Module 8: Nutrient Management 8.1: Introduction to macro- & micronutrients 8.2: Nitrogen 8.3: Phosphorous 8.4: Potassium and other nutrients 8.5: Solid & liquid nutrients produced by AD 8.6: Environmental hazards & the case for nutrient separation 8.7: Phosphorous separation strategies 8.8: Nitrogen separation strategies 8.9: Salt removal & clean water technologies 8.10: Soil nutrients & soil health 8.11: Creation & implementation of cNMP 8.12: Data collection, reporting & compliance This curriculum is adapted from: eXtension Course 3: AD, University of Wisconsin vtc.edu 8.10: Soil nutrients & soil health vtc.edu Let’s start with soil Farmers use nutrients to improve the agricultural quality of their soil: the ability of that soil to support crop growth. Physical properties of soil: Color: generally, darker soil contains more organic matter Texture: depends on the relative amounts of sand vs. silt vs. clay. Structure: size of aggregates or crumb and the presence of soil pores that allow water and air to penetrate soil Internal drainage: deep penetration of water following saturating rains Depth: distance from surface to the layer roots can’t penetrate Susceptibility to erosion: is decreased by stable surface aggregates and effective drainage vtc.edu Darby (2009) Visual inspection of soil vtc.edu Darby (2009) Chemical properties of soil Chemical properties affect the availability of soil nutrients. pH: measure of the relative acidity of alkalinity of a soil on a scale of 1 – 14 The scale is logarithmic, so a difference of 1 is 10-fold more or less acidic. 1 = acid 7 = neutral 14 = alkaline Most Vermont soils are slightly acid, pH 5 – 7. Most crops like neutral pHs of 6 – 7. Cation exchange capacity: mineral nutrients are charged ions held in soil by negatively charged clays and organic matter + Ca+2, Mg+2, K+1, Na+1, NH4+1 • CEC is a soil’s capacity to retain cations; increases with % clay & organics Nutrients • Primary macronutrients • Secondary macronutrients • Micronutrients vtc.edu Darby (2009) Soil nutrients Primary macronutrients • Nitrogen: nitrate (NO3-1) & ammonium (NH4+1) • Phosphorous: phosphates (H2PO4-1 & HPO4-2) • Potassium (K+1) Secondary macronutrients • Calcium (Ca+2) • Magnesium (Mg+2) • Sulfur (SO4-2) vtc.edu Darby (2009) Micronutrients • Iron (Fe+2) • Manganese (Mn+2) • Boron (BO3-2) • Molybdenum (MoO4-2) • Copper (Cu+2) • Zinc (Zn+2) • Chlorine (Cl-1) • Nickel (Ni+2) • Cobalt (Co+2) Soil biology Healthy soils are full of life & microbes are particularly important. vtc.edu Darby (2009) Components of the plant & soil ecosystem A health plant – soil ecosystems requires attention to each of the components of the system. vtc.edu Darby (2009) Principles of soil fertility 1. Maintaining SOM by addition of organics + conservation of soil. For dairy farms SOM is manure, cover crops, crop residues. 2. Maintaining soil biological activity / biodiversity of up to 100,000 different organisms that feed on SOM & the by-product from roots. In return organisms decompose organics, cycle & hold nutrients, degrade pollutants & improve soil structure. 3. Maintain soil tilth, the porosity of soil that allows water, oxygen & roots to infiltrate. Tilth depends on the aggregation of soil via organic matter from roots & microbes & is reduced by compaction. 4. Preventing erosion by minimizing exposure to wind & fast-running water, and maintaining SOM: cover crops, no/low till. 5. Maintaining proper soil pH in Vermont usually requires addition of lime. Soil pH of 6 – 6.8 allows rhizome bacteria to thrive symbiotically with legumes. 6. Maintaining proper nutrient balance aimed at the crops being grown. Balance is challenging when using manure whose NPK ratio is fixed. vtc.edu Darby (2009) Soil compaction There are three types of soil agricultural compaction: 1. Surface compaction is increased by growth of annual crops. Surface crusting occurs when rain falls on bare soil creating a pore-less crust. Surface compaction increases runoff & decreases germination. 1. Plow layer compaction is caused by erosion, reduced SOM, heavy field equipment, and working wet soil. 2. Subsoil compaction occurs below the tilled growing layer when heavy equipment is repeatedly run on (wet) soil. Bottom line: Minimize traffic in fields & don’t work wet soil. vtc.edu Darby (2009) Goals that create good soil fertility A healthy and balanced soil has the following characteristics: • Good water infiltration & storage • Good soil tilth (xxx) • Low rates of erosion • Good levels of organic matter • High levels of biological diversity • pH appropriate for the crop • Essential nutrients for the crop of choice It’s wise to choose a crop that the soil of a field can support and nurture. vtc.edu Darby (2009) Cornell soil health test Assesses twelve indicators of biological, physical & chemical soil properties. More expensive than simpler tests, but provides a great baseline. vtc.edu Darby (2009) 8.11: Creation & implementation of a cNMP vtc.edu What is nutrient management planning? NMP is a mixture of best management practices that aims to: 1. Optimize crop yield & quality 2. Minimize fertilizer costs 3. Protect soil & water quality How? Apply: • the right amount of fertilizer, • In the right form, • In the right place, and • At the right time. NMPs should satisfy state & federal regulations: Natural Resource Conservation Service 590 Nutrient Management Standard – the highest standard of excellence. vtc.edu Darby (2009) NMPs focus on NPK Nitrogen • Essential part of chlorophyll • Essential element for amino acid & protein production • Lack of N causes yellowing of older leaves & stunted growth Phosphorous • Used to create healthy root systems • Essential for formation of seeds & fruits (crop maturation); and • Photosynthesis, respiration, cell division & other biological processes • Lack of P causes stunted growth & purple or reddish coloration of older leaves Potassium • Regulates water use • Aids with disease resistance • Increases stem strength, photosynthesis & protein synthesis • Lack of K causes scorching or necrosis & poor root systems vtc.edu Darby (2009) Nutrient recommendations: sufficiency There are a number of different approaches or philosophies to nutrient recommendations Sufficiency approach: based on maintaining a critical level of exchangeable nutrients. Optimize soil nutrient levels to optimize crop production. Maintenance approach: aims to replace the nutrients that the crop will remove from the soil. This could allow you to calculate fertilizer need without testing soil. Drawback: plants can take up more than they need if it’s there – luxury consumption. Soil cation approach: aims to maintain proper levels of K, Mg, Ca. Problem: studies in the Northeast find that this approach is not effective. Combination approach – just what it sounds like All approaches should make use of tables of recommended nutrients for each crop in each soil and location. vtc.edu Darby (2009) Fertilizer calculations Fertilizer nutrients are usually displayed as percentages of N-P2O5-K2O So 12-24-12 is 12% N, 24%P, 12% K Examples: How many pounds of each nutrient are in 300 lb of 12-24-12? N & K = (0.12) (300 lb) = 36 lb P = (0.24) (300 lb) = 72 lb Your grass hay field requires 100 lb of N per acre. How much 46-0-0 urea do you need to spread per acre? 100 lb N = 217 lb of 46-0-0 should be spread per acre 0.46 Using the fertilizer table 20 on p.92 of “Digging In”, calculate the amount of muriate of potash that should be spread if soil tests recommend spreading 150 lb of K2O per acre for alfalfa? 150 lb = 246 lb of muriate of potash per acre 0.61 vtc.edu Darby (2009) Liquid fertilizer calculations For liquid fertilizers percentages are still used, but the density of the liquid also comes into play telling us how many pounds of nutrient there are per gallon. Examples: How many pounds of N,P,K are there in one gallon of a 9-18-9 liquid fertilizer with a density of 11.4 lb? N, K = 11.4 lb 0.09 N,K = 1 lb / gallon 1 gallon P = 11.4 lb 0.18 P = 2 lb / gallon 1 gallon So, if you want to apply 20 lb of P per acre as a starter fertilizer: 20 lb P = 10 gallons of 9-18-9 per acre 2 lb P / gallon of 9-18-9 How much N and K will that add? (10 gallons 9-18-9) (1 lb N and K/gallon) = 10 lb each of N & K vtc.edu Darby (2009) How far can you afford to haul fertilizer? Have a look at the worksheets in “Digging In” or the Excel version we prepared to allow you to do quick spreadsheet estimates: LINKS vtc.edu Darby (2009) NMP software? A variety of software tools are out there. • UVM likes goCrop, a web application • ACS (Agricultural Conservation Services) uses Crop and Field • Sosten Lungu, our agronomy professor, likes to use a variety of tools: • Purdue’s Manure Manager • RUSLE2 • simple Esxcel spreadsheets vtc.edu Darby (2009) First, get organized! You might consider creating a real or virtual binder of information organized to flow with the NMP process: • Farm information • Maps (six types!) • Soil information • Soil analysis • Manure production • Manure analysis • Field & crop information • Risk assessment (Vermont P Index) • Field-by-field planning • Record keeping • References vtc.edu Darby (2009) Six types of maps 1. Proximity map: all tracts of land used by the farm in relation to the farmstead, town and roads 2. Conservation plan map: FSA (Farm Service Agency) land tract & field numbers for any farm involved in a federal program 3. Nitrate leaching map: highlighting fields prone to leaching because of soil type 4. Topographic map 5. Environmental concern map: showing environmentally sensitive areas or land features: water, wetlands, wells, wildlife habitat, rare and threatened species 6. Soils map: showing which of Vermont’s 180 soil types are found in each field vtc.edu Darby (2009) Proximity map vtc.edu Darby (2009) Conservation map vtc.edu Darby (2009) Nitrate vtc.edu Darby (2009) Topographic vtc.edu Darby (2009) Enviro vtc.edu Darby (2009) Soils vtc.edu Darby (2009) Soil fact sheets USDA NRCS offers a Vermont Soil Fact Sheet for each of the 180 types of soil found in Vermont. • Find and download a soil fact sheets for each type of soil on your farm. vtc.edu Darby (2009) Soil sampling The key to good soil sampling is being sure that your sample is representative of the entire field. Sampling must be repeated every three years. 1. Take samples in the fall. 2. Use a sampling probe or auger. 3. For each field that you plant and fertilize as a unit, take 15 sample cores per 20 acres and combine in a 5-gallon bucket to create a composite sample. If the field is greater than 20 acres, take 2 composite samples (30 cores). If parts of a field are distinctly different, create a sample for each part. a. Use 6 inches for hay or perennial crops. b. Use 6-10 inches for corn or annual crops. 4. Discard plant material & mix all cores well. 5. Place about 1 cup of the mixture into a plastic bag. 6. Label with name, field name, sample number & date. 7. Log the sample, recording field, sample location & date. 8. Send the samples for testing. 9. Organize the results in a spreadsheet that can be sorted for trends. vtc.edu Darby (2009) Soil erosion Erosion: when soil loses its structure an travels from one place to another by wind, rain or surface water. Types: 1. Sheet erosion: removal of a uniform layer from bare soil 2. Rill erosion: in channels formed by the concentrated flow of water 3. Gulley erosion: formation of large channels (or rills) over time T value = tolerable soil loss in units of tons of soil per acre per year • T values are the amount of soil that can be formed (and therefore lost) per year to maintain steady soil levels. • Shown on the soil fact sheet vtc.edu Darby (2009) RUSLE2 RUSLE2 = revised universal soil loss equation version 2 A complex computer model that estimates potential soil losses from rill & interrill erosion caused by rain and surface water. • Considers many factors RUSLE2 reports should be run for each field and will suggest management strategies and the loss of soil predicted for each. • Goal: soil loss less than T vtc.edu Darby (2009) Create a field inventory with software Use realistic crop yields based on a good historic average! vtc.edu Darby (2009) Manure application schedule Is a working plan organized by crop and month vtc.edu Darby (2009) Management for N or P? This decision is made using using two tools: 1) the P index, and 2) soil P tests. In a perfect world, we could create the perfect fertilizer for each and every field to be ensure that each field received sufficient nutrients, but never more than it needed. This would prevent nutrient loss and pollution of water. But the world isn’t perfect, and in the real world we must find the most effective and least risky way to use manure and digester effluent as a source of recycle nutrients back into the food system. N-based or P-based management? How do we do this well? If the P index is too high, nutrient application must manage P, even if it prevents application of sufficient N. Under P-based management, any P applied to a field must be removed by the crops grown in that field. However, if the P index is low and soil can handle additional P, then nutrient application can ensure that fields receive as much N as they need. vtc.edu Darby (2009) N- or P-based nutrient management vtc.edu Darby (2009) A example: A field is given a “yellow” rating: it has a high P index & soil P levels of greater than 20 ppm. So, this field must be managed for P. Cropping plan: corn silage with a yield of 20 tons/acre (based on previous years or similar conditions) How many tons of P are removed per acre by corn silage? (20 tons) (5 lb P removed / ton) = 100 lb So how much P can you apply in spreading manure or AD effluent? 100 lb How much manure or effluent will supply 100 lb of P? On average your manure has a P concentration of 8 lb / 1000 gallons, so: (8 x 12) = 96 (pretty close to 100) (12) (1000 gallons) = 12,000 gallons of manure per acre vtc.edu Darby (2009) 8.12: Data collection, reporting & compliance vtc.edu What records should you keep? Records should be kept on a per field basis. 1. Planting & harvest dates 2. Crop yields 3. Dates and amounts of all nutrients applied (type, amount, method) For the cNMP you must have copies of: • Updated copy of your cNMP • Copies of current soil tests • Copies of current manure / effluent tests • Records of any manure transferred off-farm Keep old files on hand for at least five years. vtc.edu Darby (2009) How do you measure crop yields? Methods used include: • Weighing truckloads or wagonloads using truck scales • Measuring wagonloads Volume of each wagon Samples of each day’s harvest for dry weight U Wisconsin found that when forage dry weights were from 30 – 50%, density of forage crops could reasonably be estimated as 5 lb dry matter / cubic foot Example: A wagon is 16 ft long x 7.25 ft wide x 6 ft high = 696 ft3 DM estimate = (696 ft3) (5 lb DM / ft3) = 3,480 lb DM / wagon = 1.74 tons DM If actual DM is 28%, actual mass = 1.74 tons / 0.28 = 6.96 tons/wagon vtc.edu Darby (2009); Sid Bosworth @ UVM Extenesion Who has state reporting requirements? Farm size and operations determine how they are regulated in Vermont: Medium Farm Operations Large Farm Operations MFO LFO Mature dairy (milking or dry) 200 - 699 700 Beef or cow/calf 300 - 999 1000 Youngstock / hiefers 300 - 999 1000 horses 150 - 499 500 turkeys 16,500 – 54,999 55,000 Laying hens 25,000 – 81,999 82,000 Annual reporting using MFO or LFO forms vtc.edu Darby (2009) EQIP may be able to help EQIP, the Environmental Quality Incentives Program, is administered by NRCS as a voluntary conservation program. • Aims to combine agricultural production & environmental conservation • Offers financial & technical help for implementation of structures or management practices. • EQIP eligibility requires complete NRCS crop records for the previous year. vtc.edu Darby (2009) Recordkeeping cheat sheets Consider maintaining a summary sheet or log of: • All discrepancies between your plans and what you actually did; • Extraordinary weather; • Unexpected events, both good and bad; • Keeping this log in chronological order makes it easier to piece together events long after they’ve happened. Don’t forget to document implementation of measures required or requested by the state after your previous report. vtc.edu Darby (2009) Updating the cNMP Annual updates are critical and are easier to do if you’ve kept a cheat sheet of log, and if you tackle one section of the cNMP at at time: Farm Information Sheet: Has herd size changed? Has acreage used changed? Borrowing or leasing new fields? Has the crop plan or rotation changed? Have tilling methods or spreading methods changed? Maps & soil information can be changed by NRCS / NRCD, so give them information about fields added or removed and give them time. Soil analysis must be done every three years, so check dates, send in new samples, archive old information and add new results. Manure production: Have you added new animals or changed storage? Manure analysis needs to be done annually, so send out the sample and update that portion of the cNMP. Field information: update the crop history & yield section. Field-by-field planning must be updated if you’ve taken new soil tests. vtc.edu Darby (2009) cNMP resources www.uvm.edu/extension/cropsoil/soil-healt-and-nutrient-management www.uvm.edu/pss/vtcrops/articles/VT_Nutrient_Rec_Field_Crops_1390.pdf pss.umv.edu/ag_testing/ www.vt.nrcs.usda.gov www.vt.nrcs.usda.gov/soil/so_stat.html efotg.nrcs.usda.gov/treemenuFS.aspx?Fips=50001&MenuName=menuVT.zip www.vt.nrcs.usda.gov/technical/Nutrient_Management/ www.vermontagriculture.com/ARMES/awq/AAP.html www.vermontagriculture.com/ARMES/awq/MFO.html www.vacd.org vtc.edu Darby (2009) Sources & resources (1) This curriculum is a modification of the wonderful: • eXtension Course 3: AD, University of Wisconsin http://fyi.uwex.edu/biotrainingcenter/online-modules/series-three-anaerobic-digestion/ Additional sources & resources: Ahn, C.H., Park, H.D., Park, J.K. (2007) Enahanced biological phosphorous removal performance and microbial population changes at high organic loading rates, Journal of Environmental Engineering, 133(10): 962 – 969. AlgeEvolve (2013) Nutrient recovery through algae, The 7th AgSTAR National Conference, Indianapolis, Indiana Battistoni, P., Paci, B., Fatone, F., Pavan, P. (2006) Phosphorous removal from anaerobic supernatants: start-up and steady-state conditions of a fluidized bed reactor full-scale plant. Industrial Engineering Chemistry Research, 45: 663-9. Bishop, C.P. and Shumway, C.R. (2009) The economics of dairy anaerobic digestion with co-product marketing, Review of Agricultural Economics, 31(3): 394-410. Bowers, K.E. & Westerman, P.W. (2005) Performance of cone-shaped fluidized bed struvite crystallizers in removing phosphorous from wastewater, Transactions of the ASAE, 48: 1227-34. Chapuis-Lardy, L., Fiorini, J. Toth, J. Dou, Z. (2004) Phosphorous concentration and solubility in dairy feces: variability and affecting factors, Journal of Dairy Science, 87(12): 4334 – 4341. Churchouse, S. and Wildgoose, D. (1999) Membrane bioreactors progress from the laboratory to fullscale use. Membrane Technology, 1999(111), 4 – 8. Darby, H (2009) Digging in: a nutrient management course for farmers, UVM Extension Dery, P. & Anderson, B. (2007) Peak phosphorous, Energy Bulletin, 13 April 2007 vtc.edu Sources & resources (2) DVO (2013) Personal communication Eekert, M.H.A., van, Weijma, J., Verdoes, N., Buisonje, F.E., de, Reitsma, B.A.H., Bulk, J. van Strichting Toegepast Onderzoek Waterbeheer (STOWA) PFrear, C., Liao, W., Ewing, T., Chen, S. (2011) Evaluation of co-digestion at a commercial dairy anaerobic digester, Clean Air, Soil, Water, 39(7) 679-704. Frear, C., Wang, Z., Li, C., Chen, S. (2011) Biogas potential and microbial population distributions in flushed dairy manure and implications on anaerobic digester technology, Journal of Chemical Technology & Biotechnology, 86: 145 – 152. Gerritse, R.G. & Vriesema, R. (1984) Phosphate distribution in animal waste slurries, Journal of Agricultural Sciences, 102(1): 159-161. Global Phosphorous Research Initiative Gungor, K. & Karthikeyan, K.G. (2005) Influence of anaerobic digestion on dairy manure phosphorous extractability, Transactions in the ASAE, 48(4): 1497-1507. Gungor, K. & Karthikeyan, K.G. (2005) Probable phosphorous solid states and their stability in anaerobically digested dairy manure, Transactions of the ASAE, 48(4): 1509-1520. Gungor, K. & Karthikeyan, K.G. (2008) Phosphorous forms and extractability in diary manure: a case study for Wisconsin on-farm anaerobic digesters. Bioresource Technology, 99(2): 424-436. Halpern, D. (2013) Low cost nutrient recovery for improved project profitabiilty, 2nd Annual Anaerobic Digestion and Biogas Conference 2013, San Francisco, CA. Havlin, J.L., Beaton, J.D., Tisdale, S.L., Nelson, W.L. (2005) Soil fertility and fertilizers: an introduction to nutrient management, 7/e, Pearson, Saddle River NJ vtc.edu Sources & resources (3) ICUSD (2013) National market value for anaerobic digestion products. Report to Innovation Center for US Dairy, August Jeong, Y.K & Hwang, S.J. (2005) Optimum doses of Mg and P salts for precipitating ammonia into struvite crystals in aerobic composting, Bioresource Technology, 96: 1-6. Jiang, A., Zhang, T., Chen, S., Zhao, Q, Li, X., Frear, C. (2013) Evaluation of an integrated ammonia stripping, recovery, and biogas scrubbing system for use with anaerobically digested dairy manure, Biosystems Engineering, accepted. Kemira (2011) Case study: mechanical/chemical liquid solid separation of anaerobic digestate. The Sixth AgSTAR National Conference, Boise, Idaho Le Corre, K.S., Valsami-Jones, E., Hobbs, P., Jefferson, B., Parsons, S.A. (2007) Agglomeration of struvite crystals, Water Research 41: 419-425. Lei, X.H., Sugiura, N., Feng, C.P., Maekawa, T. (2007) Pretreatment of anaerobic digestion effluent with ammonia stripping and biogas purification, Journal of Hazardous Materials, 145(3): 391 – 397. Liao, P.H., Chen, A., Lo, K.V. (2005) Removal of nitrogen from swine manure wastewaters by ammonia stripping, Bioresource Technology, 54(1): 17 – 20. Ma, J., Kennedy, N. Yorgey, G., Frear, C. (2013) Review of emerging nutrient recovery technologies for farm-based anaerobic digesters and other renewable energy systems, Prepared for Innovation Center for US Dairy, Washington State University MHF (2013) Multiform harvest. Personal communication vtc.edu Sources & resources (4) Mino, T., Van Loosdrecht, M.C.M., Heijnen, J.J. (1998) Microbiology and biochemistry of the enhanced biological phosphate removal process, Water Research, 32(11): 3193 – 3207. Mulder, M. (2000) Basic principles of membrane technology, Kluwer Academic Publishers, Dordrecht, The Netherlands. Pedros, P.B., Simon, M.M., Brown, S.H. (2013) US Patent No. 9,398,855, USPTO Peter-Varbanets, M., Zurbrugg, C., Swartz, C., Pronk, W. (2009) Decentralized systems for potable water and the potential of membrane technology, Water Research, 43(2): 245 – 265. Sialve, B., Bernet, N., Bernard, O. (2009) Anaerobic digestion of microalgae as a necessary step to make microalgal biodiesel sustainable. Biotechnology Advances, 27: 409 – 416. Spindler, H., Bauermeister, U., Meier, T., Teske, M. (2011) US Patent No. 7,887,615, USPTO Sutton, M.A., Reis, S., Bahl, K.B. (2009) Reactive nitrogen in agroecosystems: integration with greenhouse gas interactions, Agriculture, Ecosystems & Environment, 133(3): 135 – 138. Uellendahl, H. and Ahring, B.K. (2010) Anaerobic digestion as final step of a cellulosic ethanol biorefinery: biogas production from fermentation effluent in a UASB reactor-pilot-scale results, Biotechnology Bioengineering, 107: 59 – 64. Vlaeminck, S.E., DeClippeleir, H., Verstaete, W. (2012) Microbial resource management of one-stage partial nitritation/anammox, Mcrobial Biotechnology, 5(3): 433 – 448. Wang, L., Li, Y., Chen, P., Min, M., Chen, Y.F., Zhu, J., Ruan, R.R. (2010) Anaerobic digested dairy manure as a nutrient supplment for cultivation of oil-rich green microalgae Chlorella sp. Bioresource Technology, 101(8): 2623 – 2628. vtc.edu Sources & resources (5) Weismann, U. (1994) Biological nitrogen removal from wastewater, In Biotechnics/Wastewater, 113-154, Springer, Berlin, Heidelberg. Wood, S. and Cowie, A. (2004) A review of greenhouse gas emission factors for fertilizer production, In IEA bioenergy task (Vol 38, p.20) Yanosek, K. (2002) Enhanced biological phosphorous removal from dairy manure to meet nitrogen:phosphorous crop nutrient requirements, Biological Systems Engineering, Virginia Polytechnic Institute and State University, Blacksburg, VA. Zhang, T., Bowers, K.E., Harrison, J.H., Chen, S. (2010) Releasing phosphorous from calcium for struvite fertilizer production from anaerobically digested dairy effluent. Water Environment Research, 82(1): 34-42. vtc.edu