The Fall of 2026 soil sampling season had a bit of a delayed start but has quickly shifted into high gear. When harvest is efficient, fall soil sampling is efficient, resulting in sample volumes that can challenge our laboratory’s daily maximum capacity. While our goal is to keep a consistent turn-time for all samples, it is not always possible if challenges arise in the process. Following these tips can help reduce delays in the delivery of your results.
Taking a few extra minutes to securely package your samples in an organized manner will help ensure the quickest possible return of your data. If you have any questions regarding shipping supplies, or sample packaging, please contact your ALGL representative.
While most soil test results are reported by the lab in parts per million (ppm), a notable number of soil test reports are still expressed in pounds per acre (lbs/ac). Why the two units?
First, we need to start with some fundamentals of soil testing. At the lab, we do not analyze the soil itself; we analyze the nutrient concentrations in an extracting chemical. Specifically, we measure the concentration of nutrients dissolved from the soil sample into the extracting solution.
The lab instrumentation directly measures nutrient concentrations or compares sample results to a calibration set of standards, with results expressed in either ppm or mg/kg. These two units are equivalent, so a soil sample reported in ppm reflects the direct result of the analysis.
So, where did lbs/ac come from?
In the early years of soil testing, there was a belief that soil test results would directly reflect the pounds of nutrients available to plants, much like the amount applied as an amendment. As interpretations of soil test results were developed, it became apparent that this was not the case. Unfortunately, the convention had already been widely adopted. Because pounds per acre is the unit commonly used for fertilizer applications, this incorrect convention remains a common misunderstanding more than a century later.
Converting between ppm and lbs/ac is also a controversial topic. The more common conversion is 1 ppm = 2 lbs/ac. This comes from the “rule of thumb” that an acre-furrow slice of soil (the volume of soil disturbed when moldboard plowing to a depth of 6 2/3 inches) weighs 2 million pounds. Give or take 30%.
That last statement is both a key fact and a bit of sarcasm. The actual weight of an acre-furrow slice can vary by 30% or more, depending on soil characteristics. Two pounds of nutrient in 2 million pounds of soil is the same ratio as one pound of nutrient in 1 million pounds of soil, or 1 ppm.
For many conversations, the story ends here. For others, it continues.
What if the soil sample was not collected from 0 to 6 2/3 inches deep? In that case, the soil represented by the sample does not weigh 2 million pounds, and thus the conversion should be adjusted for the actual sampling depth.
This brings two assumptions into play, and you know the saying about assumptions. Adjusting the conversion between ppm and lbs/ac assumes that the soil mass at a depth of 6 2/3 inches is 2 million pounds. However, differences in the density of various soil types and structures mean we know this assumption is not always true.
The conversion also assumes that nutrient concentrations are uniform throughout the top 10–12 inches of soil. We know this is not true either, due to nutrient stratification.
Rather than making a series of calculations based on assumptions to convert ppm to lbs/ac, perhaps it would be easier to simply work with the data in its original ppm format. This would avoid the debate, the calculated conversions, and the potential for misinterpreting soil test data.
It seems like a lot of work just to introduce additional variability into the resulting data.
There are many types of extraction methods, formulations and practices a laboratory may use to provide the best data possible. This, of course, depends on the customer’s needs and goals. Often, the industry standards will remain steady to provide consistent data sets of soil data. This is important in monitoring trends, patterns and completing long-term goals.
Occasionally, a new concept will emerge. This is also important. A great example is when Mehlich-3 came to light in the early 1980’s. The Mehlich-3 extraction allows laboratories to extract multiple nutrients with one step. This extraction not only provides more consistent results, but it benefits the consumer with more affordable testing.
To use one method of extraction as an example would be a Bray-1 phosphorus test. This was the standard since the 1940s and offered decades of research studies for calibrated recommendations. In fact, it is set at such a standard that many prefer Mehlich-3 phosphorus results to be calculated back to Bray-1 to interpret the results.
When a new method is being utilized, like the Bray-1 and Mehlich-3 scenario, it is especially important to not compare analysis results of one method to the other.
This will lead to much confusion when comparing different data sets. When comparing past analyses to the new current method of extraction, they must be calculated. Each laboratory may have their own set of calculations to switch Mehlich-3 back to a Bray-1. This is why it is very important to utilize a reputable laboratory for long-term data analysis. There are several different extraction and testing methods emerging in the marketplace. This is especially difficult to compare to past results that use different extraction methods.
To use a new extraction method for a soil sample it is necessary to use the originator’s interpretations and recommendations. A phosphorus nutrient analysis extracted by water, for example, cannot be compared to a phosphorus level extracted by Mehlich-3 for trending data purposes or finding patterns. It would be as the saying goes, “comparing apples to oranges”. This would be a fresh slate of information to be used with the originator’s set of recommendations.
Stronger acid, or extractant, can be used to show higher nutrient levels, but without calibrated recommendations that suit your region, they cannot be used with confidence. What is important is to use the method that is best for your soil, that will provide what is most plant available and has calibrated data to give agronomic recommendations.
(…another agronomy rant from another agronomist at ALGL, David Henry. Once again, this is not directed at any particular entity or person, just a response to an often-misunderstood topic in the industry.)
Asking which phosphorus extraction (Bray-1 or Mehlich-3) is “better” is like asking if inches or centimeters are better at measuring length. You are measuring the same thing, just using a different scale.
In fact, most people who work routinely work with soil test data, likely have never seen an actual Bray-1 value. This is because the Bray-1 and M3 phosphorus extractions are very well correlated to each other. This means that given either value, you can calculate what the other is with a high degree of certainty. As a result of this, most commercial soil labs adopted the M3 extraction as their routine extraction method 2 or 3 decades ago but can still report a Bray-1 value.
Why is this? You might ask. Well, the M3 extraction is also very good at extracting other nutrients. Like nearly all of them that we are interested in when growing plants. From a laboratory efficiency standpoint, M3 is far superior to Bray-1. For the end user, it really does not matter. As long as you know which value you are working with and are using the appropriate interpretations and equations, one extraction will not give you better crop production results over the other.
Most manure sources can be an incredible addition to row crop farming operations. If it is handled, and applied, in an environmentally conscious manner it will provide long lasting results for multiple growing seasons. When utilizing manure is an option, there are several factors that should be taken into consideration. The species from where it came from, feed, storage, bedding type, and application methods.
The type of manure, from which species it comes from, will have drastically different manure analysis results. To use one example, below is a table from A&L Great Lakes Laboratories depicting the differences between species with both solid and liquid forms of manure and their inorganic to organic comparisons.

Ammonium content, an inorganic form of nitrogen, will acidify the soil as it undergoes nitrification converting to nitrate. On the other hand, there are several manure sources that will increase the soil pH. This is credited to the amount of carbonates and bicarbonates are in the manure.
The type of feed and bedding can have a large impact on the alkalinity of the manure. Some manure from poultry sources, that include calcium carbonate in the feed and eggshells, can increase soil pH for the next several years after application. Bedding can also be a high source of liming material. The sand, in sand bedded dairies, can be sourced from high alkaline parent materials.
It is important to analyze the manure and know the source and type of manure before application. The ammonium content and calcium carbonate equivalent (CCE) of the manure can be determined by lab analysis. Some soil types, topography and soil nutrient levels may impair the use of manure as a fertilizer source.
It is common for nutrient issues that went unnoticed during the growing season to become apparent as harvest approaches. With the growing season coming to an end, what can be done to diagnose potential nutrient issues as corn and soybean harvest approach? The options become increasingly limited as the plant gets closer to harvest maturity.
While tissue tests are effective for identifying nutrient deficiencies during the growing season, the remobilization of nutrients within the plant, combined with the loss of dry matter due to tissue senescence, can artificially alter nutrient concentrations in the plant sample. This can occur after R3/R4 in soybeans or R3 in corn. Beyond these points, plant senescence will lead to nutrients leaving the plant and alterations in biological processes that will not be reflected in reference data. Dead and/or yellowing tissue will not produce valid tissue test results. Corn that maintains a healthy ear leaf is more likely to produce meaningful tissue test results.
Near these growth stages, “good” vs. “bad,” or perhaps more accurately “bad” vs. “worse,” tissue test comparisons can yield insight into potential deficiencies. These results can also be highly subjective and should be carefully considered. A high tissue test level at this time is not necessarily a good thing. Rather, it is often the result of an associated deficiency in which that nutrient was not efficiently used and remains in excess.
Soil tests can often be more useful at this point in the growing season. Just before harvest often reflects the lowest point of nutrient availability in the soil. Don’t forget to test for micronutrients as well. Sample the negatively impacted area directly, as it may be small enough that it is not reflected in routine soil testing. Again, comparing a “good” vs. “bad” soil test is a good practice in this situation. This may provide additional information to further define the issue, especially when more than one nutrient interaction is involved.
In corn, a stalk nitrate test can provide additional insight into the conditions leading up to the visual symptoms. Late-season issues are often identified by changes in yield parameters, such as the number or size of ears, and nitrogen often plays a role. If the “bad” corn has an excessive stalk nitrate level, the issue likely arose late in the season and limited the plant’s ability to achieve a higher yield goal. If the “bad” corn has a very low stalk nitrate level, either the nitrogen program was limiting, nitrate loss was excessive, or the root system was not developed enough to access nitrogen. Additional data can be evaluated, or additional observations can be made, to confirm or rule out these possibilities.
Digging roots and evaluating stalks should be done before harvest. Limited root development can also be associated with low phosphorus levels. Evidence of a limited root system can provide insight into late-season tissue samples or interactions with limited soil fertility.
Notice that may, may be, should, and could are used frequently in this article. Late-season diagnostic laboratory analysis can be used to help define the cause of an issue; however, a critical evaluation of the data is required. Seasonal environmental conditions and crop physiology can significantly impact laboratory results, and those effects are not predictable.
We have recently seen an increase in homeowners and tree care services interested in testing soil and leaf tissue for better nutrient management for ornamental landscape trees. While these services can certainly improve performance and appearance, fertility management for trees and other deep-rooted plants can be challenging. Please keep in mind that these comments are not meant to replace the advice of a reputable arborist. When establishing new plantings, it is best to select species that are well suited to the climate and soil types in your area.
The proper method for collecting soil samples for trees is not well defined. Some may argue that the sample should be collected to the rooting depth of the tree. Since most trees can root 10 feet deep or more, this is not very practical. A more appropriate method would be to collect the samples to a depth that can be impacted by a fertilizer application. This would be a 6-12-inch-deep sample in most situations. Deeper samples may be helpful to better understand the pH further down in the root zone, but incorporating fertilizer that deep may not be possible. Keep in mind that a tree’s root system has access to much more soil than a typical soil sample represents. So, ideal fertility levels are relatively low. Trees in a well-maintained landscape or lawn setting often do not need additional fertilizer than what is already being supplied around them.
Leaf tissue testing can be an excellent tool to help determine what nutrients may be lacking in a tree. Since soil testing has limitations, the leaf tissue can help fill in the holes. Deciduous landscape trees in the Midwest often struggle with micronutrient availability due to the alkaline subsoils that sit on top of limestone bedrock. Iron and manganese deficiencies are very common. The symptoms of micronutrient deficiency are generally chlorosis of the newer leaves. A challenge in diagnosing a nutrient deficiency visually is that damage from pests and pathogens can look very similar. One way to potentially differentiate a nutrient deficiency from disease is to look for a pattern. A nutrient deficiency is more likely to follow a distinct pattern from bottom to top or top to bottom and on the individual leaves themselves from the outer margins working in or the middle working out. Disease damage tends to be more random.
Unfortunately, one situation where soil and leaf testing does not help much is when an old, well-established tree begins to show decline. Once this has begun, fertilizer is not likely to correct the issue because it is often the result of changes in the surrounding environment.
Fall soil sampling season is soon approaching. To ensure as few disruptions as possible once the sampling begins, here are a few points to address now.
Your ALGL agronomist is available to discuss your soil sampling protocols and help find ways to streamline your fall soil sampling.
Editorial by ALGL Agronomist Jamie Bultemeier
Time has faded the memories of Paul Harvey’s radio program, but there was tremendous wisdom within it. The key to his storytelling style was holding back one key fact or element of the story until the end of the program. Paul Harvey revealed the missing link at the very end of the program, making the story or message complete. We don’t always get that missing link in agriculture, and often the audience does not want to find it. They prefer the story as it is.
Each summer, I am fortunate enough to attend and participate in a variety of events as they pertain to soil and crop fertility. Over the past few years, I have found more “data” and fewer statistics and research fundamentals. This is not an article on statistics or research design. The greater concern is the misleading messages supported by this “data.”
I get it. Stats are boring, and taking time to explain the research study behind the data is a buzzkill to a fast-paced presentation. But sometimes we need to slow the pace and fully explain the results so that the “data” is not misleading.
One such example from this summer was a farmer presenting at a field day and sharing the impacts of soil conservation on their farm. One of their key messages was that through no-till, cover crops, and improved management, they had improved soil structure and increased organic matter. The farmer had a data table showing the farm’s average soil organic matter over more than a decade, and it was increasing. This same data table also displayed the averages of several other soil test parameters, and comments were made to illustrate the shifting of soil test nitrogen and phosphorus from inorganic forms to organic forms.
The producer then went on to their next key point, noting that this new farming style afforded them the ability to reduce nitrogen rates by 60% and eliminate phosphorus fertilizer applications. The fertilizer application rates had been decreased in small increments over the past 10–15 years while maintaining yield. The crowd of fellow farmers was buzzing with excitement about the idea of massive reductions in fertilizer application rates. This would be a significant reduction in production costs at a time of low commodity prices. The presenter attributed these fertilizer reductions to improvements in soil health.
The unasked question was, “How is this possible?”
Their soil test phosphorus levels were several times higher than the levels requiring phosphorus fertilizer, and 6–8% Illinois soil did not require 250 units of N to produce an average corn yield to begin with. The farm had historically been over-fertilized, and proper soil testing had now resulted in appropriate fertilizer application rates.
Now you know the rest of the story.
But this story doesn’t end here…
The fertilizer reductions achieved had nothing to do with increased soil health. The nutrient reductions could have been achieved decades ago with sound nutrient management. Because of elevated soil fertility, there was little to no risk in making these cuts.
Most of the farmers in the room did not have the same high phosphorus levels and/or high organic matter levels, nor a critical understanding of soil fertility, yet they eagerly wanted to believe that increased soil health would allow them to make these same nutrient application reductions while maintaining, or even increasing yield.
It may. But what if it doesn’t?
When discussing soil acidity, the conversation starts with the soil pH. pH is the measurement of hydrogen (H+) in the soil. It will determine whether the acidity in the soil needs to be adjusted. Next is the buffer pH. This is not recognized by all recommendation sources, but it is a very useful tool when preventing incorrect application rates. Next is the source of lime, depending on the soil analysis, to use calcitic or dolomitic limestone. The calcium carbonate equivalent (CCE) will determine when the product will reach its full potential by neutralizing the given soil acidity and plays a large role in application timing. The last piece of the liming puzzle, although there are many logistical steps not mentioned, is incorporation.
Many recommendation sources include incorporation rates for different tillage, or no-till, scenarios. Why does this matter? When correcting soil pH, it is not just the pH and buffer pH that determines the application rate but there is a volume of soil that makes a large portion of the equation. To interpret a soil analysis, the soil pH will determine is the soil needs lime. The lower the pH number, the more hydrogen or more acidic the soil is. A 5.5 pH is ten times more acidic than a 6.5. The buffer pH will determine how much to apply. The buffer pH is measuring the reserve acidity. A strong buffered soil will have a lower buffer pH analysis. A weakly buffered soil will have a higher number.
A physical lime prill, granule or particle will only neutralize a small amount of its surroundings. If the product is applied to the surface of soil, such as when practicing no-till, it will take an extended period of time for the product to reach the root zone of the intended crop. According to The Ohio State University, lime will only move into the soil profile at a rate of approximately 1” per year. This will be highly dependent on soil type and CEC. Before converting to a no-till system, it is important to start with a manageable soil pH. Or, if the soil is erodible, utilize options such as subsurface applications.
When surface applying lime, most sources will recommend a half, or reduced, rate. This is to prevent the surface soil from becoming overly alkaline. When a seed is planted it starts at the surface level, then it taps into deeper resources as it matures. This can create nutrient availability issues early in the plant’s life, but can outgrow them as a deeper, more robust root system develops. Even though a 6-8” soil core may result in a 6.5 pH, the top few inches could be 8 and the bottom part of the core a 5 pH in a no-till scenario. Tillage, although not applicable everywhere, creates uniformity to the tillage depth. This depends on tillage type, implement characteristics, disturbance level and soil type.
Always follow calibrated recommendation resources based on lab analysis. Lime applications are not an immediate fix and can take even longer depending on application practices, soil type and lime sources.
Johnson, J. W., & Myers, D. (2015). Most asked agronomic questions: Bulletin 760, Chapter 1—Liming and pH. The Ohio State University Extension.