// Twitter Cards // Prexisting Head The Biologist Is In: May 2017

Friday, May 26, 2017

Return of the Sunflower

A few years ago I made a cross between a sunflower (var. "Russian Mammoth") and a sunchoke (probably var. "Stampede"). My goal was to eventually get a plant that produced tubers like the sunchoke, but was super-charged with the giant growth of the sunflower. The two species have different chromosome counts, which complicates things a bit.

Me standing with arm held upright above my head, next to sunflower plant in bloom where flower is another couple feet above my hand.
2014
That first cross resulted in three F1 plants. I should have grown more, but it didn't work out that way. One of the plants grew to 10ft tall, with relatively large flowers, while the other two looked more or less like the sunchoke parent. I moved by the end of this season, but I was able to go back and recover root material from the plants. I then stored the roots in a fridge over the first winter and planted them at our new place when spring came around. Only the tubers produced from the largest plant survived this process.

Our current place has routine visitations by deer who seem to find sunflower leaves delectable. The first several shoots produced by the tubers were neatly trimmed to the ground. When I finally put together some protection for them, they succeeded in sending up one final shoot. That shoot topped out at about 2ft tall and produced a single small flower. This was a far-cry from the 10ft skyscraper the tuber had come from. I was so disappointed that I didn't even take any pictures of the little plant. I assumed the repeated early-season trimmings had dwarfed it and hoped it would do better the following year.

Small patch of tall upright sunflower plants inside a chicken wire cylinder, with two adult wild turkeys standing near.
2016
I was better prepared for 2016. I made a 7ft tall chicken-wire cylinder to place around the growing plant. This kept the plant protected for most of the season. The cylinder was knocked over a couple times (either by storms or aggressive deer), but this only exposed the lower leaves to the hungry mammals. The plant grew to about as tall as the cage and bloomed, still well short of the 10 ft of the first year. Though the plant branched much more than the first year, it did so much less than the sunchoke parent.

Our new yard has lots of animal traffic besides the deer. Turkeys are commonly seen in the neighborhood, though we don't often see them in our yard.



Three small sunflower plants starting to grow up from the soil, growing inside a wood and plastic mesh cage.
2017
I'm hoping the plant will do even better in 2017. Three clusters of new shoots have been coming up near where the plant was last year and I have a slightly wider protective cage put in place. The shoots are more widely spaced than they were last year. I'm hoping this means each individual stem will be larger/taller.

The plant produced abundant seeds in the first year, but has since then produced absolutely none. I'm pretty sure this means the plant inherited the self-incompatibility mechanism from its sunchoke mother. The first year there was plenty of pollen from its siblings, but there has been none the last couple of years.

There may be a few oilseed sunflowers around this year to contribute pollen, grown from scattered birdseed. My perennial sunflower is tetraploid, so any crosses to these diploids would produce highly sterile triploid offspring. These might be interesting to grow, but they wouldn't contribute to my overall goal.



For my breeding goals to move forward, I'll need to produce more tetraploid F1s by crossing sunchoke and another giant sunflower. I don't have any sunchoke planted right now, so I probably won't be able to get flowers even if I did find some tubers soon. There are several giant sunflower varieties I could use to help make more F1s, but I'll probably keep using "Russian Mammoth" to simplify the overall genetics of the future F2s.


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Sunday, May 21, 2017

Calculations in the Woods

Cluster of three wide elongated leaves growing from woodland soil.
A. tricoccum in local woods.
Wild foods are available most times of the year in Minnesota, but one species that attracts the most interest in spring is Allium tricoccum (known as "Ramps" or "Wild Leeks"). This slow growing plant is a close relative of onions/chives that are routinely available and has a similar flavor, though aficionados will argue it has a flavor all of its own. Ramps are distinct from the commonly available onion types in that it grows broad and flat leaves, in addition to their habit of growing in the moist shade of wooded areas.

Over-harvesting of A. tricoccum has led to the species disappearing from many areas where they used to be common. The plants grow very slowly, taking several years to grow from seed to a mature plant. The plants are also sensitive to physical disruption because their fragile roots grow close to the surface. If all the plants in an area are pulled out (or accidentally killed), then it could be decades before some seeds find their way back and start towards reestablishing a population.

At this time of year, the local foraging groups are filled with people posting pictures of their (often outrageous) harvests as well as people responding with ideas about sustainable practices of harvest. Advice to, "take no more than half" or, "only take 10%" are pretty common. There doesn't seem to be any standard number. I think some mathematical analysis can maybe help clarify what might be a good rule.



[1] Lets start with a very simple model. We have a population of plants and a whole bunch of people interested in harvesting them.

If everyone harvests 1/2 of the plants...

\(\lim \limits_{n\to\infty} \frac{1}{2}^n = 0\)

...or 1/4 of the plants (thus 3/4 remain after each person harvests)...

\(\lim \limits_{n\to\infty} \frac{3}{4}^n = 0\)

...then the population still dwindles towards extinction.

In this simplified model it doesn't matter what fraction each person takes, the population will always dwindle away towards extinction. This isn't realistic, since we didn't factor in the ability of the plants to reproduce.



[2] A slightly more complicated (and realistic) model factors in how fast the plant is able to replicate itself. Lets assume a fraction of of the adult plants are able to produce another adult plant each year. This is still a pretty big simplifying (and highly optimistic, since it is quite biologically wrong) assumption, but it's a starting point to work from. Lets start by defining some terms.

\(\begin{array}{cl}
R_y & \text{Population of Ramps in year 'y'.} \\
r_i & \text{Total increase rate per year.} \\
r_h & \text{Total harvest rate per year.} \\
\end{array}\)

The population of next year is calculated from the current year population and the total rate of increase.

\(R_y(1+r_i) = R_{y+1} \)

Then we add in a term for losses due to people harvesting a percentage of the plants.

\(R_y(1+r_i)(1-r_h) = R_{y+1} \)

If we want the population to remain stable over time...

\(R_y = R_{y+1} \)

\(R_y(1+r_i)(1-r_h) = R_{y+1} \)
\((1+r_i)(1-r_h) = \frac{R_{y+1}}{R_y} \)
\((1+r_i)(1-r_h) = 1 \)
\(1-r_h = \frac{1}{1+r_i} \)
\(r_h = 1-\frac{1}{1+r_i} \)

...and we assume a third of the plants produce a second plant each year,

\(r_i = \frac{1}{3}\)

\(r_h = 1-\frac{1}{1+\frac{1}{3}} \)
\(r_h = 1-\frac{1}{\frac{4}{3}} \)
\(r_h = 1-\frac{3}{4} \)
\(r_h = \frac{1}{4} \)

...then a cumulative total of 25% of the plants could be harvested each year. If any more were harvested, then the population would be declining like in our first model.

Remember, this is the cumulative total harvest rate. This could be just one person harvesting Ramps, or it could be several people harvesting separately through the season. If two or more people come across the patch and decide to harvest some, then they would have to harvest less than the 25% we calculated and still have the population remain stable. We have to define some new terms...

\(\begin{array}{cl}
n & \text{Number of people harvesting in a year.} \\
r_{hi} & \text{Harvest rate per individual per year.} \\
\end{array}\)

The relationship between the number of individuals harvesting and the cumulative total harvest rate is pretty simple.

\((1-r_{hi})^n = (1-r_h) \)

\(\begin{array}{c|c}
{n} & {r_{hi} = 1-\sqrt[n]{\frac{3}{4}}} \\
\hline \\
{1} & {r_{hi} = 1-\frac{3}{4}} = 0.25 \\
{2} & {r_{hi} = 1-\sqrt{\frac{3}{4}}} \approx 0.13397 \\
{3} & {r_{hi} = 1-\sqrt[3]{\frac{3}{4}}} \approx 0.09144 \\
{4} & {r_{hi} = 1-\sqrt[4]{\frac{3}{4}}} \approx 0.06940 \\
{5} & {r_{hi} = 1-\sqrt[5]{\frac{3}{4}}} \approx 0.05591 \\
{\vdots} & {\vdots} \\
{10} & {r_{hi} = 1-\sqrt[10]{\frac{3}{4}}} \approx 0.02836 \\
{\vdots} & {\vdots} \\
{100} & {r_{hi} = 1-\sqrt[100]{\frac{3}{4}}} \approx 0.00287 \\
\end{array}\)

The main lesson we can take from this second model is the more people that have access to a patch of Ramps, the smaller the fraction each person can harvest for the population to remain sustainable.


Figure illustrating how Ramp plants increase in size over years.
From link.

[3] Mathematically, a more ideal model would be somewhere between the discrete series function I used above and a set of continuous differential equations expressing the same concepts as well as accounting for stochasticity in the rates. Biologically, a more ideal model would include each life stage shown in the figure at right (encompassing sexual and vegetative reproduction) as well as realistic rates for each step.

It would be a relatively simple task to construct this sort of more detailed model, but properly determining all the rates would require extensive (presumably years-long) fieldwork. Thus, I'll leave this as an exercise for the reader.



Even though the models we discussed here are incomplete, they are informative. The big lesson is that the harvesting of Ramps from publicly accessible places is a nice example of a tragedy of the commons. There really isn't a harvesting percentage that can be used as a rule of thumb to tell people in the various forums.

If you have a large patch on your own land, then you can probably harvest a decent amount each year and the patch will never be at risk. Our hypothetical model [3] above might be able to tell us precisely how much of a population could be sustainably harvested, but without all the additional information it isn't worth worrying over. You can simply pay attention to how much you harvest and notice if the patch is dwindling or not from year to year. As it is your own patch, which you find valuable, you will adjust your personal harvest rate to allow the patch to prosper.

Is there anything we can encourage foragers to do, aside from simply advising them to leave the plants alone? If you harvest only one leaf from each mature plant (never the last leaf, or from small plants), without disturbing the bulb and roots, then the plants will survive and spread each year. If everyone followed this rule, large patches of Ramps could be maintained in woodlands close to or even within large cities. Convincing people to do this will be a difficult task.


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