Manure Du Jour April 2, 2009

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Manure Du Jour April 2, 2009 Welcome A Lunchtime Webinar Series Serving Pennsylvania s Best Practices on Animal Ag, Water-, and Air Quality TODAY S FOCUS: Air Quality Housing & Barnyards Eileen Wheeler, Professor of Agricultural and Biological Engineering Pat Topper, Senior Agricultural Research Technologist Robert Graves, Professor of Agricultural and Biological Engineering Hosting Robb Meinen Penn State Dairy and Animal Science

Manure Du Jour April 2, 2009 Eileen Wheeler PSU Department of Agricultural and Biological Engineering

Manure Du Jour April 2, 2009 Patrick Topper PSU Department of Agricultural and Biological Engineering

MONITORING of EMISSIONS in PENNSYLVANIA AGRICULTURE The Use of Flux Chambers for Emission Monitoring Presented by: Patrick A. Topper Agricultural Research Technologist The Pennsylvania State University

Monitoring of Emissions in Pennsylvania Agriculture Forced Ventilation Poultry Facility As discussed earlier, measure concentration of emission leaving at the fan and measure the fan ventilation rate

Monitoring of Emissions in Pennsylvania Agriculture What if there are No fans? Naturally ventilated freestall dairy barn

Monitoring of Emissions in Pennsylvania Agriculture How do we measure emissions if the barn is naturally ventilated? Micrometeorological techniques Tracer gases including Sulphurhexafluoride (SF 6 ) and carbon dioxide (CO 2 ) Ultra-violet (UV) instruments based on differential optical absorption spectroscopy (UV-DOAS) Flux chambers Ref. Biogenic Trace Gases: Measuring Emissions from soil and Water P.A. Matson & R. C. Harris

Monitoring of Emissions in Pennsylvania Agriculture Micrometeorological techniques Tracer gases including Sulphurhexafluoride and carbon dioxide

Monitoring of Emissions in Pennsylvania Agriculture Ultra-violet (UV) instruments based on differential optical absorption spectroscopy (UV-DOAS) Uses USDA BLS metrological system for air flow Cost = $50,000.00 Cerex Environmental Services, Inc. www.cerexenv.com UV SENTRY

Monitoring of Emissions in Pennsylvania Agriculture Flux Chambers Two basic types: Non-steady state: allows gas emissions to concentrate over time Steady state: needs constant supply of clean sweep air

Monitoring of Emissions in Pennsylvania Agriculture What if the scenario requires comparison of emissions from different groups of animals in the same building, being fed different rations, either naturally ventilated or forced ventilated? Which technique works for us? Flux Chambers At Penn State in Ag Eng., we have used both types depending on the research situation; dairy cows, heifers, and layers.

Monitoring of Emissions in Pennsylvania Agriculture In lab, steady-state state flux chambers Data collection automated MatLab control of switching and data recording

1 gallon glass jars (steady state flux chambers) with manure @ as produced urine : feces At least one jar has water instead of manure. Provides background emission data Water bath controls temperature

Multi-plexer: switches instrument samples sequentially among all sample jars Uses filtered room air, flow meters, solenoids and computer program

Monitoring of Emissions in Pennsylvania Agriculture ODOR ASSESSMENT LAB MISSION To study air emissions for the development of improved agricultural management strategies. Current Project Objective: To evaluate the impact of different manure amendments on odor from dairy manure. Method: Odor panel sensory evaluation using Lab-based based olfactometry and multi-chamber steady state gas emission Detection system with multi-gas field monitor. Sponsor: USDA

Monitoring of Emissions in Pennsylvania Agriculture Provide uniform conditions that affect gas emissions Temperature-controlled water bath Dust and ammonia filtered inlet air Calibrated sweep air flow meters Sweep air 0.5 air changes/ minute But this is not Barn measurements We need to get into the field!

Monitoring of Emissions in Pennsylvania Agriculture Portable, field use, Flux Chambers Steady state flux chambers cover a portion of the manured floor surface, uses sweep air into and through the chamber, flux calculated by sweep air flowrate times change in gas concentration

Monitoring of Emissions in Pennsylvania Agriculture Non-Steady State Flux Chamber covers a portion of the floor surface, continuous concentrations recorded, sample analyzer returns air to chamber, flux calculated by change in concentration over time

Monitoring of Emissions in Pennsylvania Agriculture Flux chamber internals showing sweep air ring

Monitoring of Emissions in Pennsylvania Agriculture Used our first generation flux chamber: 2005 Consisted of a stainless steel container (chili pot) modified inside with a sweep air ring. Used a multigas instrument for emission concentrations

Monitoring of Emissions in Pennsylvania Agriculture Innova model 1412 Photoacoustic, measures up to 6 gases menu-driven software fast response time does not consume sample +/- 1% of calibration value annual calibration Cost = $42,000.00

Monitoring of Emissions in Pennsylvania Agriculture Model 1412 Photoacoustic Field Gas- Monitor interfaced with laptop. Internal sample pump flushes tubing and provides fresh sample to detection chamber Instrument requires 100-240 VAC, 50-60 Hz, during field use, powered by deep cycle batteries and an inverter

Second Generation: non-steady state, Recirculation Flux Chamber

Monitoring of Emissions in Pennsylvania Agriculture Second Generation: modified by adding recirculation sweep airflow using air pumps

Third generation: redesigned into a uniform, horizontal, recirculating airflow, non-steady state, flux chamber Used for emission monitoring : Manured soils dairy manure storage heifer emission trials poultry layers (belts and deep pits) and broilers manure

Monitoring of Emissions in Pennsylvania Agriculture Steady state, recirculating static vented flux chamber measuring emissions from a stacked manure testing site. Variable speed internal fan vent

Monitoring of Emissions in Pennsylvania Agriculture Typical data from field measurements while using a non-steady state flux chamber Time Ammonia [mg/mウ] Nitrous Oxide [mg/mウ] Methane [mg/mウ] Carbon Dioxide [mg/mウ] FC type location 9/16/2008 17:42 1.46 0.47 2.46 687.1 3rd gen. C-2 9/16/2008 17:43 8.11 0.44 5.57 748.2 9/16/2008 17:44 12.58 0.43 7.40 824.0 9/16/2008 17:45 14.77 0.42 8.72 894.1 9/16/2008 17:46 16.06 0.46 9.71 971.5 9/16/2008 17:47 4.45 0.73 3.08 730.0 9/16/2008 17:48 2.04 0.46 2.51 678.6 9/16/2008 17:49 1.73 0.47 2.72 684.3

Linear Gas Flux Equation f = V ( C C ) t At o Hutchinson and Mosier (1981) f = flux (mg NH 3 cm 2 min -1 ) V = volume flux chamber (cm 3 ) C t = gas concentration final(mg/m 3 ) C o = gas concentration inital(mg/m 3 ) A = floor area covered by flux chamber (cm 2 ) t = time (minute)

Method: Initial Gas Flux Model Non-linear relationship check C C 1 2 C C 0 1 > 1

Non-Linear Gas Flux Equation f = At ( ) 2 V C 1 C 0 C 1 C 0 ln ( 2 C C C ) C C 1 2 0 2 1 Hutchinson and Mosier (1981) f = flux (mg NH 3 cm 2 min -1 ) V = volume flux chamber (cm 3 ) C x = gas concentration (mg/m 3 ) A = floor area covered by flux chamber (cm 2 ) t = time (minute)

Monitoring of Emissions in Pennsylvania Agriculture Hutchinson and Mosier (1981) Gas Concentration C 0 C 2 C 1 t 1 t 2 Time C 3

Validation of Ammonia Emissions from Dairy Cow Manure Estimated with a Non- Steady State, Recirculation, Flux Chamber with Whole Building Emissions Principal Investigators: V. Blanes-Vidal, P. A. Topper, E.F. Wheeler constructed a special test room (2005) with a variable ventilation rate for validation of surface flux chambers. Room emission rate is compared with flux chamber flux rates. Steady State and non-steady state chambers tested, focus on non steady state!

Monitoring of Emissions in Pennsylvania Agriculture Emissions Monitoring Equipment in Use Floor description Manure depth Urine, water, feces, silage presence General environment Weather, cow activity Free stall dairy determining ammonia emissions rates from manured floor using 1 st generation flux chamber. Two different diets for each group of 60 cows.

Monitoring of Emissions in Pennsylvania Agriculture Heifer facility, measuring manure with 3 rd generation flux chamber, determining ammonia emissions rates. Six different groups of heifers, 3 different diets.

Monitoring of Emissions in Pennsylvania Agriculture Poultry layer facility, measuring manure with 4th generation flux chamber, determining ammonia and methane emissions rates. Three different diets, six different rows.

Monitoring of Emissions in Pennsylvania Agriculture Flux Chamber Weaknesses Both types of flux chambers disturb the surface (temperature, wind, pressure effects) so errors in reported calculated emission rates can occur. Works well for gases generated only from the manure, but since carbon dioxide and methane are both produced directly from the animal, flux chambers underestimate those emissions. For non-steady state flux chambers, the gas detector can not destroy the gas being measured

Monitoring of Emissions in Pennsylvania Agriculture Flux Chamber Strengths When using the non-steady state chambers, able to record many measurements in one facility (80 flux rate calculations per day) Portable, can bring chamber to the barn Rapid real time data Chambers are relatively low cost, but gas detection instruments can be expensive

MONITORING of EMISSIONS in PENNSYLVANIA AGRICULTURE The Use of Flux Chambers for Emission Monitoring Presented by: Patrick A. Topper Agricultural Research Technologist The Pennsylvania State University

Manure Du Jour April 2, 2009 Bob Graves PSU Department of Agricultural and Biological Engineering

Manure as a source? Robert E. Graves, Professor Agricultural and Biological Engineering Department 201 Agricultural Engineering Building 814 865 7155 reg2@psu.edu Penn State is committed to affirmative action, equal opportunity, and the diversity of it s work force. April 2, 2009 REG Agricultural and Biological Engineering Penn State

A look back to June 1996 www.abe.psu.edu select Extension/Fact Sheets April 2, 2009 REG Agricultural and Biological Engineering Penn State

A look back to June 1996 Manure is a biologically active material, alive with bacteria and other microorganisms that depend on the energy contained in the manure. The use of manure energy by microorganismsmicrobial activity-is a natural process of decomposition. April 2, 2009 REG Agricultural and Biological Engineering Penn State

Flow of non-fuel energy in animal production operations April 2, 2009 REG Agricultural and Biological Engineering Penn State

Look at the manure! (and its associated constituents) Manure is an energy-rich feedstuff that is filled with potentially active microorganisms. [or attracts them] These microorganisms will use the energy in manure, causing the manure to change. The challenge of biological manipulation is to manage the environment in which that change takes place in order to produce (or not produce) specific products. April 2, 2009 REG Agricultural and Biological Engineering Penn State

Today s Webinar takes a closer look April 2, 2009 REG Agricultural and Biological Engineering Penn State

What might mother nature and her workers being doing in manure? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Manure is affected by: Animal (age, health ) Bedding (type, amount,.) Ration Storage (type, time) Temperature?? Housing Management Manure removal system Treatment system Climate Precipitation?? April 2, 2009 REG Agricultural and Biological Engineering Penn State

3.77.1 liquid manure (thin slurry): Manure that by its nature,or after being diluted by water, can be pumped easily. ASAE S292.5 April 2, 2009 REG Agricultural and Biological Engineering Penn State

3.77.2 slurry manure: Manure in which the percent total solids approximates that of excreted manure for some species. The total solids content could vary by a few percent depending on whether water is added or a slight drying occurs. ASAE S292.5 April 2, 2009 REG Agricultural and Biological Engineering Penn State

3.77.3 semi-solid manure: Manure that has had some bedding added or has received sufficient air drying to raise the solids content such that it will stack but has a lower profile than solid manure, and seepage may collect around the outer edge. ASAE S292.5 April 2, 2009 REG Agricultural and Biological Engineering Penn State

3.77.4 solid manure: Manure that has had sufficient bedding or soil added, or has received sufficient air drying to raise the solids content to where it will stack with little or no seepage. ASAE S292.5 April 2, 2009 REG Agricultural and Biological Engineering Penn State

Manure Gases close in emission concern Hydrogen Sulfide-colorless, heavier than air, can cause death in seconds. Carbon Dioxide colorless, odorless, heavier than air-asphyxiating. Ammonia-lighter than air, irritant eyes, throat and lungs, low continuous exposure. Methane-flammable and odorless-lighter than air, accumulates under roofs, covers. April 2, 2009 REG Agricultural and Biological Engineering Penn State

What microbial and physical activities might be occurring? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Drive in Settling Tank? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Drive in Settling Tank? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Separated Solids? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Anaerobic Digester? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Composting? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Hoard s Dairyman March 25, 2009 April 2, 2009 REG Agricultural and Biological Engineering Penn State

Your cows: a threat to the environment? John Allen Hoard s Dairyman March 25, 2009 Carbon footprint milk typically 45% CH 4, 30% direct CO 2, 25% NO 2 Lower carbon footprints come from better farming practices, and the more efficient, more profitable farms are likely to have a lower carbon footprint than less efficient ones, April 2, 2009 REG Agricultural and Biological Engineering Penn State

A look back to June 1996 Microbial activity can create a wide range of by-products. By storing, handling, or treating manure in various ways, farmers can control the byproducts produced by this activity. April 2, 2009 REG Agricultural and Biological Engineering Penn State

The End! Questions? April 2, 2009 REG Agricultural and Biological Engineering Penn State

Question and Answers Questions received in writing will be directed to the speakers by the host. Questions not answered during the time remaining, will be posted with answers at www.aec.cas.psu.edu Recordings of this session can also be viewed at the URL listed above. Eileen Wheeler Bob Graves Pat Topper

Next Week on Manure Du Jour April 9 Program: AIR QUALITY - Air Mitigation Technologies Featuring Paul Patterson, PSU Poultry Science Bob Mikesell, PSU Dairy and Animal Science Ken Kephart, PSU Dairy and Animal Science For more information www.aec.cas.psu.edu