Pathogen Environmental Monitoring Program (PEM)
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Genetic Engineering and Sustainable Crop Disease Management: Opportunities for Case-By-Case Decision-Making
sustainability Review Genetic Engineering and Sustainable Crop Disease Management: Opportunities for Case-by-Case Decision-Making Paul Vincelli Department of Plant Pathology, 207 Plant Science Building, College of Agriculture, Food and Environment, University of Kentucky, Lexington, KY 40546, USA; [email protected] Academic Editor: Sean Clark Received: 22 March 2016; Accepted: 13 May 2016; Published: 20 May 2016 Abstract: Genetic engineering (GE) offers an expanding array of strategies for enhancing disease resistance of crop plants in sustainable ways, including the potential for reduced pesticide usage. Certain GE applications involve transgenesis, in some cases creating a metabolic pathway novel to the GE crop. In other cases, only cisgenessis is employed. In yet other cases, engineered genetic changes can be so minimal as to be indistinguishable from natural mutations. Thus, GE crops vary substantially and should be evaluated for risks, benefits, and social considerations on a case-by-case basis. Deployment of GE traits should be with an eye towards long-term sustainability; several options are discussed. Selected risks and concerns of GE are also considered, along with genome editing, a technology that greatly expands the capacity of molecular biologists to make more precise and targeted genetic edits. While GE is merely a suite of tools to supplement other breeding techniques, if wisely used, certain GE tools and applications can contribute to sustainability goals. Keywords: biotechnology; GMO (genetically modified organism) 1. Introduction and Background Disease management practices can contribute to sustainability by protecting crop yields, maintaining and improving profitability for crop producers, reducing losses along the distribution chain, and reducing the negative environmental impacts of diseases and their management. -
Chesapeake Bay Trust Hypoxia Project
Chesapeake Bay dissolved oxygen profiling using a lightweight, low- powered, real-time inductive CTDO2 mooring with sensors at multiple vertical measurement levels Doug Wilson Caribbean Wind LLC Baltimore, MD Darius Miller SoundNine Inc. Kirkland, WA Chesapeake Bay Trust EPA Chesapeake Bay Program Goal Implementation Team Support This project has been funded wholly or in part by the United States Environmental Protection Agency under assistance agreement CB96341401 to the Chesapeake Bay Trust. The contents of this document do not necessarily reflect the views and policies of the Environmental Protection Agency, nor does the EPA endorse trade names or recommend the use of commercial products mentioned in this document. SCOPE 8: “…demonstrate a reliable, cost effective, real-time dissolved oxygen vertical monitoring system for characterizing mainstem Chesapeake Bay hypoxia.” Water quality impairment in the Chesapeake Bay, caused primarily by excessive long-term nutrient input from runoff and groundwater, is characterized by extreme seasonal hypoxia, particularly in the bottom layers of the deeper mainstem (although it is often present elsewhere). In addition to obvious negative impacts on ecosystems where it occurs, hypoxia represents the integrated effect of watershed-wide nutrient pollution, and monitoring the size and location of the hypoxic regions is important to assessing Chesapeake Bay health and restoration progress. Chesapeake Bay Program direct mainstem water quality monitoring has been by necessity widely spaced in time and location, with monthly or bi-monthly single fixed stations separated by several kilometers. The need for continuous, real time, vertically sampled profiles of dissolved oxygen has been long recognized, and improvements in hypoxia modeling and sensor technology make it achievable. -
Manual for Phytoplankton Sampling and Analysis in the Black Sea
Manual for Phytoplankton Sampling and Analysis in the Black Sea Dr. Snejana Moncheva Dr. Bill Parr Institute of Oceanology, Bulgarian UNDP-GEF Black Sea Ecosystem Academy of Sciences, Recovery Project Varna, 9000, Dolmabahce Sarayi, II. Hareket P.O.Box 152 Kosku 80680 Besiktas, Bulgaria Istanbul - TURKEY Updated June 2010 2 Table of Contents 1. INTRODUCTION........................................................................................................ 5 1.1 Basic documents used............................................................................................... 1.2 Phytoplankton – definition and rationale .............................................................. 1.3 The main objectives of phytoplankton community analysis ........................... 1.4 Phytoplankton communities in the Black Sea ..................................................... 2. SAMPLING ................................................................................................................. 9 2.1 Site selection................................................................................................................. 2.2 Depth ............................................................................................................................... 2.3 Frequency and seasonality ....................................................................................... 2.4 Algal Blooms................................................................................................................. 2.4.1 Phytoplankton bloom detection -
Zoonotic Diseases Fact Sheet
ZOONOTIC DISEASES FACT SHEET s e ion ecie s n t n p is ms n e e s tio s g s m to a a o u t Rang s p t tme to e th n s n m c a s a ra y a re ho Di P Ge Ho T S Incub F T P Brucella (B. Infected animals Skin or mucous membrane High and protracted (extended) fever. 1-15 weeks Most commonly Antibiotic melitensis, B. (swine, cattle, goats, contact with infected Infection affects bone, heart, reported U.S. combination: abortus, B. suis, B. sheep, dogs) animals, their blood, tissue, gallbladder, kidney, spleen, and laboratory-associated streptomycina, Brucellosis* Bacteria canis ) and other body fluids causes highly disseminated lesions bacterial infection in tetracycline, and and abscess man sulfonamides Salmonella (S. Domestic (dogs, cats, Direct contact as well as Mild gastroenteritiis (diarrhea) to high 6 hours to 3 Fatality rate of 5-10% Antibiotic cholera-suis, S. monkeys, rodents, indirect consumption fever, severe headache, and spleen days combination: enteriditis, S. labor-atory rodents, (eggs, food vehicles using enlargement. May lead to focal chloramphenicol, typhymurium, S. rep-tiles [especially eggs, etc.). Human to infection in any organ or tissue of the neomycin, ampicillin Salmonellosis Bacteria typhi) turtles], chickens and human transmission also body) fish) and herd animals possible (cattle, chickens, pigs) All Shigella species Captive non-human Oral-fecal route Ranges from asymptomatic carrier to Varies by Highly infective. Low Intravenous fluids primates severe bacillary dysentery with high species. 16 number of organisms and electrolytes, fevers, weakness, severe abdominal hours to 7 capable of causing Antibiotics: ampicillin, cramps, prostration, edema of the days. -
Chapter 2 Disease and Disease Transmission
DISEASE AND DISEASE TRANSMISSION Chapter 2 Disease and disease transmission An enormous variety of organisms exist, including some which can survive and even develop in the body of people or animals. If the organism can cause infection, it is an infectious agent. In this manual infectious agents which cause infection and illness are called pathogens. Diseases caused by pathogens, or the toxins they produce, are communicable or infectious diseases (45). In this manual these will be called disease and infection. This chapter presents the transmission cycle of disease with its different elements, and categorises the different infections related to WES. 2.1 Introduction to the transmission cycle of disease To be able to persist or live on, pathogens must be able to leave an infected host, survive transmission in the environment, enter a susceptible person or animal, and develop and/or multiply in the newly infected host. The transmission of pathogens from current to future host follows a repeating cycle. This cycle can be simple, with a direct transmission from current to future host, or complex, where transmission occurs through (multiple) intermediate hosts or vectors. This cycle is called the transmission cycle of disease, or transmission cycle. The transmission cycle has different elements: The pathogen: the organism causing the infection The host: the infected person or animal ‘carrying’ the pathogen The exit: the method the pathogen uses to leave the body of the host Transmission: how the pathogen is transferred from host to susceptible person or animal, which can include developmental stages in the environment, in intermediate hosts, or in vectors 7 CONTROLLING AND PREVENTING DISEASE The environment: the environment in which transmission of the pathogen takes place. -
Advances in the Monitoring of Algal Blooms by Remote Sensing: a Bibliometric Analysis
applied sciences Article Advances in the Monitoring of Algal Blooms by Remote Sensing: A Bibliometric Analysis Maria-Teresa Sebastiá-Frasquet 1,* , Jesús-A Aguilar-Maldonado 1 , Iván Herrero-Durá 2 , Eduardo Santamaría-del-Ángel 3 , Sergio Morell-Monzó 1 and Javier Estornell 4 1 Instituto de Investigación para la Gestión Integrada de Zonas Costeras, Universitat Politècnica de València, C/Paraninfo, 1, 46730 Grau de Gandia, Spain; [email protected] (J.-A.A.-M.); [email protected] (S.M.-M.) 2 KFB Acoustics Sp. z o. o. Mydlana 7, 51-502 Wrocław, Poland; [email protected] 3 Facultad de Ciencias Marinas, Universidad Autónoma de Baja California, Ensenada 22860, Mexico; [email protected] 4 Geo-Environmental Cartography and Remote Sensing Group, Universitat Politècnica de València, Camí de Vera s/n, 46022 Valencia, Spain; [email protected] * Correspondence: [email protected] Received: 20 September 2020; Accepted: 4 November 2020; Published: 6 November 2020 Abstract: Since remote sensing of ocean colour began in 1978, several ocean-colour sensors have been launched to measure ocean properties. These measures have been applied to study water quality, and they specifically can be used to study algal blooms. Blooms are a natural phenomenon that, due to anthropogenic activities, appear to have increased in frequency, intensity, and geographic distribution. This paper aims to provide a systematic analysis of research on remote sensing of algal blooms during 1999–2019 via bibliometric technique. This study aims to reveal the limitations of current studies to analyse climatic variability effect. A total of 1292 peer-reviewed articles published between January 1999 and December 2019 were collected. -
Pollution Biomarkers in the Framework of Marine Biodiversity Conservation: State of Art and Perspectives
water Review Pollution Biomarkers in the Framework of Marine Biodiversity Conservation: State of Art and Perspectives Maria Giulia Lionetto * , Roberto Caricato and Maria Elena Giordano Department of Environmental and Biological Sciences and Technologies (DISTEBA), University of Salento, 73100 Lecce, Italy; [email protected] (R.C.); [email protected] (M.E.G.) * Correspondence: [email protected] Abstract: Marine biodiversity is threatened by several anthropogenic pressures. Pollution deriving from the discharge of chemical contaminants in the sea represents one of the main threats to the marine environment, influencing the health of organisms, their ability to recover their homeostatic status, and in turn endangering biodiversity. Molecular and cellular responses to chemical pollutants, known as biomarkers, are effect-based methodologies useful for detecting exposure and for assessing the effects of pollutants on biota in environmental monitoring. The present review analyzes and discusses the recent literature on the use of biomarkers in the framework of biodiversity conservation. The study shows that pollution biomarkers can be useful tools for monitoring and assessment of pollution threat to marine biodiversity, both in the environmental quality monitoring of protected areas and the assessment of the health status of species at risk. Moreover, key areas of the research that need further development are suggested, such as the development of omics-based biomarkers specifically addressed to conservation purposes and their validation in the field, the extension of the biomarker study to a wider number of endangered species, and the development of organic Citation: Lionetto, M.G.; Caricato, R.; guidelines for the application of the biomarker approach in support to conservation policies and Giordano, M.E. -
Ask a Scientist: How Do People Become Infected with Germs?
One way to think about how living things get sick is to imagine a triangle. The three corners represent the environment... ...the host... All three aspects of this triangle must come ...and the cause of the disease, together for disease to occur. Disease the Agent. agents can be non-infectious or infectious. Non-infectious agents are non-living things that are toxic to the host, like radiation or chemicals... ...while infectious agents are organisms that invade a host to survive. Only infectious agents can spread, or transmit, between hosts. Infectious disease agents, otherwise known as pathogens, A person can become infected with a must infect a host pathogen when in the same environment in order to grow, or as the agent... replicate. Human pathogens, like viruses, bacteria, and parasites, evolved to infect people. Their survival is dependent on quickly invading, making more of themselves, and efficiently transmitting to others. If a pathogen gets past a host’s defenses, it will attempt to infect the host and begin replicating itself. ...and don’t have enough protection in the form The subsequent battle between Many cells will be destroyed as of physical barriers or the germs and the body’s germs kill them through replicating pre-existing immunity. immune system will cause the and as collateral damage from the symptoms of illness. activated immune cells. That’s just how one person gets infected, but how does disease spread? Well, if sick people go around sneezing and coughing without covering their mouth or frequently washing their hands... ...they are actually spreading pathogens all over the environment around them. -
4 Study Design for Monitoring Wetlands United States Environmental Office of Water EPA 822-R-02-015 Protection Agency Washington, DC 20460 March 2002
United States Environmental Office of Water EPA 822-R-02-015 Protection Agency Washington, DC 20460 March 2002 Methods for evaluating wetland condition #4 Study Design for Monitoring Wetlands United States Environmental Office of Water EPA 822-R-02-015 Protection Agency Washington, DC 20460 March 2002 Methods for evaluating wetland condition #4 Study Design for Monitoring Wetlands Principal Contributor Warnell School of Forest Resources, University of Georgia Amanda K. Parker Prepared jointly by: The U.S. Environmental Protection Agency Health and Ecological Criteria Division (Office of Science and Technology) and Wetlands Division (Office of Wetlands, Oceans, and Watersheds) United States Environmental Office of Water EPA 822-R-02-015 Protection Agency Washington, DC 20460 March 2002 Notice The material in this document has been subjected to U.S. Environmental Protection Agency (EPA) technical review and has been approved for publication as an EPA document. The information contained herein is offered to the reader as a review of the “state of the science” concerning wetland bioassessment and nutrient enrichment and is not intended to be prescriptive guidance or firm advice. Mention of trade names, products or services does not convey, and should not be interpreted as conveying official EPA approval, endorsement, or recommendation. Appropriate Citation U.S. EPA. 2002. Methods for Evaluating Wetland Condition: Study Design for Monitoring Wetlands. Office of Water, U.S. Environmental Protection Agency, Washington, DC. EPA-822-R-02-015. This entire document can be downloaded from the following U.S. EPA websites: http://www.epa.gov/ost/standards http://www.epa.gov/owow/wetlands/bawwg ii Contents Foreword .................................................................................................................. -
Implementing and Innovating Marine Monitoring Approaches for Assessing Marine Environmental Status
Implementing and Innovating Marine Monitoring Approaches for Assessing Marine Environmental Status. Roberto Danovaro, Laura Carugati, Berzano Marco, Abigail E. Cahill, Susana de Carvalho Spinola, Anne Chenuil, Cinzia Corinaldesi, Cristina Sonia, Romain David, Antonio Dell’Anno, et al. To cite this version: Roberto Danovaro, Laura Carugati, Berzano Marco, Abigail E. Cahill, Susana de Carvalho Spinola, et al.. Implementing and Innovating Marine Monitoring Approaches for Assessing Marine Environmental Status.. Frontiers in Marine Science, Frontiers Media, 2016, 3, pp.213. 10.3389/fmars.2016.00213. hal-01448726 HAL Id: hal-01448726 https://hal.archives-ouvertes.fr/hal-01448726 Submitted on 28 Jan 2017 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. Author’s Proof Carefully read the entire proof and mark all corrections in the appropriate place, using the Adobe Reader commenting tools (Adobe Help). Do not forget to reply to the queries. We do not accept corrections in the form of edited manuscripts. In order to ensure the timely publication of your article, please submit the corrections within 48 hours. If you have any questions, please contact science.production.offi[email protected]. Author Queries Form Q1 We have ignored the below author comment in line no. -
Neglected Tropical Diseases in The
Qian et al. Infectious Diseases of Poverty (2019) 8:86 https://doi.org/10.1186/s40249-019-0599-4 SCOPING REVIEW Open Access Neglected tropical diseases in the People’s Republic of China: progress towards elimination Men-Bao Qian1, Jin Chen1, Robert Bergquist2, Zhong-Jie Li3, Shi-Zhu Li1, Ning Xiao1, Jürg Utzinger4,5 and Xiao-Nong Zhou1* Abstract Since the founding of the People’s Republic of China in 1949, considerable progress has been made in the control and elimination of the country’s initial set of 11 neglected tropical diseases. Indeed, elimination as a public health problem has been declared for lymphatic filariasis in 2007 and for trachoma in 2015. The remaining numbers of people affected by soil-transmitted helminth infection, clonorchiasis, taeniasis, and echinococcosis in 2015 were 29.1 million, 6.0 million, 366 200, and 166 100, respectively. In 2017, after more than 60 years of uninterrupted, multifaceted schistosomiasis control, has seen the number of cases dwindling from more than 10 million to 37 600. Meanwhile, about 6000 dengue cases are reported, while the incidence of leishmaniasis, leprosy, and rabies are down at 600 or fewer per year. Sustained social and economic development, going hand-in-hand with improvement of water, sanitation, and hygiene provide the foundation for continued progress, while rigorous surveillance and specific public health responses will consolidate achievements and shape the elimination agenda. Targets for poverty elimination and strategic plans and intervention packages post-2020 are important opportunities for further control and elimination, when remaining challenges call for sustainable efforts. Keywords: Control, Elimination, People's Republic of China, Neglected tropical diseases Multilingual abstracts deprived urban settings [1, 2]. -
A Comparative Study of Four Indexes Based on Zooplankton As Trophic State Indicators in Reservoirs
Limnetica, 38(1): 291-302 (2019). DOI: 10.23818/limn.38.06 © Asociación Ibérica de Limnología, Madrid. Spain. ISSN: 0213-8409 A comparative study of four indexes based on zooplankton as trophic state indicators in reservoirs Daniel Montagud1,*, Juan M. Soria1, Xavier Soria-Perpiñà2, Teresa Alfonso1 and Eduardo Vicente1 1 Cavanilles Institute of Biodiversity and Evolutionary Biology (ICBIBE). University of Valencia, 46980-Pater- na, Spain. 2 Image Processing Laboratory. University of Valencia, 46980-Paterna, Spain. * Corresponding author: [email protected] Received: 15/02/18 Accepted: 25/06/18 ABSTRACT A comparative study of four indices based on zooplankton as trophic state indicators in reservoirs This study aims to examine four recently conducted trophic state indices that are based on the density of zooplankton and designed for estimating the trophic state of inland waters. These indices include two with formulations based on quotients or ratios, the Rcla and the Rzoo-chla, which were proposed and validated in the European project ECOFRAME (Moss et al., 2003), and two with formulations based on the incorporation of a statistical tool comprising canonical correspondences analysis (CCA), the Wetland Zooplankton Index proposed in 2002 by researchers from McMaster University of Ontario (Lougheed & Chow-Fraser, 2002) and the Zooplankton Reservoir Trophic Index, an index recently designed by the Ebro Basin Authority and on which this manuscript is the first article. These indices were studied and applied in 53 heterogeneous reservoirs of the Ebro Basin. In addition, all were subsequently validated by Carlson’s Trophic State Index based on the amount of chlorophyll a (Carlson, 1977), with significant differences found between them.