Effect of Resource Indulgence on Aquatic Vascular Plants: A Closer Study of Lemna minor

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ESSAI Volume 12 Article 30 Spring 2014 Effect of Resource Indulgence on Aquatic Vascular Plants: A Closer Study of Lemna minor Ashley Padavonia College of DuPage Follow this and additional works at: http://dc.cod.edu/essai Recommended Citation Padavonia, Ashley (2014) "Effect of Resource Indulgence on Aquatic Vascular Plants: A Closer Study of Lemna minor," ESSAI: Vol. 12, Article 30. Available at: http://dc.cod.edu/essai/vol12/iss1/30 This Selection is brought to you for free and open access by the College Publications at DigitalCommons@COD. It has been accepted for inclusion in ESSAI by an authorized administrator of DigitalCommons@COD. For more information, please contact koteles@cod.edu.

Padavonia: Effect of Resource Indulgence on Aquatic Vascular Plants Effect of Resource Indulgence on Aquatic Vascular Plants: A Closer Study of Lemna minor by Ashley Padavonia (Biology 1152) Abstract P lants make up a vast majority of life on planet Earth and have been a very successful kingdom since their first appearance 450 million years ago. There are many different species that grow rapidly with various adaptations to be successful in their environments. We decided to test the growth rate and life span of Lemna minor, an aquatic vascular plant that produces mostly asexually, and created an experimental group of Lemna plants that received a fertilizer treatment. We also decided to test the effect of CO 2 concentration on Lemna due to the recent concerns on how much harm the rising CO 2 levels are causing in the biosphere. The Lemna experimental group with fertilizer treatment exhibited the least growth rate as compared to the control group and CO 2 seemed to have little significant effect on the Lemna minor. Further study needs to be conducted in order to definitively state that Lemna benefits negatively from fertilizer treatment or has an increased resistance to rising CO 2 levels. Keywords: Lemna minor, population growth, fertilizer, CO 2 levels, nutrient availability Introduction Lemna minor, also known as duckweed, is a successful aquatic vascular plant species that is found in fresh water ponds throughout North America, Africa, Asia, and Europe. Like many other plants, Lemna minor requires specific nutrients and while it is successful, it must compete with numerous other plants as well as animals in order to survive in its environment and has evolved into a highly competitive species. Some of the earliest experiments with duckweed examined its competitive nature and in a study in 1969 comparing Lemna minor with algae and phytoplankton it was discovered that, Observations made of laboratory cultures and field populations of aquatic weeds and filamentous green algae have confirmed that antagonistic activity exists between such populations when aquatic weeds or filamentous green algae are nitrogen-limited (Fitzgerald 1969). When the duckweed was in an environment with nitrogen-fixing bacteria and algae, two of its top competitors, the duckweed attempted to absorb as much nitrogen as possible in order to significantly increase reproduction and reduce competition. As a result the population of the bacteria and the filamentous algae suffered severely. Ecologists use population growth models in order to assess a particular plant species and determine how it interacts with the environment. Generally, when resources are limited and the competition is fierce, one species thrives and others suffer negatively and in extreme cases can become extinct from a habitat. The growth curve of the duckweed can be described as exponential because its population nearly doubles over time due to its great ability to beat its competitors. In a recent study of vascular epiphytes, non-parasitic plants that grow on their hosts, their ability to retrieve nutrients in dilute as well as in concentrated solutions, Vascular epiphytes possess effective mechanisms to take up potassium from both highly diluted and highly concentrated solutions, enabling the plant to incorporate this nutrient element quickly and almost quantitatively (Winkler et. al 2010). In their conclusion, Winkler and Zotz applied their findings to other nutrients that epiphytes required, such as CO 2 and sunlight, as well as other highly adapted plants such as aquatic weeds. In an article written by Brian Moss of the University of Liverpool the effects of atmospheric changes on plant growth due to global warming are discussed. Plants take in CO 2 required for survival through openings in the leaf called stomata, which close when too much Published by DigitalCommons@COD, 2014 119 1

ESSAI, Vol. 12 [2014], Art. 30 CO 2 is present in the atmosphere (Moss 2010). In a sense, the effect of increased CO 2 has a similar effect on plants as increased oxygen does to humans. A slight increase may foster productivity in growth but too much of an increase can cause a plant to become malnourished and suffocate. Plenty of research has already been done on how duckweed handles nutrient deprivation but it remains to be seen how this plant handles and excess. In order to test how Lemna minor would fare in an environment with enriched nutrients, we conducted an experiment in which some duckweed plants received excess CO 2 and some received excess CO 2 and water. Because of Lemna minor s adaptable nature I hypothesize that an enriched atmosphere of CO 2 and fertilizer treatment, will cause a marked increase in the growth of the duckweed exposed to each treatment and that plants that are exposed only to a fertilizer treatment will outperform the plants with no fertilizer and those that are only exposed to increased CO 2 levels. Materials and Methods In order to test the two points of our hypothesis we created two experimental groups from the Lemna minor plant fronds (duckweed). One group was exposed only to enriched CO 2 levels and the other was exposed to enriched CO 2 as well as the fertilizer treatment. A group of lemna that was not given fertilizer was kept at normal atmospheric CO 2 levels in order to function as out control group. Each experimental group was prepared by placing approximately three duckweed fronds into test tubes fifteen cm long in length. The tubes were then filled with filtered pond water, from a pond on site where Lemna was known to grow, and each sample was labeled. Next, half of the duckweed frond tubes were given the liquid fertilizer treatment diluted to 140 ppm. We decided to test each group s progress in an environmental chamber to eliminate the appearance of unwanted variables. Both experimental groups were exposed to an enhanced CO 2 atmosphere level of 800ppm. Each was exposed to a light level of 8000 lumens/m 2 for duration of twelve hours, along with twelve hours of darkness, for approximately two weeks. The temperature during light exposure was maintained at 25 C, and during darkness at 23 C. At the end of the duration, each test tube s frond count was counted and the experimental groups were compared by plotting the mean number of fronds for each group and then calculating the average maximal growth rate to determine if there was indeed an increase in the experimental group that had the fertilizer treatment. Results Following the described procedure, we tested three experimental groups, Lemna with fertilizer treatment, Lemna in an enriched CO 2 environment, and Lemna with fertilizer treatment and in an enriched CO 2 environment, along with a control group with no treatments. In the control group, the greatest number of fronds occurred on day 10 with an average of 6.2 per test tube. The greatest amount of growth was occurred between days 7 and 8 when the mean number of fronds jumped from 4 to 5.3 and death did not occur until day 13 which can be observed in the population growth curves in Figure 1. The intrinsic rate of growth for this population was calculated to be 0.081. When comparing the control with the Lemna fronds that received fertilizer treatment, the control group outperformed significantly which can be observed through Figure 1. In the Lemna with the fertilizer treatment the greatest amount of growth was observed between days 2 and 3 when the mean number of fronds went from 3.0 to 3.3 and by day 6 a decrease in the amount of fronds began to occur. The intrinsic rate of growth was calculated to be 0.048. The ph of the fertilized pond water was taken and there was no significant change from the untreated pond water. The experimental Lemna group that received CO 2 performed identically to the control group that received no treatments. The greatest amount of growth was observed between days 7 and 8 when the mean number of fronds also grew from 4 to 5.3. The intrinsic growth rate was calculated to be the same, 0.081, and when comparing Figure 1 and Figure 2, the population curves are also identical. The Lemna group that received the fertilizer and CO 2 treatments performed identically to the Lemna that received just fertilizer treatments and also had an intrinsic rate of growth of 0.048. At the end of the experiment, a significant amount of algae was observed in all tubes that contained fertilizer. http://dc.cod.edu/essai/vol12/iss1/30 120 2

Padavonia: Effect of Resource Indulgence on Aquatic Vascular Plants Discussion The proposed hypothesis was that the Lemna minor group with increased CO 2 treatments as well as fertilizer treatment would show the largest growth rate and that the experimental group that received only CO 2 and the control group would show the poorest growth rate. The results from the experiment did not support the hypothesis. The control group seemed to perform the best because it had the highest intrinsic growth rate and death was not observed until day 13. The Lemna that received the fertilizer treatments actually showed the least amount of growth and exhibited frond death as early as day 6 which seems inconsistent with fertilization of similar plants. However, the fertilizer treatments seemed to facilitate the unforeseen growth of aquatic algae in the test tubes. As observed in Fitzgerald s study with algae and aquatic weeds, the algae and Lemna minor grew in a limited space, and even though fertilizer was provided, a competition still arouse between the two organisms, and the Lemna became malnourished (Fitzgerald 1969). A possible change in procedure to improve future results would be the use of distilled water, instead of the use of filtered pond water, to eliminate the possibility of microorganisms competing for nutrients in the experimental Lemna systems. The enriched CO 2 environment of 800 ppm seemed to have no effect at all on the growth of the Lemna populations even though it was almost double the control value of 450 ppm. These results also do not support the hypothesis. According to the study conducted by Brian Moss that appeared in Freshwater Biology, a significant increase in CO 2 may increase growth initially in aquatic species but after long term increased exposure would affect the plant detrimentally. Based on these previous experiments, it is determined that the increased concentration of CO 2 was not significant enough to have a pronounced effect on the population growth of Lemna minor. These results show that Lemna minor must have an increased tolerance to excess CO 2 environments. Although this discovery requires further study, future findings could be useful in the field of agronomy. Perhaps these genes can be isolated from the Lemna minor plants and applied to other plant genera in order to increase resistance in plants that are very susceptible to the increased presence of CO 2 in our atmosphere today. Literature Cited Fitzgerald, George P. (1969). Some Factors in the Competition or Antagonism Among Bacteria, Algae, and Aquatic Weeds. Journal of Phycology 69: 351-359. Moss, Brian. 2010. Climate change, nutrient pollution and the bargain of Dr. Faustus. Freshwater Biology 55: 175-187. Winkler, Uwe, Zotz, G. 2010. And then there were three : highly efficient uptake of potassium by foliar trichomes of epiphytic bromeliads. Annals of Botany 106: 421-427. Published by DigitalCommons@COD, 2014 121 3

ESSAI, Vol. 12 [2014], Art. 30 Figure 1 Fi Figure 2 http://dc.cod.edu/essai/vol12/iss1/30 122 4