The 96-well microbiology plate and its plant analog?
Sunday, December 27, 2009
The 96-well microbiology plate and its plant analog?
Thursday, December 17, 2009
Murphy, B. P. and D. Bowman. 2009. The carbon and nitrogen isotope composition of Australian grasses in relation to climate. Functional Ecology 23:1040-1049.
Monday, December 14, 2009
My goal here is to codify ways papers are rejected. For authors, it should help to improve a paper, if not rebut criticisms, by understanding the categories by which reviewers and editors reject papers. For reviewers, it should help sharpen the key points to make to authors so that they can improve their work.
The examples I give are all from papers that I have had rejected, but subsequently were accepted later. Reading through them, I sometimes wonder how I ever got anything published.
1) Poor fit for a journal. If these were relationship break-up lines, this is the equivalent of “It’s not you, it’s me.” There rarely is a objective analysis of “fit”, so it’s an easy catch-all rejection. Higher profile journals are more likely to use this reason at the editorial stage. Here are two examples:
a. Science: “Although your analysis is interesting, we feel that the scope and focus of your paper make it more appropriate for a more specialized journal.”
b. Nature: “We do not doubt the technical quality of your work or its interest to others working in this and related areas of research. However, we are not persuaded that your findings represent a sufficiently outstanding scientific advance to justify publication in Nature.”
a. Example: “the authors of this manuscript have done an extremely bad job with respect to consideration of relevant literature for their review. It is specifically the duty of a research review to consider the whole range of literature in a balanced manner”. [this comment was followed by a list of 8 papers that all had one author in common].
b. “By completing a more thorough literature review and bringing concepts and information from those reports into this one, the authors could greatly strengthen this manuscript.”
a. Example: “THE FUNDAMENT [sic] PREMISE OF THIS MANUSCRIPT IS SERIOUSLY FLAWED.” Original CAPS.
b. “Their analysis is based on the supposition that changes in these drivers at any one location will have the same effects on these response variables as that which is currently seen across space in their data set. This may or not be true.”
a. The authors “used a highly controlled, if not overly-artificial experimental system to address several key theoretical questions in plant ecology”
b. “Unfortunately, this ms suffers in my opinion from too many methodological flaws to really increase our understanding”
c. “the authors seem to pick and choose certain variables and ignore others that have been demonstrated to have a major influence on plant isotope composition”
d. “The approach that they followed seems to be a sort of wild west expedition where they sampled as much as they could seemingly randomly”
a. “I was also very concerned about the conspicuous lack of critical data: Why are so many method details and results not presented?”
b. “Although the manuscript has the potential to show some interesting trends, it does not currently deliver on its objectives.”
c. “the introduction states that the aim is to determine how landscapes interact with herbivory to determine N availability, yet this does not appear to be addressed in the rest of the manuscript.”
d. “it is not entirely clear to me what they want to show with these data.”
e. “The manuscript does not live up to our expectations”
a. “The results are in complete accord with a book chapter I wrote back in 1986.” [23 years before the paper. No citation given.]
b. “In this sense, the data are confirmatory.”
c. “The questions…were certainly worth exploring, but the results seem pretty clear, pretty simple, and not too surprising.”
d. “While I do appreciate the scale of your study, this doesn’t seem like a particularly novel finding”
e. “While this was a detailed fertilization experiment with many collected data, it is not clear what it contributes to our understanding of relationships between nutrient limitation and N:P ratios for a number of reasons”
a. “I find the discussion unnecessarily speculative in places.”
a. “I don't think the analysis as currently executed is interesting enough to warrant a treatment of this length”
b. “I was taken aback by the number of co-authors (23). The reported study did not exactly crack the human genome, so the laundry-list approach towards authorship may be inappropriate for this manuscript.” [I guess length to content also applies to authorship.]
a. “occasionally one encounters run-on or circular sentences, which could use rewording.”
b. “In general, the writing is wordy, causing the reader to slog through unnecessary text, and in many places, the wording obfuscates the authors intended meaning.”
Sunday, December 13, 2009
Monday, November 30, 2009
Forage crude protein concentrations (%N * 6.25) for male and female bison over the season from Konza.
Bison are the largest native grazers in North America left. Their history is interesting, having almost gone extinct with the Pleistocene megafauna, and not having evolved into their modern form until about six to eight thousand years ago. Most of the attention on the evolution of the animals has been regarding changes in their morphology. Most of the attention to the modern animals has been their genetics and the introgression of cattle genes—finding “pure” bison. Most of the interest in their modern ecology has been on their role as a keystone in ecosystems.
Almost entirely missing from the study of modern bison has been their nutrition. There has been some work on diet—do they eat forbs or grasses; cool- or warm-season grasses. Yet, animals that ranged throughout North America and never had access to grasses like the progenitors of modern cattle would have found in northern Europe would likely face strong nutritional stress throughout much of the year. The adaptations of bison to low forage quality, no less the basic patterns of the availability of energy and protein to bison have gone all but unasked.
At Konza, Gene Towne has been collecting fecal material throughout 2009. Every two weeks, he has collected fresh pies from both males and females. Then we send the samples off to Texas A&M’s GANLab to see what the crude protein (nitrogen) and digestible organic matter (energy) was of the grass that they were eating.
If you look at the patterns from 2009, a few fascinating patterns stand out. First, the minimum protein requirements for mass gain for cattle are about 6% crude protein. Bison at Konza have about 100 day window to gain mass during the growing season. After that, there is little protein available beyond what is required for maintenance.
Second, the differences between males and females has never been observed before. Males tend to form “bachelor” herds and do their own thing until the rut—roughly August. After that, they often go off on their own again. The CP patterns show that the males are not selecting as high a quality forage early in the season, but the peak is broader. During the rut, quality is about the same as females. Afterwards, the males are selecting lower quality forage than the females. Why? Why wouldn’t the males feed in the same places on the higher forage quality. A mystery right now.
Lastly, by mid-October, CP had dropped to roughly 4.5%. Not much good green out there for anyone. Gene’s found that the bison lose about 10% of their weight during the winter, which can be up to 200 pounds for the large males. We’re beginning to see why.
Hopefully, data like this will continue to be taken at Konza for a couple of years. It’ll be fascinating to see the differences between wet and dry years on forage quality. With any luck, we can start similar measurements at a number of other TNC sites with bison to being broader comparisons.
Wednesday, November 25, 2009
If you read the latest IPCC report, there is little text on the potential effects of climate change on cattle performance. Considering there are more than 1 billion head of cattle in the world with probably about a trillion dollars in value, small changes in their performance would have large economic effects.
Here’s what the IPCC had to say about climate change and forage quality:
New Knowledge: Changes in forage quality and grazing behaviour are confirmed. Animal requirements for crude proteins from pasture range from 7 to 8% of ingested dry matter for animals at maintenance up to 24 % for the highest-producing dairy cows. In conditions of very low N status, possible reductions in crude proteins under elevated CO2 may put a system into a sub-maintenance level for animal performance (Milchunas et al., 2005). An increase in the legume content of swards may nevertheless compensate for the decline in protein content of the non-fixing plant species (Allard et al., 2003; Picon-Cochard et al., 2004). The decline under elevated CO2 (Polley et al., 2003) of C4 grasses, which are a less nutritious food resource than C3 (Ehleringer et al., 2002), may also compensate for the reduced protein content under elevated CO2. Yet the opposite is expected under associated temperature increases (see Section 188.8.131.52). Large areas of upland Britain are already colonised by relatively unpalatable plant species such as bracken, matt grass and tor grass. At elevated CO2 further changes may be expected in the dominance of these species, which could have detrimental effects on the nutritional value of extensive grasslands to grazing animals (Defra, 2000).
In all, there really wasn’t all that much that we knew about the topic.
I won’t go into detail here, but here's the latest press release from Kansas State on the Global Change Biology paper that I mentioned in an earlier post on the Wisconsin Paradox. I think that the next IPCC report should be able to say a little bit more…
K-STATE RESEARCHERS STUDYING LINK BETWEEN CLIMATE CHANGE AND CATTLE NUTRITIONAL STRESS
MANHATTAN -- Kansas State University's Joseph Craine, research assistant professor in the Division of Biology, and KC Olson, associate professor in animal sciences and industry, have teamed up with some other scientists from across the United States to look into the possible effects of climate change on cattle nutrition.
Comparing grasslands and pastureland in different regions in the U.S., the study, published in Global Change Biology, discusses data from more than 21,000 different fecal samples collected during a 14-year period and analyzed at the Texas A&M University Grazingland Animal Nutrition Lab for nutritional content.
"Owing to the complex interactions among climate, plants, cattle grazing and land management practices, the impacts of climate change on cattle have been hard to predict," said Craine, principal investigator for the project.
The lab measured the amount of crude protein and digestible organic matter retained by cattle in the different regions. The pattern of forage quality observed across regions suggests that a warmer climate would limit protein availability to grazing animals, Craine said.
"This study assumes nothing about patterns of future climate change; it's just a what if," Olson said. "What if there was significant atmosphere enrichment of carbon dioxide? What would it likely do to plant phenology? If there is atmospheric carbon dioxide enrichment, the length of time between when a plant begins to grow and when it reaches physiological maturity may be condensed."
Currently, cattle obtain more than 80 percent of their energy from rangeland, pastureland and other sources of roughage. With projected scenarios of climate warming, plant protein concentrations will diminish in the future. If weight gain isn't to drop, ranchers are likely going to have to manage their herds differently or provide supplemental protein, Craine said.
Any future increases in precipitation would be unlikely to compensate for the declines in forage quality that accompany projected temperature increases. As a result, cattle are likely to experience greater nutritional stress in the future if these geographic patterns hold as a actual example of future climates, Craine said.
"The trickle-down to the average person is essentially thinking ahead of time of what the consequences are going to be for the climate change scenarios that we are looking at and how ranchers are going to change management practices," Craine said.
"In my opinion these are fully manageable changes," Olson said. "They are small, and being prepared just in case it does happen will allow us to adapt our management to what will essentially be a shorter window of high-quality grazing."
Additional investigators on the project include Andrew Elmore at the University of Maryland's Center for Environmental Science and Doug Tolleson from the School of Natural Resources at the University of Arizona, along with the assistance of Texas A&M's Grazingland Animal Nutrition Lab.
Wednesday, November 11, 2009
Yet, the C4 photosynthetic pathway also confers greater resource use efficiency. The C4 pathway comes with increased energetic costs, but also confers greater photosynthetic water use and nitrogen use efficiency. More carbon is fixed in C4 species per unit water and nitrogen allocated to photosynthesis as internal CO2 concentrations are lower, which drives the greater WUE, and less N is needed for the same amount of photosynthesis, which drives greater NUE.
Some of the characteristics of C4 are a bit mythological. For example, although C4’s can have higher photosynthetic nitrogen use efficiency, many C4’s have high tissue N concentrations and many C3’s have as low an N concentration as the lowest C4. Not everything about plants is destined from photosynthetic properties.
That said, is there selective advantage to being more efficient with resources? Efficiency always comes at a cost. This much we know. You have to be inefficient with one resource to be more efficient with another. Light use efficiency comes at the expense of N use efficiency. N use efficiency comes at the expense of water use efficiency. Efficiency also costs time.
So what is the benefit of being efficient? For C4’s, under what conditions is it beneficial to be more efficient with water or nitrogen than C3’s. In a competitive world, efficiency in and of itself benefits no one but your competitors. The less water or nitrogen you use, the more there is for another. The benefit only comes if efficiency allows one to reduce the availability of the limiting resource below the level needed to sustain a potential competitor. Or tolerate more stressful conditions. Do C4’s reduce water or nitrogen availability to lower levels than C3’s? No evidence of that. Do C4’s tolerate lower water or nitrogen availability than C4’s? No evidence of that, either.
We also know that C4’s span a wide range of water and nitrogen availability. NADP-me type C4’s increase with mean annual precipitation, not decrease. And C4’s like the grasses we use in many lawns and golf courses have high nutrient requirements, not low, having evolved in grazing lawns that have high nutrient availability. In all, there is no evidence that C4’s preferentially occupy low water or low nitrogen habitats.
The efficiency of C4 species is one of the great mysteries of evolution. Is it an interesting by-product of selection for carbon gain under certain conditions? Or is it indirectly linked to success in ways that are not obvious? Likely, until we better understand the fundamental question of “Who wins and why?” in the plant world, that aspect of C4’s will still be a mystery.
Tuesday, October 27, 2009
For almost two decades, SLA (or its inverse alter-ego, LMA) has reigned supreme as the central functional trait of plants. SLA, i.e. specific leaf area--the ratio of leaf area to mass, has stood to represent the amount of investment into light acquisition. Entire pyramids of approaches to traits are built on the fundamental supremacy of SLA. The only thing more important than SLA in these pyramids is relative growth rate (RGR).
But why SLA? Why the ratio of area to mass? The thinking is that plants that grow fast need to absorb as much light as possible with the least amount of investment. Hence, selection favors plants that produce a lot of leaf area with little carbon investment, i.e. a high SLA. Plants in stressful or low-resource areas have low SLA, which presumably aids plants in resisting stress or maximizing the utilization of a limiting resource. Consistently, there are good correlations between SLA and RGR as well as other leaf characteristics such as photosynthetic rates, which have reinforced the primacy of SLA.
For almost all of the 20 years, there has always been a countervailing opinion of SLA that has never been rectified. If it ever was squared, SLA would likely never be measured again.
A leaf can high SLA either because it is thin or because it has low tissue density—thickness and density are the two components of SLA. In 1991, Witkowski and Lamont examined thickness and density across a series of ecological contrasts for sclerophyllous species. In short, from the patterns they observed, the authors concluded that “leaf density and thickness may respond to independently to resource and other gradients, and thus are more appropriate measures than [SLA] which confounds them.” Because thickness is so easy to measure—a quick squeezing of calipers—there is no good reason to not break down SLA to density and thickness every time.
Thickness and density have different functional roles in a leaf. They often vary independently across ecological contrasts. A thick, low density leaf and a thin, high density leaf would have the same SLA, but very different performances in most environments. By extension, SLA might be important to plant ecologists, but not to selection.
But maybe this is a bit hasty. SLA is supposed to be ecologically important and help explain the abundance of species across contrasts. Maybe SLA explains abundance better than thickness or tissue density. Surprisingly, the relative explanatory of SLA and its components have rarely been tested quantitatively. In general, this is probably the Achilles heel of most traits work. We spend more time examining relationships among traits than rigorously testing their relative predictive capacity.
Refuting the ecological importance of SLA or either of its components will not be a simple affair. It’ll take a number of studies before we understand their relative empirical importance. I’ve now done two. The first was at Cedar Creek along fertilization and disturbance gradients. The second is at Konza where I measured leaf traits for 130 grassland herbaceous species and tested their predictive capacity for species abundance across topographic, burning, and grazing contrasts. The results for Konza? SLA explained no variation in the abundance of species. Yet, tissue density did. Consistently across gradients it was tissue density not SLA that explained the abundance of species. The Cedar Creek work largely concluded the same thing.
SLA should not be buried yet, but at some point, we are going to have to fundamentally reexamine the hierarchy of traits in the ecology of plants. A dichotomous world of high SLA and low SLA (if not high RGR and low RGR) plant species might have to be replaced. Until then, at the very least, measure thickness.
Monday, October 12, 2009
Tuesday, September 29, 2009
Monday, September 7, 2009
There are a fair number of papers that are impressive for the number of times they are cited. “Instant classics” that accrue a hundred citations in a year—most in the first paragraph of a paper—and have helped define some part of a discipline.
These papers are impressive and worthy of study in hopes of replicating them, but I am more interested in papers that are likely just as important but have rarely been cited. Any scientist can use Web of Science to find the most cited paper on a topic and then cite it themselves in order to seem authoritative. But, the true scholar knows the obscure paper, one that might only have been cited a few times a year, but can make the case that the paper is as important as one cited a hundred times a year, if only the obscure one were discovered.
I do not have a comprehensive list, but it is an interesting exercise to think about what are the most important papers never to have been cited. If we restrict the list to the papers published over five years ago and have received less than five citations a year on average. And one cannot put one’s own papers on the list, which is unfortunate since most of my CV is obscure but important. (Except for the one soil CO2 flux paper in GCB. That one deserves to be obscure.) Here are ones that I came up with:
1) Wahl, S. and P. Ryser. 2000. Root tissue structure is linked to ecological strategies of grasses. New Phytologist 148:459-471. If ever there was a golden key to unlocking root function in different environments, this would be it. Why this study has not been replicated a dozen times, I do not understand. (30 cites)
2) Dietz, H. and F. H. Schweingruber. 2002. Annual rings in native and introduced forbs of lower Michigan, USA. Canadian Journal of Botany 80:642-649. The idea that you can dig up grassland plants and age them should have set fire to our understanding of plant population dynamics in grasslands. (12 cites)
3) McManus, W. R., V. N. E. Robinson, and L. L. Grout. 1977. Physical Distribution Of Mineral Material On Forage Plant-Cell Walls. Australian Journal of Agricultural Research 28:651-662. The idea that plants accumulate minerals on their cell walls and might use them for structural purposes fundamentally alters how we think of plant structure and turns plant stoichiometry on its ear. It’s never been followed up on as far as I know. (12 cites)
4) McNaughton, S. J., J. L. Tarrants, M. M. McNaughton, and R. D. Davis. 1985. Silica as a defense against herbivory and a growth promotor in African grasses. Ecology 66:528-535. This one came to mind after the previous one. Silica as structure changes the game. This became cited a bit more in 2006-7, but other than those two years never had more than 5 citations a year. (85 cites)
I’ll give this some more thought later. This is a hard list to compile (and my kids are awake now). I should be able to come up with a top ten list of obscure papers later.
Thursday, August 20, 2009
The family and I are on vacation in the Olympic Peninsula of Washington. We’ve spent the past three days at Lake Quinalt, which is on the southwest side of mountains and surrounded by temperate rainforest. A few things struck me while here. First, 15 feet of rain (the record annual precipitation) is a lot, but it can be hot and dry here. Second, it would have been wise to have bought a cooler and fast on smoothies for three days. There are few places to eat around here, especially since we are going back to Seattle to eat at places like Salumi and Pike Place Market.
The Quinalt River Valley has six record trees in it. The world’s largest western red cedar, Douglas fir, mountain hemlock, and Sitka spruce, are all in the one valley. The western red cedar is 19.5 feet across. It’s hollow in the middle and you can see daylight when you look up from within. I’m not sure where the phloem was, but there were green limbs up high. The Sitka spruce is 17 feet across and aside from being stuck between an RV park and a golf course, is impressive.
As we’ve hiked through the forests here, it has been interesting to think about how these trees have been accumulating environmental records for so long. Tree ring width and carbon and oxygen isotopes are the main records examined, but I’ve been thinking more about the nitrogen isotopes. From work I’ve done with Kendra in the past, every tree potentially has a record of nitrogen availability in its rings. The isotopic ratio of nitrogen stored in wood is largely set down initially and has been shown to track N availability. Only a small number of trees have had the N isotopes in wood measured and for the most part we are ignorant about how N availability has changed in these immense forests or others. It’s an important question since we don’t know how elevated CO2 has affected N availability or how frequently N availability might peak with disturbances, which has important implications for the ecology of these forests.
I am pretty sure we don’t have a 10 foot increment borer in the lab, but there are some long records here just waiting to be read.
Tuesday, August 11, 2009
Monday, July 6, 2009
Two papers recently came out that both deserve mention as they are important steps to better understanding the nature of coexistence and dominance in plant communities.
Wednesday, June 24, 2009
Monday, June 22, 2009
Thursday, June 11, 2009
Thursday, June 4, 2009
As the sun sets each night, most terrestrial plants close their stomata. It is reasoned that plants open their stomata to acquire CO2. At night, with no photosynthesis, there is no need to acquire CO2, and so the stomata can close.
Friday, May 22, 2009
If there is one central element to RSWP, it is not about how to quantify importance, the nature of resource limitation, or the mechanisms of competition. These fundamental questions all serve a higher purpose in the book: to understand the resource strategies of wild plants.
The broadest theories of plant strategies have differed on whether there was a common general strategy to succeeding when resources were low, or whether there were fundamentally different strategies associated with success when different resources are low. As I describe in RSWP, the most parsimonious conclusion is that there are four major strategies for growth when limiting resources are supplied uniformly over time. There is less support for the theory of a general “low-resource” strategy with variations associated with limitation by different resources than separate strategies for succeeding when water, nutrients, light, or CO2 are strongly limiting. The availabilities of resources are independent enough from one another and there are physiological and evolutionary tradeoffs in producing traits for success for each resource availability. Consequently, there is no one general strategy that covers low availability of all resources. Being built to perform well under low light precludes being competitive for nutrients which precludes acquiring water when soil water potential is low. All of these strategies might share a low maximal relative growth rate, but this appears to be a consequence of convergence. A fifth strategy is associated with success when the availabilities of all resources are high.
The five strategies I outline in RSWP are the most fundamental and widespread with regards to resources, yet it is important to recognize that no one set of traits works best across all environments that share having low availability of a given resource. For example, although both limited by nutrients, phosphorus limitation in the fynbos of South Africa has selected for plants that fundamentally different from those that dominate nitrogen-limited grasslands in Minnesota. How the multitude of environmental stresses and disturbances have shaped the world's flora are some of the most subtle questions about the forces that make our complex world beautiful. Yet, the skill of the ecologist is to appreciate the complex while seeking the simple. When we collapse the diversity of the world into its most fundamental units, we are left with the five resource strategies of wild plants.
Monday, May 11, 2009
Previously, I discussed how competition selects for suboptimal allocation patterns—at least suboptimal in the absence of competition. If this wasn’t a regressive list, I would have been getting slightly ahead of myself.
As I said before Tilman made a great advance in linking competitive success to resource availability reduction. Although his work might have been theoretically pure, its application to terrestrial systems was conceptually flawed. Plants do outcompete one another by reducing the availability of resources. Yet, the availability of nutrients in soil is not best conceptualized as the solution concentrations. Instead, it’s supplies. When nutrients are limiting, plants outcompete one another by reducing the supplies of nutrients to neighbors. Independent of reducing mineralization rates, supply reduction comes from supply preemption. Because of diffusion limitation, the plant with the most root length per unit volume of soil acquires the majority of the nutrients supplied. Each unit of root length produced reduces nutrient supplies to neighboring plants. The best competitor for nutrients is the plant that can produce the most root length.
I develop at length in RSWP the shift from concentration reduction hypotheses to supply preemption hypotheses and how it changes our outlook on plant interactions. For example, changes in soil moisture would affect prediction of competitive superiority by altering soil solution concentrations, but do not affect predictions based on supply preemption. There still is more theoretical work switching from R* models to SL* (supply per unit length), but the concepts are now more consistent with our understanding of soil nutrient dynamics, even if the are not as theoretically pure as possible. Better understanding of how plants compete for nutrients not only help us understand how competition has altered the evolution of plants, but sets us up to ultimately better understand the resource strategies of wild plants.
Tuesday, May 5, 2009
Although seemingly intractable, few other biogeochemical cycles rival N in their importance in determining how ecosystems function. Understanding the patterns of N cycling is so important that we have to continue to improve our ability to interpret natural abundance 15N patterns.
A number of coauthors and I just got a global review of 15N patterns published in New Phytologist. Details aside, it took a long time for this to happen. Although unfortunate, it gave us the opportunity to work with a number of editors and reviewers to understand the intellectual landscape better. Below I’ll post some summary thoughts on what needs to happen next in the discipline. In a later post, I’ll summarize what we learned in the paper.
1) We need CENTURY for 15N--a general model of the N cycle coupled with a stable isotope simulator to explore scenarios. 15N will not be raised up into the pantheon of ecological isotopes until the theoretical basis for patterns is worked out.
2) We need a survey to measure 15N in roots. Within-plant fractionation is the third major hypothesis for determining patterns of foliar 15N. Only 3 studies have compared 15N for leaves and roots. We'll need a lot more data to evaluate this hypothesis.
3) We need global maps of the N cycle. For all the N cycle has been measured, we do not have global, state-factor relationships with organic N uptake, N mineralization, nitrification, or gaseous N loss. We cannot make a global map of these fundamental processes. For example, time and time again reviewers choked on the idea that denitrification could be higher in sites with lower precipitation. A global synthesis would clear this up.
4) We need better measurements of the signature of available N. Measurements of soil inorganic 15N need to be as commonplace as available NH4+ and NO3-. Knowing these values are an incredible constraint on the key processes.
5) Mycorrhizal ecologists have been slow to assimilate 15N patterns into their understanding of the role of mycorrhizal fungi in plant N nutrition. For example, in Smith and Read's 3rd edition of Mycorrhizal Symbiosis, it was clear that the authors had gotten the story wrong. The attributed the higher 15N of ectomycorrhizal fungi to their reliance on enriched sources, and failed entirely to mention that ectomycorrhizal plants are depleted in 15N as much as the fungi are enriched. There is a lot of work that needs to be done to fully integrate mycorrhizal fungi into plant N nutrition. My guess is that one pressure point will be measuring 15N signatures of fungal mass and plant material in the field.
6) We need a central depository for 15N data that is better than my Macbook. Researchers being able to compare their values to global datasets quickly aids them in interpreting their data while facilitating new syntheses. Nothing new here.
Monday, May 4, 2009
When nutrients are limiting, a plant competes for a limiting nutrient supply by attempting to preempt the nutrient supply from other plants. As such, the key to acquiring the majority of a given nutrient supply is root length dominance. A consequence of supply preemption being the mechanism of competition for nutrients and root length dominance the key to preempting nutrient supplies is that plants face an evolutionary tragedy of the commons in their allocation patterns to roots. When the nutrient supply is limiting and a given plant is grown in isolation, a relatively low root length density optimizes growth. Yet, in the presence of competitors, plants that can maintain higher root length densities than are optimal in the absence of competition are able to acquire a larger fraction of the total nutrient supply and therefore would have been favored by natural selection. As such, high root length densities are more evolutionarily stable than the lower root length densities that would optimize growth in the absence of competition. This easy to see by taking a shovel to most temperate lawns. Most temperate grasses appear to have an order of magnitude more roots than is optimal for growth in the absence of competition.
The supply of light differs fundamentally from nutrient supplies in that it is largely supplied directionally. Yet, competition for light can select for plants that have canopies that are suboptimal in the absence of competition. The trunks of trees do not help a forest acquire more light—they only help an individual acquire more light than a competitor. As I discuss in RSWP, research has also shown that many plants also hold more leaves than is optimal and the leaves are held too flat. Plants that are optimizing canopy photosynthesis would hold their leaves at a higher angle in order to allow more light to penetrate deeper into the canopy where it can be used more efficiently. What would a tree with an efficient canopy look like? Probably something like a eucalyptus with its pendulous leaves and sparse canopies. It probably is no coincidence that eucalyptus are known by foresters to produce wood at some of the highest rates.
Thursday, April 30, 2009
Dave Tilman’s great advance for understanding competition over 30 years ago was to introduce the idea that competitive outcomes were determined by resource reduction. Phytoplankton that could lower the concentration of a limiting nutrient to the lowest level would become competitively superior. When applied to plants in soil, the concentration reduction hypothesis assumed that soil solutions were well-mixed and it was the average soil solution concentration that determined the rate at which a plant grew. As such, lowering the average soil solution concentration of a limiting nutrient was the key to displacing other species.
Leaving aside the assumptions of the nature of the nutrient supply, for plants in soil, resource reduction is still the mechanism for competitive displacement. Yet, it’s not concentration reduction, but supply preemption that determines competitive superiority. When nutrients are limiting, a plant competes for a limiting nutrient supply by attempting to preempt the nutrient supply from other plants. Due to the relatively slow diffusion of nutrients in soil, as roots acquire nutrients from the soil solution, nutrient supplies are partitioned among plants based on the relative amount of root length they hold in a particular soil volume. The key to acquiring the majority of a given nutrient supply is root length dominance, which reduces the availability of nutrients to others.
Although the magnitude of this conceptual shift is open, supply preemption is the proper application of resource reduction to plants growing in soil. What about other resources? As I discuss in RSWP, supply preemption is the best concept for understanding light competition, too. Water is notoriously pulsed in availability, but supply preemption rules here, too. Just a bit different than nutrients that are supplied evenly over time.
Competition research can be summarized as “who wins and why?” The secret to competing for resources is to get them before your neighbors do. Took about 30 years to nail down how that works on land, and it'll probably take another few decades likely to nail down the details.
Monday, April 27, 2009
With RSWP scheduled for publication in less than a month (at least that is what Amazon tells me), I thought it would be interesting to highlight some of what I think are the key advances of the book. A self-promoter might call this “Countdown to a New Paradigm”, I’ll just call it Countdown to Publication, I guess. [As an aside, if you ever want to promote your career, start an intellectual battle with someone on a different continent and agree not to attempt to resolve your differences. It works great every time.] I do think #5 represents a new paradigm. Not a paradigm I should be credited with, but a fundamental change in how we think of resource limitation.
The Law of the Minimum that describes the basic ecological concept of limitation was established at a time when little was known about nutrient cycling and was not applied initially to limitation by light. The three parts of Liebig’s Law of the Minimum are
1) Growth is limited by the resource that is supplied at the lowest rate relative to the demands of the plant.
2) Growth is proportional to the rate of supply of the most limiting resource.
3) Growth cannot be increased by increasing the supply of a non-limiting nutrient.
In the Liebigian world of limitation, generally only one nutrient could be limiting at a time. In a post-Liebigian world, it is likely that there is co-limitation to growth among different resources, not just serial limitation. Co-limitation is more likely to occur than would be predicted from Liebig’s Law of the Minimum because a) nutrients supplied in excess are more likely to be lost, b) species differ in the stoichiometry of demands for optimal growth, c) plants can store resources to balance temporally variable rates of supply, and d) plants can increase the availability of the most limiting resource. If there are tradeoffs in acquisition between different allocation strategies, whether for increasing supplies or acquiring a greater fraction of a given supply, co-limitation is likely to occur. Nutrients and light. Water and CO2. Nitrogen and phosphorus. I expand on this in the book, but these co-limitations fundamentally alter our approach to understand everything from global change to evolution.
The existence of co-limitation is not that novel, nor even the suggestion that it should be common. Yet, the consequences of this focus are reach far. Resource co-limitation in the post-Liebig world does not only manifest itself in responses in productivity to the addition of two resources with no increases if only one resource is added. Due to allocational tradeoffs, plants can be co-limited by multiple resources and respond to individual resources independently. Also, the only way to understand why one resource is limiting is by understanding which resource is co-limiting with it.
When resources are co-limiting, costs for different allocation strategies or the production of different structures should be evaluated with a dual-currency model. Evaluating costs with just one resource ignores the often great cost of the second resource. There is no money in ecology—it’s a bartering world with a few key staples.
Lastly, natural selection favors plants that adjust their allocation strategies such that multiple resources are co-limiting. As such, plants are also selected to balance their resource use efficiencies to match resource supply ratios. For example, plants that grow with high relative limitation of nitrogen should have higher ratios of nutrient to light use efficiencies than plants that grow in environments with greater relative limitation by light. Resource limitation provides a fundamental constraint on efficiency of resource use that makes the world predictable.
Tuesday, April 14, 2009
B0 is biomass of controls
BN is biomass with +N
BP is biomass with +P
BNP is biomass with +N+P
To make matters simple, let’s assume that there is no effect of P added alone and that the biomass of plants with N and P added is greater than unfertilized biomass.
With this, we’re trying to separate three cases.
1) Classic co-limitation (co-limitation by supply) where there is no direct effect of N (or a relatively small one).
2) Primary limitation by N and secondary limitation by P
3) Single resource limitation where there is an N effect, but no effect of P on N-fertilized plants.
First we can compare the absolute changes in biomass relative to controls and compare the N effect to the NP effect. If we calculate the co-limitation index as
then a plant that had a CI > 0 would be primarily limited by N and secondarily by P. A CI <>
The interpretation of the pattern would be that soils with low P availability are co-limited by N and P. As P availability increases plants are more likely to be primarily limited by N and secondarily limited by P.
That’s a pretty clean story, but the problem with this approach is that you cannot separate if a plant is secondarily limited by P or just limited by N.
To get around this we can calculate a co-limitation index as:
With this index, 0≤CI<0.5>
Here are the patterns for the 100 soils data:
Pretty much the same story. Plants start out co-limited by N and P at low P availability. Then as P availability increases P limitation becomes more secondary until ~30 ppm available P at which we’re into strict single limitation by N. The problem with this approach is that the relative index is sensitive to BNP. For the graph at left I had to exclude two points that had |CI|>10.
With these approaches statistical significance relative to threshold values, e.g. CI = 0 for the first index, are possible. I’m not sure how to extract them from JMP yet.
Note with a factorial resource addition experiment there are something like 9 different basic responses when you include inhibition and responses by individual resources. There will be no way to boil, but we might be able to get the most important patterns down to 2.
Sunday, April 5, 2009
How plants acquire nitrogen is one of the fundamental questions in understanding plant adaptations to low nutrient availability. For many years, plants were understood to associate with mycorrhizal fungi in order to acquire P. Later it was understood that some types of mycorrhizal fungi (ectomycorrhizal and ericoid) acquired organic N and transferred that to the host plant. Yet, for many years it was unknown whether arbuscular mycorrhizal fungi were important in the N nutrition of plants.
Leigh, Hodge, and Fitter (2009) take a big step in showing that arbuscular mycorrhizal fungi acquire N from the soil and transfer the N to plants. Building on earlier work by Hodge, the authors grew Plantago lanceolata in microcosms with two compartments. In some, plant roots had access to the second compartment which contained 13C and 15N enriched shoots. In others, only arbuscular mycorrhizal fungi could access the compartment. The authors show that the arbuscular mycorrhizal access inorganic N derived from the shoot material and transfer a large fraction of it to the plants. In one case, ~20% of the plant’s N came from the AM fungi.
In showing the ability of AM to acquire N and transfer large amounts of it to the plant, the study is an important one. The degree to which this potential is ecologically important remains to be seen. In this study, the AM fungi had access to a large, N-rich patch that the roots did not. In nature, it doesn't seem too often that an N-starved plant find's itself on the other side of a goretex barrier from a rotting carcass. Yet, if there ever is a race for a patch, can AM fungi find it before roots? Do they proliferate and therefore compete better than roots? Can they access small, rich patches that roots cannot? The experiment by Leigh, Hodge, and Fitter is an important step in our understanding. The next experiment might be the really important step.
Leigh, Hodge, and Fitter. 2009. “Arbuscular mycorrhizal fungi can transfer substantial amounts of nitrogen to their host plant from organic material” New Phytologist, 181: 199-207.