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Can plants develop their own bacterial symbionts?

Our principle task as growers is to farm soil microbes. The larger and more vigorous a population of microbes we can grow in our soil profiles, the more nutritious and healthier our crops will become. Soil biology can supply all of a crops nutritional requirements when they are well managed and well supported.

A recent fascinating book that connects many dots in the historical research which have not come to mainstream attention is Herwig Pommeresche’s Humusphere. Translated from German, it is a treasure trove of references to European research on plant, soil, and microbial interactions which have been ignored in mainstream agronomy.

Here is an excerpt on the topic of remutation, how plants can develop bacterial cells from mitochondria and chloroplasts:

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Recognizing that endocytosis takes place in plants is an important piece of support for the microbiological model of the cycle of living material, which includes microorganisms.

But there is also another area of microbiological research that seems to have completely lost the attention of the modern scientific community. It essentially represents the second half of the endosymbiosis theory developed by Lynn Margulis and the adherents of the Gaia hypothesis. This is remutation, postulated by Hugo Schanderl. In 1947, Schanderl1 had already succeeded in breeding and regenerating remutating, as he called it – living, viable microorganisms out of certain cell components, such as mitochondria and chloroplasts, from plant tissue after it died. These experiments showed that any living cell is capable of releasing new life after it has died.

Schanderl described every mutation in agricultural soil bacteriology as follows in 19702: “When a plant is buried, the soil is enriched with bacteria not only because a vast number of existing soil bacteria decompose and break down the plant corpse, multiplying tremendously in the process, but also because the soil is enriched with bacteria from higher plants as they break themselves down. Certainly, bacteria present in the soil also find abundant nutrients during composting, which allows them to multiply. But, as can be experimentally demonstrated, no bacteria need to enter from the outside whatsoever for decomposition to take place and a breeding ground of bacteria to arise.”

He continues in the same article: “A significant proportion of the bacteria regenerated from plant cell organelles present in cow dung return to the planting soil. Unlike artificial fertilizer, this kind of fertilizer is filled with life and enriches the soil with bacterial life, increasing it’s fertility.”

After more than fifty years of being ignored and denied by the sciences, the remutation model is now being indirectly confirmed by cellular and molecular research. Autonomous DNA that is independent of the cell’s nucleus has been found in both mitochondria and chloroplasts, which has led to acknowledgement of the endosymbiosis theory. In evolutionary terms, this also describes how ancient single-celled microorganisms relinquished their independence in favor of organizing into larger cells and, in a manner of speaking, were relegated into subordinate cell components.

Schanderl’s remutation model implies that all decomposing organic substances, as well as all seeds that are starting the development of new life, are most likely capable of reshaping their own cell components into autonomous microorganisms such that living plants can employ their help – if they reabsorb them from their surroundings – to carry on their metabolic processes. The question also arises as to what extent living cells are even able to absorb an exclusive diet of inorganic, water-soluble salt ions. Page 43-45

1. Rudloff, C. F. & Schanderl, H. Befruchtungsbiologie der Obstgewächse und ihre Anwendung in der Praxis. (1945).

2. Schanderl, H. Über die Isolierung von Bakterien aus normalem Pflanzengewebe und ihre vermutliche Herkunft. (1951).

2020-03-16T14:10:13-05:00February 26th, 2020|Tags: , , , |

Relay Cropping

How much can you increase farm profitability and economic performance by growing two crops on the same soil at the same time?

Different plants use moisture and sunlight differently. It is common for our first thought to be about how plants compete with each other, but what if the opposite is actually the case? Can we develop cropping systems where different plants actually complement each other?

One of the producers who has experimented with this idea extensively on grain crops is Jason Mauck from Indiana. Jason is always testing and trying new ideas, but he has moved past the experimental stage with relay cropping and is observing results more growers should be familiar with. For relay cropping to be successful, design matters. Defining optimal crop spacing for best sunlight utilization and weed suppression is critical.

I enjoyed a very interesting conversation with Jason on the podcast, you can find the episode here.

Here are some photos of Jason’s farm:

2020-03-16T14:09:36-05:00February 25th, 2020|Tags: , , , , |

Crop storability and shelf life

In many cases, perhaps even in most cases, when we observe poor crop storability, the cause is inadequate calcium in the cell membranes. Elevated calcium levels within the stored crop cell membranes provides membrane strength, and prevents the cells from leaking sugars and nutrients, which sets the stage for decay and spoiling.

Chip potatoes without adequate calcium are a good illustration. When the cell membranes do not contain adequate calcium, the cells leak sugars which settle to whichever part of the potato is the lowest, following gravity. When these potatoes are sliced and fried, the accumulated sugars burn, producing a black edge on the chip. When you fix the calcium supply problem during the fruit cell division stage, storability problems are greatly reduced or eliminated.

2020-03-16T14:04:36-05:00February 21st, 2020|Tags: , |

Treat the patient, not the lab test

We all know friends or have heard the stories of people who are not well, and visit a doctor, only to be told “Sorry, there is nothing wrong with you.”

A quote from Arden Andersen I have really appreciated is “treat the patient, and not the lab test.”

We need to do the same for our crops. when a crop is susceptible to disease or insects, and the lab reports seem to be perfect, the lab reports are obviously not reflecting reality well.

In these cases, you treat the crop, and not the lab reports. This is particularly a problem when relying on soil analysis. To such a degree that I can safely say there is no correlation between nutrients reported on most soil reports and actual crop absorption.

Treat the crop, not the lab report.

2020-03-16T14:04:12-05:00February 19th, 2020|Tags: , , |

Cultural management determines weed populations

An edited excerpt from the podcast interview with Klaas Martens:

The first year after you abandon a field that’s been in real crops—let’s say it’s been a corn field—think about what weeds will grow. Obviously there’ll be lambs quarter, pigweed, foxtail, velvetleaf, the whole range. They’re mostly seeds of weeds that make huge numbers of seeds. You may end up with millions of seeds per square foot on the field. But what grows the second year? Now from our reductionist way of thinking, we would assume that because we just made that many seeds, we should have a lot bigger problem with those weeds. But the second year, none of those plants are growing. We have other weeds growing there. And if you take that forward several more years, you start seeing goldenrod, woody plants, brambles, sumac—you know, all the thorny stuff and all the multiflora rose. And if you take it forward a few more years, you’re going back to forest.

This is something Dr. Albrecht wrote about. If you let it go for five hundred years, at least where we are, it would be back to old-growth hardwood forest—mostly oak—which Dr. Albrecht called the climax crop. That’s the kind of a steady state that nature would put the land in. This is how the land was made to work: it creates this succession where all of the species and communities—each one—changed the soil. And the reason all of those weeds that set seed didn’t grow the second year was that the plants that made them changed the soil, and that the right conditions weren’t there for those plants to grow the next year. So other plants grew. And that group, again, changed the soil, so that another group grew.

Now thinking back to what Dr. Albrecht wrote—he talked about these successions as actually being more productive, more diverse, and more vibrant than the climax crops. So that the tallgrass prairie and the oak would have been very stable, very resistant to invasions and diseases. Those plants didn’t get sick—they could tolerate flood, storms, whatever, and remain in very healthy condition. Albrecht used to tell his students to see what they were looking at—to see how nature does its crop rotation.

I started looking at a pest that forced me to start asking why it was there and what exactly it was doing in the soil. Take this back to the succession that we observe. Obviously, these plants are changing the soil, and left to their own devices, they kind of work themselves out of a job and something else grows. I had to look at everything that I could observe. I had to try to see everything there was to see—look at it through new eyes—look at it through something that is working exactly as it was intended to.

And the problem was me. If I didn’t like something, I had to own it and say, “This is the result of what I’ve done up till now. Now, how do I change that?” More importantly, how do I learn from it? So I started to study what these different weeds and pests do in the soil. And that grew into a system of how to read what the soil is saying and how to understand the language that the fields are using to try to teach us.

There was a weed that at one point I thought was going to make it impossible for us to farm organically. I was really frustrated. It seemed like this velvetleaf grew taller than the corn, no matter how carefully I cultivated—a lot of it always survived. I had a one-acre spot in particular where I ended up mowing it. The corn wasn’t going to be a crop—there was nothing developing. After about three or four years, it wasn’t quite as bad, and the area where the crop didn’t amount to much was smaller. Fast forward another three or four years, and lo and behold—my velvetleaf was getting into mid-summer and then it was starting to turn yellow. The lower leaves were turning brown, the lowest leaves had fallen off, and before the end of the summer it was dead. And not only that, but instead of being taller than the corn it was only about three to four feet tall.

So I called a friend at Cornell who is a lead ecologist. And I was still thinking completely wrong. I told him I had found a disease that was going to make me a millionaire. My brilliant idea was that we could catch those spores and make a product out of them. And my friend came out and looked the situation over. He said, “I’m familiar with these leaves, and you can go ahead with your plan. But before it can be successful, you need to explain this to me: why is it that when that disease is in your neighbor’s field, on his velvetleaf, it doesn’t hurt his velvetleaf?” And sure enough, this disease existed right across the road, and it wasn’t hurting the velvetleaf.

Now I should have been able to figure this out quicker than I did. But I have to admit, I was quite dense, and I needed quite a few lessons and to notice quite a few things before I started putting two and two together. The next thing we noticed was a second disease in that velvetleaf that a student at Cornell identified as a virus. And in the meantime, because I was paying so much attention to thinking that this was going to be my new product, I noticed that those leaves were covered with white flecks. The first time I saw it, I crawled on the ground and I said, “Look at all these white flecks—my leaves are just being eaten alive.” And the agronomist said, “You better watch out—you’re not going to have a crop left with all these insects out here.” But then we looked at the corn and there aren’t any bugs on the corn. The corn was perfectly healthy and growing well; it was only the weeds that bugs on them.

So the insects were actually carrying the virus, and the fungus was blowing on and killing them. But it wasn’t this complex that was actually killing the plants—those were just opportunists. We had changed our system so that it had become a very unhealthy soil environment for the weeds. And because the weeds were unhealthy, all these pests were moving in and were attacking the weeds. It wasn’t really the pests that killed the weeds—the pests were just there because the weeds were so sick they weren’t fit to live. 

2020-04-20T11:11:56-05:00February 18th, 2020|Tags: , , , |

The Agronomy of the future

Will not be based on chemistry but on biophysics and biology.

In the future, soil analysis will not be looking only at mineral balance and nutrient levels, but at the levels of amino acids, peptides, enzymes, carbohydrates, and other compounds that plant roots can absorb from the microbial community.

Agronomists will look at soil paramagnetism, redox, and electrical conductivity to evaluate a soil’s capacity to deliver to crop yields and quality.

Crop scouts will measure plant leaf redox and electrical activity to determine disease and insect susceptibility, and determine what treatments to apply to prevent possible infections.

The emerging knowledge of this space that is becoming more widely known is extremely exciting.

I posted a few weeks ago about Olivier Husson’s work on redox. His work is much broader and deeper than can be described in the referenced papers. He has been kind enough to appear on the podcast and to share his work in-depth in a six-hour-long webinar that we made available as a free online course on the academy that you can find here.

This will be the agronomy of the future. Enjoy.

 

2020-05-05T08:58:03-05:00February 12th, 2020|Tags: , , , , , |

The only thing that can not be overdone

Is balance. 

In regenerative and sustainable ecosystems anything can be applied to excess. 

Water can be excessive. So can oxygen. Or CO2. Or calcium, seaweed, biochar, humic acid, rock powder, liquid fish, crab shell, limestone, gypsum, manure, fertilizer, pesticides, and anything else you might name. 

You may have heard someone make a comment to the effect of “You can never apply too much of…(insert product here). 

You can be certain someone somewhere has done exactly that and suffered the consequences. Because there are always consequences of excesses. They are usually significantly worse and more difficult to deal with than deficiencies. 

2020-03-16T14:02:55-05:00February 11th, 2020|Tags: , , , |

Don’t guess when you can measure

I attribute much of our rapid learning and our track record of success at Advancing Eco Agriculture to one foundational principle. Don’t guess about anything you can measure.

Growers learn about the successes we have had reducing disease and insect pressure with specific nutrient combinations, and immediately ask the question “How much of these minerals do I need to apply to get these results?”

If we were to answer this question blind, with no data, the only reasonable recommendation is to err on the high side and make sure our recommendations are generous, otherwise, they might not work. Quite likely, the grower ends up applying products beyond what is actually needed for success. For sound recommendations that are the least expensive, and the most effective, you need good data.

A second question that gets asked almost immediately, “How much does a test cost?”

When this question gets asked to determine whether we can ‘afford’ to conduct a test, it must surely rank as one of the most shortsighted agronomy questions.

A much better question is, “How much does it cost to apply a quart of product you don’t need on a block or field?”

The biggest limiting factor in many fields is the excesses of products growers apply. This costs twice, once when you pay for the product the crop didn’t need, and again in reduced yields and quality.

Bottom line, use plant sap analysis on a consistent basis through the entire plant growing period so you know intimately what is happening with nutritional integrity. To do any less is shortsighted, penny wise and pound foolish, as the saying goes.

Don’t guess. Test.

2020-03-16T14:02:29-05:00February 10th, 2020|Tags: |

Increasing Nitrogen use efficiency

Not all forms of nitrogen are created equal. A pound of nitrogen in one form will produce a completely different crop response than a pound of nitrogen in a different form. This is why organic growers often describe requiring only a fraction of the N requirement to produce a bushel of a given crop when compared with mainstream N applications.

The ultimate ideal is for plants to absorb amino acids and proteins directly from the soil microbial population and in the form of microbial metabolites. These forms of nitrogen contribute a lot of energy to plants, much more than. That represented by the N they contain. 

The second most efficient form of N for most crops to absorb is urea, or amine nitrogen. 

The third most efficient form of N for crops to absorb is ammonium.

The least efficient form of N for crops to absorb is nitrate. Plants must use a significant amount of their photosynthetic energy to convert nitrate to amino acids and proteins. When a corn crop absorbs 80% of it’s N requirement, it requires 16% of it’s total photosynthetic energy just for nitrate conversion (Marschner) A plant also requires three times more water to convert nitrate to amino acids as compared to ammonium. These are just the beginning items on a long list of reasons why you want plants to absorb only minimal amounts of nitrate, and obtain the majority of their nitrogen from other forms, preferably directly from the microbial population.

Ultimately the goal is to develop soil microbial populations that can deliver 100% of a crops nitrogen requirement every year. This is a very realistic and achievable goal. Only if you stop killing them with synthetic N applications in the first place, of course.

While on the pathway to reducing N applications, the first step is to make certain that any applied N is rapidly consumed by the soil bacterial population, and converted to microbial proteins and amino acids. These microbial forms of N are not leachable and are available to plants even when there is less water in the soil profile.

To convert applied N, either liquid 32-0-0, liquid 28-0-0, or liquid urea 21-0-0 (the most efficient of the liquid N sources) we simply need to provide the food sources and stimulants for biology to rapidly consume the applied nitrogen. 

Here is a recipe we use on a lot of acres, very effectively:

1. 3% of the total solution (either weight/weight or volume/volume) should be humic acid. We use HumaCarb.

2. Add ATS, ammonium thiosulfate 12-0-0-26S to produce a 10:1 nitrogen to sulfur ratio in the final solution.

3. Add a carbohydrate source, we use Rejuvenate at 3% of the total solution

4. Add molybdenum, needed for the nitrate reductase enzyme. We use Rebound Molybdenum at a pint or a quart per acre.

It isn’t realistic to make universal recommendations, given the wide variability in soils, crops, and management practices, but we commonly observe that growers reduce nitrogen application rates by 30%-40% or more in the first year and produce the same or higher yields as compared with controls when using this combination. Use sap analysis to diagnose precisely whether the crop has adequate N, we don’t live in a world where we have to guess and be uneasy. Many times, we use this approach, and growers are amazed that their crops constantly show they have abundant, even surplus nitrogen. This is a start down the path to producing all your own N in the soil profile. We walk around in 78% N, the only reason we buy any is because we have destroyed the capacity of our soils to produce it’s own. 

The same solution can be used for dry N applications if you can get it applied to the dry product. 

Nitrogen management is a big topic, look for more thoughts on this in the future. 

2020-03-16T14:02:07-05:00February 8th, 2020|Tags: , , , |

Boron salts for weed control and as a desiccant

Recently I have received many questions about alternative forms of weed control, and if nutrients might be a possible means of control, specifically boron. 

This is not an area where I have personal experience, and I am not personally familiar with how to manage boron applications to produce this effect. Test for yourself, with eyes wide open, and please let me know. I would love to learn more.

From what I have been able to read, it seems that boric acid and sodium borate can be used as an effective means of killing weeds. While the information I have been able to find is not particularly clear, it seems effective control is solution concentration dependent rather than quantity per area dependent. 

Recommended rates I have been able to uncover are for either three ounces of boric acid or four ounces of sodium borate per gallon of water. Typically, boric acid contains 17% boron, and sodium borate usually contains 10% boron, so these recommended application rates don’t equal the same quantity of applied boron on a per-acre basis. 

We need to be aware of the quantity of boron being applied on a per-acre basis, and the boron sensitivity of the crops we are growing. In our agronomic recommendations, based on soil analysis and plant sap analysis we often recommend between one and three pounds of actual boron per acre per year. The rate varies with the crop, soil levels of boron, and annual rainfall. In low organic matter soils, ten inches of rainfall can leach about one-half pound of boron per acre. Thus, if you get forty inches of rainfall per year, you need to add two pounds of boron annually just to replace what the rainfall removed. As organic matter increases, and soils anion exchange capacity increases, less boron is leached through the soil profile. 

If we follow the recommended concentration rates, and apply 20 gallons of solution per acre, with each gallon containing four ounces of 10% boron, this application will give us eight ounces of actual boron per acre. This rate is well within the range of what is routinely applied as a soil amendment or nutrition source of boron on many soils and crops. This type of application would also supply much more uniform soil distribution than a broadcast application of pellets with some distance between the pellets as occurs with such small application rates. 

Obviously, this application is non-selective, and should not be applied directly on crop plants. 

With the exception of a very few boron sensitive crops, I do not expect that boron toxicity to the crop is nearly the danger that it is sometimes made out to be. Boron toxicity in most plants is simply a calcium deficiency. In cases where excessive boron was applied in the past, a foliar application of calcium will snap a crop out of boron toxicity in a matter of days, even when tissue analysis levels are ten times higher than desired values. 

What these experiences suggest to me, is that using boron salts as an herbicide is likely to produce the biggest effect on calcium deficient soils and that soils with adequate or generous calcium may require stronger application rates to produce the same effect. Of course, crop sensitivity to the boron application will also depend on soil calcium levels. 

It is important to mention that using boron as a form of weed control is specifically prohibited under USDA NOP rules for organically certified producers. It can be used as a nutrient source with restrictions, but not as an herbicide.

If you would like more information on the toxicity of boron in the environment, the National Pesticide Information Center link provides very thorough and useful information.

National Pesticide Information Center

EPA Boric acid restrictions on boron in crops (based on used for insect control in grain storage)

 

2020-03-16T14:00:49-05:00February 7th, 2020|Tags: , , |
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