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Phytotoxic Effects of Benzimidazole Fungicides on Bedding Plants
J. AMER. SOC. HORT. SCI. 121(6):1095–1102. 1996. Phytotoxic Effects of Benzimidazole Fungicides on Bedding Plants Marc W. van Iersel1 and Bruce Bugbee Crop Physiology Laboratory, Department of Plants, Soils, and Biometeorology, Utah State University, Logan, UT 84322-4820 Additional index words. Benlate DF, photosynthesis, petunia, Petunia ×hybrida Abstract. Benzimidazoles are effective and widely used fungicides, but they may be phytotoxic. We studied the effects of a single drench application of six benzimidazoles and one acetanilide fungicide on photosynthetic gas exchange, growth, development, and nutrient levels of four species of bedding plants in twenty growth-chamber and four greenhouse studies. Daily carbon gain and carbon-use efficiency were calculated from continuous crop gas-exchange measurements in the growth chambers. The maximum labeled rate of Benlate DF caused a 7- to 10-day decrease in net photosynthesis and daily carbon gain in transplants of all species. It also caused pronounced interveinal chlorosis and a 2- to 3-day delay in flowering. Growth of Benlate DF-treated plants was reduced more at high (90%) than at low (60% to 80%) relative humidity. Benlate DF had severe effects on 2-week-old petunia (Petunia ×hybrida) seedlings in plug flats, reducing photosynthesis 25% to 57%. Cleary’s 3336 WP decreased photosynthesis in some trials. Benlate DF reduced photosyn- thesis within 24 hours, but 3336 WP effects did not become apparent until 1 week after the treatment. This suggests different modes of inhibition. 3336 WP also caused leaf-tip and marginal chlorosis in impatiens (Impatiens wallerana). Mertect 340-F was extremely phytotoxic but is not labeled for drench applications (it was included because of its chemical similarity to other benzimidazoles). -
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OCCASION This publication has been made available to the public on the occasion of the 50th anniversary of the United Nations Industrial Development Organisation. DISCLAIMER This document has been produced without formal United Nations editing. The designations employed and the presentation of the material in this document do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations Industrial Development Organization (UNIDO) concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries, or its economic system or degree of development. Designations such as “developed”, “industrialized” and “developing” are intended for statistical convenience and do not necessarily express a judgment about the stage reached by a particular country or area in the development process. Mention of firm names or commercial products does not constitute an endorsement by UNIDO. FAIR USE POLICY Any part of this publication may be quoted and referenced for educational and research purposes without additional permission from UNIDO. However, those who make use of quoting and referencing this publication are requested to follow the Fair Use Policy of giving due credit to UNIDO. CONTACT Please contact [email protected] for further information concerning UNIDO publications. For more information about UNIDO, please visit us at www.unido.org UNITED NATIONS INDUSTRIAL DEVELOPMENT ORGANIZATION Vienna International Centre, P.O. Box 300, 1400 Vienna, Austria Tel: (+43-1) 26026-0 · www.unido.org · [email protected] I Tfs I 9 - 1 - October 1989 ENVIRONMENT IMPACT ANALYSIS OF THE MANUFACTURE OF BENOMYL 1. -
Identifying and Prioritizing Chemicals with Uncertain Burden of Exposure: Opportunities for Biomonitoring and Health-Related Research
UCSF UC San Francisco Previously Published Works Title Identifying and Prioritizing Chemicals with Uncertain Burden of Exposure: Opportunities for Biomonitoring and Health-Related Research. Permalink https://escholarship.org/uc/item/341329w1 Journal Environmental health perspectives, 127(12) ISSN 0091-6765 Authors Pellizzari, Edo D Woodruff, Tracey J Boyles, Rebecca R et al. Publication Date 2019-12-18 DOI 10.1289/ehp5133 Peer reviewed eScholarship.org Powered by the California Digital Library University of California A Section 508–conformant HTML version of this article Review is available at https://doi.org/10.1289/EHP5133. Identifying and Prioritizing Chemicals with Uncertain Burden of Exposure: Opportunities for Biomonitoring and Health-Related Research Edo D. Pellizzari,1 Tracey J. Woodruff,2 Rebecca R. Boyles,3 Kurunthachalam Kannan,4 Paloma I. Beamer,5 Jessie P. Buckley,6 Aolin Wang,2 Yeyi Zhu,7,8 and Deborah H. Bennett9 (Environmental influences on Child Health Outcomes) 1Fellow Program, RTI International, Research Triangle Park, North Carolina, USA 2Program on Reproductive Health and the Environment, Department of Obstetrics, Gynecology and Reproductive Sciences, University of California, San Francisco, San Francisco, California, USA 3Bioinformatics and Data Science, RTI International, Research Triangle Park, North Carolina, USA 4Wadsworth Center, New York State Department of Health, Albany, New York, USA 5Department of Community, Environment and Policy, Zuckerman College of Public Health, University of Arizona, Tucson, Arizona, -
Some Nitrobenzenes and Other Industrial Chemicals (IARC
SOME NITROBENZENES AND OTHER INDUSTRIAL CHEMICALS SOME NITROBENZENES AND OTHER INDUSTRIAL CHEMICALS SOME NITROBENZENES AND OTHER INDUSTRIAL CHEMICALS VOLUME 123 IARC MONOGRAPHS ON THE EVALUATION OF CARCINOGENIC RISKS TO HUMANS SOME NITROBENZENES AND OTHER INDUSTRIAL CHEMICALS VOLUME 123 This publication represents the views and expert opinions of an IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, which met in Lyon, 9–16 October 2018 LYON, FRANCE - 2020 IARC MONOGRAPHS ON THE EVALUATION OF CARCINOGENIC RISKS TO HUMANS IARC MONOGRAPHS In 1969, the International Agency for Research on Cancer (IARC) initiated a programme on the evaluation of the carcinogenic risk of chemicals to humans involving the production of critically evaluated monographs on individual chemicals. The programme was subsequently expanded to include evaluations of carcinogenic risks associated with exposures to complex mixtures, lifestyle factors and biological and physical agents, as well as those in specific occupations. The objective of the programme is to elaborate and publish in the form of monographs critical reviews of data on carcinogenicity for agents to which humans are known to be exposed and on specific exposure situations; to evaluate these data in terms of human risk with the help of international working groups of experts in carcinogenesis and related fields; and to indicate where additional research efforts are needed. The lists of IARC evaluations are regularly updated and are available on the Internet athttp:// monographs.iarc.fr/. -
Evaluation of Silica As an Adsorbent for Carbendazim from Aqueous Solutions
International Journal of Engineering and Technical Research (IJETR) ISSN: 2321-0869, Volume-3, Issue-2, February 2015 Evaluation of Silica as an Adsorbent for Carbendazim from Aqueous Solutions Sergio L. Laurella, Cristian M. Pis Diez, Ileana D. Lick, Patricia E. Allegretti and Mauricio F. Erben reported that carbendazim causes endocrine disruption and Abstract― Adsorption of carbendazim onto silica has been adverse effects on the spermatogenesis in male rats [6]-[8]. studied. The influence of contact time, pH, ionic strength and O temperature has been determined. The adsorption isotherms can H be described by the Langmuir model. Adsorption appears to be N O more effective as pH increases and it is not significantly affected by ionic strength of the sample (except at high I values). NH CH3 Spectroscopic and thermogravimetric results suggest that carbendazim is adsorbed in its protonated form. Results indicate N that after the treatment with silica, roughly 90% carbendazim Fig.1: Molecular structure of carbendazim. can be removed from the aqueous solutions, making this adsorbent as a potential candidate for water treatment As many other pesticides and organic compounds do, processes. carbendazim is adsorbed by a variety of surfaces, and this fact carries several environmental and technological Index Terms― adsorption, carbendazim, pesticide, silica. consequences. Previous studies showed that the interaction between soil components and organic compounds bearing I. INTRODUCTION basic sites is rather complex, involving several sorption A pesticide is a substance or mixture of substances used to mechanisms [9], [10]. As early suggested by Kah and Brown destroy, prevent and/or repel certain plague. They can be [11], specific approaches to each compound is required for classified as herbicides, fungicides or insecticides. -
Predicting the Toxicities of Chemicals to Aquatic Animal Species
Predicting the Toxicities of Chemicals to Aquatic Animal Species Dale Hoff4 Wade Lehmann1 Anita Pease2 Sandy Raimondo3 Chris Russom4 Tom Steeger2 U.S. Environmental Protection Agency 1 Office of Water, Washington, DC 2 Office of Pesticide Programs, Washington, DC 3 Office of Research and Development, Gulf Ecology Division 4 Office of Research and Development, Mid-Continent Ecology Division October 27, 2010 List of Figures ................................................................................................................................. 4 List of Tables .................................................................................................................................. 5 Glossary .......................................................................................................................................... 6 Abbreviations .................................................................................................................................. 8 1 Executive Summary .............................................................................................................. 10 2 Introduction ........................................................................................................................... 11 3 General Overview of OPP and OW Data Requirements ...................................................... 13 3.1 OPP Data Requirements ................................................................................................... 13 3.2 OW Data Requirements ...................................................................................................