The Verlot Peat Area Was Investigated by Rigg, Ac Thick
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Biogas for Agriculture
2007 IGER INNOVATIONS Biogas for agriculture Phil Hobbs, Alastair Ward and Guillermo Pardo Biogas feedstock 44 Current research 44 2007 IGER INNOVATIONS Biogas for agriculture Phil Hobbs, Alastair Ward and Guillermo Pardo he production of biogas as a fuel obtained from Biogas feedstock B I the fermentation of organic wastes has undoubted O Livestock manure slurry is the main source of G A Tbenefits for the environment . These benefits include feedstock for biogas production, having a dry matter S F both reduced methane emissions from livestock content of about 5 -15% w/w, but potentially a wide O R enterprises and the production of green energy which range of organic wastes can be used as starter A G can be fed into the national electricity grid. The heat materials, ranging from fats and greases to vegetable R I C generated from biogas production can also be used wastes . Some potential sources, such as food and U L T locally for heating livestock buildings or hot water. abattoir wastes , would need to be heat -treated before U R E Biogas is about 70% methane and 30% CO 2. The use as a biogas feedstock as a biosecurity measure, actual methane producers are microbes known as however, in order to prevent any contained ‘methanogens ’. These belong to some of the oldest pathogens escaping to reinfect farm livestock via groups of organisms on the planet , known as the grazing or other crop sources. Organic wastes Archaea . They are common in wetlands, where they imported onto the farm are also a good source of are responsible for producing marsh gas , and are also nutrients for spreading on the land and can commonly found in the gut of ruminants such as significantly reduce artificial fertiliser use , both cattle, and in their faeces . -
Lake Ballinger Fact Sheet 2011
Lake Ballinger Fact Sheet Revision Date: June 15, 2011 As a result of flooding events in August 2004, the City of Mountlake Terrace was contacted by several Edmonds residents on Lake Ballinger concerned about the high water level on the lake. In an effort to address this issue and others that were raised during discussions, the following “Lake Ballinger Fact Sheet” along with a chronological list of developments was prepared and distributed to lake residents. Information regarding the level of the lake, storm water inflow to the lake, water quality of the lake, and the ongoing efforts of the City of Mountlake Terrace, the City of Edmonds, and several other adjacent agencies to address these issues is included in this fact sheet. The fact sheet is periodically updated as new information becomes available. Lake Ballinger Fact Sheet: Watershed Area: Shoreline 22%, Snohomish County 9%, Mountlake Terrace 23%, Edmonds 25%, Lynnwood 21% Size: 107 acres (including the island) – 72 acres in Mountlake Terrace and 35 acres in Edmonds Depth: Deepest depth is approximately 35 feet Private Ownership: Three lots in Mountlake Terrace, 49 in Edmonds, Nile Temple Property Public Ownership: Lake Ballinger Golf Course, Lake Ballinger Swimming Beach and Dock Drainage Basins: Hall Creek – 66 percent of inflow Echo Lake, Aurora Village – 16 percent of inflow Non-specific areas adjacent to the lake – 18 percent of inflow Lake Ballinger Events: - 1942 - Lake Level Established by Court Order o Authorized installation of a lake outflow weir on McAleer Creek o Authorized formation of a tax district to pay for maintenance and operation of the weir - 1954 - Mountlake Terrace Incorporates - Mid 1960’s - Nile Temple filled in an area north of the existing creek site and raised the roadbed area near the first culvert downstream on McAleer Creek effectively creating a higher roadbed and effectively raising the high overflow level of the lake during large storm events. -
Muck: Causes and Corrective Actions1 Mark V
FA200 A Beginner’s Guide to Water Management—Muck: Causes and Corrective Actions1 Mark V. Hoyer, Daniel E. Canfield, Jr. and Mark Brenner2 This publication was produced by: Florida LAKEWATCH 2017 UF/IFAS School of Forest Resources and Conservation / Fisheries and Aquatic Sciences 7922 NW 71st Street Gainesville, Florida 32653-3071 Phone: 352/392-4817 FAX: 352/392-3672 E-mail: [email protected] Website: http://lakewatch.ifas.ufl.edu Copies are available for download from the LAKEWATCH website: http://lakewatch.ifas.ufl.edu/data.shtml Muck from pond at Fisheries and Aquatic Sciences, Gainesville, FL. Credits: Mark Hoyer, UF/IFAS Introduction Informational Circular 112 Muck is both the popular and the scientific term for the material found on the bottom of many depressions that Florida LAKEWATCH have held water for any length of time. It is of great impor- tance to many recreational lake users because its presence UF/IFAS Fisheries and Aquatic Sciences can ruin their enjoyment of the water body. Its dark color School of Forest Resources and Conservation and “oozy” feel lead many people to believe muck could be Gainesville, Florida an indicator of a polluted system. January 2017 Another cause for people’s distaste for muck is the stink. Bacterial decomposition of the organic matter in muck 1. This document is FA200, one of a series of the School of Forest Resources and Conservation Program in Fisheries and Aquatic Sciences, UF/IFAS Extension. Original publication date February 2017. Visit the EDIS website at http://edis.ifas.ufl.edu. 2. Mark V. Hoyer, director, Florida LAKEWATCH, UF/IFAS Program in Fisheries and Aquatic Sciences of the School of Forest Resources and Conservation; Daniel E. -
Fossil Peat of the Illinois Basin : a Guide to the Study of Coal Balls Of
^uA^^^^i 557 IL6ed no. 11 vol <=>&ued- // FOSSIL PEAT FROM THE ILLINOIS BASIN cn:.\/E' HM * Tom L. Phillips Matthew J. Avcin Dwain Berggren 9lUmH Stcde Qeol(Xjical SuMtey STATE OF ILLINOIS DEPARTMENT OF REGISTRATION AND EDUCATION COVER - A photograph (natural size) of a cellulose acetate peel showing the fossil peat preserved in a coal ball collected from the Herrin (No. 6) Coal Member near Carrier Mills, Illinois. Figure 2 describes its contents. 1976 ILLINOIS STATE GEOLOGICAL SURVEY Urbana, Illinois 61801 Jack A. Simon, M.S., Chief ILLINOIS STATE GEOLOGICAL SURVEY ithority of State of Illinois. Ch. 127. IRS. Par. 58 .25 3 3051 00004 8540 I FOSSIL PEAT OF THE ILLINOIS BASIN Goal QalU of PenntyUankM, Acje Tom L. Phillips Matthew J. Avcin Dwain Berggren Digitized by the Internet Archive in 2012 with funding from University of Illinois Urbana-Champaign http://archive.org/details/fossilpeatofilli11phil CONTENTS Introduction 1 Geology of the fossil peat deposits 3 The Illinois Basin 3 How the coal balls formed 3 Plants in fossil peat 7 Studies of fossil peat 9 Internal anatomy and external morphology 10 Plant taxonomy 11 Plant evolution 12 Palynology 13 Preparation of floras 14 Analyses of permineralized peat 14 Formation of coal balls 17 Preparing coal balls for study 17 Making coal-ball peels 18 Examining peels with a microscope 24 Mounting peel sections on glass slides 24 Recovering spores and other microfossils from coal balls 26 Preserving coal balls 28 Repairing and embedding coal-ball slices 29 Sources of materials 31 Finding coal balls 31 Materials needed 32 Selected references 33 Plates and explanations 34 . -
Odors, Explained
OdorCap Information Sheet Unique Odors w/ Encapsulation Technology Several Distinctive Odors Explained Hydrogen sulfides Gas This is the by-product of anaerobic activity. This anaerobic activity survives very well in low oxygen levels or no oxygen levels of the sewer water or the sewer transmission lines. This is the main reason to try and remove this type of bacteria from the sewer lines being in the water or the line. These levels can even become dangerous to personnel working and living around the area. Low levels Hydrogen sulfide has a very strong odor and can be smelled at levels as low as 0.005 - 0.02 parts per million (ppm). Higher levels may cause an offensive, rotten-egg odor, and can irritate eyes, nose, and throat. The lungs and nasal passages may also become inflamed. Eyes may become sore and watery. Your throat may itch, and you may start to cough. Long-term health effects of low-level hydrogen sulfide exposure are unknown. High levels At levels above 100 ppm, hydrogen sulfide is very dangerous. The gas loses its odor by overpowering the sense of smell and begins to affect the whole body. At 250 ppm, a person my quickly lose consciousness. They may experience powerful stinging of the eyes, throat, and suffer from severe lung inflammation. At 500 ppm and higher, people can have convulsions, respiratory arrest, and heart failure. High exposure levels may also cause permanent brain damage. According to the National Institute for Occupational Safety and Health (NIOSH), hydrogen sulfide is a leading cause of sudden death from workplace chemical exposure. -
Appendix a Basics of Landfill
APPENDIX A BASICS OF LANDFILL GAS Basics of Landfill Gas (Methane, Carbon Dioxide, Hydrogen Sulfide and Sulfides) Landfill gas is produced through bacterial decomposition, volatilization and chemical reactions. Most landfill gas is produced by bacterial decomposition that occurs when organic waste solids, food (i.e. meats, vegetables), garden waste (i.e. leaf and yardwaste), wood and paper products, are broken down by bacteria naturally present in the waste and in soils. Volatilization generates landfill gas when certain wastes change from a liquid or solid into a vapor. Chemical reactions occur when different waste materials are mixed together during disposal operations. Additionally, moisture plays a large roll in the speed of decomposition. Generally, the more moisture, the more landfill gas is generated, both during the aerobic and anaerobic conditions. Landfill Gas Production and Composition: In general, during anaerobic conditions, the composition of landfill gas is approximately 50 percent methane and 50 percent carbon dioxide with trace amounts (<1 percent) of nitrogen, oxygen, hydrogen sulfide, hydrogen, and nonmethane organic compounds (NMOCs). The more organic waste and moisture present in a landfill, the more landfill gas is produced by the bacteria during decomposition. The more chemicals disposed in a landfill, the more likely volatile organic compounds and other gasses will be produced. The Four Phases of Bacterial Decomposition: “Bacteria decompose landfill waste in four phases. The composition of the gas produced changes with each of the four phases of decomposition. Landfills often accept waste over a 20-to 30-year period, so waste in a landfill may be undergoing several phases of decomposition at once. -
Alaska Non-Timber Forest Products Harvest Manual for Commercial Harvest on State-Owned Lands
Alaska Non-Timber Forest Products Harvest Manual For Commercial Harvest on State-Owned Lands State of Alaska Department of Natural Resources Division of Mining, Land and Water April 2, 2008 - 1 - State of Alaska Non-Timber Forest Product Commercial Harvest Manual, April 2, 2008 Table of Contents Introduction 3 Special notices, clarifications, and general rules 4 Procedure for revision 5 Products and species descriptions 6 Bark birch 7 cedar 8 various species 9 Berries and berry-like fruits 10 Branches and stems of deciduous woody species 11 Buds and tips 12 Burls and galls 13 Cones 14 Conks 15 Cuttings – willow, dogwood & poplar 16 Diamond willow 17 Evergreen boughs 18 Floral greenery 19 Leaves and flowers of woody plants 20 Lichens ground-growing 21 tree-growing 22 Mosses and liverworts 23 Mushrooms 24 Non-woody perennial plants tender edible shoots, stems, leaves, and/or flowers 25 mature stems, leaves and flowers 26 Roots edible or medicinal 27 for fiber 28 Seed heads 29 Seeds 30 Transplants plugs 31 shrubby perennial with root ball 32 sprigs 33 tree sapling with root ball 34 Appendix I: Plants never allowed for harvest 35 Appendix II: Guidelines for non over-the-counter permit products 36 Glossary 38 Selected references 39 - 2 - State of Alaska Non-Timber Forest Product Commercial Harvest Manual, April 2, 2008 Introduction Non-timber forest products are generally defined as products derived from biological resources. Examples of non-timber forest products may include mushrooms, conks, boughs, cones, leaves, burls, landscaping transplants, roots, flowers, fruits, and berries. Not included are minerals, rocks, soil, water, animals, and animal parts. -
Restoring Silvopastures with Oak Saplings: Effects of Mulch and Diameter Class on Survival, Growth, and Annual Leaf-Nutrient Patterns
Agroforest Syst (2014) 88:935–946 DOI 10.1007/s10457-014-9737-y Restoring silvopastures with oak saplings: effects of mulch and diameter class on survival, growth, and annual leaf-nutrient patterns M. N. Jime´nez • J. R. Pinto • M. A. Ripoll • A. Sa´nchez-Miranda • F. B. Navarro Received: 13 March 2014 / Accepted: 14 August 2014 / Published online: 23 August 2014 Ó Springer Science+Business Media Dordrecht 2014 Abstract In Southwestern Spain, multifunctional leaf-nutrient concentrations were analyzed. Forty silvopastoral systems consisting of pastureland and months after planting, all treatments showed high open oak woodlands are known as Dehesas. These, survival (81 %) but only straw-mulched saplings and other similar systems of the Mediterranean basin, differed significantly (94 %) from control (74 %). are currently threatened by increasing intensive land DBH increased over time but showed no significant use. As a consequence, oak regeneration is declining differences among mulch treatments. Saplings with and is in need of adequate management and active high initial DBH showed the greatest growth and restoration. Traditional restoration practices outplant change in DBH at the end of the study period. Leaf- one-year-old, nursery-produced oak seedlings grown nutrient concentrations changed significantly in the in 250–350 cm3 containers, but establishment and year following outplanting. Bi-monthly foliar nutrient growth results are typically poor. This work examines concentration data show decreases in P, K, Zn, and B holm oak (Quercus ilex L. subsp. ballota (Desf.) and sharp increases in Ca and Fe. In this work, we Samp.) grown in a non-conventional container size provide some evidence concerning the viability of (24 l) and age (6–7 years) with three mulch treatments non-conventional oak size for restoring, regenerating, (control, stone, and straw). -
Longleaf Pine: an Annotated Bibliography, 1946 Through 1967
U.S. Department of Agriculture Forest Service Research Paper SO-35 longleaf pine: an annotated bibliography, 1946 through 1967 Thomas C. Croker, Jr. SOUTHERN FOREST EXPERIMENT STATION T.C. Nelson, Director FOREST SERVICE U.S. DEPARTMENT OF AGRICULTURE 1968 Croker, Thomas C., Jr. 1968. Longleaf pine: an annotated bibliography, 1946 through 1967. Southern Forest Exp. Sta., New Orleans, Louisiana. 52 pp. (U. S. Dep. Agr. Forest Serv. Res. Pap. SO-35) Lists 665 publications appearing since W. G. Wahlenberg compiled the bibliography for his book, Longleaf Pine. Contents Page Introduction .................................................................................................................................... 1 1. Factors of the environment. Biology........................................................................................ 2 11 Site factors, climate, situation, soil ............................................................................. 2 15 Animal ecology. Game management .......................................................................... 2 16 General botany ............................................................................................................. 2 17 Systematic botany ....................................................................................................... 6 18 Plant ecology................................................................................................................. 7 2. Silviculture............................................................................................................................... -
Wine | Spirits | Beer
WINE | SPIRITS | BEER CELLAR99 In the early days of the original Ruffino’s in Baton Rouge, business people entertaining clients would often lament that they could not order many of the well-known wines due to the restrictions of their expense accounts. Ruffin’s solution, a collection of selected cabernets and red blends, all from California, for $99 that anywhere else would fetch well over $100. Frank Family Vineyards, 2018 Machete, by Orin Swift, 2017 Palermo, by Orin Swift, 2016 Papillon by Orin Swift, 2018 Faust, Napa Valley, 2017 Cyrus, Alexander Valley, 2014 Jordan, Alexander Valley, 2016 Stag’s Leap Winery, 2016 The Prisoner Wine Co., 2018 Stout Family Vineyards, 2015 Cakebread, Napa Valley, 2018 Love Hammer, by SLO Down Wines, 2016 Duckhorn, Napa Valley, 2017 SPECIALTY COCKTAILS THE MAN-TINI | Knob Creek Bourbon – Lemon & Lime – Cognac – Agave Nectar SATSUMA MULE | Bayou Satsuma – Simple Syrup & Lime – Stoli Ginger Beer - Mint BIERE SOLLEIT | St Germain–Fresh Lemon –Ragin Cajun Ale BACK PORCH | House Infused Lemon Vodka –Hibiscus Syrup –St. Germaine Liqueur BLUE BERRY LEMON DROP | House Infused Blueberry Vodka - Fresh Lemon PEAR MARTINI | Pear Vodka -St. Germaine Liqueur –Fresh Lime PINEAPPLE INFUSION | House Infused Pineapple Vodka –Orange Liqueur –Pineapple Juice POMEGRANATE MARTINI | Citrus Vodka - Pama Liquor - Gran Gala Orange Liquor - Pomegranate Juice LAFAYETTE | BATON ROUGE | DE LA RONDE HALL | RUFFINOSRESTAURANT.COM WHISKEY JAMESON, IRISH WHISKEY JACK DANIEL’S, TENNESSEE WHISKEY, “GENTLEMAN JACK” toasted wood | sherry | -
Effects of CO2 Ratio on Emissions of Dual Fuel Diesel Engine Ilker Turgut Yilmaz*, Metin Gumus
International Journal of Smart Grid and Clean Energy Effects of CO2 ratio on emissions of dual fuel diesel engine Ilker Turgut Yilmaz*, Metin Gumus Department of Mechanical Engineering, Faculy of Technology, Marmara University, DB-103, Göztepe Campus 34722, İstanbul Turkey Abstract The problem of energy consumption is growing because of the increase in population. Energy demand is commonly supplied by the fossil fuels however they bring up against the problem of run out. Biogas is a renewable fuel which is a candidate for duel fuel diesel engines. This work focuses on the effect of carbon dioxide on exhaust emission characteristics of a duel fuel diesel engine run on synthetic biogas. Four cylinder, water cooled, turbocharged, a diesel engine with Common Rail fuel injection system is used for this investigation. A simple mixing chamber is placed between inlet manifold and air filter. Experiments have been conducted at 1750 rpm under different loads (50 N.m, 75 N.m and 100 N.m). Main fuels used in this investigation are methane, M60:C40 and M80:C20 in dual fuel mode. In dual fuel mode using biogas increases hydrocarbon, nitrogen oxide and carbon dioxide emissions. Soot emission decrease in duel fuel mode. In the light of experimental data, it is understood that electronic control unit of the diesel engine cannot manage dual fuel mode. Original electronic control unit have to be reprogrammed. Keywords: Biogas, dual fuel diesel engine, emissions 1. Introduction Internal combustion engines (IC) generate power not only vehicles but also other needs. To produce power for vehicles, locomotives, marine, irrigation, production electricity, IC engines need fuel. -
Lake Ballinger Total Phosphorus Total Maximum Daily Load: Water Quality Attainment Monitoring Report
Lake Ballinger Total Phosphorus Total Maximum Daily Load Water Quality Attainment Monitoring Report April 2008 Publication No. 08-03-007 Publication Information This report is available on the Department of Ecology’s website at www.ecy.wa.gov/biblio/0803007.html Data for this project are available at Ecology’s Environmental Information Management (EIM) website at. Search User Study ID, MBEL0002. Ecology’s Project Tracker Code for this study is 07-512. For more information contact: Publications Coordinator Environmental Assessment Program P.O. Box 47600 Olympia, WA 98504-7600 E-mail: [email protected] Phone: (360) 407-6764 Washington State Department of Ecology - www.ecy.wa.gov/ o Headquarters, Lacey 360-407-6000 o Northwest Regional Office, Bellevue 425-649-7000 o Southwest Regional Office, Lacey 360-407-6300 o Central Regional Office, Yakima 509-575-2490 o Eastern Regional Office, Spokane 509-329-3400 Any use of product or firm names in this publication is for descriptive purposes only and does not imply endorsement by the author or the Department of Ecology. If you need this publication in an alternate format, call Joan LeTourneau at (360) 407-6764. Persons with hearing loss can call 711 for Washington Relay Service. Persons with a speech disability can call 877-833-6341. Page 2 Lake Ballinger Total Phosphorus Total Maximum Daily Load Water Quality Attainment Monitoring Report by Maggie Bell-McKinnon Western Operations Section Environmental Assessment Program Washington State Department of Ecology Olympia, Washington 98504-7710 April