Tag: ammonia

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Biofiltration: Mitigation for Odor and Gas Emissions from Animal Operations

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

The proceedings, “Mitigating Air Emissions from Animal Feeding Operations”, with expanded versions of these summaries can be purchased through the Midwest Plan Service.

This Technology is Applicable To:

Species: Swine, Dairy
Use Area: Animal Housing
Technology Category: Biofilter
Air Mitigated Pollutants: Hydrogen Sulfide, Ammonia, Methane, Volatile Organic Compounds, Odors

System Summary

A biofilter is simply a porous layer of organic material, typically wood chips or a mixture of compost and wood chips, that supports a population of microbes. Odorous building exhaust air is forced through this material and is converted by the microbes to carbon dioxide and water. The compounds in the air are transferred to a wet biofilm that grows on the filter material where microorganisms breakdown the odorous compounds.

Biofiltration can reduce odor and hydrogen sulfide (H2S) emissions by as much as 95% and ammonia by 65%. The method has been used in industry for many years and was recently adapted for use in livestock and poultry systems. Biofilters work in mechanically ventilated buildings or on the pit fans of naturally ventilated buildings. Biofilters can also treat air vented from covered manure storage.

Two configurations of biofilters are being used to treat exhaust air from swine buildings: a horizontal media bed and a vertical media bed. Horizontal biofilters require more land area but are less expensive than vertical biofilters. Horizontal beds can be shallow (< 0.45 m) or deep (> 0.75 m).

Applicability and Mitigating Mechanism

Key factors influencing biofilter size and performance:

  • time the odorous gases spend in the biofilter
  • volume of air treated
  • moisture content of the filter material
  • sizing the biofilter media volume
  • selecting fans capable to push the air through the biofilter
  • choosing biofilter media

Limitations

  • Biofilters are only effective when there is a captured air stream
  • Media moisture content effects the biofilter performance, i.e. dry media results in poor odor reduction
  • Media porosity is related to the fan’s ability to move air through the biofilter. If media is less than 50% porosity most agriculture ventilation fans will not perform satisfactorily

Cost

Costs to install a biofilter include the cost of the materials—fans, media, ductwork, plenum—and labor. Typically, cost for new horizontal biofilter on mechanically ventilated buildings will be between $150 and $250 per 1,700 m3/hr (1,000 cfm). A vertical biofilter is approximately 1.5 times the cost of a horizontal biofilter. Annual operation/maintenance of the biofilter is estimated to be $5-$10 per 1,700 m3/hr (1,000 cfm). This includes the increase in electrical costs to push the air through the biofilter and the cost of replacing the media after 5 years.

Authors

R.E. Nicolai1, K.J. Janni2, D.R. Schmidt21South Dakota State University, 2University of Minnesota
Point of Contact:
Richard Nicolai, richard.nicolai@sdstate.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Practical Partial Biofiltration of Swine Exhaust Ventilation Air

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

This Technology is Applicable To:

Species: Swine
Use Area: Animal Housing
Technology Category: Biofilter
Air Mitigated Pollutants: Odor, Ammonia

System Summary

The mitigation technique discussed is to utilize biofiltration for a portion of swine barn ventilation air. The portion mitigated is that portion of air emitted into stable atmospheres. Stable atmospheres have poor vertical mixing potential and therefore gases and odors emitted tend to remain close to the earth’s surface and can therefore be sensed at longer distances downwind. It is impractical to mitigate all of the exhaust ventilation air required in swine housing. Techniques are needed that apply odor and gas mitigation to a portion of the ventilation air stream, when receptors might experience an odor event. Additionally, many barns incorporate combinations of fans and curtains (i.e. hybrid ventilated) to supply required ventilation air. Any mitigation strategy applied to barn ventilation air must be able to accommodate these hybrid ventilation systems as well.

Ventilation air exhausted during the heat of summer days is exhausted into an atmosphere that is, for the vast majority of times, very unstable providing excellent and natural mixing potential near the building source. In more stable atmospheres, typically present during the evening hours, biofiltration of a critical minimum amount of ventilation air (i.e. partial biofiltration) would reduce ammonia and odor emissions during those times when the potential for odor plumes to travel long distances is greatest. The overall effect would be a more attractive biofiltration strategy that maximizes ammonia and odor reduction potential when most needed.

Applicability and Mitigating Mechanism

  • Biofiltering of a critical minimum amount of ventilation air
  • Applies mainly to hybrid ventilated swine finishing facilities
  • Can be used as an odor “impact based” mitigation strategy

Limitations

  • Requires fan ventilation of barns up to about 81 m3/h-pig (48 ft3/min-pig)
  • Biofilter applications apply added stress to the ventilation system
  • Biofilters require ample water supply to keep the biofilter media in the 50-60% range

Cost

The biofilter application presented in this research required $4,959 for biofilter supplies and equipment including four new biofilter fans (300-head pig finishing room). Biofilter supplies, equipment, and construction labor resulted in a total implementation cost of $6,759 or $22.53/pig space. The added energy to operate the biofilter fans resulted in an additional $0.42/pig-produced.

Authors

Steven J. Hoff1, Jay D. Harmon1, Lide Chen1, Kevin A. Janni2, David R. Schmidt2, Richard E. Nicolai3, Larry D. Jacobson21Iowa State University, 2 University of Minnesota, 3South Dakota State University
Point of Contact:
Steven J. Hoff, hoffer@iastate.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Effects of Dietary Manipulation on Ammonia Emissions

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

This Technology is Applicable To:

Species: Swine
Use Area: Animal Housing
Technology Category: Diet Modification
Air Mitigated Pollutants: Ammonia

System Summary

Dietary manipulation, such as lowering crude protein with amino acid supplementation or fiber addition, is an effective method to decrease ammonia emissions from swine finishing facilities. Lowering crude protein content of the diet with amino acid supplementation markedly reduces nitrogen excretion. In studies conducted for the entire finishing period (Bundy et al., 2008; Lachmann et al., 2007), lowering crude protein content by 3 percentage units with amino acid supplementation decreases total nitrogen excretion by approximately 30% and ammonium nitrogen concentration of the slurry by 37%. The decrease in nitrogen excretion reduces the concentration of ammonium in the slurry which in turn decreases ammonia emission. Results suggest a reduction in ammonia emission of up to 50% with the use of a low protein diet. Additionally, the reduction in ammonium concentration of the slurry also reduces slurry pH which affects ammonia volatilization. Addition of fiber sources to the diet reduces urinary urea excretion which can be degraded enzymatically to ammonia. Fiber addition affects nitrogen excretory patterns and reduces ammonium nitrogen concentration of the slurry which can lead to further reductions in ammonia emissions. The reduction in crude protein content or addition of fiber sources to swine diets can reduce or change nitrogen excretion patterns resulting in marked decreases in ammonia emissions for pigs housed in facilities with shallow pit, pull-plug waste storage systems.

Applicability and Mitigating Mechanism

  • NH3 emissions from swine housing is dependent on the amount of nitrogen excreted
  • Swine typically excrete 30 to 50% of the nitrogen consumed
  • Reducing dietary crude protein with amino acid supplementation can markedly decrease nitrogen excretion
  • Addition of fiber sources to diets also has potential to influence nitrogen excretion patterns
  • These dietary manipulations can markedly decrease ammonia emissions from swine finisher facilities

Limitations

  • Correct estimation of the amino acid requirements of the pig is critical
  • Accurate supplementation of amino acids is critical to reduce risk on growth performance and carcass traits
  • Nutrient content of fiber sources is needed for diet formulation
  • Upper limits to crude protein reduction and fiber addition in diets
  • Cost of amino acid supplementation and use of nutritionist in formulation

Cost

The costs associated with dietary manipulation are solely dependent upon ingredient cost assuming growth performance and carcass traits are not adversely affected. Formulation of low protein diets involves the partial removal of soybean meal from the diet accompanied by replacement with corn and crystalline amino acids (lysine HCl, DL-methionine, L-threonine). Therefore, evaluation of implementation cost weighs the decrease in soybean meal costs versus the increase in corn and amino acid costs within the diet. Using March 2008 ingredient costs, diet costs for a conventional corn-soybean meal based diet and a low protein (-3%), amino acid supplemented diet are similar. Thus, assuming no difference in growth rate or feed intake, cost of gain and total feed cost for the finishing period are similar. Dietary costs need to be re-evaluated with changing ingredient costs.

Authors

Scott Carter, Mariela Lachmann, Justin Bundy; Oklahoma State University
Point of Contact:
Scott Carter, scott.carter@okstate.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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A Review of Manure Injection to Control Odor and Ammonia Emissions During the Land Application of Manure Slurries

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

The proceedings, “Mitigating Air Emissions from Animal Feeding Operations”, with expanded versions of these summaries can be purchased through the Midwest Plan Service.

This Technology is Applicable To:

Species: Swine, Dairy, Beef
Use Area: Land Application
Technology Category: Management (manure injection/incorporation)
Air Mitigated Pollutants: Odor, Ammonia

System Summary

Manure slurry injection provides a significant reduction in land application odor and ammonia emissions release when compared to conventional manure surface broadcasting. Release of odor and ammonia during land application can be reduced by more than 90% compared to conventional application methods (Ohio State University, 2007). Manure can be successfully injected in both conventional tillage and no-till systems with currently available equipment. Additionally, slurry tanker wagons currently used for broadcast application can also be retrofitted with Injection tool bars.

Research by Hanna et al., (2000) compared the odor and ammonia emissions from various types of manure injection techniques to slurry that was surface applied (broadcasted). Odor and ammonia tests were run for both fall and spring slurry application. Ammonia was below the detection limit (0.2 ppm) for all but two (measured at 0.6 and 1.3 ppm) of the 72 samples taken. Broadcast application required approximately four to five times more fresh air dilutions than injection to reach the odor threshold (the level at which the odor can no longer be detected) indicating much lower odor release associated with injection.

Applicability and Mitigating Mechanism

  • Injection tools create sub-surface cavities
  • Slurry is injected into the cavity directly behind the tool
  • Injection minimizes slurry exposure to air reducing odor and ammonia volatilization
  • Injection can be used with all slurry and liquid manures

Limitations

  • Injection systems are not currently commercially available for solid manures
  • Injection can require up to 30% more tractor horsepower than broadcast
  • Injection may not be desirable when the producer does not want the soil or crop root system disturbed (forages, pasture/sod)
  • Injection equipment requires more maintenance than broadcast equipment

Cost

Generally, injection is more costly than broadcast application. Injection requires more tractor horsepower and more equipment (injection tool bars). Because tool bars are pulled through the soil, wear and maintenance is greater with injection systems. Cost increases as application rate decreases and distance from the manure storage site increases. The increase in cost as application rate decreases is due to wear on the application equipment. At lower application rates, field speed is increased causing wear (and eventually maintenance) on the equipment to increase. At a 5,500 gallons per acre application rate, commercial drag hose injection cost is currently $.014/gal compared to $.0085/gal for broadcast (Puck, 2008).

Authors

Ross Muhlbauer1, Jeremy Puck2, Ben Puck2, Robert Burns1, 1Iowa State University, 2 Puck Custom Enterprises
Point of Contact:
Ross Muhlbauer, rmuhlbar@iastate.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Effects of Sodium Bisulfate in Reducing Emissions from Dairy Cow Slurry

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

This Technology is Applicable To:

Species: Dairy
Use Area: Animal Housing
Technology Category: Amendment (chemical)
Air Mitigated Pollutants: Ammonia, Methanol and Ethanol

System Summary

Sodium bisulfate may provide an effective management practice for the reduction of alcohols and ammonia emissions from dairy housing conditions. Application of sodium bisulfate (Parlor Pal) has been demonstrated to be effective in the mitigation of both ammonia and alcohols (methanol and ethanol) emissions from fresh dairy slurry. Ammonia emissions decrease with increasing levels of SBS treatment. Methanol and ethanol emissions also decrease with an increase in the amount of SBS applied.

Product should be applied to dairy drylots with a fertilizer spreader twice per week at a rate of 50 – 75 lb/1000 ft2 for control of ammonia, methanol, and ethanol emissions. However, SBS should not be spread evenly but rather topical around highly frequented cow areas (feed bunk, water troughs). Studies conducted at the University of California at Davis (UCD) showed reduction of ammonia of 61% from fresh manure. Application to enclosed drylots at UCD showed reductions of methanol and ethanol of 15-30%.

Applicability and Mitigating Mechanism

  • Emission of gaseous ammonia and alcohols from fresh slurry is dependent on pH, temperature, microbial activity and etc.
  • Bedding/surface manure pH is important factor for controlling NH3 volatilization
  • Application of SBS lowers pH of slurry and as a result reduces ammonia, methanol, and ethanol fluxes
  • Reduction in pH reduces bacterial population

Limitations

  • Sodium bisulfate must be applied consistently to manure to maintain constant emission reduction as the substance looses its effectiveness over time
  • In locations that are sensitive to salt or areas with existing high salt loading in soils, applications of SBS should be considered with care because sodium is on of its components
  • SBS is a mineral acid. Appropriate measures, as defined by the chemical supplier, should be used during the handling of SBS

Cost

Bulk cost of product delivered to the farm is $660.00/ ton. Application at 50 – 75 lb / 1000 ft2 2X / week equates to costs of between $33.00 – $49.50 / 1000 ft2 / week. Treatment of heavy use areas, approximately 30% of the total pen area, reduces total pen cost by 70%. Cost / cow assuming 4 cows / 1000 ft2 of pen area would be $2.48 – $3.71 / week treating only the heavy use areas.

Authors

Kim Stackhouse1, Jeffrey McGarvey2, Yuee Pan1, Yongijing Zhao1, Huawei Sun1, Wendi A. Jackson1, Lisa M. Nuckles1, Irina L. Malkina1, Veronica E. Arteaga1, and Frank M. Mitloehner 1University of California, Davis, 2 USDA-ARS, Albany CA
Point of Contact:
Frank Mitloehner, fmmitloehner@ucdavis.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Effectiveness of Litter Treatments for Reduction of Ammonia Volatilization in Broiler Production

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

The proceedings, “Mitigating Air Emissions from Animal Feeding Operations”, with expanded versions of these summaries can be purchased through the Midwest Plan Service.

This Technology is Applicable To:

Species: Poultry (Broiler)
Use Area: Animal Housing
Technology Category: Chemical Amendment
Air Mitigated Pollutants: Ammonia

System Summary

Recently, poultry producers have come under increased regulatory scrutiny regarding the amount and type of emissions exhausted from poultry housing during the course of normal house ventilation. Ammonia and dust have both been discussed as potential problems with poultry house exhausts. Using a litter treatment will have a direct effect on improving litter management, nutrient enrichment, and reducing ammonia volatilization from poultry house litter. Recent research completed in the Department of Poultry Science at Auburn University has focused on a series of experiments to evaluate six litter treatment strategies in reducing ammonia volatilization during broiler production.

Poultry Litter Treatment (PLTTM), granulated aluminum sulfate (Al-ClearTM) (GA), Poultry GuardTM (PG), and Hydrated Lime (HL), were applied at 24.4, 48.8, or 73.2 kg/100 m2 (50, 100, or 150 lbs/1000ft2); liquid aluminum sulfate (A-7TM) (LA), was applied at 81.4, 162.8, or 227.1 L/100m2 (20, 40, or 60 gals/1000ft2); and concentrated sulfuric acid (98% H2SO4) (SA) was applied at 9.75, 19.50, or 29.26 kg/100m2 (20, 40, or 60 lbs/1000ft2) on new pine sawdust bedding and tested against a non-treated control (CON). With the exception of lime, all agents were designed to reduce litter pH to control ammonia. Results show that increased levels of litter treatments can extend their ammonia control usefulness and most worked well with the exception of lime. In these experiments, ammonia levels were often controlled at the intermediate and highest level of application for 35 to 42 days. If more strict environmental regulations are put into effect regarding ammonia emissions from poultry facilities, litter treatments may become an important technique to allow producers to remain compliant.

Applicability and Mitigating Mechanism

  • Reductions in litter pH will effectively reduce ammonia volatilization
  • Acidifying treatments performed longer at higher levels of application
  • Lime application failed to produce any favorable results
  • Litter treatment usage is an important management tool for suppressing ammonia emissions and contributing to bird health

Limitations

  • Most litter treatments loose their effectiveness within 21 days when applied at low levels, but this can be extended if higher rates of application are employed
  • Acidifying litter treatments can be corrosive to handle
  • Costs of litter treatment are variable and attributed to distribution and marketing logistics

Cost

Delivered cost of a litter treatment is highly dependent upon transportation costs and competitive pricing offered among manufacturers and distributors. Also, costs for transporting, handling, and applying dry versus liquid products should also be considered. Due to the competitive nature of pricing among litter treatment products it is difficult to provide a reasonable and consolidated cost for the treatments tested in these experiments. However, it can be concluded that low levels only provide ammonia control during the brooding period (maybe for 3 weeks); whereas higher application rates will extend the effective period for ammonia control, but the producer must balance the cost of applying a higher level of litter treatment with benefits associated with longer ammonia control.

Authors

J.P. Blake, J.B. Hess, and K.S. Macklin, Department of Poultry Science, Auburn University
Point of Contact:
John P. Blake, blakejp@auburn.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Odorgon: Overhead Spray System to Neutralize Odors

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

This Technology is Applicable To:

Species: Poultry, Dairy, Beef, Swine
Use Area: Animal Housing
Technology Category: Chemical Amendment
Air Mitigated Pollutants: Ammonia, Hydrogen Sulfide, Odors

System Summary

Odorgon is a water based formulation that is applied in confined animal feeding operations through a high pressure mist system. Odorgon is sprayed on an automated timer basis from the ceilings through high pressure nylon lines and nozzles to neutralize malodors.

Applicability and Mitigating Mechanism

  • Unique class of cationic surfactants
  • Atomized solution sprayed at 600 psi
  • Buffer resulting in non volatile organic salts
  • Greatly reduces ammonia & hydrogen sulfide
  • Creates better environment for animals to thrive in resulting in lower mortality, less culls and less days to finish.
  • Better conditions for workers/employees
  • Mitigates neighbor/social issues

Limitations

  • Water based, subject to freezing
  • Summer use may be curtailed in

open buildings during windy conditions

Cost

Equipment cost for a 42 by 200 foot finishing building with all components installed is approximately $4900. Annual usage for this facility would average $2100 of Odorgon concentrate or .73 per animal unit but could vary with region/climate. Nursery cost for swine is .19 per animal unit. Odorgon is mixed with water at a rate of 50 parts water to 1 part concentrate resulting in a cost of $1.50 per gallon diluted. Cost also varies based on building dimensions and desired results.

Authors

Steve Opheim, VP Klean Air Inc.
Point of Contact:
Ron Hamilton, rrhamilto@aol.com

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Atomization Treatment to Improve Air Quality in a Swine Concentrated Animal Feeding Operation (CAFO)

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

The proceedings, “Mitigating Air Emissions from Animal Feeding Operations”, with expanded versions of these summaries can be purchased through the Midwest Plan Service.

This Technology is Applicable To:

Species: Swine
Use Area: Animal Housing
Technology Category: Other Treatment
Air Mitigated Pollutants: Particulate Matter (PM), Viable Bacteria, Ammonia

System Summary

Juergens Environmental Control Systems are designed to reduce particulate matter (PM), viable bacteria and ammonia and utilizes a high pressure atomization solution. Treatment consists of a formulation comprising proprietary proportions of corn oil, citric acid, ethyl alcohol, eucalyptus, vanilla and water. The formulation was developed to reduce airborne PM and ammonia through short- and long-term mechanisms. The short-term mechanisms include oil encapsulation through electrostatic attraction and coagulation. Long-term reductions occur through the suppression of dust re-suspension. Citric acid is added to neutralize gaseous ammonia. Alcohol helps dry the atomized aerosol and serves as an adjuvant so that formulation components are in complete suspension. Vanilla is added providing a deception for the olfactory senses, and eucalyptus for its respiratory medicinal property. Final formulation is atomized for 5 seconds, six times a day at a pressure of 235 psi (1620 kPa) and a rate of 45 mL/m2. The nozzles are located on the ceiling at 5 or 10 foot centers for complete coverage of the treated area and were designed to produce an aerosol 1-10 ímin diameter under conditions of this formulation and pressure.

Applicability and Mitigating Mechanism

  • Atomization treatment is effective at swine housing systems, such as in finishing, breeding and gestation production systems.
  • The oil is in a water formulation that includes alcohol, citric acid, vanilla and eucalyptus to dry and help mix the atomization solution, neutralize gaseous ammonia, and provide a pleasant odor, respectively.
  • The oil formulation is applied under high pressure, yielding micron-sized charged particles that efficiently remove PM through electrostatic attraction and coagulation.

Limitations

  • Atomization treatment is effective at swine housing systems, such as in finishing, breeding and gestation production systems.
  • The oil is in a water formulation that includes alcohol, citric acid, vanilla and eucalyptus to dry and help mix the atomization solution, neutralize gaseous ammonia, and provide a pleasant odor, respectively.
  • The oil formulation is applied under high pressure, yielding micron-sized charged particles that efficiently remove PM through electrostatic attraction and coagulation.

Cost

Field application of the atomization system and solutions are subject to change. The fixed cost of the system for 1000 – 8000-pig finishing operation averages $1.96 – $7.79 per pig per 3 year term (shipping and installation labor not included). The cost of atomization operating averages $ 0.01 per pig per day over one year. The fixed cost of the system for 500-5000-sow operation averages $9.00 – $16.00 per sow per 3 year term (shipping and installation labor not included). The cost of atomization averages $.01 per sow per day over one year.

Authors

Peter E. Juergens1, Gary L. Rapp11Juergens Environmental Control
Point of Contact:
Gary Rapp, garyrapp@westianet.net

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Ozone Application for Mitigating Ammonia Emission from Poultry Manure: Field and Laboratory Evaluations

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

The proceedings, “Mitigating Air Emissions from Animal Feeding Operations”, with expanded versions of these summaries can be purchased through the Midwest Plan Service.

This Technology is Applicable To:

Species: Poultry
Use Area: Animal Housing
Technology Category: Other Treatment
Air Mitigated Pollutants: Ammonia

System Summary

House ozonation is a controversial technique that has been used in the literature for broiler house cleaning and in-house air contaminant control. Field evaluation in this reported study suggests that ozonation cannot effectively remove ammonia from air inside the broiler houses. Moreover, it caused a negative effect on feed conversion in two of the five flocks evaluated and in the average of five flocks. The laboratory study on this technique indicates that zone does not reaction with NH3 in days even at ozone concentration above 1 ppm, which was more than 10 times higher than the health safety limit set by OSHA. The laboratory tests also show significantly higher level of fine/ultra fine particles / aerosols in the ozone treated environment as compared with the environment without ozone treatment. The direct application of ozonation technique for ammonia mitigation in the animal facilities is not recommended.

Applicability and Mitigating Mechanism

  • Ammonia may be oxidized by ozone.
  • The direct application of ozonation technique for ammonia mitigation in the animal facilities is not recommended.

Limitations

  • In-house ozonation at the threshold limits for public health standards is not effective at mitigating ammonia concentration inside the broiler houses
  • Ozone treatment had positive effects on broiler performance in two broiler flocks and adverse impact in two flocks
  • Higher level of fine / ultra fine particles / aerosols was observed in ozone treated environment.

Cost

In-house ozone application caused a negative effect on feed conversion in two of the five flocks evaluated and in the average of five flocks. After 5 flocks the ozonation treatment resulted in an economical loss of $345. Taking in consideration that installation costs are close to $20,000 for two houses, it is very unlikely that the use of ozonation is economically feasible to be used in the poultry industry

Authors

Lingjuan Wang1, Edgar O. Oviedo-Rondon2, John Small2, Qianfeng Li1, Zifei Liu11Department of Biological and Agricultural Engineering, 2 Department of Poultry Science, North Carolina State University
Point of Contact:
Lingjuan Wang, lwang5@ncsu.edu or edgar_oviedo@ncsu.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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Dust and Ammonia Control in Poultry Production Facilities Using an Electrostatic Space Charge System

Reprinted, with permission, from the proceedings of: Mitigating Air Emissions From Animal Feeding Operations Conference.

The proceedings, “Mitigating Air Emissions from Animal Feeding Operations”, with expanded versions of these summaries can be purchased through the Midwest Plan Service.

This Technology is Applicable To:

Species: Poultry
Use Area: Animal Housing
Technology Category: Other Treatment
Air Mitigated Pollutants: Particulate Matter, Ammonia

System Summary

Air quality within poultry production housing has been a major concern for years, particularly with regard to poultry health. The search for strategies to reduce particulate matter and ammonia emissions from animal housing has led to considerable interest in the poultry industry for practical systems to reduce these air emissions. An electrostatic space charge system (ESCS) was designed to reduce aerial dust and ammonia concentrations within a commercial broiler production house. A study was conducted within a commercial broiler house to evaluate the effectiveness of an ESCS for reducing dust and ammonia concentrations over a period of seven flocks. Results of this study indicate the ESCS significantly reduced airborne dust by an average of 43 percent and reduced ammonia by an average of 13 percent. Commercial application of this technology within the production house has the potential to improve in-house air quality and reduce emissions. Electrostatic fields have not been shown to produce adverse health effects in animals or humans. No differences in bird activity were observed in the form of decreased water consumption or increased mortality. No adverse effects of the continuous charge were observed in the form of stray voltage or static discharge at the feeder and water lines.

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Applicability and Mitigating Mechanism

  • An Electrostatic Space Charge System transfers a strong negative charge to airborne dust particles
  • The negatively charged particles precipitate out of the air to grounded surfaces.
  • Nitrogen compounds attached to the dust will also precipitate out of the air.
  • Application of an electrostatic space charge can be effective in reducing poultry house dust and ammonia concentrations in floor-raised meat-bird housing.
  • The system has the potential for use as an emissions control device exterior to animal housing.

 

Limitations

  • The incidences of static discharge to workers were minimal. The intensity of a discharge from direct contact with an ESCS ionizer was similar to touching a spark plug wire on a gasoline engine.

Cost

The cost of materials and installation of the experimental ESCS unit was approximately $4,000. Power consumption of the entire system was less than 100 watts during operation. It is reasonable to assume that a commercially available product would have a reduced capital outlay and quicker return on investment than the experimental prototype used within this study.

Authors

C.W. Ritz1, B.W. Mitchell2, B.D. Fairchild1, M. Czarick1, J.W. Worley11University of Georgia, 2 USDA Agricultural Research Service
Point of Contact:
Casey W. Ritz, critz@uga.edu

The information provided here was developed for the conference Mitigating Air Emissions From Animal Feeding Operations Conference held in May 2008. To obtain updates, readers are encouraged to contact the author.

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