Warming Arctic forests diverge over nutrients

March 27, 2020 by fredsingerecology

Humans continue their unique uncontrolled experiment to see how increased atmospheric carbon dioxide and the resulting warmer temperatures influence biomes worldwide. One expected outcome of this global experiment is that trees in the extreme north will show improved growth resulting from a more benign physical environment. As it turns out, some regions of the north do show this trend, while others don’t – this lack of consistent response is known as divergence. For her graduate work, Sarah Ellison, working with Patrick Sullivan, Sean Cahoon and Rebecca Hewitt, wanted to document divergence in northern Alaska, and to figure out what might be causing it.

The Wind River, near Arctic Village in the Arctic National Wildlife Refuge, is the easternmost site in the study. Credit: Patrick Sullivan.

The researchers established four study sites in four watersheds across the Brooks Range in northern Alaska. They knew from previous studies that white spruce (Picea glauca) in the western Brooks Range have shown increased growth in response to climate warming, whereas those in the central and eastern Brooks Range have not responded. Some researchers hypothesized that warmer temperatures caused moisture limitation in the eastern Brooks Range, but previous plant physiological studies done by this research team show no evidence of water stress, even in the extreme eastern portion of the range.

The four study sites within the Brooks Range from west to east: Agashashok, Kugururok, Dietrich and Wind River.

So what’s causing divergence?

At each study site, the researchers set up climate stations which collected continuous data on air and soil temperature, wind speed and direction, solar radiation, snow depth and precipitation. (Check out the following (you may need to copy and paste into your browser) for an entertaining look at the challenges of doing this research: https://youtu.be/ty6vwio9LvU).

A weather station at the Wind River sight. Credit: Sarah Ellison.

They discovered that soil temperatures were consistently warmer in the western part of the range over the course of the season.

EllisonFig2

Soil

Temp.

(deg. C)

Colder soils are often associated with low levels of available nutrients, because bacteria are less active at colder temperatures, and thus less capable of breaking down nutrients into a form that can be taken up by roots. In 2014, Ellison and her colleagues measured soil nutrient levels at each site and found generally lower levels in the central (Dietrich) and eastern (Wind River) sites.

From top: ammonium, nitrate, phosphate and total free primary amine (TFPA – a proxy for amino acids) availability in the soils at the four sites during the 2014 growing season. Error bars are +/- 1 SE.

There were several other important physiological pieces to this puzzle. Plants in the west grew more quickly than did plants in the east. Rapid growth was associated with greater photosynthetic rates in the western watersheds. The researchers measured needle nutrient concentration and found that it decreased from west to east. Each year, there was a strong correlation between needle nutrient concentration and branch extension (the measure of tree growth), but the correlation with phosphorus was generally stronger than the correlation with nitrogen.

Branch extension in relation to needle phosphorus concentration (left graph) and needle nitrogen concentration (right graph) for three years of the study.

Armed with these findings, Ellison and her colleagues decided to experimentally test whether nutrient availability was limiting growth, particularly in the eastern regions of the Brooks Range. If so, this would support the hypothesis that cold temperatures and the resulting decrease in nutrient availability were primary factors causing divergence across this vast ecosystem. In June, 2015, the researchers fertilized five trees at each site with a mixture of nitrogen, phosphorus, and potassium fertilizer, and left five similar nearby trees as untreated controls. After one year, branch extension was greatly enhanced at the most eastern site, and only slightly (insignificantly) enhanced at the most western site.

EllisonFig7top

Mean annual growth (branch extension) before and after fertilization experiment for fertilized trees (gray circles) and control trees (black circles). Bars are +/- 1 SE. Fertilization occurred in 2015 (indicated by vertical dotted lines).

For many years, forest ecologists have believed that forests in young glacial soils are nitrogen limited. This study, and a few other recent studies, thrust phosphorus into prominence as a factor that can limit forest productivity. Over time, as the climate continues to warm, soils in the eastern Brooks Range will enjoy increased microbial activity, and may no longer suffer as much from nutrient limitation.

The Agashashok mesic treeline sits on a gentle slope above the Agashashok river. Credit Sarah Ellison.

One surprising finding was that mycorrhizal growth on fine roots was more extensive in central and eastern watersheds. Abundant mycorrhizae were associated with reduced branch extension, suggesting that these mycorrhizae may be parasitic, rather than mutualistic. The researchers are in the process of expanding their study to an even greater spatial extent of 20 sites distributed across the Brooks Range, which will allow them to further explore how general their findings are across this vast biome.

note: the paper that describes this research is from the journal Ecology. The reference is Ellison, S. B. Z., Sullivan, P. F., Cahoon, S. M. P., and Hewitt, R. E.. 2019. Poor nutrition as a potential cause of divergent tree growth near the Arctic treeline in northern Alaska. Ecology100( 12):e02878. 10.1002/ecy.2878. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2019 by the Ecological Society of America. All rights reserved.

Sweltering ants seek salt

December 30, 2018 by fredsingerecology

Like humans, ants need salt and sugar. Salt is critical for a functioning nervous system and for maintaining muscle activity, while sugar is a ready energy source. In ectotherms such as ants, body temperature is influenced primarily by the external environment, with higher environmental temperatures leading to higher body temperatures. When ants get hot their metabolic rates rise, so they can go out and do energetically demanding activities such as foraging for essential resources like salt and sugar. On the down side, hot ants excrete more salt and burn up more sugar. In addition, like humans, very high body temperature can be lethal, so ants are forced to seek shelter during extreme heat. As a beginning graduate student, Rebecca Prather wanted to know whether ants adjust their foraging rates on salt and sugar in response to the conflicting demands of elevated temperatures on ants’ physiological systems.

Rebecca Prather at her field site in Oklahoma, USA. Credit: Rebecca Prather.

Prather and her colleagues studied two different field sites: Centennial Prairie is home to 16 ant species, while Pigtail Alley Prairie has nine species. For their first experiment, the researchers established three transects with 100 stations baited with vials containing cotton balls and either 0.5% salt (NaCl) or 1% sucrose. The bait stations were 1 meter apart. After 1 hour, they collected the vials (with or without ants), and counted and identified each ant in each vial. The researchers measured soil temperature at the surface and at a depth of 10 cm. The researchers repeated these experiments at 9 AM, 1 PM and 5 PM, April – October, 4 times each month.

Ants recruited to vials with 0.5% salt solution. Credit: Rebecca Prather.

Sugar is easily stored in the body, so while sugar consumption increases with temperature, due to increased ant metabolic rate, sugar excretion is relatively stable with temperature. In contrast, salt cannot be stored effectively, so salt excretion increases at high body temperature. Consequently, Prather and her colleagues expected that ant salt-demand would increase with temperature more rapidly than would ant sugar-demand.

Ant behavior in response to vials with 0.5% salt (dark circles) and 1% sucrose (white circles) at varying soil temperatures at 9AM, 1 PM (13:00) and 5PM (17:00). The three left graphs show the number of vials discovered (containing at least one ant), while the three right graphs show the number of ants recruited per vial. The Q10 value = the rate of discovery or recruitment at 30 deg. C divided by the rate of discovery or recruitment at 20 deg. C. * indicates that the two curves have statistically significantly different slopes.

The researchers discovered that ants foraged more at high temperatures. However, when surface temperatures were too high (most commonly at 1 PM during summer months), ants could not forage and remained in their nests. At all three times of day, ants discovered more salt vials at higher soil temperatures. Ants also discovered more sugar vials at higher temperatures in the morning and evening, but not during the 1 PM surveys. Most interesting, the slope of the curve was much steeper for salt discovery than it was for sugar discovery, indicating that higher temperature increased salt discovery rate more than it increased sugar discovery rate (three graphs on left).

When ants discover a high quality resource, they will recruit other nestmates to the resource to help with the harvest. Ant recruitment rates increased with temperature to salt, but not sugar, indicating that ant demand for 0.5% salt increased more rapidly than ant demand for 1% sugar (three graphs above on right).

The researchers were concerned that the sugar concentrations were too low to excite much recruitment, so they replicated the experiments the following year using four different sugar concentrations. Ant recruitment was substantially greater to higher sugar concentrations, but was still two to three times lower than it was to 0.5% salt.

Ant recruitment (y-axis) to different sugar concentrations at a range of soil temperatures (X-axis). Q10 values are to the left of each line of best fit.

Three of the four most common ant species showed the salt and sugar preferences that we described above, but the other common species, Formica pallidefulva, actually decreased foraging at higher temperatures. The researchers suggest that this species is outcompeted by the other more dominant species at high temperatures, and are forced to forage at lower temperatures when fewer competitors are present.

In a warming world, ant performance will increase as temperatures increase up to ants’ thermal maximum, at which point ant performance will crash. Ants are critical to ecosystems, playing important roles as consumers and as seed dispersers. Thus many ecosystems in which ants are common (and there are many such ecosystems!) may function more or less efficiently depending on how changing temperatures influence ants’ abilities to consume and conserve essential nutrients such as salt.

note: the paper that describes this research is from the journal Ecology. The reference is Prather, R. M., Roeder, K. A., Sanders, N. J. and Kaspari, M. (2018), Using metabolic and thermal ecology to predict temperature dependent ecosystem activity: a test with prairie ants. Ecology, 99: 2113-2121. doi:10.1002/ecy.2445 . Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2018 by the Ecological Society of America. All rights reserved.

What grows up must go down: plant species richness and soils below.

November 29, 2018 by fredsingerecology

Almost 20 years ago, Dorota Porazinska was a postdoctoral researcher investigating whether plant diversity influenced the diversity of organisms that lived in the soil below these plants, including bacteria, protists, fungi and nematodes (collectively known as soil biota). Surprisingly, she and her colleagues discovered no linkages between aboveground and belowground species diversity. She suspected that two issues were responsible for this lack of linkage. First, the early study lumped related species into functional groups – for example nematodes that eat bacteria, or nematodes that eat fungi. Lumping simplifies data collection but loses a lot of data because individual species are not distinguished. Back in those days, identifying species with DNA analysis was time-consuming, expensive, and often impractical. The second issue was that even if aboveground-belowground diversity was linked, it might be difficult to detect. Ecosystems are very complex, and many belowground species make a living off of legacies of carbon or other nutrients that are the remains of organisms that lived many generations ago. These legacy organic nutrient pools allow for indirect (and thus more difficult to detect) linkages between aboveground and belowground species.

Porazinska and her colleagues reasoned that if there were aboveground/belowground relationships, they would be easiest to detect in the simplest ecosystems that lacked significant pools of legacy nutrients. They also used molecular techniques that were not readily available for earlier studies to identify distinct species based on DNA analysis. The researchers established 98 1-m radius circular plots at the Niwot Ridge Long Term Ecological Research Site in the Colorado, USA Rocky Mountains. At each plot, they identified and counted each vascular plant, and recorded the presence of moss and lichen. They also censused soil biota by using a variety of DNA amplification and isolation techniques that allowed them to identify bacteria, archaea, protists, fungi and nematodes to species.

Field assistant Jarred Huxley surveys plants in a high species richness plot. Credit Dorota L. Porazinska.

As expected in this alpine environment, plant species richness was quite low, averaging only 8 species per plot (range = 0 – 27). In contrast to what had been found in other ecosystems, high plant diversity was associated with high diversity of soil biota.

Relationship between plant richness (x-axis) and soil biota richness (y-axis) for (A) bacteria, (B) eukaryotes (excluding fungi and nematodes), (C) fungi, and (D) nematodes. OTUs are operational taxonomic units, which represent organisms with very similar or identical DNA sequences on a marker gene. For our purposes, they represent distinct species.

Looking at the graphs above, you can see that different groups responded to different degrees; nematodes had the strongest response to increases in plant richness while fungi had the weakest response. When viewed at a finer level, some groups of soil organisms, including photosynthetic microorganisms such as cyanobacteria and green algae actually decreased, presumably in response to competition with aboveground plants for light and possibly nutrients.

Given the strong relationship between plant species richness and soil biota richness, Porazinska and her colleagues next explored whether high plant richness was associated with soil nutrient levels (nutrient pools). In general, there was a strong correlation between plant species richness and nutrient pools (see graphs below). But soil moisture, and the ability of soil to hold moisture were the two most important factors associated with nutrient pools.

Amount (micrograms per gram of soil) of carbon (left graph) and nitrogen (right graph) in relation to plant species richness.

Ecologists studying soil processes can measure the rates at which microorganisms are metabolizing nutrients such as carbon, phosphorus and nitrogen. The expectation was that if high plant species richness was associated with higher soil biota richness, and larger soil nutrient pools, then the activity of enzymes that metabolize soil nutrients should proportionally increase with these factors. The researchers found that enzyme activity was very low where plants were absent or rare, and greatest in complex plant communities. But the most important factors influencing enzyme activity were the amount of organic carbon present within the soil, and the ability of the soil to hold water.

Patchy vegetation at the field site. Credit: Cliffton P. Bueno de Mesquita.

Porazinska and her colleagues hypothesize that the relationship between plant species richness, soil biota richness, nutrient pools, and soil processes such as enzyme activity, exist in most ecosystems, but are obscured by indirect linkages between these different levels. They hypothesize that these relationships in other ecosystems such as grasslands and forests are difficult to observe. In these more complex ecosystems, carbon inputs into the soil form large legacy carbon pools. These carbon pools, and the ability of the soil to hold nutrient pools, fundamentally influence the abundance and richness of soil biota. In contrast, in nutrient-poor soils, such as high Rocky Mountain alpine meadows, legacy carbon pools are rare and small. Consequently, plants and soil biota interact more directly, and correlations between plant species diversity and soil biota diversity are much easier to detect.

note: the paper that describes this research is from the journal Ecology. The reference is Porazinska, D. L., Farrer, E. C., Spasojevic, M. J., Bueno de Mesquita, C. P., Sartwell, S. A., Smith, J. G., White, C. T., King, A. J., Suding, K. N. and Schmidt, S. K. (2018), Plant diversity and density predict belowground diversity and function in an early successional alpine ecosystem. Ecology, 99: 1942-1952. doi:10.1002/ecy.2420. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2018 by the Ecological Society of America. All rights reserved.

Seagrass scourge: when nutrient enrichment reaches the tipping point

October 24, 2017 by fredsingerecology

Sean Connell has watched as south Australia has lost vast expanses of kelp forest and seagrasses over the past years. One of the primary culprits associated with loss of seagrass meadows is excessive nutrients, particularly nitrogen, which enters the ecosystem with runoff, and causes an increase in algal epiphytes (epiphytes are small plants that grow on other plants). Epiphytes can negatively affect seagrass by blocking sunlight needed for photosynthesis, and indirectly, by increasing the rate of cellular respiration within the ecosystem, thus using up oxygen needed by seagrass for metabolic processes.

Two dolphins swim above a bed of seagrass off the south Australian coast.

Connell and his colleagues noticed that seagrass loss was often sudden; a large seagrass meadow would appear to be in good shape, and then it would abruptly disappear. They suggested that there might be a threshold effect in nutrient levels that seagrasses can tolerate; that these systems function well until a certain threshold in nutrient levels is crossed, above which there is an abrupt loss of seagrasses. They tested this hypothesis by subjecting plots of the seagrass Amphibolis antarctica to seven different concentrations of dissolved inorganic nitrogen (DIN) over a 10 month period, and monitored the abundance of epiphytes and seagrass over that timespan.

The meadows were about two km offshore from Lady Bay, Fleurieu Penninsula, Australia, in about 5 meters of water. Different amounts of nitrogen fertilizer were wrapped in nylon bags (for slow continuous release of DIN) and staked to the ocean floor. Amphibolis antarctica grows by producing new leaves at the top of each leaf cluster, but at the same time it drops old leaves. Leaf turnover, the researchers’ measure of growth, is simply new leaf production minus old leaf drop. The researchers tied on a small nylon cable at known locations on selected plants, noted how many leaves were above and below each tie at the beginning of the experiment, and recounted leaf number 10 months later. Finally, the researchers measured epiphyte growth by microscopically viewing a sample of seagrass leaves, and counting the number seagrass leaf cells that were covered by epiphytes.

Seagrass growth was relatively unaffected by all tested DIN levels.

Leaf production per day in relation to concentration of DIN.

However, leaf drop showed a strong threshold effect; leaf drop rates increased sharply between 0.13 – 0.15 mg/L of DIN.

Leaf drop per day in relation to concentration of DIN.

Putting these two graphs together, you can see (below) that leaf turnover switched from positive to negative at 0.13 – 0.15 mg/L of DIN. Negative leaf turnover translates to a sudden loss of seagrass at that threshold. At least in this system, at this location, 0.13 – 0.15 mg/L of DIN is the tipping point, beyond which the seagrass system suddenly goes into decline.

Leaf turnover per day (left y-axis and red data), and Epiphyte cover (% – right y-axis and green data), in relation to concentration of dissolved inorganic nitrogen.

The graph also shows that the tipping point coincides with an epiphyte cover of approximately 60%. It is possible that increased epiphyte cover may reduce seagrass photosynthetic rates (particularly in lower leaves), so that leaf turnover suddenly shifts into the negative zone, but the study was not designed to identify the underlying mechanism.

Seagrass meadows perform important ecosystem services, such as absorbing excess nutrients from the sediment, and providing habitat and food for a diverse group of grazers and indirectly, for their consumers. Thus seagrass conservation is vital. The danger here is that moderate levels of nutrients do not appear to have much effect on seagrass populations, but there is an abrupt shift to seagrass loss once the nutrient threshold is crossed. This makes the system very difficult to manage, because the loss occurs without warning. Australian ecologists have repeatedly failed to restore lost seagrass meadows, as simply reducing nutrient levels does not reverse the process. Thus anticipating seagrass loss before it happens is the most viable management solution for this critical ecosystem.

note: the paper that describes this research is from the journal Conservation Biology. The reference is Connell, S. D., Fernandes, M., Burnell, O. W., Doubleday, Z. A., Griffin, K. J., Irving, A. D., Leung, J. Y.S., Owen, S., Russell, B. D. and Falkenberg, L. J. (2017), Testing for thresholds of ecosystem collapse in seagrass meadows. Conservation Biology, 31: 1196–1201. doi:10.1111/cobi.12951. Thanks to the Society for Conservation Biology for allowing me to use figures from the paper. Copyright © 2017 by the Society for Conservation Biology. All rights reserved.

Nitrogen nurses

May 10, 2017 by fredsingerecology

Alfred Lord Tennyson puzzled over the conflict between love as a foundation of Christianity, and the apparent violence of the natural world.

Who trusted God was love indeed

And love Creation’s final law

Tho’ nature, red in tooth and claw

With ravine, shriek’d against his creed

The good poet would be relieved to learn that modern ecologists have uncovered a softer, gentler side of the natural world – facilitative interactions, in which one species (the facilitator) helps out a second species. In many, but not all, cases, the second species also helps out the first species. Ecologists describe these mutually-beneficial interactions as mutualisms. As an example, Mimosa luisana is a mutualist with Rhizobium bacteria, providing the bacteria with root nodules to live in and carbohydrates as an energy source, while receiving ammonia (NH₃) that the bacteria fix (convert) from atmospheric N₂. A second type of mutualism, a mycorrhizal association, is a very common facilitative interaction between plants and fungi, which grow alongside or within the plant roots. In many mycorrhizal associations, the plant provides carbohydrates to the fungi, which import and share nutrients and water.

Alicia Montesinos-Navarro and her colleagues, and researchers before them, noticed that in arid and semi-arid environments, plant-plant facilitation was most common between two plant species that were structurally and functionally very distinct, and that tended to be very distantly related to each other. In particular, M. luisana tends to associate with many different species of plants, including many cacti that look nothing like it, and are very distantly related. M. luisana is called a nurse plant, because other species tend to grow under its branches, which shade the soil and reduce water loss from evaporation. Recent work by Montesinos-Navarro and her colleagues showed another benefit of nursing – some plants receive nitrogen from these nurse plants via the network of mycorrhizal fungi.

Traditionally, ecologists have argued that associations between distantly-related plants occur because the plants have very different ecological niches, using different resources in different ways, so they are not competing with each other. Montesinos-Navarro and her colleagues argue that a second process might be important in this and other systems. Close relatives of M. luisana might tend to have high nitrogen levels and thus not benefit from nitrogen transfer from the nurse plant, while more distantly-related plants might tend to have lower nitrogen levels and thus benefit from any nitrogen arriving from M. luisana. They explored this hypothesis in the semi-arid Valley of Zapotitlan in the state of Puebla, Mexico.

Study site dominated by the columnar cactus Neobuxbaimia tetezo, Credit: Alicia Montesinos-Navarro.

Measuring nitrogen transfer from the nurse plant to the recipient is not the world’s easiest task. Fortunately there is a rare form or isotope of nitrogen, ¹⁵N, which can be distinguished from the more common ¹⁴N. The researchers soaked M. luisana leaves in urea that was made up of primarily ¹⁵N, and the leaves took up the urea. Consequently, any exported nitrogen would contain a disproportionately high concentration of ¹⁵N, resulting in high ¹⁵N levels in the recipient plant. They then measured ¹⁵N levels in 14 different species of plants that used M. luisana as their nurse. The researchers were able to test two hypotheses. First, they could see whether close relatives to M. luisana tended to have higher N-levels than more distantly related species. Second they could see whether distant relatives tended to receive more nitrogen from nurse plants than did close relatives.

Mimosa luisana branch taking up ¹⁵N-labeled urea. Credit: Alicia Montesinos-Navarro.

The graph below summarizes the results. The y-axis measures how much the ¹⁵N level in the facilitated species increased by the end of the experiment (15 days). The x-axis measures the evolutionary relationship between M. luisana and the facilitated species – more precisely how long ago the two species shared a common ancestor. Lastly, the size of the dot measures the initial difference in leaf N-levels between M. luisana and the facilitated plant.

Influence of evolutionary relationship between M. luisana and the facilitated species (x- axis) and nitrogen gradient – the initial difference in nitrogen levels between the two species (size of dots) on the amount of nitrogen imported by the facilitated species.

Several trends are evident. First, close relatives of M. luisana tended to have similar leaf nitrogen values to M. luisana (medium sized dots), while distant relatives tended to have much less nitrogen than M. luisana (largest dots). Second, the most distant relatives tended to have the greatest increase in their ¹⁵N levels, which indicates that they received the greatest nitrogen export from their nurses.

One question is how the nitrogen is transported. Montesinos-Navarro and her colleagues describe how they treated soil with a fungicide, presumably killing the mycorrhizae, which resulted in a substantial reduction in nitrogen transport. This suggests that the mycorrhizal network is important for nitrogen transport. But more pressing is what do the nurse plants get out of the relationship. The researchers suggest that the recipient plants may provide M. luisana with either water or phosphorus, both of which may be in short supply in arid environments.

This study indicates that we need to look beyond traditional niche theory, and may need to dig deeper to understand the structure of plant communities, and how facilitative interactions can explain the coexistence of very distantly related plants.

note: the paper that describes this research is from the journal Ecology. The reference is Montesinos‐Navarro, A., Verdú, M., Querejeta, J. I., & Valiente‐Banuet, A. (2017). Nurse plants transfer more nitrogen to distantly related species. Ecology, 98(5), 1300-1310. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2017 by the Ecological Society of America. All rights reserved.

Spotted salamander performance per polymorphism persistence

April 28, 2017 by fredsingerecology

His first winter at the University of Mississippi Field Station, Matt Pintar was wading through some ponds where he noticed a large number of egg masses. Clear jelly surrounded most of these egg masses, but a whitish jelly encased some of them. These egg masses were produced by the spotted salamander, Abystoma maculatum, which immediately made Pintar wonder why these differences exist within this species. Biologists use the term “polymorphism” to describe a situation like this, in which two or more forms (poly = multiple, morph = form) exist within a population.

White egg mass (left) and clear egg mass (right). Credit: Matt Pintar

Could it simply be random chance that there were two egg mass morphs? Or was one morph better than the other in getting fertilized by the appropriate sperm, or in keeping the eggs together? Alternatively, perhaps one morph was better at providing nutrients or protecting against predators. The puzzle is that if one morph was superior to the other, then that morph would be favored by natural selection, should outcompete the other, and ultimately cause the second morph to go extinct. So why did both morphs persist in this population of spotted salamanders?

Adult male spotted salamander. Credit Matt Pintar

Recently hatched larvae. Credit Matt Pintar.

Pintar and his colleague Willliam Resetarits Jr. thought it most likely that the polymorphism was a chance event that provided no benefit to the salamanders. But they did consider the alternative that one morph might be better in some conditions, while the other morph was better in other conditions. Surveys done about 25 years ago suggested that the polymorphism might be connected to differences in water chemistry, so Pintar and Resetarits decided to explore this possible link with a combination of observations of natural ponds and field experiments on artificial ponds.

Ponds at the University of Mississippi Field Station. Credit Matt Pintar.

Nutrient levels of ponds at the field station are influenced by two major factors: the type of surrounding habitat and the duration of time each pond holds water over the course of the year (the hydroperiod). Ponds surrounded by trees, as opposed to grass, have higher nutrient levels courtesy of tree leaves that fall into the ponds and leach out their nutrients. Many of these ponds dry out in the summer, so ponds with a longer hydroperiod will have more time to receive and leach nutrients from organic matter.

Ecologists often use water conductivity as a general measure of pond nutrient levels. Ponds with high conductivity have higher nutrient levels than ponds with low conductivity. Pintar and Resetarits sampled the water from 55 ponds and counted the number of white and clear egg masses from 40 ponds that had egg masses in 2015 and 2016. They found a striking relationship between conductivity and egg mass morph. White egg masses were much more common in low-nutrient (low conductivity) ponds.

Proportion of white egg masses in relation to water conductivity (a measure of nutrient level)

The researchers further explored this relationship by setting up artificial ponds that contained either low or high nutrient levels (obtained by putting leaf litter into some of the pools), and inoculating each pond with both white and clear egg masses. Pintar and Resetarits made sure that larvae were not mixed up once they hatched. They then measured the effects of both nutrient levels and morph on many variables associated with growth and development in these artificial ponds.

Some of the artificial ponds used for controlled experiments on the effects of nutrient levels. Credit: Matt Pintar.

In general, eggs from white masses had a significantly higher rate of hatching (about 80%) at both nutrient levels than did eggs from clear masses (about 60%). But eggs from white masses took longer to hatch (Figure (c) below). Importantly, larvae from white masses tended to grow better under low-nutrient conditions than did larvae from clear masses. In contrast, larvae from clear masses grew better under high-nutrient conditions than did larvae from white masses (Figures (d, e, f) below).

The relationship between nutrient level and (c) days to hatching, (d) snout-vent length (the distance between the tip of the snout and the cloacal opening), (e) total length and (f) body mass.

These findings indicate that the polymorphism is advantageous in environments with considerable variation in nutrient levels. The white morph tends to do well at low nutrient levels, while the clear morph does better at higher nutrient levels. Pintar and Resetarits suggest that these differences in growth and development are likely to translate to higher adult survival and reproductive rates. The researchers used population modeling to demonstrate that under realistic conditions in which some individuals migrate from one pond to another, both morphs will persist indefinitely in ponds of varying nutrient levels.

We still don’t know why the two morphs perform differently under these different conditions. We do know that the outer jelly layer of white egg masses have white crystals made of proteins that are not water soluble, while the outer jelly layer of clear egg masses have smaller water soluble proteins. Pintar speculates that the firmer consistency of white egg masses could cause them to degrade more slowly and to retain their constituent nutrients more effectively than do the clear morphs.

note: the paper that describes this research is from the journal Ecology. The reference is Pintar, Matthew R., and William J. Resetarits Jr. “Persistence of an egg mass polymorphism in Ambystoma maculatum: differential performance under high and low nutrients.” Ecology (2017). The print version will probably come out in May or June of this year. Meanwhile, you can access it here. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2017 by the Ecological Society of America. All rights reserved.

Metallic starlings: a rain of terror

February 22, 2017 by fredsingerecology

I am a slow learner. Several times in the past few years I have paddled my canoe under a particular sycamore tree in the New River in Radford, Virginia. Each time I do so, I am greeted by large numbers of cormorant poop bombs dropped by the dozens of cormorants that seem to find that particular tree to their liking, and this particular canoeist not to their liking. Fortunately, cormorants have bad aim, but unfortunately it is not that bad.

Daniel Natusch and three other researchers wanted to know how an analogous form of nutrient enrichment from large colonies of nesting Metallic Starlings (Aplonis metallica) affects the nearby ecosystem in a tropical Australian rainforest. They were interested in this question because it was obvious that the ground below the nesting colony trees was basically devoid of vegetation; they describe it as “an open moonscape”, contrasting sharply with the thick rainforest nearby. Other studies have shown that nutrient enrichment from bird guano leads to increased vegetation density – so why is this ecosystem different?

Lockerbie Scrub rainforest, in Cape York Peninsula, Australia, showing colony tree with dead zone (left) and a continuous rainforest (right)

Dan Natusch conducts herpetological research with his son Huxley. Credit: Jessica Lyons

The researchers compared the biological, chemical and physical environment underneath 27 different colony trees to the environment underneath a randomly chosen tree 100-200 meters from the colony tree. As expected, they found very little vegetation near colony trees, in contrast to relatively dense vegetation near the randomly chosen trees.

Vegetation cover (left) and number of live stems (right) in relation to distance from the colony or randomly chosen tree (Point 0 on X-axis). Negative numbers are downslope and positive numbers are upslope from the tree.

Soil analyses showed that the soils under the colony trees had much higher concentrations of important nutrients. For example, phosphorus levels were more than 30 times greater, and ammonium nitrogen was about four times greater under colony trees than under the randomly chosen trees. The researchers wondered whether these nutrient levels were so high that they were toxic to vegetation. That would account for the dead zone under the colony trees. An alternative hypothesis is that animals (pigs and turkeys in particular) may be attracted to these high nutrient areas under the colonies, and may either kill germinating plants by eating or trampling them.

: Feral pigs (Sus scrofa) rooting and trampling under a colony tree. Credit Daniel Natusch

To test both hypotheses, at the beginning of the breeding season the researchers covered a portion of the colony tree region with metal cages (exclosures) that prevented turkeys and pigs from gaining access. They discovered a much greater number of seedlings under the exclosures in comparison to the areas where turkeys and pigs could access the seedlings.

natuschfig7 They concluded that nutrient levels were not toxic to seedlings, but that pigs and turkeys were either eating or trampling the seedlings as they emerge. As you can see, the number of exclosure seedlings dropped sharply in July, in part because rainfall declines sharply in June, which leads to high plant mortality, particularly in the unshaded dead zone. But in addition, feral pigs broke into all of the exclosures that summer to access the seedlings and the nutrient-rich soil.

Do these dead zones actually benefit the starlings in any way? One possible advantage is that dead zones prevent snakes from climbing nearby trees and vines to gain access to the nests that are located high in the canopy of the colony tree. However there is good evidence that colony trees suffer high mortality, as 10 of the 27 colony trees died within three years of the study. Trees that fall during the nesting period could lead to the failure of all of the nests within that colony tree.

A scrub python (Morelia amethistina) puts the squeeze on a juvenile Metallic Starling. Credit Daniel Natusch.

Why do we find dead zones beneath colonies of Metallic Starlings, and increased plant growth rate, larger plant size and greater plant diversity beneath the colonies of several other bird colonies? Most previous studies have looked at sea-bird colonies on small islands that have few terrestrial herbivores, so germinating seedlings are relatively undisturbed. This study occurred in a continuous forest in tropical Australia, which harbored a large population of hungry herbivores. These contrasting findings show the important role of environmental context for understanding how ecological interactions will play out. Given that we humans are continually adding nutrients to our environment (through natural bodily function and when we fertilize our fields), we need to carefully consider the biotic and abiotic players in the ecosystem, so we can predict the effects we are having on the environment.

note: the paper that describes this research is from the journal Ecology. The reference is Natusch, D. J. D., Lyons, J. A., Brown, G. P., & Shine, R. (2017). Biotic interactions mediate the influence of bird colonies on vegetation and soil chemistry at aggregation sites. Ecology 98(2): 382-392. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2017 by the Ecological Society of America. All rights reserved.

Fred's Ecology and Environmental Tales (AKA: The FEET)

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