Chapter 9 Agricultural Waste Management Systems
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Housed Livestock, Manure Storage, Manure Processing Draft Section for a Guidance Document
Housed livestock, manure storage, manure processing Draft section for a Guidance Document Prepared by Barbara Amon and Lars Stoumann Jensen (session chairs) For discussion at the workshop on integrated sustainable nitrogen management, Brussels 30 September – 1 October 2019 This draft chapter to a planned Guidance Document on integrated sustainable nitrogen management has been prepared for the Task Force on Reactive Nitrogen under the UNECE Air Convention, with support from the European Commission. The process of drafting the Guidance Document started in connection to a workshop “Towards joined-up nitrogen guidance for air, water and climate co-benefits”, hosted in Brussels, 11-12 October 2016. The current chapter draft is based on the results from that workshop and on discussions and developments since then. It will be presented and discussed in Brussels on 30 September – 1 October at a second workshop jointly organised by the Task Force on Reactive Nitrogen and the European Commission. The content of the draft paper reflects the views only of the authors and the European Commission cannot be held responsible for any use which may be made of the information. 2 Housed livestock, manure storage, manure processing 1. Introduction and background 2. Why do we have emissions and how can they be influenced – the basics behind emission processes Nitrogen can take various forms (Fig. 1). Reactive nitrogen (Nr) includes all forms of nitrogen that are biologically, photochemically, and radiatively active. Compounds of nitrogen that are - - reactive include the following: nitrous oxide (N2O), nitrate (NO3 ), nitrite (NO2 ), ammonia + (NH3), and ammonium (NH4 ). Reactive forms of nitrogen are those capable of cascading through the environment and causing an impact through smog, acid rain, biodiversity loss, etc.1. -
Safe Use of Wastewater in Agriculture: Good Practice Examples
SAFE USE OF WASTEWATER IN AGRICULTURE: GOOD PRACTICE EXAMPLES Hiroshan Hettiarachchi Reza Ardakanian, Editors SAFE USE OF WASTEWATER IN AGRICULTURE: GOOD PRACTICE EXAMPLES Hiroshan Hettiarachchi Reza Ardakanian, Editors PREFACE Population growth, rapid urbanisation, more water intense consumption patterns and climate change are intensifying the pressure on freshwater resources. The increasing scarcity of water, combined with other factors such as energy and fertilizers, is driving millions of farmers and other entrepreneurs to make use of wastewater. Wastewater reuse is an excellent example that naturally explains the importance of integrated management of water, soil and waste, which we define as the Nexus While the information in this book are generally believed to be true and accurate at the approach. The process begins in the waste sector, but the selection of date of publication, the editors and the publisher cannot accept any legal responsibility for the correct management model can make it relevant and important to any errors or omissions that may be made. The publisher makes no warranty, expressed or the water and soil as well. Over 20 million hectares of land are currently implied, with respect to the material contained herein. known to be irrigated with wastewater. This is interesting, but the The opinions expressed in this book are those of the Case Authors. Their inclusion in this alarming fact is that a greater percentage of this practice is not based book does not imply endorsement by the United Nations University. on any scientific criterion that ensures the “safe use” of wastewater. In order to address the technical, institutional, and policy challenges of safe water reuse, developing countries and countries in transition need clear institutional arrangements and more skilled human resources, United Nations University Institute for Integrated with a sound understanding of the opportunities and potential risks of Management of Material Fluxes and of Resources wastewater use. -
Manure Management Factsheet
INDIANA NATURAL RESOURCES CONSERVATION SERVICE Helping People Help the Land. FACT SHEET Manure Management Properly managed manure can improve soil health, crop yields and reduce the risk of runoff to surface waters. June, 2014 Photo Source: IDEM NRCS works directly with farmers to manage NRCS ASSISTANCE Natural Resources manure as a valuable nutrient source in an BACKGROUND environmentally conscious manner. Properly NRCS helps farmers and landowners identify • Manure is a valuable fertilizer Conservation Service managed manure can improve soil health, natural resources concerns on their farm. containing varying amounts of nitrogen, crop yields, and reduce the risk of runoff to NRCS provides technical assistance at no cost phosphorus, potassium, micronutrients surface waters. to create a conservation plan and identify and organic matter, depending on conservation practices to address resource the livestock species and the manure MANURE MANAGEMENT concerns. handling and storage, as well as application methods. STANDARDS Practices may include nutrient application (590 standard) to address identified water quality • Manure is a cost-efficient form of Through a scientific planning process and or other concerns, or manure storage (313 and fertilizer for crops, that if managed and standards, NRCS works with farmers to 359 standards) to address an identified water applied correctly, can supply plant- address resource concerns on their farms. All quality, odor or other resource concern. nutrient needs and can enhance soil NRCS standards require -
Five Facts About Incineration Five Facts About Incineration
Five facts about incineration Five facts about incineration Across the globe, cities are looking for ways to improve their municipal solid waste systems. In the search for services that are affordable, green and easy to implement, many cities are encouraged to turn to waste-to-energy (WtE) technologies, such as incineration.1 But, as found in WIEGO’s Technical Brief 11 (Waste Incineration and Informal Livelihoods: A Technical Guide on Waste-to-Energy Initiatives by Jeroen IJgosse), incineration is far from the perfect solution and, particularly in the Global South, can be less cost-effective, more complicated and can negatively impact the environment and informal waste workers’ livelihoods. Below, we have collected the top five issues highlighted in the study that show why this technology is a risky choice: 1. Incineration costs more than recycling. How incineration may be promoted: Incineration is a good economic decision because it reduces the costs associated with landfill operations while also creating energy that can be used by the community. The reality: • In 2016, the World Energy Council reported that, “energy generation from waste is a costly option, in comparison with other established power generation sources.” • Setting up an incineration project requires steep investment costs from the municipality. • For incineration projects to remain financially stable long-term, high fees are required, which place a burden on municipal finances and lead to sharp increases in user fees. • If incinerators are not able to collect enough burnable waste, they will burn other fuels (gas) instead. Contract obligations can force a municipality to make up the difference if an incinerator doesn’t burn enough to create the needed amount of energy. -
What Is Nonpoint Source Pollution?
What is Nonpoint Source Pollution? Nonpoint Source Pollution, or people pollution, is a contamination of our ground water, waterways, and ocean that results from everyday activities such as fertilizing the lawn, walking pets, changing motor oil and littering. With each rainfall, pollutants generated by these activities are washed into storm drains that flow into our waterways and ocean. They also can soak into the ground contaminating the ground water below. Each one of us, whether we know it or not, contributes to nonpoint source pollution through our daily activities. As a result, nonpoint source pollution is the BIGGEST threat to many of our ponds, creeks, lakes, wells, streams, rivers and bays, our ground water and the ocean. The collective impact of nonpoint source pollution threatens aquatic and marine life, recreational water activities, the fishing industry, tourism and our precious drinking water resources. Ultimately, the cost becomes the burden of every New Jersey resident. But there's good news - in our everyday activities we can stop nonpoint source pollution and keep our environment clean. Simple changes in YOUR daily lifestyle can make a tremendous difference in the quality of New Jersey's water resources. Here are just a few ways you can reduce nonpoint source pollution. LITTER: Place litter, including cigarette butts and fast food containers, in trash receptacles. Never throw litter in streets or down storm drains. Recycle as much as possible. FERTILIZERS: Fertilizers contain nitrates and phosphates that, in abundance, cause blooms of algae that can lead to fish kills. Avoid the overuse of fertilizers and do not apply them before a heavy rainfall. -
Manure Management for Water Quality: Costs to Animal Feeding Operations of Applying Manure Nutrients to Land
Manure Management for Water Quality: Costs to Animal Feeding Operations of Applying Manure Nutrients to Land Marc Ribaudo, Noel Gollehon, Marcel Aillery, Jonathan Kaplan, Robert Johansson, Jean Agapoff, Lee Christensen, Vince Breneman, and Mark Peters Chapter 1–Introduction Livestock and poultry manure can provide valuable sion affecting the potential for contamination of water organic material and nutrients for crop and pasture resources by manure nutrients (Mulla et al., 1999). growth. However, nutrients contained in animal manure can degrade water quality if they are over- Recent policies and programs for increasing the effi- applied to land and enter water resources through cient use of nutrients and protecting water quality from runoff or leaching. The nutrients of greatest water nutrient runoff all emphasize the importance of proper- quality concern are nitrogen and phosphorus. Animal ly handling animal manure. The Unified Strategy for waste is a source of both. Animal Feeding Operations, jointly developed by the U.S. Department of Agriculture (USDA) and the A shift in the livestock and poultry industry over the Environmental Protection Agency (EPA) in 1999, past several decades toward fewer, larger operations states: “Land application is the most common, and has prompted public concern over the use and disposal usually most desirable method of utilizing manure of animal manure. Manure lagoon spills in North because of the value of the nutrients and organic mat- Carolina and pfiesteria piscicida outbreaks in North ter. Land application should be planned to ensure that Carolina and Maryland have raised public concerns the proper amounts of all nutrients are applied in a about the way manure is stored and handled. -
2.2 Sewage Sludge Incineration
2.2 Sewage Sludge Incineration There are approximately 170 sewage sludge incineration (SSI) plants in operation in the United States. Three main types of incinerators are used: multiple hearth, fluidized bed, and electric infrared. Some sludge is co-fired with municipal solid waste in combustors based on refuse combustion technology (see Section 2.1). Refuse co-fired with sludge in combustors based on sludge incinerating technology is limited to multiple hearth incinerators only. Over 80 percent of the identified operating sludge incinerators are of the multiple hearth design. About 15 percent are fluidized bed combustors and 3 percent are electric. The remaining combustors co-fire refuse with sludge. Most sludge incinerators are located in the Eastern United States, though there are a significant number on the West Coast. New York has the largest number of facilities with 33. Pennsylvania and Michigan have the next-largest numbers of facilities with 21 and 19 sites, respectively. Sewage sludge incinerator emissions are currently regulated under 40 CFR Part 60, Subpart O and 40 CFR Part 61, Subparts C and E. Subpart O in Part 60 establishes a New Source Performance Standard for particulate matter. Subparts C and E of Part 61--National Emission Standards for Hazardous Air Pollutants (NESHAP)--establish emission limits for beryllium and mercury, respectively. In 1989, technical standards for the use and disposal of sewage sludge were proposed as 40 CFR Part 503, under authority of Section 405 of the Clean Water Act. Subpart G of this proposed Part 503 proposes to establish national emission limits for arsenic, beryllium, cadmium, chromium, lead, mercury, nickel, and total hydrocarbons from sewage sludge incinerators. -
Litter Decomposition on Directly Revegetated Tailings at the Kidston Gold Mine, North Queensland, Australia1
LITTER DECOMPOSITION ON DIRECTLY REVEGETATED TAILINGS AT THE KIDSTON GOLD MINE, NORTH QUEENSLAND, AUSTRALIA1 Andrew H. Grigg2 Abstract. An investigation of litter decomposition was undertaken at the Kidston Gold Mine in north Queensland, Australia with the aim of assessing the status of nutrient cycling capacity on a directly-revegetated tailings dam. Weight losses from leaf litter contained in litterbags placed in a 5-year old revegetated section of the dam were not significantly different from losses observed at two unmined reference sites over the 18 month study period, representing a rapid improvement in nutrient cycling capacity in the reconstructed ecosystem. However, fitted decay curves for each site predicted a slower decay constant and a longer litter half-life on the dam, which indicated that full pre-mining capability had not yet been achieved. Weight loss in the reconstructed system was most constrained by the low build-up of microbial biomass within the surface soil, which is expected to take at least 10 years to achieve pre-mining levels. In contrast, weight losses in the unmined sites appeared more related to the abundance of invertebrate fauna rather than microbial content. The results presented here of a developing system suggest that the importance of different factors affecting decomposition will reflect those that are most limiting over the course of ecosystem recovery. Additional Key Words: nutrient cycling, ecosystem recovery, microbial biomass, invertebrates. _____________________ 1Paper presented at the 2002 National Meeting of the American Society of Mining and Reclamation, Lexington KY, June 9-13, 2002. Published by ASMR, 3134 Montavesta Rd., Lexington, KY 40502. -
ANIMAL AGRICULTURE: Waste Management Practices GAO/RCED-99-205
United States General Accounting Office Report to the Honorable Tom Harkin, GAO Ranking Minority Member, Committee on Agriculture, Nutrition, and Forestry, U.S. Senate July 1999 ANIMAL AGRICULTURE Waste Management Practices GAO/RCED-99-205 United States General Accounting Office GAO Washington, D.C. 20548 Resources, Community, and Economic Development Division B-282871 July 26, 1999 The Honorable Tom Harkin Ranking Minority Member Committee on Agriculture, Nutrition, and Forestry United States Senate Dear Senator Harkin: The production of livestock and poultry animals, also known as animal agriculture, is important to the economic well-being of the nation, producing $98.8 billion per year in farm revenue. This production also contributes to the viability of many rural communities and the sustainability of an adequate food supply for the American public. However, concern over pollution resulting from intensive livestock and poultry production—in which large numbers of animals are held in confined production facilities—has increased in recent years. Nationwide, about 130 times more animal waste1 is produced than human waste—roughly 5 tons for every U.S. citizen—and some operations with hundreds of thousands of animals produce as much waste as a town or a city.2 These large volumes of waste threaten surface water and groundwater quality in the event of waste spills, leakage from waste storage facilities, and runoff from fields on which an excessive amount of waste has been applied as fertilizer. Furthermore, as animal production is increasingly concentrated in larger operations and in certain regions of the country, commonly used animal waste management practices may no longer be adequate for preventing water pollution. -
The Complete Chemical Storage Guide for Wastewater Treatment
The Complete Chemical Storage Guide for Wastewater Treatment How to build effective storage solutions for chemicals commonly used in the wastewater treatment process Introduction In addition to physical treatment (such as screening and filtering processes) and biological treatment (which includes oxidation ponds and lagoons), chemicals are essential in wastewater treatment. Wastewater treatment requires even more aggressive usage and larger amounts of chemicals than municipal drinking water treatment. As a result, proper and safe storage of the chemicals used in the wastewater treatment process is always an important consideration. This guide was developed to address common chemical storage challenges found in wastewater treatment and to provide sensible storage solutions. In the first section, we outline the five steps of a wastewater treatment process, as well as the common chemicals involved in each step. In the second section, you’ll learn more about each chemical, along with its appropriate storage considerations. Contact Us at 877-591-4827 www.polyprocessing.com E-MAIL: [email protected] Table of CONTENTS The Roles of Chemicals in the Wastewater 3 Starting with the Chemical–Tailored Storage for Lifetime Cost Savings 4 Sodium Hypochlorite 5 Sulfuric Acid 6 Ferric Chloride, Aluminum Chloride, and Polymers 7 Sodium Hydroxide 8 Hydrochloric Acid 9 How to Build the Perfect Storage System for Your Wastewater Application 10 About Poly Processing 10 p. 2 The Roles of Chemicals in the Wastewater Treatment Process Removing Solid Particles To facilitate the removal of solid particles within wastewater, chemicals such as ferric chloride, polymers, and alums are used to produce positive charges. These are intended to neutralize negatively charged solid particles. -
Energy Recovery from Sewage Sludge: the Case Study of Croatia
energies Article Energy Recovery from Sewage Sludge: The Case Study of Croatia Dinko Đurđevi´c 1,* , Paolo Blecich 2 and Željko Juri´c 1 1 Energy Institute Hrvoje Požar, 10000 Zagreb, Croatia; [email protected] 2 Faculty of Engineering, University of Rijeka, 51000 Rijeka, Croatia; [email protected] * Correspondence: [email protected] Received: 26 April 2019; Accepted: 16 May 2019; Published: 20 May 2019 Abstract: Croatia produced 21,366 tonnes of dry matter (DM) sewage sludge (SS) in 2016, a quantity expected to surpass 100,000 tonnes DM by 2024. Annual production rates for future wastewater treatment plants (WWTP) in Croatia are estimated at 5.8–7.3 Nm3/people equivalent (PE) for biogas and 20–25 kgDM/PE of sewage sludge. Biogas can be converted into 12–16 kWhel/PE of electricity and 19–24 kWhth/PE of heat, which is sufficient for 30–40% of electrical and 80–100% of thermal autonomy. The WWTP autonomy can be increased using energy recovery from sewage sludge incineration by 60% for electricity and 100% of thermal energy (10–13 kWhel/PE and 30–38 kWhth/PE). However, energy for sewage sludge drying exceeds energy recovery, unless solar drying is performed. 2 The annual solar drying potential is estimated between 450–750 kgDM/m of solar drying surface. The lower heating value of dried sewage sludge is 2–3 kWh/kgDM and this energy can be used for assisting sludge drying or for energy generation and supply to WWTPs. Sewage sludge can be considered a renewable energy source and its incineration generates substantially lower greenhouse gases emissions than energy generation from fossil fuels. -
Marine Litter Legislation: a Toolkit for Policymakers
Marine Litter Legislation: A Toolkit for Policymakers The views expressed in this publication are those of the authors and do not necessarily reflect the views of the United Nations Environment Programme. No use of this publication may be made for resale or any other commercial purpose whatsoever without prior permission in writing from the United Nations Environment Programme. Applications for such permission, with a statement of the purpose and extent of the reproduction, should be addressed to the Director, DCPI, UNEP, P.O. Box 30552, Nairobi, Kenya. Acknowledgments This report was developed by the Environmental Law Institute (ELI) for the United Nations Environment Programme (UNEP). It was researched, drafted, and produced by Carl Bruch, Kathryn Mengerink, Elana Harrison, Davonne Flanagan, Isabel Carey, Thomas Casey, Meggan Davis, Elizabeth Hessami, Joyce Lombardi, Norka Michel- en, Colin Parts, Lucas Rhodes, Nikita West, and Sofia Yazykova. Within UNEP, Heidi Savelli, Arnold Kreilhuber, and Petter Malvik oversaw the development of the report. The authors express their appreciation to the peer reviewers, including Catherine Ayres, Patricia Beneke, Angela Howe, Ileana Lopez, Lara Ognibene, David Vander Zwaag, and Judith Wehrli. Cover photo: Plastics floating in the ocean The views expressed in this report do not necessarily reflect those of the United Nations Environment Programme. © 2016. United Nations Environment Programme. Marine Litter Legislation: A Toolkit for Policymakers Contents Foreword ..................................................................................................