Onward to Manizales

13 Jan 2017

After arriving in Bogota late last night, I awoke to sunshine and the sounds of traffic this morning. In addition to myself and Jaime Escobar, our crew includes Mark Brenner and Jason Curtis from the University Florida, who are here to collect a lake-sediment cores from high-elevation lakes in the paramo. After a breakfast of eggs, fresh fruit, and good coffee we took a taxi across Bogota to a place where we could store the lake coring equipment, as we won’t need it until next week.

My first impression of Bogota was that driving in this city of 9 million people is a terrifying thrilling experience. Although lanes may or may not be marked, any lane delineation is clearly just a suggestion. Vehicles seem to drive wherever they please, weaving in and out of traffic while motorcycles (and there are a lot of them) drive between the cars and trucks. The roads twist and turn and I felt like we were driving in circles at times, even when we weren’t navigating the traffic-merging madness of a roundabout. Jugglers and dancers performed at some of the stoplights, and I couldn’t help but admire them for their bravery, as pedestrians do not appear to have the right-of-way at all. The one piece of advice I received before coming to Colombia was not to drive, and this was definitely excellent advice.

In the early afternoon we flew from Bogota west to Manizales, which is a city of about 400,000 people. The view of the Colombian landscape was fantastic, with mountains covered in coffee and plantains.  Coffee is planted even on the very steep slopes. The flight was a bit bumpy as we dropped into Manizales, and I was glad that I only had a muffin for lunch.

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All made of bamboo.

Our hotel was just outside the city and was very nice with beautiful gardens, wetlands, and a fenced area with several ostriches and a deer. The hotel property backed up against a nature reserve, and the diversity of rain forest vegetation and birds was impressive. I wished I had been able to fit my binoculars into my luggage! It was fun to see a number of floating plants and floating-leaved plants that my EES-386 students will soon know, including abundant Azolla, Salvinia, water hyacinth (Eichhornia crassipes), and water lilies (Nymphaea sp.). Some pictures of the hotel ground are below.

We then drove into Manizales to meet with scientists in the Departamento de Ciencias Geológicas at the University of Caldas. We had a tour of their labs and facilities, and discussed our plans for our exploration of the paramo tomorrow. Several of the geologists will join us in the field.

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Entrance to University of Caldas. Security is paramount in Colombia.

Adventure and Collaboration in Colombia

12 Jan 2017

As I write this, I am flying above the Florida Everglades at night. The contrast between the Miami-Fort Lauderdale region and the adjacent Florida Everglades is quite striking – lines and lines of bright lights to the east and nothing but blackness to the west. Although a century of degradation has led to the largest restoration effort ever attempted, you still have to admire the resistance of this large wetland to human pressure. Shortly, we will continue southward over the Atlantic on our way to South America…

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Bogota, Colombia.

I am on my way to Bogota, Colombia to initiate and develop a new collaboration focused on better understanding the long-term hydrological and ecological history of high-elevation Andean ecosystems. My primary collaborator is Jaime Escobar of the Universidad del Norte in Barranquilla.  Our focus is on the paramo, an extremely biodiverse ecosystem (one of 25 global biodiversity hotspots) located above the tree line and below the permanent snowline in the Andes of tropical South America and the highlands of Costa Rica. Up to 60% of its plant species are endemic, which means they are found nowhere else in the world. Together with the surrounding Andean forest the region is home to 50% of the plant diversity found in mountain ecosystems. In addition to its high conservation value, the paramo and its watersheds store and supply critical water resources to major Andean rivers and cities. High-altitude tropical ecosystems such as the paramo are expected to experience very high rates of temperature change in the coming decades, with stronger and longer dry seasons, yet little is known about the how the hydrology and ecology of these ecosystems may respond to these anticipated changes.

This new collaboration will focus on understanding the ecological and hydrological sensitivity of paramo ecosystems and their watersheds through investigating the long-term environmental history of the region. Lakes and peatlands are scattered across the paramo, and they preserve records of past ecological and hydrological history in their sediments and deposits.  The long-term perspectives provided by these paleoenvironmental reconstructions will potentially help assess climate model projections, anticipate climate-induced ecological and hydrological impacts, and assist in risk assessment and adaptive management efforts.  For the next ten days we will explore the paramo, collecting ecological and paleoecological samples and discussing ideas to further develop our research and educational collaboration.  I’ll be posting updates and pictures as our adventure proceeds…

 

Tweeting from the field. Ecology 2016.

A summary of course-related tweets for EES-152 (Ecology) in Fall 2016.  What fun we have had!

 

State of the forest, 2016

General ecology (EES-152) students have finished resurveying a portion of the Lehigh Experimental Forest, with the goal of assessing changes in tree growth, mortality, and recruitment since 2013. A total of 690 trees were measured from across the forest, representing more than a 1/4 of all trees. In the three years since 2013, 70 of these 690 trees have died and only three new trees have established in the study area.  Data for the dominant tree species are shown in the plot below.

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Tree abundance, mortality, recruitment, and growth rates in the Lehigh University Experimental Forest, 2013-2016. Relative frequency data are from 2013 (M. Spicer, MS thesis 2014) and indicate the percent of each species present (based on a total of 690 trees). Total mortality and recruitment across the time period are shown as percentages. The average increase in basal area of individuals of each species is shown, with the mean value for all species indicated with the vertical dashed line. Total change in basal area for each species, incorporating mortality losses and basal-area gains, is also shown.

We will use these data to discuss the processes controlling forest dynamics as the semester progresses.  However, for now, students should answer the following questions:

  1. The dbh measurements were converted into estimates of area, assuming that each tree was a perfect circle in cross-section. Why do you think basal area was used to compare growth rates among the different species? Why was this expressed as the average change in basal area per tree? What factors might have caused the observed differences in radial growth among species?
  2. What does the pattern of mortality and recruitment suggest about the future of the Lehigh Experimental Forest? What factors might have caused the differences in mortality among species during these two years? What factors might be contributing to the lack of new tree recruitment in the forest?
  3. Assuming the rates of total tree recruitment and mortality are representative of future years, when will there be no trees left in this forest?  In 2013, there were ~2000 trees in the forest. Show your work and describe how you arrived at your estimate.  Do you think it is likely that the trees will really be gone by this time?  Why or why not?
  4. Which species had both very high mortality and very low growth during this time period? Do some research on current threats to this particular species, and summarize your research in a short paragraph.

New invaders in the Lehigh Valley? Or just summer visitors?

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Water hyacinth (Eichhornia crassipes) and water lettuce (Pistia stratiotes) growing in the Lehigh Canal. Most colonies in this picture are water hyacinth, although the light green colony in the middle is water lettuce. (RK Booth, 20 Sep 2016)

Back in June an alligator was found in the Lehigh Canal. Apparently it wasn’t the first one found in the broader Lehigh Valley.

But perhaps just as surprising are a couple of potentially new plant arrivals. Or are they just summer visitors?  Last week I noticed sizable populations of two aquatic plant species, water lettuce (Pistia stratiotes) and water hyacinth (Eichhornia crassipes), in the canal at Sand Island in Bethlehem. Both of these species float unattached on the water surface, like the more common duckweeds, and they often grow in dense mats that make fishing and boating difficult, crowd out other plant species, and alter water chemistry and light penetration. To my knowledge, neither species is confirmed to occur naturalized in Pennsylvania  but it is not uncommon to see them cultivated in backyard ponds (USDA Plants: water hyacinth, water lettuce).

 

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The Lehigh Canal at Sand Island, Bethlehem PA. In September 2016, water lettuce and water hyacinth occurred in scattered colonies along much of the canal length shown in this Google image.

The populations of water lettuce and water hyacinth in the Lehigh Canal consist of scattered colonies extending from about the Hill-to-Hill Bridge (Route 378) east past the New Street Bridge (Fahy Bridge), to about the point where the Sand Island Trail meets the towpath (D&L Trail). The total distance is about a half mile.  The water lettuce appears to cover a slightly greater distance than the water hyacinth, and the plants are generally smaller in height as you head east (downstream) from the Main Street Bridge.

Water lettuce and water hyacinth are tropical or subtropical in origin. The two species have dramatically expanded their range in warmer regions in recent years, where they have cause considerable ecological and recreational impacts. However, given that both species are sensitive to freezing temperatures, they have not not been regarded as major threats in the Northeast. However, some uncertainty about this assumption has emerged in the last several years. For example, a few years ago populations were found in the lower Great Lakes (Adebayo et al. 2010), and resurveys found both species in three subsequent years (Maclsaac et al. 2016), raising concerns about the potential for the establishment of persistent populations in more northerly locations.  Although freezing typically kills individuals of both species they can produce seeds that survive cold temperatures; in fact, water lettuce seeds can still be viable after a few weeks in solid ice (Pieterse et al. 1981).  Maclsaac et al. (2016) suggested that the two species likely persist in the lower Great Lakes due to annual reintroductions by humans (both species are sold for ponds/aquariums), but also noted that at least in the case of water hyacinth, seasonal regeneration from viable seeds may be occurring.

For background, the Lehigh Canal was built in 1827 to transport anthracite coal from the upper Lehigh Valley, and it remained in operation until the early 1940s. Heavy transportation and industrial activity along the canal and river corridor, as well the development of the surrounding Allentown-Bethlehem-Easton region led to numerous environmental problems, including pollution, habitat degradation, the spread of invasive species, and eutrophication of the canal. However, the towpath along the canal is now a natural-area corridor and the old towpath is a great place to bike, run, hike, fish, bird, and observe nature from within the urban and suburban matrix of the Lehigh Valley. Near Sand Island in Bethlehem, the canal itself gets pretty green by mid-summer, as the slow-moving water warms and algae proliferate.  Invasive eurasian water milfoil (Myriophyllum spicatum) and curly-leaf pondweed (Potamogeton crispus) are common submerged plants within the canal, and provide a favorable substrate for filamentous algae.   The habitat is ideal for water lettuce and water hyacinth, except for the fact that it freezes in the winter.

Have these species been in the canal in previous summers? Are these populations persisting, or did this expansion occur just this year?  Perhaps the two species came into the canal with the pet alligator 🙂   Although this was the first time I noticed the two floating species, I don’t frequent this particular area of the towpath often.  Will they reemerge next summer?  Are they producing viable seed? Lots of questions, and certainly something to watch. The observations have been submitted to iMap Invasives, a database of invasive species.

Of course, floating plants are also very good at moving.  Maybe not as fast as an alligator, but fast enough for me to watch a cluster of water lettuce floating down the canal.  Perhaps on its way to Easton?

Literature Cited

Adebayo, A., E. Briski, O. Kalaci, M. Hernandez, S. Ghabooli, B. Beric, F. Chan, A. Zhan, E. Fifield, T. Leadley, and H. MacIsaac. 2011. Water hyacinth (Eichhornia crassipes) and water lettuce (Pistia stratiotes) in the Great Lakes: playing with fire? Aquatic Invasions 6: 91-96. DOI 10.3391/ai.2011.6.1.11.

MacIsaac, H.J., A.P. Eyraud, B. Beric, and S. Ghabooli. 2016. Can tropical macrophytes establish in the Laurentian Great Lakes? Hydrobiologia 767: 165-174. doi:10.1007/s10750-015-2491-y

Pieterse, A. H., L. Delange, and L. Verhagen. 1981. A study on certain aspects of seed germination and growth of Pistia stratiotes L., Acta Botanica Neerlandica 30: 47–57. doi:10.1111/j.1438-8677.1981.tb00386.x

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