New York Corn Production During the Last 25 Years

Bill Cox, Department of Crop and Soil Sciences, Cornell University

Grain corn in NY from 2009-2013 had an average annual value of $440M, greater than the entire annual value of all fresh market vegetables or the total fruit crop in NY during this same period.
Grain corn in NY from 2009-2013 had an average annual value of $440M, greater than the entire annual value of all fresh market vegetables or the total fruit crop in NY during this same period.

Corn is by far the most important crop produced in the USA in both acreage and value. NY growers typically plant ~1,150,000 acres annually, making NY the 17th leading state in the USA in corn acres. NY is unique, however, in that planted corn acreage fluctuates between an approximate 50:50 ratio of grain corn and corn silage. Consequently, NY has historically been a leading corn silage producing state. Indeed, NY dairy producers planted approximately 500,000 acres in 2012 and 2013, making NY the 2nd leading state in the USA in corn silage acres. The NY Crop Reporting Service typically focuses on how NY agricultural commodities rank nationally so the importance of corn silage is highlighted but the importance of corn grain is often overlooked. This article will focus on the acreage and value of corn produced for grain and for silage over the last 25 years to emphasize the importance of both to the NY agricultural economy.

Total annual NY corn acreage averaged ~1,150,000 during the 1989-1993 and 1994-1998 time periods (Fig.1). Total NY corn acreage, however, dipped ~1% during the 1999-2003 and 2004-2008 time periods, averaging ~1,050,000 annually. The lower total corn acreage from 1999-2008 can be attributed mostly to the marked decline in corn grain acres during that 10-year period. Annual corn grain acreage averaged ~600,000 from 1989-1998 but dipped to ~510,000 from 1999-2008. The decrease in corn acres from 1994-1998 to 1999-2003 corresponded, as expected, with the decreased market price for grain corn (~$3.00/bushel to ~$2.55/bushel, respectively in NY).

Fig.1. 5-year averages of annual total and grain corn acres and corn silage acres planted in NY over the last 25 years.

Annual NY corn silage acreage, however, remained steady from 1989-2003 averaging ~540,000 during this period. In fact, annual corn silage acreage actually exceeded corn grain acres during the 1999-2003 period (~535,000 vs.495,000 acres, respectively). Milk prices remained similar during the 1994-1998 and 1999-2003 periods (~$14/ and ~$13.85/cwt, respectively), which probably contributed to stable corn silage acreage during this period.  Annual corn grain acreage (~525,000), however, once again exceeded corn silage acreage (~480,000) during the 2004-2008 time period.

Planting grain corn with a new 20” corn planter in 2013, one of the many new planters purchased in the last few years by corn growers, greatly stimulating the agricultural equipment industry in upstate NY.
Planting grain corn with a new 20” corn planter in 2013, one of the many new planters purchased in the last few years by corn growers, greatly stimulating the agricultural equipment industry in upstate NY.

Corn grain prices rebounded during this period (~$3.50/bushel), especially in 2007, prompting more growers, even dairy producers, to plant corn for grain, which partially explains the ~10% decrease in annual NY corn silage acres during 2004-2008. The decrease in corn silage acres during the 2004-2008 period, however, is somewhat surprising because milk prices increased to $17/cwt during this 5-year period.

The annual value of corn silage produced in NY was consistently greater than that of grain corn from 1989 through 2008 (Fig.2). Annual corn silage value in NY showed a strong linear increase during this period, an average increased value of ~$20M during each 5-year period (~$185M during 1989-1993 to ~$260M during 2004-2008). In contrast, the annual value of grain corn in NY fluctuated during this 20-year period (an average value of ~$150M from 1989-1993, to ~$190M from 1994-1998, decreased to only $~130M from 1999-2003, but rebounded to ~$250M from 2004-2008).

Fig.2. 5-year averages of the annual value of the total corn crop, grain corn, and corn silage crop in NY over the last 25 years.

The ratio of acreage and value of both crops, however, have changed dramatically in the last 5 years (Fig. 1 and 2). Annual corn grain acres increased greatly in NY (and in the USA) to an average of ~635,000 during 2009-2013. Obviously, the market price for corn (~$5.75/bushel) was the overwhelming factor in increased NY corn grain acreage during this period. The increase in acres and prices, coupled with relatively high yields, resulted in a dramatic increase in the annual grain corn value in this recent 5-year period (~$440M from 2009-2013). Corn silage acreage remained steady (~475,000) during the 2009-2013 period, despite the increase in average milk prices from ~$17 to ~$18.50/cwt. Nevertheless, the annual value of corn silage, driven by the increase in grain corn and subsequently corn silage prices, increased the annual value of corn silage to ~$375M during the most recent 5-year period.

Milk prices are close to record highs (but will probably fluctuate over the next 5 years); whereas corn prices are at their lowest since 2009. So it will be interesting to see how the ratio of corn silage to grain corn acreage will play out over the next 5 years in NY. In the meantime, let us celebrate the positive impact that grain corn has had on the NY agricultural economy in the last 5 years. Indeed, the average value of grain corn exceeded the average value of the entire fresh market vegetable industry or the total fruit industry from 2009-2013 (Fig.3).

Fig.3. 5-year averages of the annual value of the all fresh market vegetables, all fruit (includes apples, grapes, tart and sweet cherries, peaches, pears, blueberries, strawberries, and raspberries), grain corn, and corn silage crop in NY over the last 25 years.

Not only has the crop value increased dramatically, but the increased acreage and value has spurred new industries (ethanol and grain storage industries) and stimulated other upstate NY industries (trucking, increased sales of seed and other agricultural inputs, increased sales of agricultural equipment including the purchase of hundreds  of new planters and corn combines, etc.). Obviously, the grain corn industry has had a tremendous, yet unacknowledged, value-added effect on the upstate NY economy. In conclusion, isn’t it time to report the value of our crops on a NY state basis instead of on a national basis? Instead of highlighting that NY is the 5th leading tart cherry state ($2.85M value), 4th leading pear state ($2.35M value), 8th leading strawberry state ($6.88M value), 4th leading sweet corn state ($68.4M), 4th leading fresh market snap bean state ($33.4M) but 21st corn grain state ($688M) in 2012, wouldn’t it be far more informative to say that NY grain corn was the 2nd leading agricultural commodity in NY in 2012?

Print Friendly, PDF & Email

Transformation of Soybean from a Minor to a Major NY Crop

Bill Cox, Department of Crop and Soil Sciences, Cornell University

Cox-SoybeanCrop Image
Soybeans prior to harvest. Photo Credit: Bill Cox

Most politicians and urbanites in New York are familiar with the dramatic rise of the wine industry in upstate New York, especially in the Finger Lakes region, over the last 25 years. Indeed, nary a week passes without a press release on the growth of the booming wine industry. Likewise, politicians and urbanites are familiar with the increase in organic agriculture over the last 10 years, the dramatic increase in Greek yoghurt production and consumption in New York over the last 5 years, and the potential growth of hops and barley production in support of the developing micro-brewery industry in New York in the next 5 years. What most, if not all of these individuals are unaware of, is that soybean is the agricultural commodity in New York that has increased the most in both acreage and value over the last 25 years. The $195M value of soybean in 2012 ranked the crop as the 6th leading agricultural commodity in New York.  Based on acreage and value, soybean is no longer a minor crop but clearly a major NY agricultural commodity.

Fig. 1. Soybean acreage in New York from 1988 through 2012.

Soybean acreage in New York approximated 40,000 in the late 1980s and increased to ~300,000 acres in 2012 (Fig.1). This 7.5 fold increase in acreage is only exceeded by its 20-fold increase in value since the late 1980s. The annual soybean value approximated $5M in the late 1980s, soaring to almost $200M in 2012 (Fig.2).

Fig. 2. Soybean value in New York from 1988-2012.

Preliminary estimates indicate that soybean value in New York approximated $170M in 2013 (probably will be revised upward because USDA-NASS estimated the market price of the 2013 NY soybean crop at $12.50, much lower than the price that some NY growers have sold their old 2013 crop at over the last two months).  To place the value of soybean in perspective, Fig. 3 compares the value of soybean with the value of all fresh market and all fruits produced in New York since 1988.

Fig. 3. Value of fresh market vegetables, all fruit, and soybean in New York from 1988-2013 (excluding the unreported 2013 fruit crop).

Soybean value averaged less than 4% of the entire fresh market vegetable industry in the late 1980s and early 1990s. Incredibly, the average value of the NY soybean crop approximated 40% of the entire fresh market vegetable value in 2012 and 2013! Obviously, soybean is no longer a minor crop but a major New York agricultural commodity.

Conclusion
March planting intentions indicate that New York growers will plant 330,000 acres in 2014
. If planting intentions are realized, New York growers will plant record acreage in 2013. New York soybeans averaged 48 bushels/acre in 2013, tied for the highest State average yield on record. Clearly, the crop is thriving in New York. It is time for politicians, administrators at agricultural colleges, and urbanites to recognize and welcome the fact that soybean is a major New York agricultural commodity.

References
National Agricultural Statistics Service. 2013. 2013 New York Annual Statistics Bulletin. http://www.nass.usda.gov/Statistics_by_State/New_York/Publications/Annual_Statistical_Bulletin/2012/2012%20page12-19%20-Field%20Crops.pdf)

Print Friendly, PDF & Email

Acetochlor Herbicide Stewardship – New York State

arp logo DEC Logo Cornell logo

Acetochlor herbicide products received registration approval in New York in February 2013 providing New York growers with a valuable new tool and an expanded array of options for weed control.  A chloroacetamide herbicide, acetochlor is already widely used across the United States for weed control in corn and is consistently effective for control of grasses and small-seeded broadleaf weeds.  It has been shown that acetochlor is very effective on velvetleaf, pigweed species, common ragweed, common lambsquarters, smartweed, and eastern black nightshade as compared to other chloroacetamide herbicides.   Acetochlor premixes now available in New York provide broad spectrum weed control and can play an important role in herbicide resistance management.

Integral to the New York State registration, the Acetochlor Registration Partnership (ARP) members Monsanto and Dow AgroSciences agreed to implement a product stewardship program to promote the responsible use of acetochlor products in New York State for protection of water resources.  Developed in coordination with Cornell University and the New York State Department of Environmental Conservation, the educational outreach reinforces the general responsibility that users have for proper handling and application of pesticide products and for acetochlor products specifically.  It is expected that this initiative will contribute to the long-term sustainability of weed control options needed for production agriculture in New York.

The foundation of the Acetochlor Stewardship Program for New York is the development and communication of information which will reinforce the knowledge of farmers, dealers, distributors, and custom applicators for responsible use of acetochlor products.  Key elements include:  (1) Water Quality Best Management Practices for Acetochlor; (2) Acetochlor Stewardship Slide Deck; (3) Quick Reference Card for Label Requirements; and (4) Use of multiple methods and channels for communicating the information including the opportunity for obtaining continuing education credits.

Label Use Restrictions

While the Water Quality Best Management Practices for Acetochlor are a set of voluntary Best Management Practices (BMPs) to reduce the likelihood that acetochlor will impact water resources, an understanding of label use restrictions is important and is a point of emphasis with the program.  Label use restrictions are mandatory requirements and they summarized below.

Use restrictions common to all acetochlor-containing products:

  • Not for Sale, Sale into, Distribution and/or Use In Nassau and Suffolk Counties of New York State
  • New York State “Restricted Use” pesticide product is restricted in its purchase, distribution, sale, use and possession, and each product may only be purchased and used by a certified applicator.  In addition, any person that distributes, sells, offers for sale, purchases for the purpose of resale, or possess for the purpose of resale is required to have been issued a commercial permit. Atrazine-containing premixes are also Federal Restricted Use Products.
  • Do not apply directly to water, or to areas where surface water is present or to intertidal areas below the mean high water mark.
  • Do not flood irrigate to apply or incorporate.
  • Do not apply this product through any type of irrigation system, unless otherwise directed by approved supplemental labeling in possession of the user at the time of application.
  • Do not apply this product using aerial application equipment.
  • Product must be used in a manner which will prevent back-siphoning into wells, spills or improper disposal of excess pesticide, spray mixtures or rinsates.

Water Quality BMPs for Acetochlor

Water Quality Best Management Practices for Acetochlor work in conjunction with the “Core BMPS for All Agricultural Herbicides” currently available on Cornell’s Pesticide Safety Education Program (PSEP) website.  They are provided as a series of voluntary options.  Producers, crop consultants, and extension specialists should select options most appropriate for a given farming operation, soil types and geography, tillage and cultivation practices, and irrigation and runoff management.

The BMP document lists each practice, describes its use along with the benefits of adopting that practice.  The BMPs are summarized here:

  1. Adopt the “Core BMPs for All Agricultural Herbicides” when applying acetochlor.
  2. Limit acetochlor applications to the lowest effective labeled rate.
  3. Maintain application setbacks from surface water, tile inlets, wells, and sinkholes as directed by product labeling.
  4. Maintain vegetative filter strips between areas where acetochlor is applied and points where field runoff enters surface water, tile inlets, and sinkholes.
  5. Adopt conservation tillage practices appropriate for your farm’s topography and in karst areas.
  6. Use precision application methods.

The Water Quality BMPs for Acetochlor are available at [http://psep.cce.cornell.edu/facts-slides-self/facts/waterquality.aspx].  Always read the product label.  Label use requirements are legally enforceable.

Acetochlor Products Registered in New York States (as of October 15, 2013):

Degree® Xtra, Harness®, Harness® Xtra, Harness® Xtra 5.6L, TripleFLEX® and Warrant® are registered trademarks of Monsanto Company

FulTime® NXT, Keystone®, Keystone® LA, Keystone® LA NXT, Keystone® NXT, SureStart®, Surpass® EC, Surpass® NXT are trademarks of The Dow Chemical Company (“Dow”) or an affiliated company of Dow

Additional Information

Additional information regarding the Acetochlor Stewardship Program is available on-line [http://psep.cce.cornell.edu/facts-slides-self/facts/waterquality.aspx], at arpinfo.com,  or by contacting the Monsanto or Dow AgroSciences representative in your area.

Acetochlor products which also contain atrazine have label use restrictions driven by atrazine requirements.  Users must follow the most restrictive requirements on the product labels for applications.  The table below summarizes restrictions for atrazine-containing acetochlor products and compares them with acetochlor products not containing atrazine.

Label Use Restriction

For acetochlor products containing atrazine

For acetochlor products NOT containing atrazine

Use within 50 feet of any well, including abandoned wells, drainage wells, and sink holes. Not allowed On the following soil types, do not apply this product within 50 feet of any well where the depth to groundwater is 30 feet or less:  sands with less than 3% organic matter; loamy sands with less than 2% organic matter; or sandy loams with less than 1% organic matter.
Mixing, loading, rinsing, or washing of this product into or from pesticide handling or application equipment or containers within 50 feet of any wells, including abandoned wells, drainage wells, and sink holes without impervious containment. Not Allowed Not Allowed
Mixing or loading within 50 feet of perennial or intermittent streams, rivers, natural or impounded reservoirs. Not Allowed Not Allowed
66 foot application setback from points where field surface water enters perennial or intermittent streams or rivers.  If applied to highly-erodible land, the 66 foot buffer from runoff entry points must be planted to crop, seeded with grass, or other suitable crop. Required Not Required
200 foot application setback from all natural or impounded lakes and reservoirs. Required Not Required
Use restrictions in tile-outletted fields and terraced fields containing standpipes. Required.  See product labels for specifics. Not Required

 

 

Print Friendly, PDF & Email

Case Study – Part II: Central NY Farm Applies Adapt-N Rates on Whole Farm, Saves Money and Reduces Environmental Impact

Bianca Moebius-Clune1, Maryn Carlson1, Daniel Moebius-Clune1, Harold van Es1, Jeff Melkonian1 and Keith Severson2, 1 Department of Crop and Soil Sciences, Cornell University and 2 Cornell Cooperative Extension Cayuga County

Farm Background
Donald and Sons Farm in Moravia, NY grows about 1,300 acres of corn and soybean annually. Robert and Rodney Donald have been practicing variable rate N application for a number of years, taking advantage of their RTK-GPS system for soil sampling, input applications and yield monitoring. Until 2011, the farm used N application rates recommended by A&L Great Lakes Laboratories, based on soil tests done by field management unit. The Donalds applied the bulk of their fertilizer N at sidedress time, as they knew that early season applications run the risk of losses during wet springs. Recommendations ranged across their farm from 195 to 260 lbs of total N per acre, of which the Donalds applied 22 at planting.  In 2011, they spent $107,000 on N fertilizer – four times what they spent in 2000, due to increasing prices and a shift toward ever-higher recommended rates as yield potentials increased.

These large expenditures were a strong incentive to seek new tools to optimize application rates. As Rodney put it, “Money talks…and with what we are getting in corn for what we are putting on in ammonia, we’re not gaining.” In 2011, the Donalds decided to collaborate on the NY state-wide Adapt-N beta-testing effort. After the dry spring, the Adapt-N recommendation for their trial field was only 80 lbs N/acre, while their standard recommendation was 220 lbs N/acre. To their surprise, there was no yield penalty from reducing the N rate by 140 lbs N/acre. In state-wide trials, 2011 Adapt-N results were also very promising: 86% of trials showed higher profits using the Adapt-N rate, with an average increased profit of $35/acre (Moebius-Clune et al, 2012).

“I was pretty amazed with the program,” said Robert, who decided to participate in a workshop on Adapt-N at Cornell University in March 2012. He added, “Once you get the hang of the program it’s easy to use.”

The Adapt-N tool is transforming the way N recommendations are made by using high-resolution climate data and a dynamic simulation model to provide weather-adjusted, site-specific, in-season nitrogen recommendations. What sets Adapt-N apart from other methods for determining crop N needs is its explicit accounting for the interaction between early season weather and other factors like soil characteristics and management decisions. After a dry spring, N that has mineralized from organic sources or was applied early in the season remains available in the soil, so less needs to be sidedressed. But in a wet spring, N is easily lost from the system and thus more fertilizer N must be applied. That difference between years could be as much as 100 lb N/ac. Not only does such unmanaged uncertainty cut deeply into growers’ profits, but the environmental consequences are significant: leaching of excess nitrate affects water quality, and denitrification contributes to emissions of nitrous oxide, a potent greenhouse gas, that also depletes the ozone layer. Realizing that recommendations from Adapt-N could lead to significant savings for the farm (estimated at $70,000 for 2011 after a very dry spring with low losses) the Donald Brothers decided they were on board.

Anhydrous sidedress rig ready to head to the field.

Whole Farm Implementation of Adapt-N Rates
For the 2012 growing season, the Donalds used Adapt-N on their whole farm and implemented numerous trials. Robert entered the farm’s 90 management units into his account that spring via the user-friendly Adapt-N interface. “I spent one Saturday afternoon and all day on Sunday,” Robert noted. Between June 8 and 21, Rodney sidedressed 922 acres of corn, using their RTK-GPS system to target their variable rates. Recommendations from Adapt-N varied from 65 to 190 lbs N/acre among management units, depending on local temperature, precipitation, soil texture and organic matter content (varying from 1-6%), as well as the date of sidedressing. On each day of sidedressing, Robert entered updated N recommendations into their system (provided by the daily automatic Adapt-N sidedress alerts) for the fields to be sidedressed that day. He transferred this information to their calibrated RTK-GPS-guided anhydrous ammonia sidedresser via a USB device to automatically adjust N rates on-the-go.

Adapt-N data card used with RTK-GPS on 922 acres of corn. Check strips sidedressed with “Old Way” data card that contained their conventional rates.

Rodney sidedressed entire fields with the Adapt-N rate, except for single or replicated comparison strips of the conventional “old” rate implemented on 15 of their 18 corn fields. Most of the  strip trials followed an AOOA design (with “A” representing the Adapt-N rate and “O” representing the old rate).

Agronomic, Economic and Environmental Results
N rates as applied and yield monitor data for each trial area were retrieved from the Donalds’ AgLeader software at the end of the season. Yields and fertilizer application rates were visualized in map format and quantified within management units or as field-length strips.

Based on analysis of GIS data from the entire farm, Adapt-N resulted in profit gains in 83% of the trials. Averaged across all trials, savings were approximately $42/ac, with estimated total savings of over $30,000 for the farm after the fairly normal 2012 spring. Fields reached or exceeded the estimated yield potential in almost all cases, indicating that the Adapt-N recommended rates were high enough to achieve the expected yield. Yield losses were negligible (2 bu/ac) despite N fertilizer reductions by an average of 87 lbs/ac across all 24 fields.  Yield maps visually emphasized the lack of yield response in the higher N rate strips for almost all trials, as well as the potential impact of field variability on harvest yield.

Left: N application map for Trials 48-50 retrieved from calibrated anhydrous sidedresser – the green strip indicates the high rate grower-N strip, and the grey rectangle indicates a zero-N section (data not discussed here). Right: Yield map retrieved from calibrated yield monitor, with no visually apparent yield increase with higher Grower-N rate.
Comparison of yield and profit using the “Old” N application rates vs. those recommended by Adapt-N. N rates represent total N in lbs/ac applied as inorganic fertilizer in 2012.
Percent of trials with profit gain resulting from reduced Adapt-N rate (20 trials, $55/ac), profit losses resulting from underestimated expected yield input (4 trials, -$27/ac), and trials with unexplained profit losses (none).

The only cases of profit loss occurred in four trials, all exceeding the expected yield by up to 35 bu/ac. Yield losses could have been minimized with more precise expected yield inputs; the Donalds had entered a flat yield potential of 200 bu/ac for all fields, rather than basing the input on past field-specific yield records. Adapt-N is a precise tool that already accounts for the risks of uncertainty and differential losses from over and under-fertilization. Therefore, a good estimate of expected yield is critical to attaining accurate N recommendations.

Savings from whole-farm implementation of Adapt-N were coupled with significant environmental benefits. Informed by Adapt-N, the Donalds applied a non-area-weighted average of 87 lbs/ac less than recommended by A&L Laboratories across the implemented trials. The decrease in N applications reduced simulated total environmental N losses (until 12/15/2012) by an average of 70 lbs/ac, and reduced N leaching losses by an average of 10 lbs/ac.  In total, they saved about 67,000 lbs of unneeded N in 2012.

Refining Adapt-N Use in 2013
When asked whether they were planning to use Adapt-N again next year, Robert answered with an unequivocal “Oh yeah!” and added, “Gotta refine our use of the tool some.” Robert recognizes that for a precision tool like Adapt-N, a reasonable expected yield is particularly important. One of the biggest things Robert plans to change: He will use variable estimated yields for each management unit in 2013, based on 3 to 5 years of yield records for each management unit. He noted that one of his fields in Scipio, NY “won’t do 175 in the best of years. That’s where N is wasted,” while, “other fields can regularly reach 250 bu/ac” if given enough nitrogen. Also, he plans to use the new soil series name inputs that became available last June to further improve the precision of the recommendations.

The trials implemented at Donald & Sons Farm have greatly helped the team assess Adapt-N’s performance and demonstrate the efficacy of using the tool in conjunction with GPS equipment. Growers with similar technological capabilities can likewise maximize the potential of Adapt-N to improve their profits and reduce N inputs and losses.

More information. Adapt-N supporting publications, an in-depth training webinar, and access to the web-interface are available at http://adapt-n.cals.cornell.edu. This case study has been supported by  funds from New York Farm Viability Institute, the USDA-NRCS Conservation Innovation Program, and the International Plant Nutrition Institute.

Print Friendly, PDF & Email

Adapt-N Proves Economic and Environmental Benefits in Two Years of Strip-Trial Testing in New York and Iowa

Bianca Moebius-Clune, Maryn Carlson, Harold van Es, and Jeff Melkonian, Department of Crop and Soil Sciences, Cornell University

Adapt-N (http://adapt-n.cals.cornell.edu) is an on-line tool that uses a simulation model to incorporate location-specific, early season weather information, as well as soil and crop management inputs, to generate precise N sidedress recommendations for corn.

We conducted a total of 84 strip trials in 2011 and 2012 (Figure 1) in NY (56), Iowa (27) and Minnesota (1) to test how well Adapt-N predicts corn N needs at sidedress time. Yield data and estimated leaching losses from all 84 trials show that, when used correctly, the Adapt-N tool significantly increased grower profits and decreased environmental losses. Thus, Adapt-N provided an economic benefit to growers, while also minimizing N losses to the environment in almost all instances. With increasing interest in Adapt-N among growers, consultants, and agricultural service providers throughout the United States and beyond, Adapt-N use has the potential to reduce corn agriculture’s contribution to greenhouse gas emissions, groundwater pollution, and hypoxia in our estuaries, while substantially increasing grower profits.

This article summarizes the results of all 84 trials (Table 1, Figure 2) and describes specific trials that provide insights into how to most effectively use Adapt-N.

Methods
We completed 18 replicated strip trials in 2011, and 42 in 2012, on commercial and research farms throughout New York. We also conducted 9 strip trials in 2011, and 19 in 2012 on commercial farms throughout Iowa (1 trial in Minnesota is included with the Iowa trials in 2012). The trials involved grain and silage corn in fields with varying management history (i.e. organic amendments, crop rotation, tillage practices, etc.). Sidedress treatments involved at least two rates of nitrogen, a conventional “Grower-N” rate based on current grower practice and an “Adapt-N” recommended rate.  A simulation was run for each field just prior to sidedressing to determine the weather-adjusted Adapt-N rate.

Yields were measured by weigh wagon, yield monitor, or in a few cases by representative sampling (two 20 ft x 2 row sections per strip). Partial profit differences between the Adapt-N recommended and Grower-N management practices were estimated through a per-acre partial profit calculation. Yields were used as measured, regardless of statistical significance, since the statistical power to detect treatment effects is inherently low for two-treatment strip trials. For corn grain, a 2011 grain price of $5.50/bu and 2012 price of $6.00/bu were assumed. For silage, $50/T was used in both 2011 and 2012, based on reported NY silage prices. A nitrogen fertilizer price of $0.60/lb was used, based on reported NY and IA fertilizer prices.

Total N losses to the environment (atmosphere and water) and N leaching losses in 2011 and 2012 were estimated for each treatment through model simulations through October 30 for 2011 NY trials, and through December, 15 in 2012 trials.

More detailed descriptions of the 2011 and 2012 methods were provided in previous WCU articles (Moebius-Clune et al., 2012; Moebius-Clune et al., 2013).

Economic Comparison
Profit gains from the use of Adapt-N were considerable.  Profits increased in 80% of all NY trials, in 75% of all IA trials, and in 79% of all 84 trials when growers followed Adapt-N recommendations. Profit gains of $27/ac on average ($31/ac in NY, $20/ac in IA) were primarily attributed to fertilizer cost savings due to lower Adapt-N recommended rates without significant yield losses. Profit gains were also achieved in some instances where Adapt-N recommended higher N rates, and consequent yield increases were achieved (3 trials). Adapt-N rates resulted in average N input reductions of 66 lbs/ac in NY, 32 lbs/ac in IA, and 54 lbs/ac overall. Yield losses decreased by only 1 bu/ac on average in the 84 trials (a statistically insignificant yield loss), indicating that Adapt-N’s reduced N recommendations were generally justified.

Because of the potential impact of field variability on the results of a single trial, analysis of all 84 trials provides the most meaningful assessment of Adapt-N performance and likelihoods for improving grower profits. A look at specific trials can provide insight into effective use of the tool. Yield losses (not always statistically significant), and sometimes profit losses, occurred in several 2012 trials where the user’s ‘expected yield’ input in Adapt-N was an underestimate of the yield achieved with the higher N rate (7 trials in 2012). Adapt-N is a precise tool that already fully accounts for the risks of uncertainty and differential losses from over and under-fertilization.  If the yield potential of the field is higher than the ‘expected yield’ provided to the model, Adapt-N is more likely to recommend insufficient N to achieve a higher yield.  Therefore, a good estimate of expected yield is crucial to attaining accurate N recommendations. Analyzing 3 to 5 years of yield history to determine the expected yield input will maximize the accuracy of yield predictions and thus improve Adapt-N recommendations.

Adapt-N recommended a higher N rate than grower practice in 10% of trials, mostly due to wet spring conditions. In 3 of these 8 trials, the higher N rate resulted in a profit increase due to corresponding yield gains, thus justifying the higher N rate. In the 5 instances where a higher Adapt-N rate resulted in profit losses, unpredictable late-season drought conditions resulted in substantial yield reductions below the expected yield in both treatments. Due to insufficient water availability, the crop was unable to make use of the additional N applied in the Adapt-N treatment, thus the additional N fertilizer cost contributed to profit losses. While such individual situations are not preventable, because post-sidedress drought cannot be predicted by tools currently available, assessment of all trials shows that use of the Adapt-N rate provided increased profitability, while decreasing N inputs, in most cases.

In 2011, Adapt-N recommendations in corn-soybean rotations were low due to a deficiency in how Adapt-N implemented soybean N crediting. However, savings from N reductions in 80% of these trials were large enough to compensate for the respective yield reductions. This error was corrected, and no further profit losses occurred in 2012 trials where corn followed soybean (Moebius-Clune et al., 2013).

Large N input reductions achieved with the use of Adapt-N can often compensate for small yield losses with the lower N rate. For example in one of the 2012 Iowa trials, Adapt-N recommended 0 lbs N/ac as compared with the conventional N rate of 75 lbs N/ac. Despite a yield reduction (9 bu/ac), the Adapt-N rate did not decrease profit (+$1/ac), due to the large reduction in sidedress fertilizer and operational expense. This trial is one of many that demonstrate that growers currently applying high rates of N can realize significant profit gains by using Adapt-N even if yields are somewhat reduced.

Environmental Benefits
Adapt-N reduced N rates by 54 lbs N/ac on average, in 90% of trials, resulting in significant reductions in N losses to the environment. By the end of the growing season, simulated N leaching losses decreased by an average of 10 lbs N/ac, and total N losses decreased by an average of 34 lbs N/ac. In 2012, simulated total N losses and particularly leaching losses of sidedress-applied excess nitrogen remained relatively low by December due to widespread dry conditions during the growing season in NY and especially in IA. Further losses of residual excess N have occurred over the winter and spring months of 2011-2012 and 2012-2013. In silage trials, the pre-plant application of manure, and consequent lower inorganic fertilizer rates at sidedress time, limits the potential magnitude for reductions in N losses in comparison with non-manured fields, although Adapt-N can nevertheless significantly reduce fertilizer application in these systems.

Conclusions
Two consecutive growing seasons of on-farm strip trial testing have shown that Adapt-N is an effective tool for N management in corn systems, resulting in profit gains in 79% of trials, on average by $27/ac ($31/ac in NY and $20/ac in IA). When accounting for the now implemented correction of a soybean credit model deficiency, and underestimated yield potential inputs, we estimate that profit gains would have been achieved in 88% of trials to date. Other pointers for attaining the most accurate Adapt-N recommendations include:

  • Estimate expected yield based on 3 to 5 years of accurate yield information.
  • Use representative manure test results from actual manure inputs to reduce the margin of error associated with manure applications.
  • Create field locations in Adapt-N by discrete management unit. Determine management units by several key factors: i.e. soil type, historical yield data, and organic matter content.
  • Take management unit specific soil samples at least every 3 years to determine an accurate organic matter content value, ideally to a 12” depth.
  • Run Adapt-N on the sidedress date if possible – use the daily alert feature for automatic updated recommendations on all fields.

In summary, Adapt-N strip trial results from 2011 and 2012 have shown that using Adapt-N to predict corn N needs at sidedress time provides economic advantages to growers as well as environmental benefits due to more precise management of N. Adapt-N thus provides a strong incentive to shift N applications to sidedress time, ultimately increasing grower profits and reducing N losses to the environment in both wet and dry years.

For more information: The Adapt-N tool and training materials are accessible through any device with internet access (desktop, laptop, smartphone, tablet) at http://adapt-n.cals.cornell.edu/. Information on account setup and the recorded 3/21/2013 in-depth training webinar are posted. Adapt-N users can elect to receive email and/or cell phone alerts providing daily updates on N recommendations and soil N and water status for each field location in Adapt-N.

Acknowledgements:  The development and testing of the Adapt-N tool was supported through funds from Cornell University, USDA-NIFA Special Grants on Computational Agriculture and the Agricultural Ecosystems Program (U.S. Rep. Maurice Hinchey-NY), Northern NY Agricultural Development Program, a USDA-NRCS Conservation Innovation Program, NY Farm Viability Institute, International Plant Nutrition Institute, and MGT Envirotec. We are grateful for the cooperation in field activities from Bob Schindelbeck, Keith Severson, Kevin Ganoe, Sandra Menasha, Joe Lawrence, and Anita Deming of Cornell Cooperative Extension, from Mike Davis at the Willsboro Research Farm, from Dave DeGolyer, Dave Shearing and Jason Post at the Western NY Crop Management Association, from Eric Bever and Mike Contessa at Champlain Valley Agronomics, from Mark Ochs and Ben Lott at Mark Ochs Consulting, and from Peg Cook at Cook’s Consulting in New York, from Kevin Kuehner of Minnesota Department of Agriculture, and from Shannon Gomes, Hal Tucker, Michael McNeill, and Frank Moore at MGT Envirotec in Iowa. We also are thankful for the cooperation of the many farmers who implemented these trials on their farms. In particular we would like to acknowledge Robert and Rodney Donald for implementing farm-wide trials on most of their fields (Moebius-Clune et al., 2013b).

References
Moebius-Clune, B., M. Carlson, D. Moebius-Clune, H. van Es, and J. Melkonian. 2013. Case Study – Part II: Donald & Sons Farm Implements Adapt-N Rates on Whole Farm, Saves Money and Environment. What’s Cropping Up? TBD.

Moebius-Clune, B., M. Carlson, H. van Es, and J. Melkonian. 2013. Adapt-N Increased Grower Profits and Decreased Nitrogen Inputs in 2012 Strip Trials. What’s Cropping Up? Preview.

Moebius-Clune, B., H. van Es, and J. Melkonian. 2012. Adapt-N Increased Grower Profits and Decreased Environmental N Losses in 2011 Strip Trials. What’s Cropping Up? No. 2, 22.

Print Friendly, PDF & Email

Adapt-N Increased Grower Profits and Decreased Nitrogen Inputs in 2012 Strip Trials

Bianca Moebius-Clune, Maryn Carlson, Harold van Es, and Jeff Melkonian, Department of Crop and Soil Sciences, Cornell University

Adapt-N is an on-line tool for precision nitrogen management in corn (grain, silage, sweet), which has been available to growers in the Northeast and five Midwestern states for the past two years.  It is a computational tool based on the concept that seasonal corn N needs can be estimated much more accurately in the late spring when factoring in weather, soil and management information.  The main question for growers and other stakeholders is whether the tool provides recommendations that increase profits and reduce environmental impacts.  We are answering those questions through on-farm strip trials.  The 2011 results were reported by Moebius-Clune et al. (What’s Cropping Up? Vol. 22, No. 2, 2012) and showed very encouraging results.  We are discussing the 2012 strip trial results in this article, and a summary article for all site-years is also included in this volume.

Adapt-N (http://adapt-n.cals.cornell.edu) uses a well-calibrated computer model, and combines user information on soil and crop management with high-resolution weather information, to provide N sidedress recommendations and other simulation results on nitrogen gains and losses. As a result of 2011 beta-testing, several improvements to Adapt-N were implemented for the 2012 growing season, including adjusted soil type, previous crop, manure and irrigation input options. Model routines for soybean N contributions were adjusted to avoid artificially low N recommendations that had occurred in 2011 and an uncertainty-adjusted price-ratio correction factor to optimize profits from N application was also incorporated into the Adapt-N tool. This factor takes into account several key realities that affect farmer profit: 1) the prices of fertilizer and grain, 2) the variable risks associated with over- and under-fertilizing, and 3) the reduced uncertainty in the optimum N rate with use of this precision tool. Using a fertilizer to grain price ratio of 0.1 ($0.60/lb N: $6 bu grain) Adapt-N subtracted 8 lb N/ac from the model-predicted Agronomic Optimum N Rate (AONR) to determine the Economic Optimun N Rate (EONR).

On-Farm Strip Trials. We completed 42 replicated strip trials on commercial and research farms throughout New York and 19 replicated strip trials in Iowa (1 trial in Minnesota, included with the “Iowa trials”) on commercial farms during the 2012 growing season. The trials involved grain and silage corn, with and without manure application, and different rotations (corn after corn, corn after soybean or other; Table 1). Sidedress treatments involved at least two rates of nitrogen, a conventional “Grower-N” rate based on current grower practice and an “Adapt-N” recommended rate, based on a simulation run just prior to sidedressing. In 2012 NY trials, all but three Adapt-N rates were lower than conventional N rates (by 20 to 138 lbs/ac; Table 1). In 2012 Iowa trials, all but two Adapt-N rates were lower than the conventional N rates (by 20 to 100 lbs/ac; Table 1). Growers in IA and NY implemented field-scale strips with 2-7 (usually 4) replications per treatment.

Yields were measured by weigh wagon, yield monitor, or in a few cases by representative sampling (two 20 ft x 2 row sections per strip). Partial profit differences between the Adapt-N recommended and Grower-N management practices were estimated through a per-acre partial profit calculation:

Profit = [Adapt-N yield – Grower-N yield] * crop price – [Adapt-N rate – Grower-N rate] * price of N + Sidedress operation savings/loss

Yields were used as measured, regardless of statistical significance, since the statistical power to detect treatment effects is inherently low for two-treatment strip trials, but averaging across large numbers of trials provides good statistical power for assessing Adapt-N performance. For corn, a 2012 grain price of $6.00/bu was assumed ($7.00/bu minus $1.00/bu for drying, storing and trucking from PA Custom Rates; USDA, 2012). For silage, $50/T was used based on reported NY silage prices of $25-75/T. A nitrogen fertilizer price of $0.60/lb N was used (reported prices ranged from $0.42 – $0.80/lb N in NY and IA). When Adapt-N recommended no need for sidedressing and the Grower-N rate was greater than 0 lbs/ac, sidedress operational savings of $8/ac were added to the profit. If Adapt-N recommended an application of N and the Grower-N rate was 0 lbs/ac N, a loss of $8/ac was subtracted from the profit. Agronomic and economic outcomes of these trials were used to assess Adapt-N performance.

Results
Agronomic and economic comparisons between Grower-N and Adapt-N treatments for each trial are provided for NY and IA trials in Table 1 and Figure 1, and as averages in Table 2.

NY corn after corn trials (Figure 1 a-c). Adapt-N rates in all of the NY grain after grain trials resulted in N input reductions of 82 lb N/ac on average. In all but one trial, no significant yield loss was measured with these reduced N rates. Adapt-N rates provided a profit advantage over conventional N rates in almost all trials (by $1.62 to $88.20/acre). In 4 of the 5 instances where Adapt-N rates resulted in profit losses, actual yield achieved with the higher N rate exceeded the expected yield used in the Adapt-N simulation (by 9 bu/ac to 35 bu/ac) to estimate the sidedress rate. In each of these four cases, a more appropriate expected yield would have been available from existing yield records, and would have likely resulted in a sufficient recommendation from Adapt-N.

NY corn after soybean or other crops (Figure 1 d-f). Adapt-N rates in all NY corn grain after soybean trials (or after other crops such as wheat, oats, silage) consistently resulted in profit increases (of $7.64 to $105.30/acre). These results demonstrate that the soybean N crediting method used for 2012 successfully corrected the 2011 error. Harvest data show that, despite large N input reductions in Adapt-N treatments (average 56 lbs/ac), reductions in yields were negligible in all trials and only statistically significant in one case (Trial 34). In the only trial where Adapt-N recommended a higher rate (by 23.5 lbs/ac, Trial 22), yield increased by 6 bu/ac and a profit was realized despite higher fertilizer cost.

NY silage (Figure 1 g-i).  Adapt-N rates in 4 of 6 NY silage trials resulted in N input reductions (22.5 – 50 lbs/ac). No statistically significant yield loss with these reduced N rates was found (average 0 T/ac difference when N rates were decreased). Adapt-N rates provided a measured profit advantage over conventional N rates in two of these trials (by $48 and $58/acre) when N rates were reduced by 50 lbs/ac. Profit losses in the other four cases were due to field variability, underestimated yield potential, small N rate differences, and/or drought. Two of these trials (17 and 18) registered a profit loss due to small yield losses because yields were higher than the ‘expected yield’ entered into Adapt-N, in addition to artificially low Grower-N rates as the grower was already reducing N rates to near Adapt-N rates (55-75 lb/ac below standard recommendations that use current yield potentials). In comparison to standard recommendations, these trials would constitute profit gains with Adapt-N use. In two trials, Adapt-N rates were higher by 10-11 lbs/ac, justified by the expected yield input of 22 and 24 T/ac respectively (Trials 14 and 15). Due to drought, measured yields were well below expected yields (by 5.3 and 11.8 tons), and due to field variability, measured yields were lower in plots with the higher Adapt-N rate, resulting in a calculated profit loss.

Silage trials were less numerous, and exhibited greater yield variability than non-manured grain trials, making it more difficult to assess Adapt-N performance. Factors contributing to such variability are low precision in manure testing and application (in comparison to synthetic fertilizer), unevenness of spreading, and the effects of drought in several trial locations. An overall assessment of the currently available data in silage trials for 2011 and 2012 (Moebius-Clune et al. 2013a) suggests that the model is handling these well, and that profit gains are achieved particularly with large N use reductions at sidedress, but further testing is desirable.

IA corn grain trials (Figure 1 j-l). The majority of 2012 Iowa trial results were impacted by abnormally droughty conditions. Still, Adapt-N rates in all but two of the 19 IA trials resulted in N input reductions (by 36 lb/ac on average). Except for one trial, no significant yield loss was measured with these reduced N rates. Adapt-N rates provided a profit advantage over conventional N rates in 74% of the trials (by $1.49 to $81.20/acre). In one of the three trials where N reductions resulted in profit losses, actual yield achieved with the higher N rate exceeded expected yield used in Adapt-N by 9 bu/ac (Trial 62), resulting in a profit loss despite N savings. In the 2 trials (65 and 73) where Adapt-N recommended a higher rate than the conventional N rate (by 30 lb/ac and 40 lb/ac respectively; the latter was accidentally implemented as 70 lb/ac), the expected yield was not attained due to mid-season drought, resulting in profit losses from unnecessary N application.

Conclusions
Our 2012 Adapt-N trials affirm our 2011 conclusions: The value of the Adapt-N tool is substantial, resulting in significant N input and loss reductions and in profit savings in 77% of all trials (Table 2, Figure 2). Of the 2012 recommendation errors, half (7 trials) were preventable with better expected yield inputs, and only 5% were unexplained. Recommendation errors in 2012 resulting in profit losses mostly occurred in instances where expected yield either exceeded or underestimated actual yield, thereby demonstrating the importance of a good estimate of the expected yield in generating accurate N recommendations using Adapt-N. Drought conditions during the growing season resulted in abnormally low yields in several trials. Obviously, Adapt-N or other N recommendation methods are unable to account for abnormal weather events that occur after the window for sidedressing has passed. The tool was, however, successful in adjusting for the significant effects of early season conditions to recommend N fertilizer needs more precisely.

Over the 2012 growing seasons, 61 trials indicate that:

  • Grower profits increased on average by $32/ac in NY, and by $17/acre in IA trials with the improved 2012 model version.
  • N application rates were significantly reduced in almost all cases, by 54 lbs N/ac on average, and thus post-growing season losses of excess N to the environment were decreased substantially.
  • Yield losses were generally negligible (-1 bu/ac average across all trials), despite the reduced N inputs
  • Higher N recommendations were justified by higher yields when drought was not the greater limiting factor.
  • 77% of Adapt-N recommendations provided increased grower profits over current rates in 2012, when including inadequate expected yield inputs, 87% when these are excluded.
  • Model inputs, especially yield expectation, must be carefully chosen to represent field-specific conditions.

In all, growers can realize large savings with the use of Adapt-N, which also provides strong incentives to shift the bulk of N applications to sidedress time, and will in the long term decrease environmental losses.

For more information: The Adapt-N tool and training materials are accessible through any device with internet access (desktop, laptop, smartphone, tablet) at http://adapt-n.cals.cornell.edu/. Information on account setup and the recorded 3/21/2013 in-depth training webinar are posted there. Adapt-N users can elect to receive email and/or cell phone alerts providing daily updates on N recommendations and soil N and water status for each field location in Adapt-N.

Acknowledgements:  The development and testing of the Adapt-N tool was supported through funds from Cornell University, USDA-NIFA Special Grants on Computational Agriculture and the Agricultural Ecosystems Program (U.S. Rep. Maurice Hinchey-NY), Northern NY Agricultural Development Program, a USDA-NRCS Conservation Innovation Program, NY Farm Viability Institute, International Plant Nutrition Institute, and MGT Envirotec. We are grateful for the cooperation in field activities from Bob Schindelbeck, Keith Severson, Kevin Ganoe, Sandra Menasha, Joe Lawrence, and Anita Deming of Cornell Cooperative Extension, from Mike Davis at the Willsboro Research Farm, from Dave DeGolyer, Dave Shearing and Jason Post at the Western NY Crop Management Association, from Eric Bever and Mike Contessa at Champlain Valley Agronomics, from Mark Ochs and Ben Lott at Mark Ochs Consulting, and from Peg Cook at Cook’s Consulting in New York, from Kevin Kuehner of Minnesota Department of Agriculture, and from Shannon Gomes, Hal Tucker, Michael McNeill, and Frank Moore at MGT Envirotec in Iowa. We also are thankful for the cooperation of the many farmers who implemented these trials on their farms. In particular we would like to acknowledge Robert and Rodney Donald for implementing farm-wide trials on most of their fields (Moebius-Clune et al., 2013b).

References
Moebius-Clune, B., M. Carlson, H. van Es, and J. Melkonian. 2013a. Adapt-N Proves Economic and Environmental Benefits in Two Years of Strip-Trial Testing in New York and Iowa. What’s Cropping Up? Preview.

Moebius-Clune, B., M. Carlson, D. Moebius-Clune, H. van Es, and J. Melkonian. 2013b. Case Study – Part II: Donald & Sons Farm Implements Adapt-N Rates on Whole Farm, Saves Money and Environment. What’s Cropping Up? TBD.

Moebius-Clune, B., H. van Es, and J. Melkonian. 2012. Adapt-N Increased Grower Profits and Decreased Environmental N Losses in 2011 Strip Trials. What’s Cropping Up? 22. [URL verified 4/27/13].

Print Friendly, PDF & Email