Draft Aquatic Life Ambient Water Quality Criteria for Aluminum 2017

Total Page:16

File Type:pdf, Size:1020Kb

Draft Aquatic Life Ambient Water Quality Criteria for Aluminum 2017 United States Office of Water EPA-822-P-17-001 Environmental Protection 4304T July 2017 Agency DRAFT AQUATIC LIFE AMBIENT WATER QUALITY CRITERIA FOR ALUMINUM 2017 EPA-822-P-17-001 DRAFT AQUATIC LIFE AMBIENT WATER QUALITY CRITERIA FOR ALUMINUM - 2017 (CAS Registry Number 7429-90-05) July 2017 U.S. ENVIRONMENTAL PROTECTION AGENCY OFFICE OF WATER OFFICE OF SCIENCE AND TECHNOLOGY HEALTH AND ECOLOGICAL CRITERIA DIVISION WASHINGTON, D.C. ii NOTICES This document provides information to states and tribes authorized to establish water quality standards under the Clean Water Act (CWA), to protect aquatic life from toxic effects of aluminum. Under the CWA, states and tribes are to establish water quality criteria to protect designated uses. State and tribal decision makers retain the discretion to adopt approaches on a case-by-case basis that differ from these criteria when appropriate. While this document contains EPA’s scientific recommendations regarding ambient concentrations of aluminum that protect aquatic life, it does not substitute for the CWA or EPA’s regulations; nor is it a regulation itself. Thus, it cannot impose legally binding requirements on EPA, states, tribes, or the regulated community, and might not apply to a particular situation based upon the circumstances. EPA may change this document in the future. This document has been approved for publication by the Office of Science and Technology, Office of Water, U.S. Environmental Protection Agency. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. This document can be downloaded from: https://www.epa.gov/wqc/aquatic-life-criteria-and-methods-toxics. iii FOREWORD Section 304(a)(l) of the Clean Water Act of 1977 (P.L. 95-217) requires that the Administrator of the Environmental Protection Agency (EPA) publish water quality criteria that accurately reflect the latest scientific knowledge on the kind and extent of all identifiable effects on health and welfare that might be expected from the presence of pollutants in any body of water, including ground water. This document is a draft ambient water quality criteria (AWQC) document for the protection of aquatic life based upon consideration of all available information relating to effects of aluminum on aquatic organisms. The term "water quality criteria" is used in two sections of the Clean Water Act, section 304(a)(l) and section 303(c)(2). The term has a different program impact in each section. In section 304, the term represents a non-regulatory, scientific assessment of ecological effects. Criteria presented in this document are such scientific assessments. If water quality criteria associated with specific surface water uses are adopted by a state or EPA as water quality standards under section 303, they become applicable Clean Water Act water quality standards in ambient waters within that state or authorized tribe. Water quality criteria adopted in state water quality standards could have the same numerical values as criteria developed under section 304. However, in many situations states might want to adjust water quality criteria developed under section 304 to reflect local environmental conditions and human exposure patterns. Alternatively, states and authorized tribes may use derive numeric criteria based on other scientifically defensible methods but the criteria must be protective of designated uses. It is not until their adoption as part of state water quality standards, and subsequent approval by EPA, that criteria become Clean Water Act applicable water quality standards. Guidelines to assist the states and authorized tribes in modifying the criteria presented in this document are contained in the Water Quality Standards Handbook (U.S. EPA 2014). This handbook and additional guidance on the development of water quality standards and other water-related programs of this Agency have been developed by the Office of Water. This draft document presents recommendations only. It does not establish or affect legal rights or obligations. It does not establish a binding norm and cannot be finally determinative of the issues addressed. Agency decisions in any particular situation will be made by applying the Clean Water Act and EPA regulations on the basis of specific facts presented and scientific information then available. Elizabeth Southerland Director Office of Science and Technology iv ACKNOWLEDGEMENTS Technical Analysis Lead Diana Eignor, Office of Water, Office of Science and Technology, Health and Ecological Criteria Division, Washington, DC Reviewers (2017) Elizabeth Behl and Kathryn Gallagher, Office of Water, Office of Science and Technology, Health and Ecological Criteria Division, Washington, DC EPA Peer Reviewers (2017) Nicole Shao and Robert Cantilli, U.S. EPA, Office of Research and Development, Office of Science Policy, Washington, DC Russ Hockett, U.S. EPA, Office of Research and Development, Mid-Continent Ecology Division, Duluth, MN Jan Gilbreath and Joseph Adamson, U.S. EPA, Office of Policy, Office of Regulatory Policy and Management, Washington, DC Lee Schroer and Alexis Wade, U.S. EPA, Office of General Counsel, Washington, DC Steve Ells and Matthew Lambert, U.S. EPA, Office of Land and Emergency Management, Washington, DC Lars Wilcut and Heather Goss, U.S. EPA, Office of Water, Office of Science and Technology, Washington, DC David Hair and Janita Aguirre, U.S. EPA, Office of Water, Office of Wastewater Management, Washington, DC Jennifer Phillips, U.S. EPA Region 5, Chicago, IL Mark Jankowski, U.S. EPA Region 10, Seattle, WA We would like to thank Russ Erikson, U.S. EPA, Office of Research and Development, Mid- Continent Ecology Division, Duluth, MN and Bill Stubblefield, Oregon State University, for their technical support and contributions to this document. v TABLE OF CONTENTS Page Notices ........................................................................................................................................... iii Foreword ........................................................................................................................................ iv Acknowledgements ......................................................................................................................... v Table of Contents ........................................................................................................................... vi List of Tables ............................................................................................................................... viii List of Figures .............................................................................................................................. viii List of Appendices ......................................................................................................................... ix Acronyms ........................................................................................................................................ x Executive Summary ....................................................................................................................... xi 1 Introduction and Background ................................................................................................. 1 2 Problem Formulation .............................................................................................................. 2 2.1 Overview of Aluminum Sources and Occurrence .............................................................. 2 2.2 Environmental Fate and Transport of Aluminum in the Aquatic Environment ................. 7 2.3 Mode of Action and Toxicity .............................................................................................. 9 2.3.1 Water Quality Parameters Affecting Toxicity .......................................................... 13 2.4 Conceptual Model ............................................................................................................. 14 2.4.1 Conceptual Diagram ................................................................................................. 14 2.5 Assessment Endpoints ...................................................................................................... 17 2.6 Measurement Endpoints.................................................................................................... 18 2.6.1 Overview of Toxicity Data Requirements ................................................................ 19 2.6.2 Measures of Effect .................................................................................................... 20 2.7 Analysis Plan .................................................................................................................... 24 2.7.1 pH, Hardness and DOC Normalization .................................................................... 27 2.7.2 Acute Criterion.......................................................................................................... 35 2.7.3 Chronic Criterion ...................................................................................................... 36 3 Effects Analyses.................................................................................................................... 36 3.1 Acute Toxicity to Aquatic Animals .................................................................................. 37 3.1.1 Freshwater ................................................................................................................. 37 3.1.2 Estuarine/Marine
Recommended publications
  • Sydney Harbour: What We Do and Do Not Know About a Highly Diverse Estuary
    Marine and Freshwater Research 2015, 66, 1073-1087 © CSIRO 2015 http://dx.doi.org/10.1071/MF15159_AC Supplementary material Sydney Harbour: what we do and do not know about a highly diverse estuary E. L. JohnstonA,B, M. Mayer-PintoA,B, P. A. HutchingsC, E. M. MarzinelliA,B,D, S. T. AhyongC, G. BirchE, D. J. BoothF, R. G. CreeseG, M. A. DoblinH, W. FigueiraI, P. E. GribbenB,D, T. PritchardJ, M. RoughanK, P. D. SteinbergB,D and L. H. HedgeA,B AEvolution and Ecology Research Centre, School of Biological, Earth and Environmental Sciences, University of New South Wales, Sydney, NSW 2052, Australia. BSydney Institute of Marine Science, 19 Chowder Bay Road, Mosman, NSW 2088, Australia. CAustralian Museum Research Institute, Australian Museum, 6 College Street, Sydney, NSW 2010, Australia. DCentre for Marine Bio-Innovation, School of Biological, Earth and Environmental Sciences, University of New South Wales, Sydney, NSW 2052, Australia. ESchool of GeoSciences, The University of Sydney, Sydney, NSW 2006, Australia. FCentre for Environmental Sustainability, School of the Environment, University of Technology, Sydney, NSW 2007, Australia. GNew South Wales Department of Primary Industries, Port Stephens Fisheries Institute, Nelson Bay, NSW 2315, Australia. HPlant Functional Biology and Climate Change Cluster, University of Technology, Sydney, NSW 2007, Australia. ICentre for Research on Ecological Impacts of Coastal Cities, School of Biological Sciences, University of Sydney, NSW 2006, Australia. JWater and Coastal Science Section, New South Wales Office of Environment and Heritage, PO Box A290, Sydney, NSW 1232, Australia. KCoastal and Regional Oceanography Lab, School of Mathematics and Statistics, University of New South Wales, NSW 2052, Australia.
    [Show full text]
  • Two Freshwater Shrimp Species of the Genus Caridina (Decapoda, Caridea, Atyidae) from Dawanshan Island, Guangdong, China, with the Description of a New Species
    A peer-reviewed open-access journal ZooKeys 923: 15–32 (2020) Caridina tetrazona 15 doi: 10.3897/zookeys.923.48593 RESEarcH articLE http://zookeys.pensoft.net Launched to accelerate biodiversity research Two freshwater shrimp species of the genus Caridina (Decapoda, Caridea, Atyidae) from Dawanshan Island, Guangdong, China, with the description of a new species Qing-Hua Chen1, Wen-Jian Chen2, Xiao-Zhuang Zheng2, Zhao-Liang Guo2 1 South China Institute of Environmental Sciences, Ministry of Ecology and Environment, Guangzhou 510520, Guangdong Province, China 2 Department of Animal Science, School of Life Science and Enginee- ring, Foshan University, Foshan 528231, Guangdong Province, China Corresponding author: Zhao-Liang Guo ([email protected]) Academic editor: I.S. Wehrtmann | Received 19 November 2019 | Accepted 7 February 2020 | Published 1 April 2020 http://zoobank.org/138A88CC-DF41-437A-BA1A-CB93E3E36D62 Citation: Chen Q-H, Chen W-J, Zheng X-Z, Guo Z-L (2020) Two freshwater shrimp species of the genus Caridina (Decapoda, Caridea, Atyidae) from Dawanshan Island, Guangdong, China, with the description of a new species. ZooKeys 923: 15–32. https://doi.org/10.3897/zookeys.923.48593 Abstract A faunistic and ecological survey was conducted to document the diversity of freshwater atyid shrimps of Dawanshan Island. Two species of Caridina that occur on this island were documented and discussed. One of these, Caridina tetrazona sp. nov. is described and illustrated as new to science. It can be easily distinguished from its congeners based on a combination of characters, which includes a short rostrum, the shape of the endopod of the male first pleopod, the segmental ratios of antennular peduncle and third maxilliped, the slender scaphocerite, and the absence of a median projection on the posterior margin.
    [Show full text]
  • An Analysis of Primary and Secondary Production in Lake Kariba in a Changing Climate
    AN ANALYSIS OF PRIMARY AND SECONDARY PRODUCTION IN LAKE KARIBA IN A CHANGING CLIMATE MZIME R. NDEBELE-MURISA A thesis submitted in partial fulfillment of the requirements for the degree of Doctor Philosophiae in the Department of Biodiversity and Conservation Biology, University of the Western Cape Supervisor: Prof. Charles Musil Co-Supervisor: Prof. Lincoln Raitt May 2011 An analysis of primary and secondary production in Lake Kariba in a changing climate Mzime Regina Ndebele-Murisa KEYWORDS Climate warming Limnology Primary production Phytoplankton Zooplankton Kapenta production Lake Kariba i Abstract Title: An analysis of primary and secondary production in Lake Kariba in a changing climate M.R. Ndebele-Murisa PhD, Biodiversity and Conservation Biology Department, University of the Western Cape Analysis of temperature, rainfall and evaporation records over a 44-year period spanning the years 1964 to 2008 indicates changes in the climate around Lake Kariba. Mean annual temperatures have increased by approximately 1.5oC, and pan evaporation rates by about 25%, with rainfall having declined by an average of 27.1 mm since 1964 at an average rate of 6.3 mm per decade. At the same time, lake water temperatures, evaporation rates, and water loss from the lake have increased, which have adversely affected lake water levels, nutrient and thermal dynamics. The most prominent influence of the changing climate on Lake Kariba has been a reduction in the lake water levels, averaging 9.5 m over the past two decades. These are associated with increased warming, reduced rainfall and diminished water and therefore nutrient inflow into the lake. The warmer climate has increased temperatures in the upper layers of lake water, the epilimnion, by an overall average of 1.9°C between 1965 and 2009.
    [Show full text]
  • Appendix 3.6: Chronic Effects Benchmarks
    October 2013 SHELL CANADA ENERGY Appendix 3.6: Chronic Effects Benchmarks Project Number: 13-1346-0001 REPORT APPENDIX 3.6: CHRONIC EFFECTS BENCHMARKS Table of Contents 1.0 INTRODUCTION ............................................................................................................................................................... 1 2.0 CHRONIC EFFECTS BENCHMARKS ............................................................................................................................. 1 2.1 Updated Canadian Council of Ministers of the Environment Protocol .................................................................. 2 2.2 Application ........................................................................................................................................................... 2 2.3 Screening of Constituents for Chronic Effects Benchmark Development ............................................................ 3 2.4 Assessment Methods .......................................................................................................................................... 6 2.4.1 General Approach .......................................................................................................................................... 6 2.5 Procedure ............................................................................................................................................................ 9 2.5.1 Step 1: Creation of a Toxicological Database ...............................................................................................
    [Show full text]
  • Sydney Harbour a Systematic Review of the Science 2014
    Sydney Harbour A systematic review of the science 2014 Sydney Institute of Marine Science Technical Report The Sydney Harbour Research Program © Sydney Institute of Marine Science, 2014 This publication is copyright. You may download, display, print and reproduce this material provided that the wording is reproduced exactly, the source is acknowledged, and the copyright, update address and disclaimer notice are retained. Disclaimer The authors of this report are members of the Sydney Harbour Research Program at the Sydney Institute of Marine Science and represent various universities, research institutions and government agencies. The views presented in this report do not necessarily reflect the views of The Sydney Institute of Marine Science or the authors other affiliated institutions listed below. This report is a review of other literature written by third parties. Neither the Sydney Institute of Marine Science or the affiliated institutions take responsibility for the accuracy, currency, reliability, and correctness of any information included in this report provided in third party sources. Recommended Citation Hedge L.H., Johnston E.L., Ayoung S.T., Birch G.F., Booth D.J., Creese R.G., Doblin M.A., Figueira W.F., Gribben P.E., Hutchings P.A., Mayer Pinto M, Marzinelli E.M., Pritchard T.R., Roughan M., Steinberg P.D., 2013, Sydney Harbour: A systematic review of the science, Sydney Institute of Marine Science, Sydney, Australia. National Library of Australia Cataloging-in-Publication entry ISBN: 978-0-646-91493-0 Publisher: The Sydney Institute of Marine Science, Sydney, New South Wales, Australia Available on the internet from www.sims.org.au For further information please contact: SIMS, Building 19, Chowder Bay Road, Mosman NSW 2088 Australia T: +61 2 9435 4600 F: +61 2 9969 8664 www.sims.org.au ABN 84117222063 Cover Photo | Mike Banert North Head The light was changing every minute.
    [Show full text]
  • Jorge Carlos PENICHE-PÉREZ1, Carlos GONZÁLEZ-SALAS2, Harold VILLEGAS-HERNÁNDEZ2, Raúl DÍAZ-GAMBOA2, Alfonso AGUILAR-PERERA2, Sergio GUILLEN-HERNÁNDEZ2, and Gaspar R
    ACTA ICHTHYOLOGICA ET PISCATORIA (2019) 49 (2): 133–146 DOI: 10.3750/AIEP/02516 REPRODUCTIVE BIOLOGY OF THE SOUTHERN PUFFERFISH, SPHOEROIDES NEPHELUS (ACTINOPTERYGII: TETRAODONTIFORMES: TETRAODONTIDAE), IN THE NORTHERN COAST OFF THE YUCATAN PENINSULA, MEXICO Jorge Carlos PENICHE-PÉREZ1, Carlos GONZÁLEZ-SALAS2, Harold VILLEGAS-HERNÁNDEZ2, Raúl DÍAZ-GAMBOA2, Alfonso AGUILAR-PERERA2, Sergio GUILLEN-HERNÁNDEZ2, and Gaspar R. POOT-LÓPEZ2* 1Unidad de Ciencias del Agua, Centro de Investigación Científica de Yucatán, Cancún, Quintana Roo, México 2Departamento de Biología Marina, Facultad de Medicina Veterinaria y Zootecnia, Universidad Autónoma de Yucatán, Mérida, Yucatán, México Peniche-Pérez J.C., González-Salas C., Villegas-Hernández H., Díaz-Gamboa R., Aguilar-Perera A., Guillen- Hernández S., Poot-López G.R. 2019. Reproductive biology of the southern pufferfish, Sphoeroides nephelus (Actinopterygii: Tetraodontiformes: Tetraodontidae), in the northern coast off the Yucatan Peninsula, Mexico. Acta Ichthyol. Piscat. 49 (2): 133–146. Background. Overexploitation of fishery resources has led to the capture of alternative species of a lower trophic level, considered previously unprofitable or unfit for human consumption. The southern pufferfish, Sphoeroides nephelus (Goode et Bean, 1882), is a bycatch species of the recreational fishery in the USA and Mexico. Unlike other species of the genus Sphoeroides, there is no background on their reproductive cycle. Therefore, this study aimed to describe several reproductive traits (sex ratio, gonadal development, annual reproductive cycle, and fecundity) of specimens from the northern coast of the Yucatan Peninsula, Mexico. This kind of information might serve as a point of reference for its potential use either in the pharmaceutical industry, aquarium trade, as well as in aquaculture.
    [Show full text]
  • EDGE of EXISTENCE 1Prioritising the Weird and Wonderful 3Making an Impact in the Field 2Empowering New Conservation Leaders A
    EDGE OF EXISTENCE CALEB ON THE TRAIL OF THE TOGO SLIPPERY FROG Prioritising the Empowering new 10 weird and wonderful conservation leaders 1 2 From the very beginning, EDGE of Once you have identified the animals most in Existence was a unique idea. It is the need of action, you need to find the right people only conservation programme in the to protect them. Developing conservationists’ world to focus on animals that are both abilities in the countries where EDGE species YEARS Evolutionarily Distinct (ED) and Globally exist is the most effective and sustainable way to Endangered (GE). Highly ED species ensure the long-term survival of these species. have few or no close relatives on the tree From tracking wildlife populations to measuring of life; they represent millions of years the impact of a social media awareness ON THE of unique evolutionary history. Their campaign, the skill set of today’s conservation GE status tells us how threatened they champions is wide-ranging. Every year, around As ZSL’s EDGE of Existence conservation programme reaches are. ZSL conservationists use a scientific 10 early-career conservationists are awarded its first decade of protecting the planet’s most Evolutionarily framework to identify the animals that one of ZSL’s two-year EDGE Fellowships. With Making an impact are both highly distinct and threatened. mentorship from ZSL experts, and a grant to set in the field Distinct and Globally Endangered animals, we celebrate 10 The resulting EDGE species are unique up their own project on an EDGE species, each 3 highlights from its extraordinary work animals on the verge of extinction – the Fellow gains a rigorous scientific grounding Over the past decade, nearly 70 truly weird and wonderful.
    [Show full text]
  • Fish, Various Invertebrates
    Zambezi Basin Wetlands Volume II : Chapters 7 - 11 - Contents i Back to links page CONTENTS VOLUME II Technical Reviews Page CHAPTER 7 : FRESHWATER FISHES .............................. 393 7.1 Introduction .................................................................... 393 7.2 The origin and zoogeography of Zambezian fishes ....... 393 7.3 Ichthyological regions of the Zambezi .......................... 404 7.4 Threats to biodiversity ................................................... 416 7.5 Wetlands of special interest .......................................... 432 7.6 Conservation and future directions ............................... 440 7.7 References ..................................................................... 443 TABLE 7.2: The fishes of the Zambezi River system .............. 449 APPENDIX 7.1 : Zambezi Delta Survey .................................. 461 CHAPTER 8 : FRESHWATER MOLLUSCS ................... 487 8.1 Introduction ................................................................. 487 8.2 Literature review ......................................................... 488 8.3 The Zambezi River basin ............................................ 489 8.4 The Molluscan fauna .................................................. 491 8.5 Biogeography ............................................................... 508 8.6 Biomphalaria, Bulinis and Schistosomiasis ................ 515 8.7 Conservation ................................................................ 516 8.8 Further investigations .................................................
    [Show full text]
  • Study on the Ethiopian Freshwater Molluscs, Especially on Identification, Distribution and Ecology of Vector Snails of Human Schistosomiasis
    Jap. J. Trop. Med. Hyg., Vol. 3, No. 2, 1975, pp. 107-134 107 STUDY ON THE ETHIOPIAN FRESHWATER MOLLUSCS, ESPECIALLY ON IDENTIFICATION, DISTRIBUTION AND ECOLOGY OF VECTOR SNAILS OF HUMAN SCHISTOSOMIASIS HIROSHI ITAGAKI1, NORIJI SUZUKI2, YOICHI ITO2, TAKAAKI HARA3 AND TEFERRA WONDE4 Received for publication 17 February 1975 Abstract: Many surveys were carried out in Ethiopia from January 1969 to January 1971 to study freshwater molluscs, especially the intermediate and potential host snails of Schistosoma mansoni and S. haematobium, to collect their ecological data, and to clarify the distribution of the snails in the country. The gastropods collected consisted of two orders, the Prosobranchia and Pulmonata. The former order contained three families (Thiaridae, Viviparidae and Valvatidae) and the latter four families (Planorbidae, Physidae, Lymnaeidae and Ancylidae). The pelecypods contained four families : the Unionidae, Mutelidae, Corbiculidae and Sphaeriidae. Biomphalaria pfeifferi rueppellii and Bulinus (Physopsis)abyssinicus are the most important hosts of S. mansoniand S. haematobium respectively. The freshwater snail species could be grouped into two distibution patterns, one of which is ubiquitous and the other sporadic. B. pfeifferirueppellii and Bulinus sericinus belong to the former pattern and Biomphalaria sudanica and the members of the subgenus Physopsis to the latter. Pictorial keys were prepared for field workers of schistosomiasis to identify freshwater molluscs in Ethiopia. Habitats of bulinid and biomphalarian snails were ecologically surveyed in connection with the epidemiology of human schistosomiasis. Rain falls and nutritional conditions of habitat appear to influence the abundance and distribution of freshwater snails more seriously than do temperature and pH, but water current affects the distribution frequently.
    [Show full text]
  • Reproductive Biology of the Yellowspotted Puffer Torquigener Flavimaculosus (Osteichthyes: Tetraodontidae) from Gulf of Suez, Egypt
    Egyptian Journal of Aquatic Biology & Fisheries Zoology Department, Faculty of Science, Ain Shams University, Cairo, Egypt. ISSN 1110 – 6131 Vol. 23(3): 503 – 511 (2019) www.ejabf.journals.ekb.eg Reproductive biology of the Yellowspotted Puffer Torquigener flavimaculosus (Osteichthyes: Tetraodontidae) from Gulf of Suez, Egypt. Amal M. Ramadan* and Magdy M. Elhalfawy Fish reproduction and spawning laboratory, Aquaculture Division, National Institute of Oceanography and Fisheries, Egypt. *Corresponding author: [email protected] ARTICLE INFO ABSTRACT Article History: The present study assesses reproductive biology of Yellowspotted Received: May 1, 2019 Puffer Torquigener flavimaculosus, were collected seasonally from Accepted: Aug. 29, 2019 commercial catches at the Attaka fishing harbor in Suez from winter 2017 Online: Sept. 2019 until autumn 2018. The sex ratio was found 1:1.08 for male and female, _______________ respectively. The fish length at first sexual maturity (L50) was 8.2 cm for males and 9.5 cm for females. In addition, the allometric pattern of gonadal Keywords: growth was studied to validate the use of the gonado-somatic index (GSI) in Gulf Suez assessments of the reproductive cycle. The highest peak of GSI (10.5 ± T. flavimaculosus 1.012%) and (4.3 ± 0.084%) for female and male were recorded in summer, Yellowspotted Puffer respectively. Values for hepato-somatic index (HSI) is very high and strong Gonado-somatic index inverse relationship with gonado-somatic index (GSI) we inferred that lipid Hepato-somatic index reserves in the liver play an important role in gonad maturation and Somatic condition factor spawning. Somatic condition factor (Kr) also varied, albeit less so, Spawning throughout the year, suggesting that body fat and muscle play lesser roles in providing energy for reproduction.
    [Show full text]
  • Annual Report 2012 English
    Annual Report 2012 Annual Report 2012 The Mohamed bin Zayed Species Conservation Fund provides financial support to species conservation projects worldwide. In 2012, The Mohamed bin Zayed Species Conservation Fund supported 217 projects in 75 countries with more than $1.5m. More than $1.36m was granted to species listed as Critically Endangered, Endangered, or Vulnerable by the IUCN Red List. Your Highness In 2012 the Fund has been able to greatly aid the global effort to conserve the diversity of life by continuing its success and giving $1.5m to more than 200 projects worldwide. Since its inception, the Fund has now disbursed more than $8.7m to targeted species conservation work, implemented through nearly 825 projects in more than 125 countries across six continents. The impact of the Fund continues to amaze me. Among the more than 200 projects supported in 2012, the financial support provided by the Fund helped train a pilot in Kenya who is now patrolling rhino habitat for poachers; it helped locate the breeding grounds of a sea bird previously thought to be extinct; it aided in the discovery of several new tree species in Mexico and many new species of spiders in India; it protected the habitat of a butterfly in Nepal and that of a cave-dwelling amphibian in Croatia. The stories of success are replicated across many species, in many locations across the globe. In 2012, the Fund received more than 1,500 grant applications – a statistic clearly indicating the global urgency of species conservation and the popularity of the Fund.
    [Show full text]
  • Laboratory Feeding of Bulinus Truncatus and Bulinus Globosus with Tridax Procumbens Leaves
    Vol. 5(3), pp. 31-35, March 2013 DOI: 10.5897/JPVB 13.0109 Journal of Parasitology and ISSN 2141-2510 © 2013 Academic Journals http://www.academicjournals.org/JPVB Vector Biology Full Length Research Paper Laboratory feeding of Bulinus truncatus and Bulinus globosus with Tridax procumbens leaves O. M. Agbolade*, O. W. Lawal and K. A. Jonathan Department of Plant Science and Applied Zoology, Parasitology and Medical Entomology Laboratory, Olabisi Onabanjo University, P.M.B. 2002, Ago-Iwoye, Ogun State, Nigeria. Accepted 18 March, 2013 Suitability of Tridax procumbens leaves in laboratory feeding of Bulinus truncatus and Bulinus globosus was assessed in comparison with Lactuca sativa between September and October, 2011. The snails were collected from Eri-lope stream in Ago-Iwoye, while T. procumbens were collected from the Mini Campus of the Olabisi Onabanjo University, Ago-Iwoye, Ijebu North, Southwestern Nigeria. For B. truncatus, fresh, sun-dried and oven-dried T. procumbens were used, while only fresh T. procumbens were used for B. globosus. The mean percentage survivals of B. truncatus fed with fresh, sun-dried and oven-dried T. procumbens compared with those of the corresponding control snails showed no significant difference (2 = 0.51, 1.85, and 2.21, respectively). B. truncatus fed with fresh T. procumbens had the highest mean live-weight percentage increase (46.4%) as compared to those fed with sun-dried and oven-dried (2 = 45.65). The mean percentage survival of B. globosus fed with fresh T. procumbens (79.2%) was similar with that of the control (84.6%) (2 = 0.18).
    [Show full text]