Section 5.3 – Estimating Land Requirement

Slides:

Advertisements

Similar presentations

Clain Jones, Andrew John, Adam Sigler, Perry Miller and Stephanie Ewing Department of Land Resources and Environmental Sciences Effect of Agricultural.

Advertisements

Digestate handling.

Phosphorus and Potassium CNMP Core Curriculum Section 5 – Nutrient Management.

Phosphorus Index Based Management Douglas Beegle Dept. of Crop and Soil Sciences Penn State University

Daily Manure Production Per Animal We have estimates of manure production –4.5 kg/day/hd for swine (liquid manure) –45-50 kg/day/hd for dairy cow (liquid)

2013 KY NRCS (590) Nutrient Management Standard Highlights: NRCS 590 is now only required for producers applying to receive NRCS financial or technical.

Chapter 6: Record Keeping. Record Keeping Record keeping is needed to keep up with the management of the waste application system.Record keeping is needed.

CENTURY ECOSYSTEM MODEL Introduction to CENTURY. WHY CENTURY Evaluate Effects of Environmental Change Evaluate Changes in Management.

Waste Handling for Poultry Production Lori Marsh, Associate Professor, Biological Systems Engineering, Virginia Tech.

Managing Ammonia in Agriculture USDA Research Efforts.

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.

Environmetal problems related to manure management Greenhouse gas emission from manure stores.

Cover crop workshop, Oct 21 st 2009 Bradford Farm Maetee Patana-Anake*, Tim Reinbott # and Bill Jacoby* *Biological Engineering # Bradford Farm Research.

S TATE T ECHNICAL M EETING February 14, AGENDA Ag Water Quality Plans Nutrient Management Plans – Options for producers.

Nutrient Management Planner Certification Program Planner Certification Training Dr. Mark Risse Biological and Agricultural Engineering Agricultural Pollution.

Waste Handling for Swine Production Lori Marsh, Associate Professor, Biological Systems Engineering, Virginia Tech.

Section 4 - Manure Production Colorado CNMP Workshop Manure & Wastewater Production Prepared by J.E. Andrews, PE, NRCS - Lakewood, CO.

G. B. Reddy and Richard Phillips

Nutrient Management Planning Alan Sutton Department of Animal Sciences.

Logo Certified Nutrient Management Planning7-1 Module 7: Manure Utilization By Hailin Zhang.

Managing Manure Nutrients for Crop Production – Using DDGS, an Agronomists Viewpoint. Joel DeJong ISU Extension Field Specialist/Crops September 27, 2006.

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.

Managing Manure for Crop Production when Feeding DDGS Kyle Jensen ISU Extension Field Specialist-Crops.

MANURE HANDLING AND STORAGE TO MINIMIZE N LOADING OF THE ENVIRONMENT Reason to store manure –Preserve and contain manure nutrients until it can be spread.

Nutrient Inventory and Storage and Handling (Planner Training) John W. Worley.

Curtis Dell USDA-ARS-PSWMRU University Park, PA

Opportunities for Methane Capture in the Intensive Livestock Industry.

Nutrient Budgets For CNMPs Nutrient Management Planners Training March 31, 2009 Bobby Smith County Extension Coordinator UGA Cooperative Extension Morgan.

Multi-State CNMP Symposium November 30 th – December 1 st, 2010 Mark Garrison, Environmental Engineer Eric Hurley, Nutrient Management Specialist.

Nutrient Management Planner Certification Program Pump and Haul Systems.

Value of swine manure to grow finish operations 2015 Wisconsin Pork Expo Jerry May, MSU Extension Educator

Bill Jokela, Jason Cavadini, and Mike Bertram

Adjusting N:P ratios in liquid dairy manure through nitrification and chemical phosphorus removal to match crop fertilizer requirements Background Nutrient.

Agricultural BMPs to Reduce N Emissions Jessica G. Davis Colorado State University.

Nebraska CNMP Program 1 Rick Koelsch University of Nebraska Tools for Integrating Feed Program into NMP or CNMP.

Review of Scenario Builder BMP crediting Christopher F. Brosch University of Maryland Extension Chesapeake Bay Program Office

Soil Respiration Unit: Soil Science. Objectives O Define: soil respiration and soil microbes O Explain the role of soil respiration in determining soil.

Livestock and the Environment From foukeffa.org Written by Johanna Davis Revised by Nicki Schaefer GA Ag Ed Curriculum Office To accompany the Georgia.

What Are We To Do With All Of This Stuff? Jeff Porter Environmental Engineer Manure Management Team USDA-NRCS.

Nitrogen fertilizer use efficiency in rice. Contents  Introduction  Nitrogen dynamic in lowland rice soil  Methods of Nitrogen losses from rice fields.

Ricky & Gena.  In animal protein (organic)  In amino acids (organic)  In the soil  In the atmosphere.

Soil Nitrogen Unit: Soil Science.

Nutrient Issues Review of Nutrient Management Issues Addressed by EPA NODA for Proposed CAFO Regulations.

Waste Storage System Closure CNMP Core Curriculum Section 4 — Manure and Wastewater Storage and Handling.

Regional Gross Nutrient Balances Hungary RISSAC HCSO.

Precision Management beyond Fertilizer Application Hailin Zhang.

Nutrient Management Summary CNMP Core Curriculum Section 5 – Nutrient Management.

Manure Management and Water Quality By Jeff Lorimor, Iowa State University, Ames 32-1.

MANURE MANAGEMENT PLAN SUMMARY – MMP NBS Completing a Manure Management Plan Workshop v

Manure Problem Solving December 17, 2009 CraigW. Yohn WVU Extension Agent and Certified Crop Advisor.

Bob Woods Area Extension Agronomy Specialist

Livestock and the Environment

Livestock and the Environment

Manure Management in No-till

Livestock and the Environment

Manure management plan summary – MMP NBs

6/23/2018 Sequential and Total Effect of Traditional and Emerging Manure Treatment Processes on Dairy CAFO: Gaseous Emission and Nutrient Fate Khalil,

Chapter 15 Organic Amendments.

What Are We To Do With All Of This Stuff?

Biogeochemical Cycles

Excretion – Anne Miek Kremer

USEPA Inventory for U.S. using IPCC Guidelines

Manure’s Fertility Value

Overview of US EPA & State Manure Management Regulations

Poultry Litter as Fertilizer?

Modern Soil Health.

Screens: 35% of mass transferred to solid phase 35% P and 30% N in solid phase Simple screens and filter-bands produce a solid phase with a very high.

Section 5.4 – Nitrogen Management

Section 5.1 – Strategic & Annual Planning

Nutrient Management Planning

Presentation transcript:

Section 5.3 – Estimating Land Requirement Nutrient Management Section 5.3 – Estimating Land Requirement Adapted CNMP Core Curriculum Presented by: Roberto Maisonnave, Ag Engineer & M. Sc. International Environmental Consultant robermaison@hotmail.com www.ambientagro.com

Objectives Relation between number of pigs with crop land needed for the agronomic usage of manure. Impact of your waste treatment system in the annual volume of available manure and nutrients. Relevance of the agricultural cropping system in your manure management plan.

Manure Nutrients Production Number of Animals Nitrogen Phosphorus Hd Kg/yr 1 8,55 3,26 5.000 42.750 16.300 These values are only a function of animal type, live weight and diet Relatively uniform within a reasonable range

Treatment & Storage N & P Number of Animals NITROGEN Kg/yr (after losses) Produced Anaerobic Lagoon Aboveground tank 100% 50% 80% 5.000 42.750 21.400 34.200 Number of Animals PHOSPHORUS Kg/yr (after losses) Produced Anaerobic Lagoon Aboveground tank 100% 20% 90% 5.000 16.300 3.250 14.650 Ammonia-N volatilization is the main process of N loss to the atmosphere Nitrification / denitrification? Sedimentation is the main physical process involved in P loss from the liquid phase Solid Separation? Composting? The 80% sedimentation factor is a function of proper anaerobic lagoon design. Solid separation and composting will not necessarily reduce the available phosphorus in the lagoon liquid fraction but it will anticipate the moment of usage. Solid settlement in anaerobic lagoon bottom will defer the need of land application to the end of lagoon life time. The role of microbes…

Land Application System AL vs ST Number of Animals AVAILABLE NUTRIENTS Kg/yr (after losses) Sprinkler Irrigation broadcasted Underground Injection N @ 50% P @ 90% N 90% P @ 100% 5.000 10.700 2.950 19.250 3.250 Number of Animals AVAILABLE NUTRIENTS Kg/yr (after losses) Surface Broadcasted Underground Injection N @ 40% P @ 70% N 90% P @ 100% 5.000 13.700 10.250 30.780 14.650 N-NH3 Volatilization P drift and minimal runoff

Available Nutrients Summary Manure Production AL SI UI Kg/yr N & PAN* 42.750 21.400 10.700 19.250 P 16.300 3.250 2.950 AL: Anaerobic Lagoon SI: Sprinkler Irrigation UI: Underground Injection PAN*: Plant Available Nitrogen

Cropping System Crops / year: Corn, Wheat/Soybean, garden crops Tillage system Fallow period Decay time for manure decomposition (direct human consumption crops)

Land Requirement Example #1 Excreted N Storage Tank with Manure Injection Lagoon with Broadcast Application Hectares per 1,000 sows 58 hectares 35 hectares 14 hectares Hectares per 1,000 nursery pigs 17 hectares 10 hectares 4 hectares Hectares per 1,000 slaughter pigs produced 40 hectares 24 hectares Hectares per 5,000 slaughter pigs 200 hectares 120 hectares 50 hectares 10.000 kg/ha Corn @ 22 kg N/ton grain N-based application

Land Requirement Example # 2 Number Animals N P2O5 Anaerobic Lagoon + Sprinkler Soy-N Soy-P Corn-N Corn-P Kg/yr Ha/yr SOW 2.000 24.777 19.343 17 42 28 38 NURSERY 7.000 23.338 23.090 116 45 FINISHER 14.000 119.758 104.390 83 232 136 205 TOTALS 23.000 168.873 146.823 117 390 192 289 Swine Ex AU excel file 10.000 kg/ha Corn, 4.500 kg/ha Soybeans

Unbalance Manure N/P ratio Generally, Manure: 5N / 1P Crop Uptake: 3N / 1P N based application: P over application P based application: N shortage

Summary 5.000 Finishing Site will produce a fairly constant amount of manure, nitrogen and phosphorus. Select a Treatment & Storage and Land Application System that not only comply with Environmental Regulations but also fit in your agricultural production scenario.

Summary Cropping system is flexible but SOIL AG POTENTIAL is not. Be realistic about crops and yields. Different crops and rotations for different soil nutrient scenarios.