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Phytoextraction and Phytostabilisation Approaches of Heavy Metal Remediation in Acid Mine Drainage with Case Studies: a Review - 6129
Mang – Ntushelo: Phytoextraction and phytostabilisation approaches of heavy metal remediation in acid mine drainage with case studies: a review - 6129 - PHYTOEXTRACTION AND PHYTOSTABILISATION APPROACHES OF HEAVY METAL REMEDIATION IN ACID MINE DRAINAGE WITH CASE STUDIES: A REVIEW MANG, K. C. – NTUSHELO, K.* Department of Agriculture and Animal Health, University of South Africa, South Africa (e-mail: [email protected]; phone: +27-(0)-748-366-063) *Corresponding author e-mail: [email protected]; phone: +27-(0)-789-027-944 (Received 5th Aug 2018; accepted 5th Oct 2018) Abstract. This review discusses phytoextraction and phytostabilisation of acid mine drainage (AMD) alongside with their benefits and limitations with case studies. Furthermore, plants associated with these two approaches of phytoremediation and impact of AMD on aquatic macrophytes used for phytoremediation were also reviewed. Both phytoextraction and phytostabilisation approaches are promising technologies in remediating AMD. However, their limitation of low metal removal and the lack of knowledge of minimum amendments required for their effective remediation call for the proposal, herein made, to combine aquatic macrophytes, as well as include plants from a wide range of families capable of phytoextraction and phytostabilisation in the remediation of AMD. Keywords: aquatic macrophytes, conventional treatment, hyperaccumulators, phytoremediation Introduction The activities of the mine cause the production of acidic water that flows down to nearby water bodies causing long term impairment to biodiversity and waterways. The acidic water produced by the mines is termed acid mine drainage (AMD). Acid mine drainage also known as acid rock drainage is a process that occurs as a result of the contact between oxygenated water and mineral pyrite which leads to the oxidation of the pyrite and the production of acids (Evangelou, 1995; Blowes et al., 2003). -
Aquatic Macrophyte Spirodela Polyrrhiza As a Phytoremediation Tool in Polluted Wetland Water from Eloor, Ernakulam District, Kerala
IOSR Journal Of Environmental Science, Toxicology And Food Technology (IOSR-JESTFT) e-ISSN: 2319-2402,p- ISSN: 2319-2399. Volume 5, Issue 1 (Jul. - Aug. 2013), PP 51-58 www.Iosrjournals.Org Aquatic macrophyte Spirodela polyrrhiza as a phytoremediation tool in polluted wetland water from Eloor, Ernakulam District, Kerala. Anil Loveson, Rajathy Sivalingam and Syamkumar R. School of Environmental Studies, Cochin University Of Science and Technology Abstract: This study involved a laboratory experiment on the efficiency of the plant duckweed Spirodela polyrrhiza in improving the quality of two polluted wetlands of Eloor industrial area, Ernakulam, Kerala. The efficiency was tested by measuring some of physicochemical characteristics of the control and plant treatments after each eight days. All the parameters show considerable rate of reduction. In wetland I, The highest rates of reduction after 8 days of treatment were for heavy metals, accounting 95%, 79%, and 66% for Lead, Copper and Zinc, respectively, followed by 53% for Chromium, 45% for Mercury, 26% for Cobalt, 20% for manganese and 7% for Nickel. Other factors like pH, BOD, COD, Nitrate, Phosphate , sulphate, TDS, TSS and Turbidity reduced by 12%, 37%, 49%, 100%, 36%, 16%, 53%,85% and 52% respectively. In wetland II also heavy metals were removed with Cd(100%), Fe(98%), Pb(91%), Cu(74%) Zn(62%) and Hg(53%) removed more efficiently. The results showed that this aquatic plant can be successfully used for wastewater pollutants removal. Other physiochemical parameters like pH, BOD, COD, Nitrate, Phosphate , sulphate, TDS, TSS and Turbidity reduced by 14%, 40%, 60%, 100%, 38%, 65%, 73%, 85%, and 51% after 8 days of treatment. -
Nature Conservation
J. Nat. Conserv. 11, – (2003) Journal for © Urban & Fischer Verlag http://www.urbanfischer.de/journals/jnc Nature Conservation Constructing Red Numbers for setting conservation priorities of endangered plant species: Israeli flora as a test case Yuval Sapir1*, Avi Shmida1 & Ori Fragman1,2 1 Rotem – Israel Plant Information Center, Dept. of Evolution, Systematics and Ecology,The Hebrew University, Jerusalem, 91904, Israel; e-mail: [email protected] 2 Present address: Botanical Garden,The Hebrew University, Givat Ram, Jerusalem 91904, Israel Abstract A common problem in conservation policy is to define the priority of a certain species to invest conservation efforts when resources are limited. We suggest a method of constructing red numbers for plant species, in order to set priorities in con- servation policy. The red number is an additive index, summarising values of four parameters: 1. Rarity – The number of sites (1 km2) where the species is present. A rare species is defined when present in 0.5% of the area or less. 2. Declining rate and habitat vulnerability – Evaluate the decreasing rate in the number of sites and/or the destruction probability of the habitat. 3. Attractivity – the flower size and the probability of cutting or exploitation of the plant. 4. Distribution type – scoring endemic species and peripheral populations. The plant species of Israel were scored for the parameters of the red number. Three hundred and seventy (370) species, 16.15% of the Israeli flora entered into the “Red List” received red numbers above 6. “Post Mortem” analysis for the 34 extinct species of Israel revealed an average red number of 8.7, significantly higher than the average of the current red list. -
Staff, Visiting Scientists and Graduate Students 2011
Staff, Visiting Scientists and Graduate Students at the Pescara Center December 2011 2 Contents ICRANet Faculty Staff……………………………………………………………………. p. 17 Adjunct Professors of the Faculty .……………………………………………………… p. 35 Lecturers…………………………………………………………………………………… p. 72 Research Scientists ……………………………………………………………………….. p. 92 Short-term Visiting Scientists …………………………………………………………... p. 99 Long-Term Visiting Scientists …………………………………………………………... p. 117 IRAP Ph. D. Students ……………………………………………………………………. p. 123 IRAP Ph. D. Erasmus Mundus Students………………………………………………. p. 142 Administrative and Secretarial Staff …………………………………………………… p. 156 3 4 ICRANet Faculty Staff Belinski Vladimir ICRANet Bianco Carlo Luciano University of Rome “Sapienza” and ICRANet Einasto Jaan Tartu Observatory, Estonia Novello Mario Cesare Lattes-ICRANet Chair CBPF, Rio de Janeiro, Brasil Rueda Jorge A. University of Rome “Sapienza” and ICRANet Ruffini Remo University of Rome “Sapienza” and ICRANet Vereshchagin Gregory ICRANet Xue She-Sheng ICRANet 5 Adjunct Professors Of The Faculty Aharonian Felix Albert Benjamin Jegischewitsch Markarjan Chair Dublin Institute for Advanced Studies, Dublin, Ireland Max-Planck-Institut für Kernphysis, Heidelberg, Germany Amati Lorenzo Istituto di Astrofisica Spaziale e Fisica Cosmica, Italy Arnett David Subramanyan Chandrasektar- ICRANet Chair University of Arizona, Tucson, USA Chakrabarti Sandip P. Centre for Space Physics, India Chardonnet Pascal Université de la Savoie, France Chechetkin Valeri Mstislav Vsevolodich Keldysh-ICRANet Chair Keldysh institute -
Automated Imaging of Duckweed Growth and Development 2 3 Kevin L
bioRxiv preprint doi: https://doi.org/10.1101/2021.07.21.453240; this version posted July 22, 2021. 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 4.0 International license. 1 Automated imaging of duckweed growth and development 2 3 Kevin L. Cox Jr.1,2, Jordan Manchego3, Blake C. Meyers1,4, Kirk J. Czymmek1 *, Alex Harkess3,5 * 4 5 1 Donald Danforth Plant Science Center, St. Louis, MO 63132 6 2 Howard Hughes Medical Institute, Chevy Chase, MD 20815 7 3 HudsonAlpha Institute for Biotechnology, Huntsville, AL 35806 8 4 Department of Biology, University of Missouri, Columbia, MO 65211 9 5 Department of Crop, Soil, and Environmental Sciences, Auburn University, Auburn, AL 36849 10 11 *Correspondence: Alex Harkess ([email protected]) or Kirk J. Czymmek 12 ([email protected]) 13 14 ORCID IDs: 15 K.L. Cox: 0000-0003-2524-8988 16 J. Manchego: XXXX-XXXX-XXXX-XXXX 17 B.C. Meyers: 0000-0003-3436-6097 18 K.J. Czymmek: 0000-0002-5471-7395 19 A. Harkess: 0000-0002-2035-0871 20 21 Keywords: Lemna, time-lapse, PlantCV, microscopy bioRxiv preprint doi: https://doi.org/10.1101/2021.07.21.453240; this version posted July 22, 2021. 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 4.0 International license. -
Phylogeny and Phylogenetic Nomenclature of the Campanulidae Based on an Expanded Sample of Genes and Taxa
Systematic Botany (2010), 35(2): pp. 425–441 © Copyright 2010 by the American Society of Plant Taxonomists Phylogeny and Phylogenetic Nomenclature of the Campanulidae based on an Expanded Sample of Genes and Taxa David C. Tank 1,2,3 and Michael J. Donoghue 1 1 Peabody Museum of Natural History & Department of Ecology & Evolutionary Biology, Yale University, P. O. Box 208106, New Haven, Connecticut 06520 U. S. A. 2 Department of Forest Resources & Stillinger Herbarium, College of Natural Resources, University of Idaho, P. O. Box 441133, Moscow, Idaho 83844-1133 U. S. A. 3 Author for correspondence ( [email protected] ) Communicating Editor: Javier Francisco-Ortega Abstract— Previous attempts to resolve relationships among the primary lineages of Campanulidae (e.g. Apiales, Asterales, Dipsacales) have mostly been unconvincing, and the placement of a number of smaller groups (e.g. Bruniaceae, Columelliaceae, Escalloniaceae) remains uncertain. Here we build on a recent analysis of an incomplete data set that was assembled from the literature for a set of 50 campanulid taxa. To this data set we first added newly generated DNA sequence data for the same set of genes and taxa. Second, we sequenced three additional cpDNA coding regions (ca. 8,000 bp) for the same set of 50 campanulid taxa. Finally, we assembled the most comprehensive sample of cam- panulid diversity to date, including ca. 17,000 bp of cpDNA for 122 campanulid taxa and five outgroups. Simply filling in missing data in the 50-taxon data set (rendering it 94% complete) resulted in a topology that was similar to earlier studies, but with little additional resolution or confidence. -
Wild Flowers of the Cornish Valleys and Lizard Peninsula
Wild Flowers of the Cornish Valleys and Lizard Peninsula Naturetrek Tour Report 19 – 22 May 2021 Sea Sandwort View Burnet Rose Thrift Report and images compiled by Pip O’Brien Naturetrek Mingledown Barn Wolf’s Lane Chawton Alton Hampshire GU34 3HJ UK Naturetrek T: +44 (0)1962 733051 E: [email protected] W: www.naturetrek.co.uk Tour Report Wild Flowers of the Cornish Valleys & Lizard Peninsula Tour participants: Pip O’Brien (Leader) with six Naturetrek clients Day 1 Wednesday 19th May The group met up in the car park of our Helston hotel after some epic trips across England. Everyone was determined to make the most of sunshine on the first day of what for many, was their first real trip out in almost 18 months. We headed straight out on the Lizard peninsula past Culdrose Naval station and through the pretty village of Gunwalloe, down to Church Cove. Every hedge was hazed navy blue with Bluebells and clouds of Cow Parsley brushed the van on the narrow lanes. In glorious late afternoon sunshine, we wandered out of the car park towards the cove. The Cornish hedges were covered in the glossy green leaves of Sea Beet (Beta maritima) interspersed with Danish Scurvygrass (Cochlearia danica) that was coming to the end of its flowering season. As we got nearer to the beach, one wall was covered from top to bottom with a blanket of Sea Sandwort (Honckenya peploides) in full flower. The cliffs were dotted with Common Scurvygrass (Cochlearia officinalis) and huge mounds of Thrift (Armeria maritima). Up on top of the cliffs we came across our first blue Spring Squills (Scilla verna). -
Biodiversity Action Plan
CORRIB DEVELOPMENT BIODIVERSITY ACTION PLAN 2014-2019 Front Cover Images: Sruwaddacon Bay Evening Lady’s Bedstraw at Glengad Green-veined White Butterfly near Leenamore Common Dolphin Vegetation survey at Glengad CORRIB DEVELOPMENT BIODIVERSITY ACTION PLAN 1 Leenamore Inlet CORRIB DEVELOPMENT 2 BIODIVERSITY ACTION PLAN LIST OF CONTENTS 2.4 DATABASE OF BIODIVERSITY 39 3 THE BIODIVERSITY A CKNOWLEDGEMENTS 4 ACTION PLAN 41 FOREWORd 5 3.1 ESTABLISHING PRIORITIES FOR CONSERVATION 41 EXECUTIVE SUMMARY 6 3.1.1 HABITATS 41 1 INTRODUCTION 8 3.1.2 SPECIES 41 1.1 BIODIVERSITY 8 3.2 AIMS 41 1.1.1 WHAT is biodiversity? 8 3.3 OBJECTIVES AND acTIONS 42 1.1.2 WHY is biodiversity important? 8 3.4 MONITORING, EVALUATION 1.2 INTERNATIONAL AND NATIONAL CONTEXT 9 AND IMPROVEMENT 42 1.2.1 CONVENTION on BIODIVERSITY 9 3.4.1 MONITORING 42 1.2.2 NATIONAL and local implementation 9 3.4.2 EVALUATION and improvement 43 1.2.3 WHY A biodiversity action plan? 10 TABLE 5 SUMMARY of obJECTIVES and actions for THE conservation of habitats and species 43 3.4.3 Reporting, commUNICATING and 2 THE CORRIB DEVELOPMENT VERIFICATION 44 AND BIODIVERSITY 11 3.4.3.1 ACTIONS 44 2.1 AN OVERVIEW OF THE CORRIB 3.4.3.2 COMMUNICATION 44 DEVELOPMENT 11 3.5 STAKEHOLDER ENGAGEMENT AND FIG 1 LOCATION map 11 PARTNERSHIPS FOR BIODIVERSITY 44 FIG 2 Schematic CORRIB DEVELOPMENT 12 3.5.1 S TAKEHOLDER engagement and CONSULTATION 44 2.2 DESIGNATED CONSERVATION SITES AND THE CORRIB GaS DEVELOPMENT 13 3.5.2 PARTNERSHIPS for biodiversity 44 3.5.3 COMMUNITY staKEHOLDER engagement 45 2.2.1 DESIGNATED -
Vermeulen / Johnston PLANTS
Vermeulen / Johnston PLANTS - Homeopathic and Medicinal Uses from a Botanical Family Perspective Reading excerpt PLANTS - Homeopathic and Medicinal Uses from a Botanical Family Perspective of Vermeulen / Johnston Publisher: Saltire Books http://www.narayana-verlag.com/b11643 In the Narayana webshop you can find all english books on homeopathy, alternative medicine and a healthy life. Copying excerpts is not permitted. Narayana Verlag GmbH, Blumenplatz 2, D-79400 Kandern, Germany Tel. +49 7626 9749 700 Email [email protected] http://www.narayana-verlag.com 16. Araliaceae 27/8/11 13:17 Page 485 FAMILY ARALIACEAE – ORDER APIALES Botanical Keys ⅷ Ivy and Ginseng family with 43 genera holding about 1450 species of rather stout-stemmed and little-branched shrubs or trees, often strong-smelling and with large and prominent scars from the fallen leaves. ⅷ Distribution: Worldwide, but centred in tropics. ⅷ Sister family to Apiaceae and by some authorities included in a broadly circum- scribed Apiaceae. ⅷ Leaves often compound, with broad, more or less sheathing leaf-bases. ⅷ Flowers small, in compound inflorescences, usually either capitate [head-like] or umbellate. ⅷ Fruit a globose drupe with several seeds. Ltd ⅷ Classified in order Apiales by both Cronquist and Dahlgren. ⅷ Compare other families in order Apiales: Apiaceae [Umbelliferae]; Pitto- sporaceae. ARALIACEAE IN HOMEOPATHYBooks Homeopathic name Common name Abbreviation Symptoms Aralia californica Elk-clover Aral-c. None Aralia hispida Bristly sarsaparilla Aral-h. 5–10 Aralia nudicaulis Wild sarsaparilla Aral-nu. None Aralia racemosa American spikenard Aral. c. 240 Aralia spinosa Devil’s-walking-stick Aral-sp. None Eleutherococcus senticosus Siberian ginseng Eleut. None 1Saltire 2 Ginseng Ginseng Gins. -
Red List of Vascular Plants of the Czech Republic: 3Rd Edition
Preslia 84: 631–645, 2012 631 Red List of vascular plants of the Czech Republic: 3rd edition Červený seznam cévnatých rostlin České republiky: třetí vydání Dedicated to the centenary of the Czech Botanical Society (1912–2012) VítGrulich Department of Botany and Zoology, Masaryk University, Kotlářská 2, CZ-611 37 Brno, Czech Republic, e-mail: [email protected] Grulich V. (2012): Red List of vascular plants of the Czech Republic: 3rd edition. – Preslia 84: 631–645. The knowledge of the flora of the Czech Republic has substantially improved since the second ver- sion of the national Red List was published, mainly due to large-scale field recording during the last decade and the resulting large national databases. In this paper, an updated Red List is presented and compared with the previous editions of 1979 and 2000. The complete updated Red List consists of 1720 taxa (listed in Electronic Appendix 1), accounting for more then a half (59.2%) of the native flora of the Czech Republic. Of the Red-Listed taxa, 156 (9.1% of the total number on the list) are in the A categories, which include taxa that have vanished from the flora or are not known to occur at present, 471 (27.4%) are classified as critically threatened, 357 (20.8%) as threatened and 356 (20.7%) as endangered. From 1979 to 2000 to 2012, there has been an increase in the total number of taxa included in the Red List (from 1190 to 1627 to 1720) and in most categories, mainly for the following reasons: (i) The continuing human pressure on many natural and semi-natural habitats is reflected in the increased vulnerability or level of threat to many vascular plants; some vulnerable species therefore became endangered, those endangered critically threatened, while species until recently not classified may be included in the Red List as vulnerable or even endangered. -
Industrial Wastewater Treatment Using Spirodela Polyrhiza
Journal of Pharmacognosy and Phytochemistry 2017; 6(4): 892-895 E-ISSN: 2278-4136 P-ISSN: 2349-8234 Industrial wastewater treatment using Spirodela JPP 2017; 6(4): 892-895 Received: 15-05-2017 polyrhiza Accepted: 16-06-2017 Vibha Yadav Vibha Yadav, B Mehra and Abhishek James Department of Environmental Science and NRM, College of Forestry, SHUATS, Allahabad, Abstract Uttar Pradesh, India Industrial wastewater treatment can be done by using Spirodela polyrhiza in different retention time. This study investigates the use of Spirodela polyrhiza improves the quality of industrial wastewater B Mehra parameters like negative log of hydrogen ion concentration (PH), Electrical Conductivity (EC), Chemical Department of Environmental oxygen demand (COD), Total hardness, sulphates, Total dissolve solids (T.D.S.). This study also Science and NRM, College of signifies the Spirodela polyrhiza can be used for accumulation of toxic metals. It was found that after 60 Forestry, SHUATS, Allahabad, days retention time the reduced level of pH was 7. At initial, maximum chloride content was 214.93 mg/l Uttar Pradesh, India however the minimum Chloride content after treatment was 173.70 mg/l. Value of total hardness present Abhishek James in water before treatment was 1603 mg/l however the minimum hardness after treatment was 968mg/l. Department of Environmental Maximum COD at initial time was 202.66 mg/l however the minimum COD after retention time was Science and NRM, College of found as 64mg/l. Amount of Chromium (VI) before introducing macrophyte was 0.0401 mg/l however Forestry, SHUATS, Allahabad, the minimum Chromium (VI) after introducing macrophyte was 0.0233mg/l. -
A Study on Arsenic and Copper Extraction Capacity of Spirodela Polyrhiza from Water
Vol. 6(1), pp. 1-9, January 2015 DOI: 10.5897/JCECT2014.0342 Articles number: F083B8B50061 Journal of Civil Engineering and Construction ISSN 1996-0816 ©2014 Copyright © 2015 Technology Author(s) retain the copyright of this article http://www.academicjournals.org/JCECT Full Length Research Paper A study on arsenic and copper extraction capacity of Spirodela polyrhiza from water Sourav Ray1*, S. Islam, D. R. Tumpa1, M. A. Kayum1 and S. D. Shuvro2 1Department of Construction Management, Nelson Mandela Metropolitan University, Port Elizabeth, South Africa. 2Business School, Nelson Mandela Metropolitan University, Port Elizabeth, South Africa. Received 17 October, 2014; Accepted 3 December, 2014 Heavy metals such as arsenic (As), copper (Cu), chromium (Cr), Hg, lead (Pb) and cobalt (Co) cause adverse effects on living organisms by their toxic nature. To remove heavy metals, a variety of conventional treatment technologies have been tested which are not economical and user friendly. So, natural remediation method such as phytoremediation is becoming more popular where plants are used. Phytoremediation is a cost effective and eco-friendly method. This paper accounts the study to exercise the phytoremediation potential of the aquatic plant Spirodela polyrhiza for arsenic and copper removal from water. To carry out the study, six plastic bowls each carrying 1 L distilled water were taken where arsenic and copper of known concentration was added for preparing a solution, which contained 1.0, 0.9, 0.7, 0.6, 0.5, and 0.3 mg/L of arsenic and 5.0, 4.6, 4.2, 3.8, 3.4 and 3.0 mg/L of copper.