The Challenge to Produce More Food and Energy with Less Pollution
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Putting Drinking Water First to Address Nutrient Pollution
Putting Drinking Water First to Address Nutrient Pollution “Nutrient pollution remains one of the greatest challenges to our Nation’s water quality and presents a growing threat to public health and local economies — contributing to toxic harmful algal blooms, contamination of drinking water sources, and costly impacts on recreation, tourism, and fisheries.” 1 — Joel Beauvais, Deputy Assistant Administrator, U.S. EPA, September 22, 2016 Since the passage of the Clean Water Act in 1972 the United States has made great progress in cleaning up industrial chemicals and sewage pollution, but has failed to significantly reduce run-off of nutrient pollution into our nation’s rivers, lakes, and bays. Nutrient pollution refers to nitrogen and phosphorus, which are essential life elements that have enabled agriculture production in the United States to thrive, but at a huge cost to water quality. The agriculture industry, the largest water polluter in the country, is largely exempt from Clean Water Act protections/programs. When it rains, nutrient-rich fertilizer and animal waste pour into nearby streams and rivers, contributing to toxic algal outbreaks Sources of Excess Nutrients and dead zones downstream. This pollution also seeps into groundwater. Urban storm water runoff, wastewater treatment AGRICULTURE Fertilizer runoff plant discharges, failing septic tanks, and fossil fuel emissions (nitrogen and are other sources of nitrogen and phosphorus pollution.2 phosphorus) and Pollution from nitrogen and phosphorus is one of the most animal waste pervasive water quality problems in the U.S.3 and there is increasing concern about their impact on drinking water. INDUSTRY Chemical discharge Nutrients and Water Quality and waste Excess nutrients can cause algae to grow faster than aquatic ecosystems can process, resulting in algal outbreaks that are URBAN LIFE Sewage and green, red, or brown, and appear like paint or thick scum on waste runoff the surface of water. -
Global Availability of Phosphorus and Its Implications for Global Food Supply: an Economic Overview by Markus Heckenmüller, Daiju Narita, Gernot Klepper
Global Availability of Phosphorus and Its Implications for Global Food Supply: An Economic Overview by Markus Heckenmüller, Daiju Narita, Gernot Klepper No. 1897 | January 2014 Kiel Institute for the World Economy, Hindenburgufer 66, 24105 Kiel, Germany Kiel Working Paper No. 1897 | January 2014 Global Availability of Phosphorus and Its Implications for Global Food Supply: An Economic Overview Markus Heckenmüller, Daiju Narita, Gernot Klepper Abstract: Being of crucial importance for agricultural production and also having experienced significant price volatility, phosphate and its future availability have drawn growing attention from both academics and the public over the last years. This paper overviews the recent literature and data on the availability of phosphorus and discusses the economic aspects of phosphate scarcity by describing major price determinants of the global phosphate market. We show that past price fluctuations of phosphate rock and phosphate fertilizers are not a reflection of physical phosphate rock depletion but rather attributable to numerous other demand- and supply-side factors. Given the current reserve estimates for phosphate rock, neither an exhaustion of global reserves nor a peak event is likely to occur within this century. However, these estimates are subject to a significant degree of uncertainty. Moreover, the global distribution of phosphate production and reserves is highly skewed and has the potential to pose a threat to food security in developing countries through factors such as the volatility -
Peak Phosphorus – the Next Inconvenient Truth
Peak Phosphorus – The Next Inconvenient Truth Arno Rosemarin Stockholm Environment Institute Phosphorus Seminar Gamla Stan May 19, 2010 The linear path of phosphorus in modern times (Princeton Univ.) Vaccari, 2009 countries as well, mainly in the north; so th the north; so well, mainly in countries as Sulfuric acid which is usedin 90% of the Phosphorus Reserves are in 90% ofthePhosphorus 5 Countries extracting the phosphorus is extracting ere are several geopolitical us challenges ahead of ere are several found in a limited number of a found in Caldwell, SEI, based on USGS, 2009 Phosphate Rock Economic Reserves, 1997-2009 (from USGS summaries) 20 000 000 18 000 000 16 000 000 China k 14 000 000 12 000 000 China Moroc c o & W. Sahara osphate roc South Africa hh 10 000 000 United States Morocco/West Sahara Jordan 8 000 000 Other countries 00 tonnes p 00 1 6 000 000 4 000 000 2 000 000 0 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 The definition of economic rock reserves is not standardised. China has changed the definition twice after joining the WTO in 2003. In 2009 they downgraded their economic reserve by 30%. There is a need for a world standard and global governance – still non-existent. Depletion of Global Economic Phosphorus Reserves 16000000 14000000 12000000 10000000 years from 2008 tons cc reserve (2% scenario) 8000000 2% annual increase in extraction reserve (1% scenario) 00 metri 00 1% annual increase in extraction 1 6000000 4000000 010 22 2000000 rin, SEI n USGS data aa oo 0 Rosem Based 1 4 7 10131619222528313437404346495255586164 -
Phosphate Rocks!
Essay By: Jacob Kollen Phosphate Rocks! INTRODUCTION On approximately two thirds of the world’s arable land, phosphorus is a plant growth limiting nutrient (Lambers et al., 2013). Agriculture utilizes roughly 80% of the mined phosphate rock as fertilizer, with the remaining 20% being utilized in products such animal feed supplements, food preservatives, pesticides, fungicides, herbicides, water treatments, cosmetics, and metallurgy (Sattari, 2012). Currently we derive approximately 63% of our phosphorus fertilizer from phosphate rock, with the remainder being derived from animal manure, sewage sludge, and guano (Rittman, 2011). Phosphate rock reserves are finite, which leads to a predicament: we will run out of phosphate rock eventually. The concept, stressed by peak resource theory, is that once global reserves are depleted by half, economic factors will drive resource prices high and unattainable by many (Cordell and White, 2013). Phosphorus does not have a substitute in biomass production. Unlike energy resources, we cannot look to other resources to mitigate our dependency upon phosphate rock (Gilbert, 2009). Phosphorus has potential to be recycled (Rittman, 2011). On a large scale, if agriculture gears itself to derive phosphorus fertilizer from recycled phosphorus we can avoid phosphorus resource scarcity. BACKGROUND Low levels of phosphorus in soils results in phosphorus deficiencies in crops which will grow poorly and can be diagnosed by observing leaves turning a blue-green color. Farmers apply phosphorus fertilizers to agricultural soils to mitigate crop growth limitation by phosphorus. Known global phosphate rock reserves are concentrated in just a handful of countries. Phosphate rock reserves that contain at least 8.5 x 1013 tons of phosphate rock are located in Morocco, China, Algeria, Syria, Jordan, South Africa, the United States and Russia (Jasinski, 2013). -
INI2016 De Vries Wim1
Impacts of dietary changes on global scale nitrogen losses to air and water Wim de Vries1,2, Jia Wei1, Hans Kros1, David Windhorst3 and Lutz Breuer3 1Alterra, Wageningen University and Research Centre (WUR), PO Box 47, 6700 AA Wageningen, The Netherlands 2Environmental Systems Analysis Group, Wageningen University, PO Box 47, 6700 AA Wageningen, The Netherlands 3Justus-Liebig University of Giessen, Heinrich-Buff-Ring 26, 35392 Gießen, Germany Abstract A simple fast calculation approach has been developed that gives insight in the overall effects of dietary changes on nitrogen (N) emission to air and water by 2050 for ten identified world regions. The impact of dietary change on N fertilizer and N manure applications and related emissions was based on the consumption of crop and animal commodities, making use of the FAO data from 1961 to 2005 and extrapolating the data towards 2050 in response to five dietary change scenarios. Scenarios included a ‘North American Diet’ (NAD), a ‘Same Diet’ (SD), a ‘Business-as-Usual’ (BAU) diet; a ‘Demitarian Diet’ (DD) and a ‘Vegan Diet’ (VD). The calculated N2O and NH3 emissions and N leaching/runoff for the reference year (i.e. 2005) showed good agreement with various literature estimates. N2O was the most persistent problem, even increasing under the VD scenario, due to the increased use of N fertilizer to cultivate food crops and the assumed high contribution of N fertilizer to N2O emission. NH3 emissions increased three times in the NAD scenario, while it decreased by 13% in the VD scenario. This happens because NH3 emissions mainly follow the N manure trends. -
Capturing the Lost Phosphorus
Marquette University e-Publications@Marquette Civil and Environmental Engineering Faculty Civil, Construction, and Environmental Research and Publications Engineering, Department of 8-2011 Capturing the Lost Phosphorus Bruce E. Rittmann Arizona State University at the Tempe Campus Brooke Mayer Marquette University, [email protected] Paul Westerhoff Arizona State University at the Tempe Campus Mark Edwards Arizona State University at the Polytechnic Campus Follow this and additional works at: https://epublications.marquette.edu/civengin_fac Part of the Civil and Environmental Engineering Commons Recommended Citation Rittmann, Bruce E.; Mayer, Brooke; Westerhoff, Paul; and Edwards, Mark, "Capturing the Lost Phosphorus" (2011). Civil and Environmental Engineering Faculty Research and Publications. 34. https://epublications.marquette.edu/civengin_fac/34 Marquette University e-Publications@Marquette Civil, Construction and Environmental Engineering Faculty Research and Publications/College of Engineering This paper is NOT THE PUBLISHED VERSION; but the author’s final, peer-reviewed manuscript. The published version may be accessed by following the link in the citation below. Chemosphere, Vol. 84, No. 6 (August 2011): 846-853. DOI. This article is © Elsevier and permission has been granted for this version to appear in e-Publications@Marquette. Elsevier does not grant permission for this article to be further copied/distributed or hosted elsewhere without the express permission from Elsevier. Capturing the Lost Phosphorus Bruce E. Rittmann -
Peak Phosphorus
Peak Phosphorus A Potential Food Security Crisis TARIEL MÓRRÍGAN Global Climate Change, Human Security, and Democracy Global & International Studies University of California Social Sciences & Media Studies Building, Room 2006 Santa Barbara, CA 93106-7065 [email protected] ~ February 21, 2010 Peak Phosphorus “There are no substitutes for phosphorus in agriculture.” ~ United States Geological Survey, 2009 Summary • Phosphorus is an element necessary for all life . Phosphorus is one of the three major nutrients required for plant growth: nitrogen (N), phosphorus (P), and potassium (K). • Global phosphorus production most likely peaked in 1989 . If global phosphorus production has not yet peaked, it will likely do so by 2033. • The quality of remaining phosphate rock is decreasing and the production costs are increasing. • Global reserves will start to run out within 50–100 years . • Once phosphorus supplies are exhausted, phosphorus will need to be recovered and reused in order to avoid a massive global food security crisis . There are no substitutes for phosphorus in agriculture . • In 2007–2008, the price of phosphate rock increased dramatically worldwide due to increased agricultural demand and limited supplies of phosphate rock. The average U.S. price in 2008 was more than double that of 2007, and was four-times greater than that of 2004. Average spot prices from North Africa and other exporting regions increased more than five-times the average price in 2007. • Most of the world's farms do not have or do not receive adequate amounts of phosphorus . Feeding the world's increasing population will accelerate the rate of depletion of phosphate reserves. -
Missing Global Governance of a Critical Resource Preliminary Findings from 2 Years of Doctoral Research
Paper prepared for SENSE Earth Systems Governance, Amsterdam, 24th-31st August, 2008 The Story of Phosphorus: missing global governance of a critical resource Preliminary findings from 2 years of doctoral research Dana Cordell PhD Candidate [email protected] Institute for Sustainable Futures, University of Technology Sydney, Australia and Department of Water and Environmental Studies, Linköping University, Sweden Abstract Phosphorus is a critical resource for food production in the form of fertilizers, yet current global phosphate reserves could be depleted this century. More concerning is a global peak in phosphorus production – peak phosphorus – based on current official estimates of world resources, is estimated to occur around 2030, only decades after the likely peak in oil production. The situation for phosphorus is worse than for oil however, as there is no substitute for phosphorus in food production. Demand for phosphorus will increase over the next 50 years as the world population is projected to increase by 50% and with changing diets. While the exact timing of peak production might be disputed, it is widely known within the industry that the quality of remaining phosphate rock is decreasing, and costs are increasing. The price of phosphate rock has increased 700% in 14 months alone. Yet unlike water, energy and nitrogen, there is no international organisation which has taken on responsibility for the long-term stewardship or management of phosphorus resources for global food security. Institutional arrangements surrounding the global phosphorus cycle are fragmented and phosphorus sustainability is perceived quite differently by different stakeholders. In the absence of any deliberate international oversight, phosphorus resources are governed by the forces of the international market and national interest. -
From Waste to Plate: Examining the Role of Urban Biosolids in Recycling Phosphorus
FROM WASTE TO PLATE: EXAMINING THE ROLE OF URBAN BIOSOLIDS IN RECYCLING PHOSPHORUS A THESIS PRESENTED TO THE FACULTY OF ARCHITECTURE, PLANNING, AND PRESERVATION COLUMBIA, UNIVERSITY Submitted IN partial FULFILLMENT OF THE REQUIREMENT FOR THE DEGREE MASTER OF SCIENCE IN URBAN PLANNING MARLA WEINSTEIN May, 2013 ABSTRACT Phosphorus, a nutrient found in soil, is vital to plant life and therefore essential to our global food supply. Naturally recycled by ecosystem services, human cities have interrupted this cycle as phosphorus now accumulates in urban areas rather than returning to the land. In turn, we have turned to mined phosphates to supplement fertilizers and ensure our global food supply. As phosphorus deposits are a limited resource, however, we face future phosphorus shortages and threats to the security of our food supply. Biosolids, or treated waste, is a byproduct of our sewage treatment system and represent an opportunity for phosphorus recovery and recycling. This research (1) examines the role of biosolids in replenishing the natural phosphorus cycle and reducing our dependence on mined-phosphates by (2) examining the case study of NYC biosolid management in order to gain insight that can be extracted and applied to other global cities. Ultimately findings suggest biosolids can relink the natural cycle, framing biosolids as a resource, rather than a waste, for urban areas and recommend cities promote biosolid demand through contracting, land application siting, and investments in nutrient recovery technologies. ACKnowledgements A special thanks to: Professor Elliott Sclar, Thesis Advisor Professor Steve Cohen, Thesis Reader Michael, Nancy, & Bethany Weinstein Rebecca Kuss, Samantha Lazar, & Lorie Grushka EXECUTIVE SUMMARY 5 BACKGROUND 6 METHODOLOGY 13 FINDINGS 14 ANALYSIS 17 CONCLUSIONS 20 EXECUTIVE SUMMARY Simply stated, ecosystem services are the benefits we receive from healthy functioning ecosystems. -
The Influence of Food Choices on Nitrogen Emissions and the European Environment
‘Nitrogen on the Table’ assesses the influence of food choices on nitrogen Table on the Nitrogen pollution, greenhouse gas emissions and land use in Europe. The European Nitrogen Assessment (ENA) identified agriculture as a major source of nitrogen losses. Nitrogen The current total loss of reactive nitrogen from European Union agriculture amounts to an estimated 6.5 - 8 million tonnes per year, representing around 80 % of reactive nitrogen emissions to the EU environment. These nitrogen losses affect our air quality (through ammonia and its links to particulate matter), water quality (through nitrates), biodiversity and soil quality (through increased nitrogen deposition) and greenhouse gas balance (through the release of nitrous oxide). Assessment Nitrogen European the of Report Special A on the Table The present ENA Special Report has been prepared by the Expert Panel on Nitrogen and Food of the UNECE Task Force on Reactive Nitrogen. It examines nitrogen and other pollution losses from the food system and assesses the potential impacts of alternative diets on emissions of nitrogen to air and water. It then considers the potential impacts on land-use change and associated greenhouse gas emissions. The influence of food choices The study finds that reductions in reactive nitrogen emissions associated with decreased intake of meat and dairy products would have substantial benefits, not only within the EU, but also at continental and on nitrogen emissions and the global scales. The scenarios also match to consumption patterns that are better -
Processes Controlling Biosphere Atmosphere Interactions of Ammonia
Controlling environmental nitrogen: How can it be done? How will it reduce impacts? Mark Sutton TFRN EXPO Milan 10 July 2015 The innocent polluters The innocent polluters Feedlots with 100,000 cattle Chicken farms with 2,000,000 Global Nr production & dispersion Human Nr 60 Production: 30 10 -1 (Tg yr ) 9 8 1860: 15 7 1995: 156 6 5 2005: 191 4 3 2 2005 sources: 1 0.75 Haber Bosch: 120 0.5 Biol N fixn: 50 0.25 0.1 -2 -1 NOx emission: 40 AtmosphericAtmospheric Nr Nr deposition deposition (mg (mg N N m m-2yearyear-)1) 0 Galloway et al. Science (2008) Simplified view of the Nitrogen Cascade Greenhouse gas balance Stratospheric High temperature ozone loss combustion & industry Nitrous Oxide Tropospheric (N2O) ozone formation Urban air Particulate quality Matter Nitrogen oxides Ammonium nitrate (NOx) in rain (NH4NO3) Fertilizer manufacture Further emission Ammonia of NOx & N2O (NH ) carrying on Nr 3 the cascade Crop biological nitrogen fixation Crops for food & animal feed Eventual Intended denitrification N flow to N2 Terrestrial Eutrophication Livestock farming N in Unintended r for food Natural ecosystems N flows manure Soil acidification N form in Leached Nitrate Nitrate in streams, the cascade (NO -) 3 groundwater & Freshwater Eutrophication coastal seas Environmental concern from Nr Marine Eutrophication Five key threats The WAGES of too much nitrogen Water quality Air quality Greenhouse balance Ecosystems Soil quality Plus better food & energy supply European Nitrogen Assessment, 2011 Lichen: Cladonia uncialis Ammonia contributes substantially to particulate matter (PM) concentrations • Reduced visibility • Human heath impacts Castell’ Arquato, near Parma, Italy NH3 emission Nitrogen Damage Costs & Sources EU Damage cost: 70 - 320 billion € / year Nature 14 April 2011 EU benefit-cost ratios: NH3 & NOx mitigation UNECE Air Convention: Task Force on Reactive Nitrogen NH3 NOx Van Grinsven et al. -
Biology Ecosystems May 19, 2020 High School Applied Biological Science
High School Science Virtual Learning Biology Ecosystems May 19, 2020 High School Applied Biological Science Lesson: Human Impact on Ecosystems Air and Water Pollution Objective/Learning Target: Students will understand the effect of human influences on air and water pollution. Bell Ringer Activity 1. What type of human impact is happening in this picture? 2. What type of human impact is happening in this picture? Bell Ringer Answers 1. Crude oil drilling where we extract oil from the earth by drilling wells in underground reservoirs. 2. This is air pollution where we release large/harmful quantities of things such as gas, particulates, and biological molecules into the atmosphere of the earth. Let’s Get Started! Lesson Activity: Directions: 1. Read the articles on water and air pollution. 2. Take notes on how humans have impacted water and air quality. Links: article #1, article #2, article #3 Practice Questions 1. What is a “dead zone,” and what is its cause? 2. Why is watershed management important to maintaining good water quality in a large river or lake? 3. What causes acid rain? 4. What two environmental effects are mainly associated with the burning of fossil fuels? 5. The human population (about 7.8 billion) may reach 9 billion by 2100. Most of those people will live in cities. Predict the impact of city growth on natural ecosystems and farmland. What will happen if sustainable development is not achieved? Answers to Practice Questions 1. A dead zone is an area of freshwater or seawater that is oxygen-poor. Dead zones are caused by excess amounts of nitrogen and phosphorus that is found in raw sewage.