Life Cycle Assessment on Different Synthetic Routes of ZIF-8 Nanomaterials
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Title Effect of Ph Values on the Formation and Solubility Of
CORE Metadata, citation and similar papers at core.ac.uk Provided by Kyoto University Research Information Repository Effect of pH Values on the Formation and Solubility of Zinc Title Compounds Takada, Toshio; Kiyama, Masao; Torii, Hideo; Asai, Author(s) Toshihiro; Takano, Mikio; Nakanishi, Norihiko Bulletin of the Institute for Chemical Research, Kyoto Citation University (1978), 56(5): 242-246 Issue Date 1978-12-20 URL http://hdl.handle.net/2433/76795 Right Type Departmental Bulletin Paper Textversion publisher Kyoto University Bull.Inst. Chem.Res., Kyoto Univ., Vol. 56, No. 5, 1978 Effect of pH Values on the Formation and Solubility of Zinc Compounds Toshio TAKADA,Masao KIYAMA,Hideo TORII, Toshihiro AsAI* Mikio TAKANO**,and Norihiko NAKANISHI** ReceivedJuly 31, 1978 Aqueoussuspensions, prepared by mixingthe solution of NaOHand that ofzinc sulfate,chloride or nitrate,were subjected to agingat 25,50, and 70°C. Examinationof the productsby X-ray pow- der diffractionshowed that zinc oxide,basic zinc sulfate, chloride and nitrate are formeddepending mainlyon the pH. Their solubilitiesin the suspensionmedia with differentpH valueswere deter- mined at 25°C. INTRODUCTION In our laboratory, iron oxides and oxide hydroxides were prepared by wet methods such as the hydrolysis and slow oxidation of aqueous solutions of iron salts. The condi- tions for the formation of the oxides and oxide hydroxides') were reported together with their properties.2l The formation of a variety of products must be considered to be due to the difference in the nature -
Assessment of Forest Pests and Diseases in Protected Areas of Georgia Final Report
Assessment of Forest Pests and Diseases in Protected Areas of Georgia Final report Dr. Iryna Matsiakh Tbilisi 2014 This publication has been produced with the assistance of the European Union. The content, findings, interpretations, and conclusions of this publication are the sole responsibility of the FLEG II (ENPI East) Programme Team (www.enpi-fleg.org) and can in no way be taken to reflect the views of the European Union. The views expressed do not necessarily reflect those of the Implementing Organizations. CONTENTS LIST OF TABLES AND FIGURES ............................................................................................................................. 3 ABBREVIATIONS AND ACRONYMS ...................................................................................................................... 6 EXECUTIVE SUMMARY .............................................................................................................................................. 7 Background information ...................................................................................................................................... 7 Literature review ...................................................................................................................................................... 7 Methodology ................................................................................................................................................................. 8 Results and Discussion .......................................................................................................................................... -
How Water Quality in Transboundary River Systems Affects Water, Sanitation, and Foreign Policy
How Water Quality in Transboundary River Systems Affects Water, Sanitation, and Foreign Policy | 1 How Water Quality in Transboundary River Systems Affects Water, Sanitation, and Foreign Policy David Tipping, 2001 By David C. Tipping Edited by Yeareen Yun Disclaimer: The views and opinions expressed in this article are those of the author and do not necessarily reflect the official policy or position of any agency of the Australian government. Assumptions made within the analysis are not reflective of the position of any Australian government entity, or other organization or professional association. 1. INTRODUCTION Access to adequate water supply and sanitation is the core premise of local level water security. Effective management of transboundary river basin systems and water quality risks is therefore fundamental to social progress and quality of life. Improved water quality management benefits many individual lives in riparian nations, and, as demonstrated by the annual new year blessing of the fish migrations, society at large throughout the Mekong River Basin. In 2001, the author investigated the use of sustainable development indicators to improve the institutional effectiveness of international environmental management regimes. A new framework was designed to evaluate beneficial uses of water. In addition, a case study was developed on the Lower Mekong River Basin system, which integrated measures of water and environmental quality and socio-economic development. The research objectives were: (1) improving the understanding of water quality issues; (2) benchmarking water resources management performance at local, national and regional levels; and (3) enhancing technical and administrative capabilities of transboundary river basin management regimes through capacity development focused on the achievement of sustainable development objectives, and obligations and duties under international law. -
Assessment of Forest Pests and Diseases in Native Boxwood Forests of Georgia Final Report
Assessment of Forest Pests and Diseases in Native Boxwood Forests of Georgia Final report Dr. Iryna Matsiakh Forestry Department, Ukrainian National Forestry University (Lviv) Tbilisi 2016 TABLE OF CONTENT LIST OF TABLES AND FIGURES .................................................................................................................................. 2 ABBREVIATIONS AND ACRONYMS ........................................................................................................................... 5 EXECUTIVE SUMMARY .................................................................................................................................................. 6 INTRODUCTION .............................................................................................................................................................. 10 1. BACKGROUND INFORMATION ............................................................................................................................ 11 1.1. Biodiversity of Georgia ........................................................................................................................................ 11 1.2. Forest Ecosystems .................................................................................................................................................. 12 1.3. Boxwood Forests in Forests Habitat Classification ................................................................................. 14 1.4. Georgian Forests Habitat in the Context of Climate Change -
Guide 3 – Fish Farmer's Guide to Combating Parasitic
GUIDE 3 – FISH FARMER’S GUIDE TO COMBATING PARASITIC INFECTIONS IN COMMON CARP AQUACULTURE e-NIPO: 833-20-103-X A Series of ParaFishControl Guides to Combating Fish Parasite Infections in Aquaculture. Guide 3 This project has received funding from the European Union’s Horizon 2020 research and innovation programme under grant agreement No. 634429 (ParaFishControl). This output reflects only the author’s view and the European Union cannot be held responsible for any use that may be made of the information contained therein. Wherever the fish are, that's where we go. “ Richard Wagner “ Common carp is the third most cultivated freshwater species in the world. Carp aquaculture is usually performed in a semi-intensive manner, in earthen ponds, where parasitic diseases can easily compromise fish health, especially in the hot summer months, leading to production and economic losses. This guide provides useful information about the biological background of five parasites, their diagnostics and control measures. © A.S. Holzer List of Authors Dr Astrid S. Holzer, Principal Investigator and Team Leader Institute of Parasitology Biology Centre of the Czech Academy of Sciences, Czech Republic Email: [email protected] Dr Pavla Bartošová-Sojková, Researcher Institute of Parasitology Biology Centre of the Czech Academy of Sciences, Czech Republic Email: [email protected] Honorary Prof. Csaba Székely, Scientific Advisor and Team Leader Institute for Veterinary Medical Research, Centre for Agricultural Research, (former Hungarian Academy of Sciences), Hungary Email: [email protected] Dr Gábor Cech, Senior Researcher, Institute for Veterinary Medical Research, Centre for Agricultural Research, (former Hungarian Academy of Sciences), Hungary Email: [email protected] Dr Kálmán Molnár, Retired Scientific Advisor, Fish Pathology and Parasitology Research Team, Institute for Veterinary Medical Research, Centre for Agricultural Research (former Hungarian Academy of Sciences), Hungary Prof. -
Difference Between Haplontic and Diplontic Life Cycles
Difference Between Haplontic and Diplontic Life Cycles www.differencebetween.com Key Difference – Haplontic vs Diplontic Life Cycles In the context of biology, a biological life cycle is a sequence of changes a particular organism undergoes through means of reproduction (sexual or asexual) which finally returns to the original starting phase. This procedure differs from one organism to the other. During sexual reproduction, the life cycle includes the change of ploidy; the alternation of haploid (n) and diploid (2n) stages. Meiosis occurs during the change over from a diploid stage to a haploid stage. With regards to change of ploidy, life cycles are of three types. They are, haplontic, diplontic and haplodiplontic. In a haplontic life cycle, the haploid stage is typically multicellular and results in the formation of a diploid (2n) cell, which is a zygote. The zygote undergoes meiosis, which results in the formation of haploid (n) cells. In a diplontic life cycle, the diploid stage is typically multicellular, and meiosis occurs during gamete formation which results in the production of haploid (n) gametes. During fertilization, the haploid (n) gametes fuse together in the formation of a diploid (2n) zygote, and it mitotically divides and produces a multicellular diploid (2n) organism. This is the key difference between haplontic and diplontic life cycles. What is a Haplontic Life Cycle? Haplontic life cycle involves the formation of a haploid (n) single cell by the meiosis of a diploid (2n) zygote. This phenomenon could be explained with sporic meiosis – the process of formation of spores. In this process, the zygote mitotically divides and produces multicellular sporophyte which is diploid (2n). -
FINAL COMPASS Aquaculture Roundtable Brief
Science in Action: Exploring the Future of U.S. Aquaculture A COMPASS Roundtable on Ocean Aquaculture As the population continues to expand—both domestically and globally—identifying secure, safe sources of protein is a critical need. With two-thirds of the planet covered in water, it is logical to turn to the ocean as an arena for producing food. Globally, aquaculture is the fastest growing food sector,[i] underscoring the importance of understanding the scientific, policy, and social implications of ocean aquaculture. As with all types of cultivated food production, there are complex and interwoven challenges and opportunities in ocean aquaculture.[ii] Indigenous knowledge and current research can answer questions around environmental safeguards, ecological impacts, long-term sustainable use of marine resources, and the social dimensions of ocean aquaculture. While we’ve developed a deeper scientific understanding of aquaculture, there remains a gap between the state of the science, federal policy, and public perceptions of ocean aquaculture in the U.S.[iii] In order to help provide research insights on the science related to aquaculture, COMPASS convened a roundtable discussion with scientists and policymakers in July 2019. The Roundtable examined ways that science can inform safe, sustainable, and socially acceptable ocean aquaculture in the United States. In preparation, COMPASS staff examined the U.S. aquaculture landscape by speaking with more than 50 scientists, managers, policymakers, and tribal representatives. These stage-setting conversations reflected the key concerns surrounding ocean aquaculture such as best management practices, economics, pollution, interactions with wild populations, and climate change. They also highlighted some of the scientific, technological, and cultural advancements in contemporary aquaculture that could address and reduce some of the perceived risks. -
Toxicological Profile for Zinc
TOXICOLOGICAL PROFILE FOR ZINC U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry August 2005 ZINC ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. ZINC iii UPDATE STATEMENT A Toxicological Profile for Zinc, Draft for Public Comment was released in September 2003. This edition supersedes any previously released draft or final profile. Toxicological profiles are revised and republished as necessary. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology/Toxicology Information Branch 1600 Clifton Road NE Mailstop F-32 Atlanta, Georgia 30333 ZINC vi *Legislative Background The toxicological profiles are developed in response to the Superfund Amendments and Reauthorization Act (SARA) of 1986 (Public law 99-499) which amended the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA or Superfund). This public law directed ATSDR to prepare toxicological profiles for hazardous substances most commonly found at facilities on the CERCLA National Priorities List and that pose the most significant potential threat to human health, as determined by ATSDR and the EPA. The availability of the revised priority list of 275 hazardous substances was announced in the Federal Register on November 17, 1997 (62 FR 61332). For prior versions of the list of substances, see Federal Register notices dated April 29, 1996 (61 FR 18744); April 17, 1987 (52 FR 12866); October 20, 1988 (53 FR 41280); October 26, 1989 (54 FR 43619); October 17, 1990 (55 FR 42067); October 17, 1991 (56 FR 52166); October 28, 1992 (57 FR 48801); and February 28, 1994 (59 FR 9486). -
UNIVERSITY of CALIFORNIA, IRVINE Synthesis of Gallium Zinc
UNIVERSITY OF CALIFORNIA, IRVINE Synthesis of Gallium Zinc Oxynitride Solid Solution by Flame Spray Pyrolysis THESIS submitted in partial satisfaction of the requirements for the degree of MASTER OF SCIENCE In Chemical and Biomolecular Engineering by Ewa Richard Chukwu Thesis Committee: Assistant Professor Erdem Sasmaz, Chair Assistant Professor Iryna Zenyuk Associate Professor Ali Mohraz 2020 © 2020 Ewa Richard Chukwu DEDICATION To The Almighty God who only him knows the end of a journey right from the beginning. Do not fear, for I am with you; Do not be dismayed for I am your God; I will strength you and help you; I will uphold you with my right hand of righteousness. Isaiah 49:10 ii TABLE OF CONTENTS LIST OF FIGURES……………………………………………………………. .iv LIST OF TABLES……….………………………………………………………vi ACKNOWLEDGEMENT………………………………….…………………...vii ABSTRACT……………………………..……………………………………....viii CHAPTER 1: Introduction………………………………………………..…........1 CHAPTER 2: Literature Review…………………………..………….........….......4 CHAPTER 3: Experimentation..............................................................................27 CHAPTER 4: Results and Discussions……………...…………………...............34 CHAPTER 5: Conclusion and Recommendation….….…..……………..............50 CHAPTER 6: Future Work …………………..………………….…...................53 REFERENCES………..…...……………………………………….…….............69 APPENDIX A.............………………………………………………..…..............83 APPENDIX B.................……………………………………………..…..............86 ii LIST OF FIGURES Fig.1: Flame synthesis versus wet chemistry……………………………………....5 -
Survivability of Moss and Fungal Spores in Tests Simulating
Biological Sciences in Space, Vol.25 No.2-4, 83-92,Takahashi, 2011 Y. et al. Original Paper Survivability of Moss and Fungal spores irradiated for 30 min. On the other hand, a colony did not develop if the spores were Spores in Tests Simulating taken off the beads and irradiated for 10 min. Conditions of the ISS Outer Wall This indicates that UV does not penetrate to the other side of the beads, and so the spores on Yuichi Takahashi1*, Hirofumi Hashimoto2, that side can be protected from UV radiation. 3 1 ©2011 Jpn. Soc. Biol. Sci. Space; Article ID: Takuo Nakagawa and Shinpei Shibata 112502011 1Department of Astrophysics, Interactive Symbio- sphere Science, Yamagata University Graduate Key words; fungi, moss, spore, survivability, thermal cycle treatment, UV irradiation School of Science and Engineering, Kojirakawa- machi 1-4-12, Yamagata-City, Yamagata 990-8560, Introduction Japan 2 Institute of Space and Astronautical Science, There are many factors that can influence the survivability JAXA, Yoshinodai 3-1-1 Chuo-ku, Sagamihara- of terrestrial life (TL) in interstellar and interplanetary space, City, Kanagawa 252-5210, Japan for example full-spectrum electromagnetic radiation from 3Inspection room, Kojirakawa-Shiseidoh Hospital, the sun, temperature fluctuations, cosmic particle radiation, Higashihara-machi 1-12-26, Yamagata-City, Ya- vacuum, and microgravity. However, space conditions can magata 990-0034, Japan only be partially simulated in ground experiments. Recently, several experiments have investigated the possibility of TL Abstract survival in space, for example EXPOSE-E (ESA Human Space Flight (2010) Expose, http:// smsc.cnes.fr/EXPOSE/), BIORISK (Baranow et al., 2009; Novikova et al., 2010) and To investigate whether terrestrial life (TL) can BIOPAN (De la Torre Noetzel et al., 2007; Devara et al., survive in interstellar and interplanetary space, 2010), while another one, TANPOPO, will take place in the an experiment was performed to simulate near future. -
Botany 12Th (Presented by Biology Wing DIET KUD H.O.D Sushma Gupta H.O.D Renuka Nagpal and Rashpal Singh Under the Guidance of Sh
1 | Page Botany 12th (Presented by Biology Wing DIET KUD H.O.D Sushma Gupta H.O.D Renuka Nagpal and Rashpal Singh Under the Guidance of Sh. Devinder Handoo H.O.D I/c DIET Kud) Unit-01 Reproduction in Flowering Plants Unit-01Marks- 07 ❖ Asexual reproduction Asexual reproduction is a mode of reproduction by which offspring arise from a single parent, and inherit the genes of that parent only, it is reproduction which does not involve meiosis, or fertilization. A more stringent definition is agamogenesis which is reproduction without the fusion of gametes. Asexual reproduction is the primary form of reproduction for single-celled organisms such as the archaea, bacteria, and protists. Many plants and fungi reproduce asexually as well. While all prokaryotes reproduce asexually (without the formation and fusion of gametes), mechanisms for lateral gene transfer such as conjugation, transformation and transduction are sometimes likened to sexual reproduction. A lack of sexual reproduction is relatively rare among multicellular organisms, particularly animals, for reasons that are not completely understood. Current hypotheses suggest that asexual reproduction may have short term benefits when rapid population growth is important or in stable environments, while sexual reproduction offers a net advantage by allowing more rapid generation of genetic diversity, allowing adaptation to changing environments. Developmental constraints may underlie why few animals have relinquished sexual reproduction completely in their life-cycles. Contents • 1 Types o 1.1 Binary fission o 1.2 Budding o 1.3 Vegetative reproduction o 1.4 Spore formation o 1.5 Fragmentation o 1.6 Parthenogenesis o 1.7 Agamogenesis o 1.8 Apomixis and nucellar embryony • 2 Alternation between sexual and asexual reproduction 2 | Page • 3 Examples in animals Types of Asexual Reproduction 1. -
The Biogeomorphological Life Cycle of Poplars During the Fluvial Biogeomorphological Succession: a Special Focus on Populus Nigra L
Open Archive TOULOUSE Archive Ouverte ( OATAO ) OATAO is an open access repository that collects the work of Toulouse researchers and makes it freely available over the web where possible. This is an author-deposited version published in : http://oatao.univ- toulouse.fr/ Eprints ID : 11091 To link to this article : doi:10.1002/esp.3515 URL : http://dx.doi.org/10.1002/esp.3515 To cite this version : Corenblit, Dov and Steiger, Johannes and González, Eduardo and Gurnell, Angela M. and Charrier, Gaspard and Darrozes, José and Dousseau, Julien and Julien, Frédéric and Lambs, Luc and Larrue, Sébastien and Roussel, Erwan and Vautier, Franck and Voldoire, Olivier The biogeomorphological life cycle of poplars during the fluvial biogeomorphological succession: a special focus on Populus nigra L. (2014) Earth Surface Processes and Landforms . ISSN 0197- 9337 Any correspondance concerning this service should be sent to the repository administrator: [email protected] DOI: 10.1002/esp.3515 The biogeomorphological life cycle of poplars during the fluvial biogeomorphological succession: a special focus on Populus nigra L. D. Corenblit, 1,2 * J. Steiger, 1,2 E. González, 3 A. M. Gurnell, 4 G. Charrier, 1,2 J. Darrozes, 5 J. Dousseau, 1,2 F. Julien, 6 L. Lambs, 6 S. Larrue, 1,2 E. Roussel, 7 F. Vautier 7 and O. Voldoire 1,2 1 Clermont Université, Maison des Sciences de l ’Homme, 4 rue Ledru, 63057, Clermont-Ferrand Cedex 1, France 2 CNRS, UMR 6042, GEOLAB – Laboratoire de géographie physique et environnementale, 63057, Clermont-Ferrand,