Ammonia volatilization from urea David E. Kissel University of Georgia.

Slides:



Advertisements
Similar presentations
Water in the Atmosphere
Advertisements

Nitrogen Loss Research
Cooperator: Jeff Whitmus, Research Assistant pH 2.5 to 3.5 units urea prill urease NH 4 + OH - NH 4 + OH - NH 4 + OH - NH 4 + OH - NH 4 + OH - NH 4 +
Soil Fertility and Nutrient Bioavailability Sponsored by the DEST program China Higher Education Strategic Initiatives © The University of Adelaide.
Nitrogen Source Issues Dale Leikam Kansas State University Manhattan, KS.
 Nitrogen › Not available › NH3 is the devil  Phosphorus › Not available › Around for a long time › Ortho P is better than Poly P.
Class evaluations.
Interactions of Earth Systems
Chapter 19 – Production of Ammonia. Properties of Ammonia.
Ammonia Volatilization from Wet Animal Manures C.W. Wood, J.J. Meisinger, P.A. Moore, Jr., and R.B. Thompson Auburn University, USDA-ARS, Beltsville, MD.
FERTILIZERS. Fertilizer Defined Fertilizer – material applied to soil or plants to supply essential elements Four categories: MineralInorganic Organic.
Objectives: i. Outline the steps in the manufacture of ammonia from its elements, by the Haber Process. ii. Discuss the uses of ammonia iii. Assess the.
An integrated study of nutrient leaching and greenhouse gas emissions Tyson Ochsner and Rodney Venterea Soil and Water Management Research Unit Agricultural.
Nitrogen Sources and Turf Response Laurie Trenholm UF-IFAS Turf Specialist.
Nitrogen Dynamics of Soils  Introduction  Forms and Role of Nitrogen in Soils & Plants  Nitrogen Fixation  Distribution of Nitrogen (N-Cycle)  Nitrogen.
The Nitrogen Cycle. Significance of the Nitrogen Cycle to Organisms  Allows nitrogen to be available in a usable form to organisms that need it  Provides.
EFISIENSI PUPUK DAN PEMUPUKAN NITROGEN Bahan kajian MK Pemupukan Dosen: Prof Dr Ir Soemarno MS Jur Tanah FP UB, 2011.
Mineral Nutrition & Management Dr. Richard Rosecrance California State University, Chico.
The nitrogen cycle. Why is the cycle important and what is nitrogen used for? Not many organisms can use nitrogen directly from the air (78%) Recycling.
Core Training Feb 9th In-Service
Soil pH Paulo Pagliari Department of Soil, Water, and Climate
E NVIRONMENTAL CHEMISTRY E 12. water and soil. W ATER AND SOIL Solve problems relating to the removal of heavy- metal ions, phosphates and nitrates from.
Nitrogen Information N By: Becky McGuire. Key Facts a. N is in every plant cell b. N is 78% of atmosphere c. Production of N comes from ammonia (NH3)
Lecture 12a Soil Chemistry / Soil pH Soil pH is the single most important chemical property of the soil (like soil texture is to the physical properties)
Nitrogen Sources for Cotton Across the Belt
III. Fertilizers: Utilization and Types. Introduction  World demand for increased food, feed, and fiber production necessitates us of fertilizers.
Environmental Factors That Influence Herbicide Performance Dr. Eric P. Prostko Extension Weed Specialist University of Georgia Tifton.
Oklahoma State University Department of Plant and Soil Sciences Oklahoma State University Department of Plant and Soil Sciences Nitrogen Loss from Urea.
Soil Fertility and Nutrient Cycling in Grazed Systems Miguel L. Cabrera Crop & Soil Sciences University of Georgia.
Nutrient Cycling Amy Shober, Ph.D. UF/IFAS Gulf Coast REC Advanced Soils & Fertilizers Topics for Master Gardeners 1 of 14 ©2008 University of Florida-IFAS.
What is the name given to the lines on the weather map, and what are they connecting?
Managing Manure for Crop Production when Feeding DDGS Kyle Jensen ISU Extension Field Specialist-Crops.
The Nitrogen Cycle Science 10 “Old Outcomes”. The Importance of Nitrogen Nitrogen is a main ingredient in fertilizer. Why does fertilizer produce better.
SOIL Medium: The soil mixture is the plant’s source for food, water, and support The soil mix will have effect on the health, vitality, and appearance.
PRODUCTION OF UREA. Urea is a white dry organic compound and a crystalline substance and has minimum of 46% Nitrogen calculated in dry state. M.P: 132.
(commercial fertilizers)
Residue Biomass Removal and Potential Impact on Production and Environmental Quality Mahdi Al-Kaisi, Associate Professor Jose Guzman, Research Assistant.
Scheme of the equilibrium Environmental Compartments Model.
1. Meteorology Chapter 1 Introduction to the Atmosphere Meteorology \ Dr. Mazin sherzad.
Properties of Water. Water: 2 atoms of hydrogen, one of oxygen Held together by strong, covalent bond - electrons are ‘shared’ Water molecules interact.
Soil Electrical Conductivity
Moisture Moisture = Water Vapor (gas) Gets into the atmosphere by: 1.Evaporation = liquid to gas (opposite of condensation) 2.Transpiration = plants release.
Soil Respiration Unit: Soil Science. Objectives O Define: soil respiration and soil microbes O Explain the role of soil respiration in determining soil.
NITROGEN CYCLE Department of Plant and Soil Sciences Oklahoma State University Stillwater, OK Tel: (405)
Soil Nitrogen Unit: Soil Science.
Gas and Aerosol Partitioning Over the Equatorial Pacific Wenxian Zhang April 21, 2009.
Jac J. Varco1, Robert E. Earnest1, and Jimmy D. Johnson2
Fertilizing for No-till
What Happens to Precipitation?
Soil Bulk Density Unit: Soil Science. Objectives O Define: ammonification, available water holding capacity, nitrification, bulk density, denitrification,
What Happens to Precipitation?
Irrigation Measurements and Cost Topic #2073 Megan Burgess.
IAFNR Plant and Soil Sciences Module
Soil pH P & K N & S Secondary & Micros Multi- Nutrient Variable Application In-Season Cues  Much like a Ladder › One Step at a Time.
Soil Acidity and Review of Colloid Charge. Mineral Charge.
Moisture in the Atmosphere Beaker demo. Humidity Humidity - how much moisture is in the air. Saturated air is air that is full of water. Dew point is.
Nutrient Cycles Reduce, Reuse, Recycle!!. I. Biogeochemical Cycles a.a.k.a. nutrient cycles b.Nature does not throw anything away c.Cycle – the path from.
Nitrogen sources for Topdressing Using Variable Nitrogen Fertilizers.
Pretreat Yourself to a Better Investment. Position in the Field AVAIL: For growers worldwide who want to maximize their crops’ phosphorus fertilizer performance.
Where do Enhanced Efficiency Nitrogen Fertilizers and Split N Applications Fit? Cynthia Grant and Alan Moulin AAFC - Brandon Research Centre Nicolas Tremblay.
Nitrogen Stability: Protecting Your Nitrogen Investment
Soil Bulk Density/Moisture/Aeration
Nitrogen sources for Topdressing Winter Wheat In Oklahoma
HOW CAN WE REDUCE VOLATILIZATION LOSSES?
Name:- Guajarati dharmesh Enrollment no Subject – chemical process industries-1 SEM-3 Subject code
Wolfram Zerulla BASF SE, Agricultural Center Limburgerhof
Hydrologic Cycle, Properties of Water, Factors affecting Life in Water
HOW CAN WE REDUCE VOLATILIZATION LOSSES?
Nutrient Cycles Chapter 16: Ecosystems.
Presentation transcript:

Ammonia volatilization from urea David E. Kissel University of Georgia

Overview Evolution of Urea consumption Definitions Urea Dissolution and Diffusion Urea Hydrolysis Ammonia Volatilization Research Results Summary

Urea Ammonium nitrate Nitrogen solutions Total compound N / / % Millions of tonnes USA Evolution of N Fertilizers Consumption Anhydrous ammonia

Overview Evolution of Urea consumption Definitions Urea Dissolution and Diffusion Urea Hydrolysis Ammonia Volatilization Research Results Summary

Definitions Dissolution: urea absorbs water and converts from solid to liquid Hydrolysis: urea converts to ammonium (NH 4 + ) Diffusion: movement due to motion of molecules –Urea has no charge, diffuses easily –NH 4 + has charge, diffuses slowly

Overview Evolution of Urea consumption Definitions Urea Dissolution and Diffusion Urea Hydrolysis Ammonia Volatilization Research Results Summary

Urea Dissolution Urea has to be dissolved before it can be hydrolyzed

Urea Dissolution Urea has to be dissolved before it can be hydrolyzed Urea can absorb water from the atmosphere and from the soil/crop residue

Urea Dissolution Urea has to be dissolved before it can be hydrolyzed Urea can absorb water from the atmosphere and from the soil/crop residue Absorption of water from the atmosphere depends on relative humidity (RH)

Urea Dissolution Urea has to be dissolved before it can be hydrolyzed Urea can absorb water from the atmosphere and from the soil/crop residue Absorption of water from the atmosphere depends on relative humidity (RH) Critical relative humidity (CRH) is the RH at which urea dissolves

Effect of Temperature on CRH and Water Solubility of Urea

Urea RH > CRH (80%) Crop residue Urea dissolution and diffusion Dry Soil

Urea Urea dissolution and diffusion Urea Crop residue Urea 1/2 inch Wet Soil

Urea Crop residue Urea 2 inches

Urea Urea Diffusion into Soil Urea Diffusion Depth Determined by soil moisture

Urea Diffusion into Soil (after 10 days)

Overview Evolution of Urea consumption Definitions Urea Dissolution and Diffusion Urea Hydrolysis Ammonia Volatilization Research Results Summary

Urea Hydrolysis Urea 2 Urease enzyme + H+H+ 2 NH 4 + Urease is derived from crop residues and soil microorganisms

Urea Crop residue Urease inhibitor Urea

Overview Evolution of Urea consumption Definitions Urea Dissolution and Diffusion Urea Hydrolysis Ammonia Volatilization Research Results Summary

(aq) Soil solution NH 4 + NH 3 Volatilization Process Urea Atmosphere Clay OM NH 4 + Hydrolysis NH 4 + (aq) + Equilibrium H+H+ (gas) Soil air + H +

Effect of soil pH on NH 3 as % of Total N

(aq) Soil solution NH 4 + NH 3 Volatilization Process Urea Atmosphere Clay OM NH 4 + Hydrolysis NH 4 + (aq) + Equilibrium H+H+ (gas) Soil air + H +

Increase in soil pH depends on soil H + buffering capacity Higher clay and OM contents lead to higher soil H + buffering capacity

Atmosphere H+H+ H+H+ H+H+ H+H+ H+H+ H+H+ H+H+ NH 4 + Urea NH 4 + Urea ½ inch pH 6789 NH 4 + CEC H+H+ Urea Urea hydrolyzes on the soil surface

H+H+ H+H+ H+H+ H+H+ H+H+ H+H+ H+H+ H+H+ NH 4 + Urea NH 4 + Urea 2 inches pH 67 NH 4 + Urea CEC Urea hydrolyzes below the soil surface

Soil + Effect of Temperature on NH 3 Volatilization NH 4 + Urea H+H+ ½ inch Temperature

Effect of Temperature on Urea Hydrolysis

Soil + Effect of Temperature on NH 3 Volatilization NH 4 + Urea H+H+ ½ inch Temperature

Effect of Temperature on % of NH 3 pH = 8.5

Soil + Effect of Temperature on NH 3 Volatilization NH 4 + Urea H+H+ ½ inch Temperature

Effect of Temperature on Conversion of Aqueous NH 3 to Gaseous NH 3

Soil + Effect of Temperature on NH 3 Volatilization NH 4 + Urea H+H+ ½ inch Temperature

Soil Wind speed + Effect of Wind Speed on NH 3 Volatilization NH 4 + Urea H+H+ Atmosphere ½ inch

Ammonia Loss (% of Applied N) UAN UREA Nitamin 51mm Replication II UAN UREA Nitamin 51mm Replication I Days After Application UAN UREA Nitamin 51mm Replication III

Optimum Conditions for Volatilization Small diffusion depth into soil RH > CRH High temperature High wind speed Low pH buffering capacity

Overview Evolution of Urea consumption Definitions Urea Dissolution and Diffusion Urea Hydrolysis Ammonia Volatilization Research Results Summary

Urea Applied to Pasture - Fall 2004 Days after application NH 3 loss (% of applied N) Soil water content (g g -1 ) Rainfall (mm) Nitamin® UAN Urea Rainfall Soil water content Temp = 47 o F

Days after application NH 3 loss (% of applied N) Nitamin® UAN Urea Soil water content (g g -1 ) Rainfall (mm) Rainfall Soil water content Temp = 63 o F Urea Applied to Pasture – Spring 2005

Urea NH 4 + Atmosphere Clay OM Urea NH 4 + (aq) + Equilibrium NH 4 + (aq) H+H+

Days after application NH 3 loss (% of applied N) Nitamin® UAN Urea Rainfall Soil water content Soil water content (g g -1 ) Rainfall (mm) Temp = 62 o F Urea Applied to Pasture - Fall 2005

Time of RH above CRH in the first 30 d Time of RH > CRH (h) Total: RH > CRH =19 days 63 % Days after application

Urea Atmosphere Urea Soil water content (0.07 g g -1 ) RH > CRH (80%) Permanent wilting point (0.04 g g -1 ) Fescue thatch NH 4 +

Temp = 69 o F Urea Applied to Pasture – Spring 2006

Urea NH 4 + Atmosphere NH 4 + (aq) + Equilibrium NH 4 + (aq) H+H+ Soil water content (0.15 g g -1 ) Field capacity (0.18 g g -1 ) CEC

Ammonia volatilization losses under field conditions Fertilizer Ammonia loss (% of applied N) Fall 2004 Urea UAN Nitamin® 19 a* 6 b Spring a 13 a 14 a Within a column, values followed by the same letter are not significantly different according to Fisher’s LSD at p=0.05 Summary of Pasture Results Fall 2005Spring a 33 b 34 b 24 a 18 a

Summary for Pastures/No-Till Dry Soil, Dry Residue, RH < CRH: OK Dry Soil, Dry Residue, RH > CRH: not OK Wet Soil, Wet Residue: not OK Apply on dry soil, dry residue, expected low RH, and hope for 1 inch of rain whenever it rains. Apply on wet soil if 1 inch rain/irrigation is expected.

Summary for Clean-Till Crops Dry Soil: OK Wet Soil: not OK Apply on dry soil and hope for 1 inch of rain whenever it rains. Apply on wet soil if 1 inch of rain/irrigation is expected.

Summary for Pastures/Crops Knifed or disked in Dribbled Broadcast Knifed of disked in better than Dribbled Dribbled better than Broadcast

Urea Applied to Pine Plantations March 14 – April 12 (59 o F) Rain

Urea Applied to Pine Plantations 66 o F Rain

Laboratory Results (77 o F, 90% RH)

Organic Layer NH 4 + CEC Urea Pine needle photo

Urea NH 4 + Organic Layer NH 4 + CEC Pine needle photo

Summary for Pine Plantations Dry Forest Floor, RH < CRH: OK Dry Forest Floor, RH > CRH: not OK Wet Forest Floor: not OK Apply on dry forest floor, with expected low RH, and hope for 1 inch of rain whenever it rains. Apply on wet forest floor if 1 inch rain is expected.

Questions?