonia oceanica By Emily Hardison and Scott Borsum Abstract This study focuses on the relationship between Posidonia oceanica leaves and the epiphytes that live on those leaves at Stareso Research center in Calvi Bay, Corsica. We determine patterns of epiphyte accrual along Posidonia oceanica leaves for depths of 5m, 10m, 15m, and 20m and calculate the abundance of epiphytes across this depth range and the biomass of epiphytes in Posidonia oceanica bed at each depth, through in water measurements and characterizing epiphyte loads of samples brought onshore. We show that epiphytes aggregate in depth specific and leaf-side specific patterns along Posidonia leaves, cause degradation of live Posidonia tissue, and contribute a significant amount of biomass to Posidonia oceanica beds and detritus. We attempt to explain why certain patterns of epiphyte accrual are seen by determining that the convex side of the leaf most commonly faces up towards the sun. Introduction Posidonia oceanica is a protected endemic seagrass species in the Mediterranean Sea. This species is particularly interesting because of the large role it plays in maintaining a healthy and diverse Mediterranean ecosystem. It grows in vasts meadows and provides habitats, food, and nursery areas for a wide array of species (Boudouresque C. et al., 2006). Despite its energy expensive lifestyle, Posidonia is able to survive in the nutrient poor waters of the Mediterranean Sea (Lepoint, 2002). Posidonia is often inhabited by epiphytes. Previous research has shown that epiphyte load on Posidonia leaves has a negative relationship with depth (Lopez, 2012). Light attenuates with depth and can therefore become a limiting factor for primary producers, like Posidonia. -
Birds of the East Texas Baptist University Campus with Birds Observed Off-Campus During BIOL3400 Field Course
Birds of the East Texas Baptist University Campus with birds observed off-campus during BIOL3400 Field course Photo Credit: Talton Cooper Species Descriptions and Photos by students of BIOL3400 Edited by Troy A. Ladine Photo Credit: Kenneth Anding Links to Tables, Figures, and Species accounts for birds observed during May-term course or winter bird counts. Figure 1. Location of Environmental Studies Area Table. 1. Number of species and number of days observing birds during the field course from 2005 to 2016 and annual statistics. Table 2. Compilation of species observed during May 2005 - 2016 on campus and off-campus. Table 3. Number of days, by year, species have been observed on the campus of ETBU. Table 4. Number of days, by year, species have been observed during the off-campus trips. Table 5. Number of days, by year, species have been observed during a winter count of birds on the Environmental Studies Area of ETBU. Table 6. Species observed from 1 September to 1 October 2009 on the Environmental Studies Area of ETBU. Alphabetical Listing of Birds with authors of accounts and photographers . A Acadian Flycatcher B Anhinga B Belted Kingfisher Alder Flycatcher Bald Eagle Travis W. Sammons American Bittern Shane Kelehan Bewick's Wren Lynlea Hansen Rusty Collier Black Phoebe American Coot Leslie Fletcher Black-throated Blue Warbler Jordan Bartlett Jovana Nieto Jacob Stone American Crow Baltimore Oriole Black Vulture Zane Gruznina Pete Fitzsimmons Jeremy Alexander Darius Roberts George Plumlee Blair Brown Rachel Hastie Janae Wineland Brent Lewis American Goldfinch Barn Swallow Keely Schlabs Kathleen Santanello Katy Gifford Black-and-white Warbler Matthew Armendarez Jordan Brewer Sheridan A. -
Morpho-Chronological Variations and Primary Production in Posidonia
Morpho-chronological variations and primary production in Posidonia sea grass from Western Australia Gérard Pergent, Christine Pergent-Martini, Catherine Fernandez, Pasqualini Vanina, Diana Walker To cite this version: Gérard Pergent, Christine Pergent-Martini, Catherine Fernandez, Pasqualini Vanina, Diana Walker. Morpho-chronological variations and primary production in Posidonia sea grass from Western Aus- tralia. Journal of the Marine Biological Association of the United Kingdom, Cambridge University Press, 2004, 84 (5), pp.895-899. 10.1017/S0025315404010161h. hal-01768985 HAL Id: hal-01768985 https://hal.archives-ouvertes.fr/hal-01768985 Submitted on 17 Apr 2018 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. J. Mar. Biol. Ass. U.K. (2004), 84, 895^899 Printed in the United Kingdom Morpho-chronological variations and primary production in Posidonia sea grass from Western Australia P Ge¤rard Pergent* , Christine Pergent-Martini*, Catherine Fernandez*, O Vanina Pasqualini* and Diana Walker O *Equipe Ecosyste' mes Littoraux, Faculty of Sciences, -
Use of Posidonia Oceanica Seedlings from Beach- Cast Fruits for Seagrass Planting
DOI 10.1515/bot-2012-0200 Botanica Marina 2013; 56(2): 185–195 Jorge Terrados * , Arnaldo Mar í n and David Celdr á n Use of Posidonia oceanica seedlings from beach- cast fruits for seagrass planting Abstract: Posidonia oceanica seedlings produced from biological productivity, nutrient cycling, carbon burial beach-cast fruits were planted in an area where this and sediment stabilisation (Hemminga and Duarte 2000 ). Mediterranean seagrass was lost as a consequence of fish- In the last century, human populations in coastal zones farming. The effects of substratum type (dead matte vs. have been rapidly increasing. This has increased anthro- meadow) and planting level (above vs. below bottom sur- pogenic impacts on seagrass ecosystems, in turn leading face) on seedling survivorship and leaf development were to a worldwide decline of seagrasses (Orth et al. 2006a , evaluated after 3 years. Seedling capacity to resist uproot- Waycott et al. 2009 ). Seagrass declines have stimulated ing was also tested by comparing survivorship and leaf interest in seagrass restoration research, and several development after 2 years in seedlings firmly anchored approaches have been used (Fonseca et al. 1998 , Treat in dead matte by artificial means (mesh-pot) with those and Lewis 2006 , Paling et al. 2009 ) because adaptation to planted without any anchoring other than their roots. Sur- local conditions and to the features of the seagrass species vivorship in dead matte was 44 % after 3 years and was to be planted is required. A record of seagrass presence in not affected by planting level. Seedling planting inside the past, knowledge about what caused seagrass loss and the meadow led to complete mortality after 3 years. -
Wood Duck (Aix Sponsa), EC 1606 (Oregon State University Extension
EC 1606 • April 2007 $1.00 Wood Duck Photo: Dave Menke, U.S. Fish and Wildlife Service Aix sponsa by Z. Turnbull and S. Sells he wood duck is so beautiful that its populations have increased, and today scientifi c name, Aix sponsa, means populations are at healthy levels. T “water bird in bridal dress.” Being Wood ducks are very popular for hunt- so beautiful (and tasty!), by the 1880s, ing. In fact, there are more wood ducks the once-abundant wood duck was disap- harvested each year in the United States pearing quickly due to hunting and habitat than any other game bird except mallards. loss. But not just hunters appreciate wood In the 1910s, wildlife managers acted ducks. Bird watchers and other people quickly to help save wood ducks. Laws who spend time outdoors love their were passed to protect migratory birds, beauty. hunting was controlled, and habitat was Common predators of wood ducks are protected. Wood duck nest boxes were raccoons, gray and red foxes, great horned created in the 1930s. Slowly, wood duck owls, some snakes, and minks. In a group of 10 newly hatched wood ducks, usu- ally only one or two survive past their fi rst 2 weeks. Predation is a main cause of such low survival rates. Dump nests occur when one or more females follow another to her nest and add their own eggs to the fi rst female’s eggs. When this occurs, there may be 50 or more eggs. They usually are abandoned, leading to a decline in successful hatch- ings in the area. -
Review of the Status of Introduced Non-Native Waterbird Species in the Area of the African-Eurasian Waterbird Agreement: 2007 Update
Secretariat provided by the Workshop 3 United Nations Environment Programme (UNEP) Doc TC 8.25 21 February 2008 8th MEETING OF THE TECHNICAL COMMITTEE 03 - 05 March 2008, Bonn, Germany ___________________________________________________________________________ Review of the Status of Introduced Non-Native Waterbird Species in the Area of the African-Eurasian Waterbird Agreement: 2007 Update Authors A.N. Banks, L.J. Wright, I.M.D. Maclean, C. Hann & M.M. Rehfisch February 2008 Report of work carried out by the British Trust for Ornithology under contract to AEWA Secretariat © British Trust for Ornithology British Trust for Ornithology, The Nunnery, Thetford, Norfolk IP24 2PU Registered Charity No. 216652 CONTENTS Page No. List of Tables...........................................................................................................................................5 List of Figures.........................................................................................................................................7 List of Appendices ..................................................................................................................................9 EXECUTIVE SUMMARY..................................................................................................................11 RECOMMENDATIONS .....................................................................................................................13 1. INTRODUCTION.................................................................................................................15