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Development of a Mobile Process to Extract Phosphorous from Livestock Waste as a Valuable Fertilizer Gene Hoilman Bioresource Engineering Dept. Oregon State University
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Defining the Problem Manure spreading is traditional method of disposing of wastewater from confined animal feeding operations (CAFO’s) Wastewater application supplies N and P Applications typically account for uptake of nitrogen; usually applying phosphorous in excess Environmental and regulatory concerns arise
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Environmental Concerns P unused by crops can enter water bodies via runoff Extra P in water bodies can increase algal growth Aesthetic and recreational detriment during algal bloom Increased oxygen demand when algae senesce
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Regulatory Concerns EPA is requiring comprehensive nutrient management plan as part of CAFO permitting process Accounting for P will increase land needed for application – may not be an option A method of P removal directly from the waste may be of help
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Identifying a Solution As pH of a solution increases, some phosphorus-containing compounds precipitate from solution Struvite: MgNH 4 PO 4 +6H 2 O N removed, but small percent of total Supplemental Mg 2+ usually needed Hydroxylapatite: Ca 5 (PO 4 ) 3 OH
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Identifying a Solution End-Product Reusability Struvite identified as a slow-release fertilizer (Bridger et al, 1962) Wide crop applicability Non-burning Currently sold as fertilizer amendment in Japan Hydroxylapatite mentioned as potential fertilizer (Momberg and Oellermann, 1992) Research not available on actual useage
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Identifying a Solution The Mobile Process Concept Many smaller CAFO’s may not have money to invest in permanent P removal plant Mobile nutrient removal service could help these farms Removal as struvite creates Double income
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Existing methods Overview Several precipitation processes currently exist Reviewed these for potential adaptation to mobile process All reviewed processes intended for permanent, on site installation Several types of wastewaters treated These include municipal and livestock wastewaters
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Existing Methods Reactor Types Fluidized Bed Reactors Provide seed material Spontaneous Nucleation Reactors Seed material not provided Both used to make struvite, hydroxylapatite, or mixture of both
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Adaptation to Mobile Process – Reactor Style Minimize hydraulic retention times (HRT’s) Minimize necessary materials Provide for ease of harvest Spontaneous Nucleation Reactor Chosen Low HRT’s Possible (Munch & Barr, 2000)
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Adaptation to Mobile Process – Chemicals Sodium Hydroxide for pH Adjustment High solubility allows quick pH adjustment Magnesium Chloride for supplemental Mg 2+ Also highly soluble Adjusting pH and Mg 2+ with separate chemicals allowed full control of optimization
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Jar Tests Mg 2+ :O-PO 4 molar ratio and pH adjusted with control Jar tests investigated chemical dosing and reaction time Suggested: High solids content can interfere No supplemental Mg 2+ Maximum necessary HRT = 30 min Reactor pH = 8.5 Control group jars showed O-PO 4 removal during tests
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Control Group O-PO 4 Removal Aeration of wastewater increases pH by driving out CO 2 (Battistoni, 2002) Long time needed to achieve pH comparable to chemical adjustment Chemical adjustment of pH remains best way to achieve low HRT
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Pilot Plant – General Information Adapted from design of Munch & Barr (2000) Built with cone-bottomed rapid mix tank and PVC sewer pipe Cost to build: ~ $1000
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Pilot Plant Process
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Pilot Plant Operation Flow rates of chemicals calculated based on flow rate of waste Waste and chemical flow into reactor initiated simltaneously Waste flows in and out of the reactor continuously until reactor shut down precipitate settled and harvested after shut down
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Pilot Tests Pilot plant tested at Rickreall Dairy in Rickreall, Oregon Acceptable solids content Hydraulic Retention Times Tested: 5 min 10 min (supplemental Mg 2+ ) 20 min 50 min Experiments ran for 3 to 24 hours
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Pilot Plant Results O-PO 4 removal did not significantly vary with HRT ranged between 60%-70% 5 min HRT produced poor quality precipitate 10, 20 and 50 min HRT’s all provided adequate precipitate qualities
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Pilot Plant Results (cont.) Hydroxylapatite formed in tests not supplementing Mg 2+ Struvite formed in test that supplemented Mg 2+ Product suspended in effluent even at high HRT’s (low flow rates) Prompted redesign of mobile process
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“Curve Balls” No difference in NH 4 removal when struvite formed vs. hydroxylapatite Most NH 4 removal due to volatilization Struvite-NH 4 comparably small
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“Curve Balls” Mg 2+ :O-PO 4 Ratio Ratio of removed Mg 2+ :O-PO 4 was not 1:1 in the test forming struvite Other Mg 2+ containing precipitates may have formed Bobierrite and magnesite are possibilities (Dempsey, 1997; Wentzel, 2001)
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“Curve Balls” Calcium Carbonate Product was predominantly calcite (calcium carbonate) Total P only about 0.7% by weight Diet of cows heavily supplemented with calcium carbonate Serves to buffer stomach acid
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Implications for Full Scale Mobile Process Design modification: Rapid mix reactor Design flow rate and rapid mix tank volume to achieve 10 min HRT Additional long, wide settling basin may provide conditions for suspended product to settle Wastewaters originating from livestock being fed calcium carbonate present problems
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Conclusions Project successful in removing a large portion of soluble phosphorus from a livestock wastewater With design modifications, a mobile process to remove phosphorus from wastewater could be successful Further tests with modified design and different wastewater are needed to confirm feasibility of the process
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Acknowledgements Louie Kazemier, Jim Cole, and the staff of Rickreall Dairy Graduate Committee: Dr. J. Ronald Miner, Dr. Fred Ramsey, Dr. John Bolte, Dr. Prasad Tadepalli Sandy Lovelady, Yan Ping Liu Qian, and the staff of the CAL Dr. Mohammed Azizian, Enviro. E. Dept. Dr. John Selker, Bioengineering Dept.
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