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osunpk

osunpk

Since 2008 I have served as the Precision Nutrient Management Extension Specialist for Oklahoma State University. I work in Wheat, Corn, Sorghum, Cotton, Soybean, Canola, Sweet Sorghum, Sesame, Pasture/Hay. My work focuses on providing information and tools to producers that will lead to improved nutrient management practices and increased profitability of Oklahoma production agriculture

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OSUNPK Fertilizer Market Outlook: Urea Turns Higher in an Uneven Market

Oklahoma’s clearest fertilizer move over the past two weeks was urea’s return to higher ground. The September 18 USDA average rose $36.08 per ton, or 5.9%, to $646.28. Anhydrous ammonia also increased $39 per ton, while UAN 28% edged higher and UAN 32% slipped. The split among nitrogen products is a useful reminder that one product’s direction does not automatically describe the whole nitrogen market.

Price-source note: The accompanying graphic’s Oklahoma average, minimum, and maximum come from the USDA Agricultural Marketing Service Oklahoma Production Cost Report. USDA does not identify contributing dealers. Named public dealer cash quotes, including Two Rivers Cooperative, are tracked separately and are not blended into USDA statistics.

USDA described urea as the clear exception in an otherwise uneven market, with increases reported consistently across its contacts. That local move contrasts with recent evidence of softer international urea values. India’s landed import cost reportedly fell to about $406 per metric tonne in August, 57% below its May peak, while Indian stocks reached 7.51 million tonnes—78% above a year earlier. Those numbers suggest improved global availability, but they do not guarantee lower Oklahoma replacement costs. Timing, inland freight, dealer inventory position, product form, and the price paid for the next load can create a different local signal.

Anhydrous ammonia’s increase deserves attention as fall application approaches, even though it remained below its July level. UAN’s mixed movement also fits a market in which inventory coverage differs by product. In August, fertilizer analyst Josh Linville noted that UAN and ammonia manufacturers had strong forward sales positions even as urea benchmarks weakened. That observation remains relevant to the current divergence, though it should be treated as market context rather than a forecast.

Phosphate prices barely moved in the Oklahoma report, but the cost picture underneath them is less quiet. USDA said phosphorus-fertilizer production inputs have risen sharply, adding upward pressure and near-term uncertainty. International reporting also placed August DAP values above April levels, with freight disruptions cited as a factor. Ammonia and sulfur are major variable inputs in phosphate production, so strength or supply disruption in either market can eventually affect DAP and MAP replacement values. AMS and ATS moved lower locally this period, but sulfur-market risk remains relevant to both products and to phosphate manufacturing.

Another cost pressure sits outside the fertilizer table. USDA reported Oklahoma farm diesel up $0.72 per gallon in two weeks to a record $5.44 average for this series. The fertilizer graphics exclude delivery and application charges, as they should, but higher fuel costs can still raise the total cost of getting product to the field.

Over the next several weeks, watch whether Oklahoma urea gains persist across another report, whether fall NH₃ demand strengthens, and whether phosphate input pressure reaches posted retail values. India’s purchasing pace, global urea availability, sulfur and ammonia supply, freight, and local moisture conditions all remain important. These forces are pulling in different directions, so the present data support caution rather than a definitive price call.

For Oklahoma producers and dealers, compare products on both a cash-per-ton and nutrient-cost basis, then verify pickup or FOB terms and all service charges. Where soil tests allow flexibility, product fit, timing, and availability may matter as much as the posted price.

Fertilizer markets, local prices, and availability can change quickly. Confirm current prices and terms with local dealers before purchasing.

Market Sources

This report is produced via Chat GPT Plus Work, with review by Brian Arnall.

Soil Your Undies: When a Great Demo Gets Asked to Do Too Much

I often say that in K–12 education we teach a lot of things in black and white. Students first need to understand the basic concepts: plants need nutrients, microorganisms decompose organic matter, and soils are biologically active. Then somewhere through a bachelor’s degree, or simply through enough years of experience, we learn that agriculture is rarely that black and white. There are a lot of shades of gray. Keep studying, researching, farming, or advising long enough and you eventually realize there aren’t just 256 shades of gray. There is also ROYGBIV. There is a whole spectrum of interactions and conditions that determine what happens in the soil.

I think the “Soil Your Undies” demonstration fits that progression perfectly. It is a great black and white teaching tool. Bury a pair of 100% cotton underwear, wait several weeks, and dig them back up. Sometimes there isn’t much left besides the elastic waistband. Students can see that something happened belowground, and that opens the door to conversations about microorganisms, decomposition, carbon cycling, and the fact that soil is a living system. As a teaching demonstration, that is hard to beat.

Where I become more cautious is when we take that intentionally simple lesson and make a much more complicated conclusion: the pair with less cotton remaining came from the healthier soil or represents the better management practice. That is where we need to move beyond black and white.

SOIL YOUR UNDIES Challenge pulled from USDA Natural Resources Conservation Service Facebook page posted on June 21, 2024

To begin with we must know what the microbes are eating.

Cotton fiber itself gives us the first clue about what this test measures. Cotton is approximately 95% cellulose, and standardized cotton strips have been used by soil scientists for decades specifically as an index of cellulose decomposition (Latter et al., 1988; Tiegs et al., 2013). Cellulose is a long chain of glucose molecules and one of the major structural components of plant material. Its decomposition depends on organisms capable of producing cellulolytic enzymes that break those chains into smaller compounds that microorganisms can use.

Therefore, when cotton underwear disappears, we can make a scientifically defensible statement: the soil environment supported cellulose decomposition during the time the underwear was buried. That is useful information but notice how specific that statement is. We did not measure the total number of microorganisms, microbial diversity, or every biological process occurring in that soil, and we certainly did not measure everything encompassed by the much broader term soil health. Research comparing cotton-strip decomposition with microbial biomass illustrates that distinction. Walton and Allsopp (2007) found a relatively poor relationship between cotton-strip measurements and microbial biomass measured by substrate-induced respiration (r² = 0.26). They recommended using cotton strips alongside other physical and chemical soil indicators rather than as a stand-alone biological measurement. Soil can contain a substantial microbial population without necessarily destroying a pair of underwear quickly.

Is breaking down cellulose what the soil needs to be doing?

Cellulose decomposition is important. Crop residues contain cellulose, and their decomposition is part of carbon and nutrient cycling. But agriculture does not necessarily need every microbial process operating at its maximum rate all the time. Depending on the production system, time of year, and management objective, we may be more interested in nutrient mineralization or immobilization, aggregate formation, disease suppression, nitrogen transformations, carbon stabilization, or simply keeping residue on the soil surface. Faster cellulose decomposition is therefore not automatically better; it tells us that this specific biological process was occurring more rapidly under those conditions. This does not make the cotton test wrong. It means we need to be precise about the question it answers.

The scientific cotton-strip assay has successfully detected differences in cellulose decomposition among soils and management systems. Nachimuthu et al. (2022), for example, found differences in cotton-strip degradation among long-term crop rotation and tillage treatments. That supports the conclusion that management can affect cellulose decomposition. It does not automatically establish that the management practice producing the fastest cellulose decomposition created the healthiest soil. Margenot and Wade (2023) raised a similar concern about the interpretation of soil enzyme activities, cautioning against taking a measurement of a specific biological process and assuming that it scales directly to broader soil functions or outcomes. Measuring a process and determining what that process means for the functioning of the soil are two different questions.

Now add some gray: nitrogen

This is where the soil fertility specialist in me starts asking questions. Cotton provides microorganisms with a lot of carbon but almost no nitrogen. Yet microorganisms cannot live on carbon alone. They need nitrogen to produce proteins and enzymes and to build new microbial biomass. The microorganisms colonizing that cotton therefore must obtain much of what they need from the surrounding soil. Imagine taking one soil and thoroughly mixing it. We start with the same microbial community, organic matter, texture, pH, temperature, and water content. Divide it into two treatments and bury identical pieces of cotton. The only major difference is mineral nitrogen: one treatment has very little available NH₄-N and NO₃-N, while the other has an adequate supply. Would the underwear necessarily decompose at the same rate? There is good reason to believe it may not.

Nottingham et al. (2018) examined nutrient limitation during cellulose decomposition by adding cellulose and individual nutrients to soils. Nitrogen addition produced the largest fungal growth response associated with cellulose, and the researchers concluded that nitrogen was an important limitation to fungal growth and cellulose decomposition in the soils they studied. The implication for our underwear is important. Cotton in the higher N soil could potentially disappear faster without that soil starting with more microorganisms or a “healthier” microbial community. The organisms capable of decomposing cellulose may simply have better access to the nitrogen required to grow and produce the enzymes needed to exploit this large carbon source. That does not mean adding nitrogen fertilizer will always make underwear disappear faster. Microbial responses to N depend on the soil, microbial community, nutrient status, substrate, and environment. Other nutrients may become limiting, and long-term N additions can alter microbial communities and decomposition processes in ways that are very different from a short-term response to available N. That complexity is exactly the point: we started with a black-and-white demonstration of biological activity, but bringing in the mineral N conversation now add many shades of gray. 

Then comes pH—and more color

Soil pH adds another layer because it does more than simply make microbes “more” or “less” active. It can change which groups of microorganisms are most active. I have plenty of work discussing how quickly soil pH can change across landscape and how much our management also significantly impacts soil pH. Across agricultural soils, bacterial growth and diversity generally increase as strongly acidic soils approach neutral conditions, while fungi tend to become relatively more important as pH declines. Rousk et al. (2009, 2010), working across soils ranging from approximately pH 4 to 8, documented substantial shifts in bacterial and fungal growth and in the fungal relationship across the pH gradient. That distinction matters for an underwear test because both bacteria and fungi participate in cellulose decomposition. A lower-pH soil may have reduced bacterial growth while maintaining a comparatively greater fungal contribution. At a higher pH, the balance can shift toward bacteria. The microbial community doing the work can therefore change substantially without a corresponding black-and-white change from “poor biology” to “good biology.”

There is also evidence that pH can affect cellulose decomposition itself. Work with volcanic soils found that cellulose decomposition potential was related to both soil pH and microbial N availability, rather than simply to the amount of microbial biomass present. This creates an interesting possibility for the underwear demonstration: two soils could contain similar amounts of microbial biomass but decompose cotton at different rates because one provides a more favorable chemical and nutritional environment for the organisms capable of using cellulose. I would also be careful about turning that into another simple rule such as “higher pH equals faster cotton decomposition.” As soils move from strongly acidic conditions toward the range where many agricultural crops are grown, bacterial activity generally increases, but fungi, bacteria, extracellular enzymes, nutrient availability, and cellulose decomposition do not all respond to pH in exactly the same way. Very acidic conditions can suppress some processes while favoring organisms better adapted to acidity. That is a much more interesting biological story than simply labeling one soil as having more microbial activity than another.

Then comes ROYGBIV

Nitrogen and pH are only two variables. Soil moisture determines whether microorganisms can remain active and whether substrates and nutrients can move through the soil. Texture influences water retention, aeration, nutrient availability, aggregation, and microbial habitat, so identical cotton buried in a sandy soil and a clay soil is not necessarily experiencing the same environment. Phosphorus, sulfur, or another nutrient can limit microbial growth even when carbon and nitrogen are abundant. Finally, the microbial community itself matters because different bacterial and fungal populations differ in their ability to produce the enzymes needed to attack cellulose.

What we see when we dig up the underwear is therefore the integrated result of microbial community × substrate × nitrogen × other nutrients × moisture × pH × texture × time, along with interactions among them. A difference in cotton decomposition is real, but the underwear alone cannot tell us which of those factors produced the difference. More importantly, it cannot tell us whether the difference represents better or worse management. That distinction between a soil health indicator and the soil function or outcome it is intended to represent is increasingly being emphasized in the soil health literature (Maharjan et al., 2024).

That is no longer black and white. That is ROYGBIV.

Keep burying the underwear

None of this is an argument to stop Soil Your Undies. Keep doing it. Use it in classrooms, bury underwear at field days, have students predict what will happen, and put underwear in contrasting soils so they can see that decomposition happens below ground. It makes an invisible biological process visible, and that makes it a great teaching tool.

Where I think we need to be more careful is when we turning that demonstration into a scorecard for soil health or management practices. A producer should not dig up two pairs of underwear and conclude that the field with less cotton remaining necessarily has more microorganisms, better management, greater fertility, or healthier soil. Too many biological, chemical, and environmental factors influence cellulose decomposition for the underwear alone to support those conclusions.

Perhaps that distinction provides an even better way to use the demonstration. With younger students, Soil Your Undies can teach the black and white: microorganisms live in soil and decompose organic materials. With more advanced students, farmers and agronomists, the same demonstration can teach the gray by asking, why did these two pieces of cotton decompose differently? Once we start asking about water, nitrogen, pH, texture, nutrients, microbial communities, and all of the possible interactions, we get to ROYGBIV.

This distinction becomes especially important when the demonstration is used with students or audiences without an agricultural or soil science background. If two management systems are compared and the one with less cotton remaining is presented as the “better” practice, we may be teaching a conclusion the test cannot support. Those audiences may not yet have the background to recognize the effects of moisture, nitrogen, pH, texture, or microbial community on cellulose decomposition. The demonstration can then unintentionally introduce bias toward management practice rather than teach how complex soil biological processes really are.

So, keep burying the underwear. Just don’t ask it to answer more than it can.

Graphic showing factors impacting cellulosic breakdown in soils. Created with the assistance of CHATGPT

References

  • Chew, I., Obbard, J.P., & Stanforth, R.R. 2001. Microbial cellulose decomposition in soils from a rifle range contaminated with heavy metals. Environmental Pollution 111:367–375. doi:10.1016/S0269-7491(00)00094-4.
  • Latter, P.M., Bancroft, G., & Gillespie, J. 1988. Technical aspects of the cotton strip assay in soils. International Biodeterioration 24:25–47. doi:10.1016/0265-3036(88)90073-5.
  • Maharjan, B., Das, S., Thapa, V.R., & Sharma Acharya, B. 2024. Soil health cycle. Agrosystems, Geosciences & Environment 7:e20504. doi:10.1002/agg2.20504.
  • Margenot, A.J., & Wade, J. 2023. Getting the basics right on soil enzyme activities: A comment on Sainju et al. (2022). Agrosystems, Geosciences & Environment 6:e20405. doi:10.1002/agg2.20405.
  • Nachimuthu, G., Hundt, A., Palmer, B., Schwenke, G.D., & Knox, O.G.G. 2022. Cotton strip assay detects soil microbial degradation differences among crop rotation and tillage experiments on Vertisols. Journal of Microbiological Methods 200:106558. doi:10.1016/j.mimet.2022.106558.
  • Nottingham, A.T., Hicks, L.C., Ccahuana, A.J.Q., Salinas, N., Bååth, E., & Meir, P. 2018. Nutrient limitations to bacterial and fungal growth during cellulose decomposition in tropical forest soils. Biology and Fertility of Soils 54:219–228. doi:10.1007/s00374-017-1247-4.
  • Rousk, J., Brookes, P.C., & Bååth, E. 2009. Contrasting soil pH effects on fungal and bacterial growth suggest functional redundancy in carbon mineralization. Applied and Environmental Microbiology 75:1589–1596.
  • Rousk, J., Bååth, E., Brookes, P.C., Lauber, C.L., Lozupone, C., Caporaso, J.G., Knight, R., & Fierer, N. 2010. Soil bacterial and fungal communities across a pH gradient in an arable soil. ISME Journal 4:1340–1351.
  • Tiegs, S.D., Clapcott, J.E., Griffiths, N.A., & Boulton, A.J. 2013. A standardized cotton-strip assay for measuring organic-matter decomposition in streams. Ecological Indicators 32:131–139. doi:10.1016/j.ecolind.2013.03.013.
  • Walton, N.G., & Allsopp, D. 2007. Comparison of methods for measuring soil microbial activity using cotton strips and a respirometer. Journal of Microbiological Methods 69:322–329.

OSUNPK Fertilizer Market Outlook: Nitrogen Decline Pauses 9.7.26

The most important fertilizer-market development of the past two weeks is not another sharp price move, but the pause that followed August’s nitrogen decline. Oklahoma’s September 4 report shows urea down only $4.40 per ton, UAN 32% down $5.72, and anhydrous ammonia down $5.00. UAN 28%, phosphate, potash, AMS, and ATS were unchanged. Looking back four weeks, however, the nitrogen correction remains substantial: urea is down 6.6%, UAN 28% is down 8.7%, UAN 32% is down 5.7%, and NH3 is down 5.8%.

Price-source note: The accompanying graphic’s Oklahoma average, minimum, and maximum come from the USDA Agricultural Marketing Service Oklahoma Production Cost Report. USDA does not identify contributing dealers. Named public dealer cash quotes, including Two Rivers Cooperative, are tracked separately and are not blended into USDA statistics.

USDA attributes the quiet local market to weak demand under persistent heat and drought. That distinction matters. Stable prices caused by limited field activity do not necessarily indicate that replacement costs or global supply risks have settled. As fall demand develops, local bids may respond differently depending on dealer inventory, transportation, and when replacement tons were purchased.

Nitrogen markets continue to balance large international buying programs against improved availability. In recent public commentary, StoneX fertilizer analyst Josh Linville pointed to India’s 1.7-million-ton urea purchase and identified Brazil as the next major demand cycle to watch. A completed Indian tender can absorb prompt supply, but the next direction depends on whether Brazilian demand arrives strongly enough to keep exporters engaged. Product type also matters because Brazil typically needs granular urea, while much of China’s available export supply has been prilled.

Phosphate remains a different story. Oklahoma DAP and MAP prices were unchanged, but the global market still carries support from restricted Chinese exports and elevated sulfur and ammonia costs. Linville also highlighted the arrival of Moroccan phosphate cargoes following the suspension of U.S. countervailing duties, including an MAP vessel that is more relevant to U.S. demand than the earlier TSP shipment. Additional import competition could improve availability, but one or two vessels do not by themselves reset the market.

Sulfur is part of that phosphate equation. It is required to manufacture phosphoric acid, so constrained sulfur trade can support DAP and MAP production costs. The same global pressure does not translate directly into identical local movement for AMS and ATS; both remained unchanged in Oklahoma this period. Those products should therefore be evaluated on actual sulfur need, formulation, and local cash price rather than assumed movement from phosphate headlines.

The next items to watch are Oklahoma rainfall and fall field activity, Brazilian urea purchasing, additional Indian tenders, Chinese export volumes, Moroccan phosphate arrivals, sulfur availability, and inland freight. These forces remain capable of moving in opposite directions, so the current pause should not be read as a firm price forecast.

For Oklahoma producers, this is a good time to compare products on both dollars per ton and cost per pound of the needed nutrient. Quotes should be placed on the same pickup or FOB basis, with application, blending, delivery, and tax separated before making comparisons.

Fertilizer markets, local prices, and availability can change quickly. Confirm current prices and terms with local dealers before purchasing.

Market Sources

This report is produced via Chat GPT Plus Work, with review by Brian Arnall.

OSUNPK Fertilizer Market Outlook: Local Nitrogen Prices Break Lower 8.24.26

The most important movement of the past two weeks is the decline in Oklahoma nitrogen references. From August 7 to August 21, UAN 28% fell $39.70 per ton, urea fell $38.73, and anhydrous ammonia fell $46.00. USDA attributes the weakness to reduced demand as persistent heat and limited rainfall constrain field activity across the state.

Price-source note: The accompanying graphic’s Oklahoma average, minimum, and maximum come from the USDA Agricultural Marketing Service Oklahoma Production Cost Report. USDA does not identify its contributing dealers. Named public dealer cash quotes, including Two Rivers Cooperative, are monitored separately and are not blended into the USDA statistics.

The local decline does not mean that global nitrogen risk has disappeared. StoneX reported August 19 that India secured about 1.7 million metric tons in its latest urea tender with ample offers, including an expected contribution from China. That supply response eased immediate pressure, but attention now shifts toward Brazil’s September-through-December import window. Brazil needs granular urea, while much of China’s available export supply is prilled, so timing, product form, and destination still matter.

Josh Linville’s August 12 market commentary likewise described a well-supplied Indian tender and a weaker NOLA urea market, while cautioning that UAN and ammonia manufacturers held strong forward sales books. That distinction matters in Oklahoma: a softer urea benchmark can move faster than UAN or ammonia when producers have already covered substantial forward demand. Local weather can amplify the difference by weakening spot demand even while manufacturer positions remain supported.

Phosphate prices were nearly unchanged in the Oklahoma report, but their cost structure remains exposed to ammonia and sulfur. CoBank noted August 13 that Middle East disruptions and Russian supply constraints have affected ammonia production and sulfur availability, while China’s phosphate exports remain sharply restricted. Linville also highlighted sulfur as a bottleneck because a large share of globally traded sulfur normally moves through the Strait of Hormuz. Those pressures can raise the cost of producing DAP and MAP even when local posted values are temporarily steady. They also deserve attention for AMS and ATS, although Oklahoma’s reported averages changed little this period.

Potash remains the quietest major nutrient. Its production base is less directly tied to Middle East natural gas and sulfur, although ocean freight and broader logistics can still affect delivered replacement costs.

Over the next several weeks, watch Oklahoma rainfall and fall field demand, Brazil’s urea buying pace, the mix of Chinese exports, further Indian tenders, phosphate operating rates, sulfur availability, and freight. These forces point in different directions, so the current local nitrogen decline should be read as a market development rather than a definitive forecast.

For Oklahoma producers and dealers, the practical step is to compare current cash quotes on the same pickup or FOB basis and separate material price from delivery and application. Soil-test needs and product fit should remain central; price movement alone does not determine the best nutrient plan.

Fertilizer markets, local prices, and availability can change quickly. Confirm current prices and terms with local dealers before making purchasing decisions.

Market Sources

This report is produced via Chat GPT Plus Work, with review by Brian Arnall.

Sulfur Fertilizer in Wheat: Is It a Have-To?

Brian Arnall, Precision Nutrient Management Extension Specialist.

Sulfur has become a much bigger part of the fertility conversation over the last several years, and for good reason. We are producing higher-yielding crops, removing more nutrients from our fields, and receiving less sulfur from atmospheric deposition than we did several decades ago. But that does not mean sulfur fertilizer has become a “have-to” application for every wheat field.

Sufur deficiency seen is a wheat field near Fairfax Ok, in 2024.

Ms. Kelby Linn’s research provides a good example of why soil testing still matters. Across the environments in this study, sulfur fertilizer did not increase wheat grain yield. The soil was able to supply enough sulfur to meet the yield demand of the crop. When fertilizer margins are tight, that is important. Applying a nutrient that is already present in sufficient amounts is an expense without a yield return. At the same time, these results should not be interpreted to mean that sulfur fertilizer is unnecessary. Sulfur management is ultimately a mass-balance issue. Every bushel we harvest removes nutrients from the field. As yields increase, nutrient removal increases. If we continually remove more sulfur than the soil and other sources can supply, at some point we have to replace it.

That is why I am more concerned about sulfur in intensive, high-yield production systems, particularly on sandier soils and soils with lower organic matter. These soils generally have less capacity to supply sulfur, while a high-yielding crop is removing more of it. That combination increases the likelihood of sulfur becoming limiting. This is where soil testing becomes a valuable management tool. Rather than treating sulfur as something wheat either “always needs” or “never needs,” we should identify the fields where soil supply is unlikely to meet crop demand and put our fertilizer dollars there.

It is also important not to carry the wheat results presented here across every cropping system. Our ongoing work in corn has shown more response to sulfur fertilizer than we have observed in wheat. That fits the larger nutrient-removal discussion, particularly as we push corn yields higher. We will share two years of data after this year’s corn harvest.

Kelby’s research also raises another interesting question. If the soil already contains enough sulfur to maximize wheat grain yield, does additional sulfur do anything? His work suggests that it can. The response may not be additional bushels, but changes in how nitrogen is used and, ultimately, the quality and functionality of the grain.

Understanding Sulfur’s Role Beyond Grain Yield

Kelby Linn and Brian Arnall

Why Nitrogen and Sulfur Must Work Together

Nitrogen (N) has long been recognized as the most important nutrient for winter wheat production. It is a primary driver of vegetative growth, grain yield, and grain protein concentration, making N management the focus of most wheat fertility programs across Oklahoma. Sulfur (S) plays a different but complementary role. Nitrogen supplies the building blocks needed to produce proteins, while S is needed to form sulfur-containing amino acids such as cysteine and methionine. These amino acids contribute to the bonds that strengthen gluten proteins and influence dough strength, elasticity, and overall baking performance. When S becomes limiting, wheat may continue to take up N but may be less efficient at incorporating that N into functional storage proteins. Therefore, the relationship between N and S may become increasingly important as N rates and yield potential increase. The literature suggest that relationship can be wrong in both directions were N is in excess and S is deficient can cause yield loss but also where S is in excess and N is deficient we can experience loss.

Understanding the System

To better understand how S behaves under different N environments, field trials were conducted across north-central Oklahoma and south-central Kansas during the 2023–2025 growing seasons. The objective was to determine whether S responses differed when N was limiting compared with a high-N production environment.

Two N fertilizer rates were evaluated using ammonium sulfate (AMS) and urea:

  • 60 lb N/ac, representing a sub-optimal or N-limited environment
  • 140 lb N/ac, representing a high-N environment where S could have greater potential to become limiting

Each N rate was combined with five S rates supplied as AMS: 0, 5, 10, 20, and 30 lb S/ac.

Sulfur was applied before jointing, between Feekes 4 and 6, with the top-dresss N application, when wheat nutrient uptake is increasing and the crop is transitioning toward reproductive development. This allowed us to evaluate the influence of S on grain production, N utilization, and grain quality under both N-limited and high-N conditions.

Soil testing was an important part of interpreting the results. Across the locations, sulfate-S was present in the soil profile before fertilizer application. Soil test S varied among sites and depths, reinforcing that the amount of S already available to the crop can differ considerably among fields.

Table 1. Average composite soil sample results of pH, organic matter (OM), nitrate, and SO4 for all locations of the S interaction study.

First, What Happened to Yield?

Nitrogen remained the dominant factor controlling grain yield. Across environments, average wheat yield increased from 46 bu/ac with the lower N rate to 56 bu/ac with the higher N rate. Sulfur, however, did not significantly increase grain yield. Soil tests indicated that the sites generally contained measurable sulfate-S, which correctly predicted the lack of a yield response. If grain yield had been our only measurement, the story could have ended there. But the addition of S affected several characteristics related to how the grain performed during milling and dough development, particularly under the high-N treatment.

Why Wheat Quality Matters

Most Oklahoma wheat producers market wheat based primarily on grain yield and protein concentration. Once wheat moves farther through the grain chain, however, millers and commercial bakeries evaluate additional characteristics that determine how the flour performs. Hard red winter wheat is valued for its ability to produce strong bread flour. That ability depends not only on the amount of protein in the grain but also on the structure and functionality of those proteins. Nitrogen applications generally increases grain protein concentration, while S can influence the composition of those proteins. Adequate S promotes the formation of S-containing proteins involved in strong gluten networks. As a result, two wheat samples with similar protein concentrations can potentially behave differently during milling and baking.

Looking Beyond Grain Protein

Several measurements were used to evaluate wheat and flour quality. Grain protein represents the total protein concentration of the kernel and remains an important factor in wheat marketing. Flour protein measures the protein concentration after the bran and other components have been removed during milling. Other measurements tell us more about milling and baking performance. Milling yield describes how much usable flour can be produced from the grain, while flour ash is an indicator of the amount of mineral material remaining in the flour and can help evaluate milling efficiency. Falling number provides information about alpha-amylase activity and potential preharvest sprouting. Gluten index is particularly useful for evaluating gluten strength. A higher gluten index generally indicates stronger gluten that can better maintain dough structure during mixing and fermentation.

What Happened When We Made Dough?

One of the unique aspects of this study was evaluating flour with DoughLAB analysis. Rather than measuring only grain or flour composition, DoughLAB measures how flour behaves during mixing. Development time measures how long the dough must be mixed to reach optimum consistency. Dough stability measures how long the dough maintains that consistency before beginning to break down. Mixing tolerance index, or MTI, measures how rapidly the dough weakens after optimum development. Water absorption measures the amount of water required to produce dough at a standard consistency.

Of these measurements, dough stability provided one of the more interesting S responses. Under the high-N treatment, average dough stability increased from approximately 6 minutes without S to nearly 15 minutes at the highest S rate. Greater dough stability indicates that the gluten network was able to withstand mixing for a longer period before breaking down. For commercial baking, this can be important because stronger, more stable dough generally provides greater tolerance during mixing and more consistent performance during processing.

What Did We Learn?

Image created utilizing ChatGPT

Across these environments, N remained the primary factor controlling grain yield. Increasing N increased average yield, while adding S did not provide a significant yield response. However, the absence of a yield response did not mean S had no effect on the wheat. Under high-N conditions, S improved several measurements associated with grain and dough functionality, including gluten strength, dough development, and dough stability.

These results help separate two questions that are sometimes treated as the same question: Does the crop need S to produce more grain, and does S influence what happens inside the grain?

At the locations included in this study, the answer to the first question was no. The soils supplied enough S that additional fertilizer did not increase yield. The second question was more complicated. Sulfur influenced characteristics associated with protein functionality and end-use quality, particularly when N supply was high. That does not mean S should be applied routinely to improve wheat quality. For producers, the first fertilizer decision should still be based on whether the crop is likely to become S deficient. Soil testing, soil texture, organic matter, yield potential, and production history all provide information that can help make that decision. The larger lesson from this work is that S has a role in wheat beyond simply producing more bushels. Understanding that role helps us make better fertilizer decisions while continuing to put fertilizer where it is most likely to provide a return.

Data drawn from The Influence of Sulfur Under Nitrogen Extremes in Winter Wheat.
Linn, Kelby DeeAnn.   Oklahoma State University ProQuest Dissertations & Theses,  2026. 32668685.

Cheap Nitrogen is not always the best Nitrogen, Timing matters

Brian Arnall: Precision Nutrient Management Extension Specialist, Oklahoma State University

In 2020, we published a summary of four OSU trial series comparing pre-plant nitrogen (N) to in-season N in grain-only winter wheat. https://osunpk.com/2020/09/10/value-of-in-season-application-for-grain-only-wheat-production/ Since then, three of those trial series have made it through peer review, and additional analyses have added considerably more data to the story. From both historic data from Dr. Raun’s program and new work. All together, these studies now represent more than 90 Oklahoma site-years across a wide range of environments, N rates, and application timings. So, after several more years of research, has the conclusion changed?

Does waiting to apply nitrogen cost wheat yield?

Across these studies, moving N from pre-plant to a properly timed in-season application generally maintained or increased grain yield. How often in-season N increased yield varied among datasets. Souza et al. found that winter wheat could recover from early N stress without sacrificing yield over a surprisingly wide application window. In other studies, in-season N was statistically similar to pre-plant N. The important point is that delaying N did not automatically mean giving up yield.

The Regional N study started by Dr. Raun 2in 2009, adds an important environmental piece to the story. Split N out yielded pre-plant N in approximately 29% of the 52 site-years, specifically those classified as highly responsive to N. These years tend to be wetter environments with greater yield potential. In the remaining 71%, split and pre-plant N produced statistically similar yields. Across all 52 site-years, splitting N never resulted in a significant yield loss compared with pre-plant N.

When a yield advantage with in-season N occurred, it could be meaningful. One study found a single in-season application produced approximately 8% greater yield than a full-rate pre-plant application. Sharry’s Gallagher/Green Hammer study found a single Feekes 4 (spring green up) application averaging approximately 11% greater yield than a single pre-plant application across two varieties and four site-years. The Regional N analysis found an approximately 5.4 bu/ac, or 14%, advantage for split N over pre-plant N in highly N-responsive environments, while there was no difference in the remaining environments. The message isn’t that in-season N always produces more wheat. It doesn’t. Properly timed in-season N generally maintained yield, and about 58% of the time increased it.

Protein Tells an Even More Consistent Story

Protein responded more consistently to N timing than yield. Later N increased grain protein across nearly every dataset. In the Regional N study, split N increased protein by 0.8 percentage points above the pre-plant compared with a 1.1-point increase from all N applied in-season. That advantage occurred across every environmental response category.  In the end yield response to delayed N depends heavily on environment. The protein response is considerably more consistent.

If In-Season N Works, Is There a Reason to Split It?

Once the decision is made to move N away from a full pre-plant application, another question follows: should some N still go out pre-plant and the remainder in-season, or can the entire rate wait until the growing season? Two datasets tested that question directly, and neither found a consistent yield advantage to splitting N over a single, well-timed in-season application.

Sharry’s study found that a single green up application out-yielded both two-way and three-way splits by approximately 4.4 to 9.4 bu/ac at the site-years where treatments differed. At no site-year did a split application out-yield the single in-season timing. Abiola (2025) reached essentially the same conclusion. A single in-season application matched or exceeded a 50/50 pre-plant/in-season split across the timings evaluated. There was, however, an important exception. As the single in-season application was pushed into late March and April, having some N already applied reduced the potential downside.

Splitting N appears to be more about risk management than yield management.

Putting some N out early provides insurance against weather, field conditions, equipment problems, or other factors that prevent the planned in-season application from being made on time. If a single in-season application can be made at the proper time, however, these data provide little evidence that splitting N improves yield. So, in the end you reduce the “risk” but double application cost.

Timing Still Matters

None of this should be interpreted as saying N can be applied whenever it is convenient. The window for applying N to grain-only winter wheat is wider than many growers assume, but it isn’t unlimited. As application moves later, the opportunity for unfavorable weather to interfere with N availability becomes increasingly important.

The Regional N study provides a good example. For post top-dress applied N rainfall alone explained 27% of the site-to-site variation in how much the crop responded to N. The environments where split N increased yield over pre-plant N were generally the wetter, higher-yielding environments.

Waiting on N is a management strategy. Waiting too long is not.

Moving N in-season allows the rate decision to be made when considerably more is known about stand, growing conditions, and yield potential. But that flexibility only has value if the application is made while the crop can still effectively use the N. The data shows that the most risk adverse timing falls in the January to mid-March time frame.

What About Fertilizer Price?

Agronomy is only part of the decision. Anhydrous ammonia can provide a substantial cost-per-pound-of-N advantage over fertilizer sources typically used for in-season applications. When that price gap becomes large, the in-season strategy needs to create enough additional value through yield, protein, improved N-rate decisions, or reduced N loss to pay for the more expensive source.

The break-even calculation is straightforward: Additional N cost per acre ÷ wheat price = additional bushels needed to break even. At a 100 lb N/ac rate, every $0.10/lb difference in N price represents $10/ac in fertilizer cost.

For example, if the in-season N source costs $0.30/lb N more, that is a $30/ac disadvantage before the crop is planted. At $4.00 wheat, in-season N needs to produce 7.5 additional bu/ac to cover that difference. At $5.00 wheat, it needs 6 bu/ac, and at $6.00 wheat, it needs 5 bu/ac.

The range becomes fairly large as the difference in N price changes. At a 100 lb N/ac rate and wheat prices between $4 and $6/bu, a $0.20/lb N-price difference requires roughly 3 to 5 additional bu/ac, while a $0.50/lb difference requires roughly 8 to 13 additional bu/ac.

That doesn’t make either strategy automatically more profitable. In environments where yield is the same, the cheaper N source has the economic advantage. Where in-season N increases yield or protein, the economics can move in the other direction. There is also another economic benefit to waiting that is harder to put into a simple table: by waiting, the producer can adjust the N rate to the yield potential that is there rather than the yield potential hoped for before planting.

So fertilizer price adds another question to the N-timing decision: How much is the flexibility of waiting worth this year?

After more than 90 Oklahoma site-years, there is little evidence that grain-only winter wheat inherently benefits from having the entire N requirement available before planting. A properly timed in-season application generally maintains yield and can increase yield under responsive conditions. The opportunity to increase grain protein is even more consistent. Waiting also allows the final N decision to be made when the producer knows considerably more about the crop, weather, and realistic yield potential.

Splitting N does not appear to provide an additional yield benefit over a single, properly timed in-season application. Its primary value is insurance against missing that application window. But fertilizer price matters. When anhydrous or another pre-plant source provides N substantially cheaper than the available in-season source, those savings have real value and should be weighed against the potential benefits of waiting. There isn’t one N-timing strategy that wins every year. The goal isn’t simply to maximize yield or minimize fertilizer cost. It is to choose the N source, rate, and timing combination that provides the best economic return for the conditions in front of you.

These conclusions apply to grain-only winter wheat. Dual-purpose wheat requires sufficient fall growth for forage production and has a different early-season N requirement.

If you have any questions or comments, please feel free to reach out.

Brian Arnall
b.arnall@okstate.edu

Sources

Souza, J.L.B., Antonangelo, J.A., Silva, A.O., Reed, V., and Arnall, B. 2022. Recovery of Grain Yield and Protein with Fertilizer Application Post Nitrogen Stress in Winter Wheat (Triticum aestivum L.). Agronomy 12:2024.

Abiola, S.O., Souza, J.L.B., Sharry, R., Derrick, J.R., Maatougui, M., and Arnall, D.B. 2025. Split nitrogen applications provide no benefit over a single well timed application in rainfed winter wheat. Frontiers in Plant Science 16:1698494.

Ballagh, B., Ballagh, A., Bushong, J., and Arnall, D.B. The Effect of Nitrogen Fertilizer Placement and Timing on Winter Wheat Grain Yield and Protein Concentration.

Sharry, R. 2025. Response to nitrogen timing of varying winter wheat genotypes Dissertation, https://hdl.handle.net/20.500.14446/344867

Regional N study. 52 Oklahoma site-years, 2009–2023, Okstate Soil Fertility data unpublished.

Oklahoma Nitrogen Prices Continue to Move Lower 8.10.26

Nitrogen prices continued to decline in Oklahoma during the past two weeks, led by anhydrous ammonia. The statewide NH₃ reference fell $72 per ton to $875, while urea and both UAN concentrations also declined. The four-week decrease now exceeds 10% for NH₃ and approaches 7% for UAN 28. Phosphate and potash prices, meanwhile, have changed very little.

The Oklahoma average, minimum and maximum prices shown in the accompanying graphic come from the USDA AMS Oklahoma Production Cost Report. USDA collects FOB asking prices from Oklahoma distributors but does not identify the contributing dealers or disclose the number of observations. Public cash quotes from named dealers, including Two Rivers Cooperative, are tracked separately and are not blended into the USDA regional statistics.

The immediate Oklahoma explanation for softer nitrogen prices is relatively straightforward: hot, dry conditions have slowed fertilizer movement. USDA reported reduced demand across the fertilizer market, with triple-digit temperatures accelerating corn dry-down and allowing harvest to begin in parts of the state. With limited field activity and the primary summer application season behind us, dealers have less nearby demand supporting nitrogen values.

International nitrogen conditions are also becoming less restrictive. Fertilizer-market analyst Josh Linville reported that urea values continue to face pressure from weaker demand and a second round of approved Chinese exports. Additional Chinese availability matters because it gives international buyers another major supply origin and reduces competition for other export tons.

Nutrien’s second-quarter results reinforce the mixed nature of the nitrogen market. Global nitrogen benchmarks remained elevated, but second-quarter nitrogen sales volumes were lower. The market will now be watching whether increased export availability is sufficient to offset upcoming fall demand and additional international purchasing.

Phosphate remains a different story. Oklahoma DAP was unchanged during the latest reporting period, while MAP declined only $1.25 per ton. Stable local prices should not be interpreted as evidence that upstream supply risks have disappeared. Linville reported that Moroccan TSP and MAP are moving toward North America, which could improve regional availability. However, phosphate production continues to face elevated sulfur and ammonia costs and limited export availability from some traditional suppliers. These factors may support replacement costs even while weak seasonal demand keeps Oklahoma prices from moving higher.

Potash remains the most stable major nutrient. Oklahoma’s reported average increased only 50 cents per ton. Nutrien reported higher global potash benchmarks and record first-half sales volumes, but it also reported record production. Strong supply performance helps explain why firm global demand has not produced a significant Oklahoma price movement.

For Oklahoma producers, the most important development is the continued separation between nitrogen and phosphate markets. Lower nitrogen quotes may create purchasing opportunities, but the wide reported ranges make direct comparisons essential. Phosphate prices are locally steady but remain exposed to sulfur, ammonia and import-supply risks. Confirm the cash price, nutrient analysis, pickup or delivery basis, quote expiration and application charges before comparing dealer offers.

Fertilizer markets, local prices and product availability can change quickly. Confirm all prices and terms with local dealers before making purchasing decisions.

**The Oklahoma average, minimum and maximum prices shown in the accompanying graphic come from the USDA AMS Oklahoma Production Cost Report. USDA collects FOB asking prices from Oklahoma distributors but does not identify the contributing dealers or disclose the number of observations. Public cash quotes from named dealers, including Two Rivers Cooperative, are tracked separately and are not blended into the USDA regional statistics.

Market Sources

This report is produced via Chat GPT Plus Work, with review by Brian Arnall.

OSUNPK Fertilizer Market Outlook — July 27, 2026

Produced by Chat GPT Work, reviewed by Brian Arnall, OSU Precision Nutrient Management.

Oklahoma fertilizer markets moved in two different directions during the latest reporting period. Nitrogen prices generally declined, while phosphate and potash remained nearly steady. That local stability does not mean the broader market is free of risk. International production costs, sulfur availability, trade flows and large import programs continue to influence the prices Oklahoma producers may encounter later in the season.

The USDA’s July 24 Oklahoma report placed urea at an average of $672.29 per ton, down $14.42 from the previous report. UAN 28 declined $16 to $472.60, UAN 32 fell $5 to $548.86, and anhydrous ammonia declined $29 to $947. One reported urea quote fell by approximately $300 per ton, while an NH₃ quote moved below $900 and a UAN 28 quote dropped below $400. Those individual movements contributed to unusually wide ranges and should not be treated as representative statewide prices without verification.

The USDA attributed part of the softer market to reduced fertilizer demand during triple-digit heat. Seasonal demand also appears less urgent following major spring and early-summer applications. However, the spread between low and high quotes remains substantial: $365 per ton for urea, $232 for UAN 28 and $225 for NH₃. Those differences make product basis, location and service charges particularly important when comparing offers. (USDA Oklahoma Production Cost Report)

International nitrogen conditions remain uncertain. Fertilizer-market analyst Josh Linville recently identified the resumption of vessel traffic through the Strait of Hormuz and the possibility of renewed Chinese urea exports as potentially bearish influences. Either development could improve global availability. However, fertilizer remains expensive relative to grain prices, and freight, energy or geopolitical disruptions could quickly change the cost calculation. (Josh Linville market commentary)

Oklahoma phosphate prices showed little immediate movement. DAP averaged $952.78, an increase of $2.22, while MAP held at $942.88. The local numbers appear quiet, but upstream phosphate conditions deserve attention. Linville has noted renewed strength in international phosphate values as limited sulfur availability and high production costs constrain output.

Sulfur matters because it is used to produce sulfuric acid, a critical input in manufacturing phosphoric acid and finished phosphate fertilizers such as DAP and MAP. Ammonia is another important production input. Consequently, higher sulfur or ammonia costs can support phosphate prices even when Oklahoma retail quotations have not yet responded. This is an upstream warning signal rather than a prediction that local prices must rise. (Josh Linville on phosphate and sulfur, World Bank fertilizer-market analysis)

Potash remained the quietest major nutrient in Oklahoma. The reported average increased only 75 cents to $491.55, with a range of $460 to $550. Global potash supply is geographically broader than the supply chain for several nitrogen and phosphate inputs. Expanded or recovering shipments from major producing regions may help moderate market pressure, although trade restrictions, transportation constraints and regional demand can still affect delivered costs.

International buying also remains important. India reported importing more than 3.2 million metric tons of urea and DAP during its first fiscal quarter and is pursuing longer-term overseas supply agreements. Large import programs can affect competition for available urea and phosphate cargoes, especially when export availability is already uncertain. (Times of India fertilizer-import report)

For Oklahoma producers, the current report offers a somewhat more favorable nitrogen signal, but not a uniform one. Wide quote ranges mean that comparison shopping may be as important as the regional average. Phosphate prices are locally stable, while sulfur availability and production costs remain meaningful external risks. Potash is comparatively steady.

Before acting on any quotation, confirm the nutrient analysis, cash-price basis, pickup or delivery terms, quote expiration and whether application or blending charges have been separated. UAN quotations should always be identified as either 28% or 32% before comparison.

Market Sources

Don’t Let the Heavy Rains Fool You – Scouting for Sorghum Aphids and Chinch Bugs in Sorghum

Ashleigh Faris, Cropping Systems Entomologist and IPM Coordinator

Depending on where you are in Oklahoma, you may have had anywhere between just under 0.5” or over 7.5” of rain in the last 7 days. If you were on the higher end, you may think that the rainfall has helped to prevent or wash off any insect pests building up in your summer crops. Unfortunately, this isn’t case; this morning sorghum aphids and chinch bugs were detected in research plots in northern Payne County. With rain out of the forecast and typical summer temperatures kicking in these insects, and other pests, can start to take off. Both pests have the potential to inflict severe economic damage if left unchecked, particularly during vulnerable crop stages or near recently harvested wheat. Scout now, and if needed, get together a plan to help you keep these economically damaging pests in check.

Sorghum Aphid, Melanaphis sorghi

Formerly known as the sugarcane aphid, the sorghum aphid can infest sorghum at any growth stage but causes the most severe damage from the boot to soft dough stages. The aphids form dense colonies on the undersides of leaves and produce heavy amounts of honeydew that can negatively affect plant growth and severely impede harvest.

Identification: Sorghum aphids are small aphids with light tan to pale yellow bodies, black feet, black antennae, and black cornicles (the two “tailpipes” on the back of the abdomen) (Figure 1).They almost exclusively reside on the underside of the leaves, often nestled against the midrib (Figure 2).

Figure 1. Sorghum aphids are light tan to yellow in color, have black legs, black antennae, and black cornicles (two tailpipe-like appendages at the tip of their abdomen. Photo credit: Oklahoma State University IPM.

Figure 2. Sorghum aphid nymphs and adults along the midrib of a sorghum leaf. Photo credit: Ashleigh M. Faris, Oklahoma State University Extension.

How to Scout Sorghum Aphids: Begin scouting once a week and increase to twice a week once the aphid is detected. There are two primary ways to scout:

  • Option A: The Glance-N-Go App (Recommended) Download the SCA Glance-N-Go App (available on Apple and Google Play). Enter your control cost (/bushel). Sample two leaves per plant until the app tells you whether to treat or not. It tracks the threshold automatically based on your specific economic variables.
  • Option B: The Pen-and-Paper Method
  • Walk 90 feet into the field. Inspect the top and bottom leaves of 3 consecutive plants, walk 5 rows over, and sample 3 more plants. (This is 1 “stop” = 6 plants).
  • Walk 30 feet in an inverted “U” shape to your next stop and repeat.
  • Complete 9 total stops (54 plants total).
  • Record the number of plants that have 50 or more aphids.

Sorghum Aphid Economic Threshold: If using the manual method (Option B), the threshold to treat is when 25% of the plants are infested with 50 to 125 aphids per leaf. Do not spray before the threshold is met, as premature spraying can disrupt the natural enemies (lady beetles, lacewings, parasitic wasps) that naturally keep sorghum aphid populations in check.

Sorghum Aphid Management: Sivanto 200 SL and Transform WD are recommended insecticides as both are soft on beneficials and provide good residual. Follow label rates and directions. Coverage is critical so apply with high water volume (5+ gallons/acre by air; 10+ gallons/acre by ground). Avoid pyrethroids. Using pyrethroids to control secondary pests (like headworms once at grain fill) even when aphid numbers are low will wipe out beneficial insects, frequently causing sorghum aphid populations to explode.

Chinch Bug, Blissus leucopterus

Newly seeded sorghum (think double-crop and late planted sorghum for this time of the year) is especially at risk for chinch bug damage. Chinch bugs frequently migrate into sorghum fields looking for a new food source once adjacent wheat fields mature and are harvested.

Identification: Adult chinch bugs are about 1/8 inch long, black body with white wings folded over their back. The wings have distinctive black, triangular markings (Figure 3). Chinch bug nymphs (immatures) are bright red/orange right after hatching (Figure 4). They gradually darken to brown/black as they mature. They do not have wings but do have a light-colored band across their abdomens.

Figure 3. Chinch bug nymphs photographed with a microscope. Nymphs are wingless, early nymphal stages are orange to red in color with a white band, later nymphal stages are darker in color. Photo credit: Jacie Guerrero and Nikolai Thielepape, Department of Entomology and Plant Pathology, Oklahoma State University Extension.

Figure 4. Chinch bug adults have black bodies and white wings that give a triangular shape to the chinch bug’s back when folded over. Photo credit: Ashleigh M. Faris, Oklahoma State University Extension.

How to Scout Chinch Bugs: Focus on border rows adjacent to harvested wheat or thin stands. Double-cropped sorghum planted directly into wheat stubble is at the highest risk, but we have detected chinch bugs in full-season planted sorghum throughout North Central Oklahoma. Chinch bugs pierce the plant and suck the sap, injecting toxins as they feed. Look for stunting, wilting, reddish discoloration on the stalk, or poor root development (Figure 5).Check the leaf blades, but importantly, look under the leaf collars/sheaths and down at the base of the plant near the soil line where the chinch bugs hide (Figure 6).

Figure 5. Chinch bug damage and chinch bug nymph on sorghum stalk. Photo credit: Ashleigh M. Faris, Oklahoma State University Extension.

Figure 6. Chinch bug nymphs and damage to sorghum stalks found by peeling back lower sheaths of damaged sorghum stalks.Photo credit: Ashleigh M. Faris, Oklahoma State University Extension.

Chinch Bug Economic Threshold: For sorghum seedlings (less than 6 inches), treat if 2 or more chinch bugs are found on 20% of the plants.Larger plants (over 1 foot), treat if you find 10 or more chinch bugs per plant.

Chinch Bug Management: The best defense is an insecticide seed treatment (e.g., Gaucho, Poncho, or Cruiser), which provides about two to three weeks of early control. Avoid planting sorghum directly adjacent to poor wheat stands if possible.If migrating populations breach the threshold, foliar pyrethroids are the primary option (e.g., lambda-cyhalothrin or zeta-cypermethrin). Because chinch bugs hide behind leaf sheaths and at the soil level, high water volume is essential to achieve proper penetration and coverage on small plants. Spot treatments on border rows are often enough if the migration is caught early and chinch bugs have not spread into the field.

Dr. Ashleigh Faris’s Cropping Systems Entomology IPM team is currently conducting chinch bug insecticide efficacy trials. Stay tuned for the results!

For detailed insecticide rates and grazing/post-harvest intervals, always consult the product’s label guidelines and read the label carefully before application.

Banding P for Acidic Soils: Its not the time to be paying for poor practice.

I am bringing this topic back to the surface now with the current outlook on phosphorus fertilizer. If you have heard its not only becoming more expensive but the supply is short and will likely stay short through summer into the fall, which wont help prices. So this year’s wheat crop, we need to be prepared to be smart with Phosphorus, and applying an extra 30lbs to band aid for soil acidity should not be in the cards. Look at it this way, if the phosphorus was at $0.66 a lb that $20 that could be spent on a ton of lime. That lime will last 3-5 years, while that P needs to be added every year. Not only that, but the lime will help root growth (better when we dry up), produce significantly more biomass, and make the phosphorus you’ve applied in the past available again for plant uptake. So make the plans now to soil sample as soon as this crop is off, you can get a soil test recommendation and plan for the lime trucks. This is also not the year to just apply phosphorus for the sake of applying. Soil tests are inexpensive relative to buying excess fertilizer.

Current quotes on 4.24.26 are at $0.54 + per lbs P2O5 with DAP at $830 a ton.

Quick Fertilizer Price Calculation:
Urea at $860 a ton means N is $0.93 a lbs.
DAP at $830 has $334 worth of $0.93 nitrogen and $495 of phosphorus at $0.54 a lb.

Banding P as a band-aid for soil acidity, not so cheap now.

Original Blog Posted in 2021

Whoi Cho, PhD student Ag Economics advised by Dr. Wade Brorsen
Raedan Sharry, PhD Student Soil Science advised by Dr. Brian Arnall
Brian Arnall, Precision Nutrient Management Extension.

In 2014 I wrote the blog Banding P as a Band-Aid for low-pH soils. Banding phosphate to alleviate soil acidity has been a long practiced approach in the southern Great Plains. The blog that follows is a summary of a recent publication that re-evaluated this practices economic viability.

Many Oklahoma wheat fields are impacted by soil acidity and the associated aluminum (Al) toxicity that comes with the low soil pH. The increased availability of the toxic AL3+ leads to reduced grain and forage yields by impacting the ability of the plant to reach important nutrients and moisture by inhibiting root growth. Aluminum can also tie up phosphorus in the soil, further intensifying the negative effects of soil acidity. More on the causes and implication of soil acidity can be found in factsheet PSS-2239 or here (https://extension.okstate.edu/fact-sheets/cause-and-effects-of-soil-acidity.html). The acidification of many of Oklahoma’s fields has left producers with important choices on how to best manage their fields to maximize profit.

Wheat Trial, Cimarron Valley Research Station

Two specific management strategies are widely utilized in Oklahoma to counter the negative impacts of soil acidification: Lime application and banding phosphorus (P) fertilizer with seed. While banding P with seed ties up Al allowing the crop to grow, this effect is only temporary, and application will be required every year. The effects of liming are longer lasting and corrects soil acidity instead of just relieving Al toxicity. Historically banding P has been a popular alternative to liming largely due to the much lower initial cost of application. However, as P fertilizers continue to increase in cost the choice between banding P and liming needed to be reconsidered.

A recent study by Cho et al.,2020 compared the profitability of liming versus banding P in a continuous wheat system considering the impacts that lime cost, wheat price and yield goal has on the comparison. This work compared the net present value (NPV) of lime and banded P.  The study considered yield goal level (40 and 60 bu/ac) as well as the price of P2O5 fertilizer and Ag Lime. The price of P2O5 used in this study was $0.43 lb-1 while lime price was dictated by distance from quarry, close to quarry being approximately $43 ton-1  and far being $81 ton-1. For all intents and purposes these lime values are equivalent to total lime cost including application. Wheat prices utilized in the study were $5.10 bu-1  and $7.91 bu-1. It is important to note that baseline yield level was not considered sustainable under banded P management in this analysis. This resulted in a decrease in yield of approximately 3.2 bu ac-1  per year. This is attributable to the expected continued decline in pH when banding P is the management technique of choice.

The analysis in this work showed that lime application is cost prohibitive in the short term (1 year) when compared with banding P regardless of lime cost, yield goal level, and wheat value (within the scope of this study). This same result can be seen over a two-year span when yield is at the lower level (40 bu ac-1). While in the short-term banding P was shown to be a viable alternative to liming, as producers are able to control ground longer lime application becomes the more appealing option, especially when producers can plan for more than 3 years of future production. In fact, under no set of circumstances did banding P provide greater economic return than liming regardless of crop value, yield, or liming cost when more than 3 years of production were considered and only under one scenario did banded P provide a higher NPV in a 3-year planning horizon.

While historically banding P was a profitable alternative to lime application for many wheat producers the situation has likely drastically changed. At the time of writing this blog (09/17/2021) Diammonium Phosphate (DAP) at the Two Rivers Cooperative was priced at $0.78 lb-1. of P2O5. This is a drastic increase in P cost over the last year or so since Cho et al. was published in 2020. With P fertilizer prices remaining high it will be important for producers to continue to consider the value of liming compared to banded P. This is particularly crucial for those producers who can make plans over a longer time frame, especially those more than 3 years.

Addendum: As fertilizer prices have continued to rise a quick analysis utilizing the $0.78 lb-1 of P2O5was completed to consider the higher P fertilizer cost. Under this analysis an estimated decrease in NPV of approximately $38 an acre for P banding occurred. When considering this change in NPV, lime application becomes the more profitable option for alleviation of soil acidity symptoms even in the short term (assuming lime price values are equivalent to the previous analysis). This underlines the fact that it is imperative to consider the impact on profitability of the liming vs. banding P decision in the current economic climate for agricultural inputs.

Link to the Open Access Peer Reviewed publication “Banding of phosphorus as an alternative to lime for wheat in acid soil” https://doi.org/10.1002/agg2.20071