Interactions between dominant hydrophytic species of the wetlands of western Mexico mediated by fire and nitrate concentration

 

Interacciones entre especies hidrófitas dominantes de humedales del occidente de México mediadas por el fuego y la concentración de nitratos

 

Wilber Montejo-Mayo¹, Ek del-Val², Mariela Gomez-Romero², Erick de la Barrera², y Roberto Lindig-Cisneros^2,3

 

¹ Facultad de Biología, Universidad Michoacana de San Nicolás de Hidalgo, Morelia, Michoacán, México.

² Centro de Investigaciones en Ecosistemas, Universidad Nacional Autónoma de México. Apartado Postal 27, Admón. 3, Santa María, CP 58091, Morelia, Michoacán, México.

 

Recibido: 17 octubre 2013.
Aceptado: 23 enero 2015.

 

Summary

Wetland plant community dynamics are strongly driven by abiotic factors such as nutrient levels and fire. In wetlands where invasive species are present assessing the role of abiotic factors in plant-plant interactions is fundamental for both understanding community dynamics and management. In this study the interaction between pairs of species was quantified between one non-invasive (Schoenoplectus americanus), one that can become overdominant after human disturbances (Typha domingensis) and one that has an invasive lineage present in North America (Phragmites australis), growing under different nitrate concentrations and subjected to fire. All species responded by increasing growth to nitrate addition, but depending on the species, the response was significant for different variables. Phragmites for height and root biomass, Typha for aerial and root biomass and Schoenoplectus for all variables. Interactions between species were complex and differed between sampling years. For the first year, only the effect of Typha on itself was significant. For the second year, the effect of Typha was negative on Phrangmites, the effect of Schoenoplectus was negative on itself and, the effect of Typha and Phragmites was negative on Typha. The effect of fire was significant for Phragmites and Schoenoplectus, not burned plant were taller. Interactions between plants were altered by fire, the presence of Schoenoplectus benefited the performance of Typha, and the opposite was also true. For early stages of these species growth, the strongest competition occurs between the native species, allowing the invasive to mostly respond to nitrate levels, and fire have a strong effect also on the interactions between the natives and not with the invasive.

Key words: wetland, negative interactions, management, nutrients, ecological restoration.

 

Resumen

La dinámica de comunidades vegetales de humedales está influenciada por factores abióticos, como los nutrimentos y el fuego. En humedales en donde hay especies invasoras, determinar el papel de factores abióticos en las interacciones planta-planta es fundamental para entender la dinámica de la comunidad y para su manejo. En este estudio, la interacción entre pares de especies fue cuantificada entre una no invasora (Schoenoplectus americanus), una que puede volverse sobredominante como consecuancia de disturbios humanos (Typha domingensis) y una que posee un linaje que es invasor en norteamérica (Phragmites australis), las cuales crecieron bajo diferentes concentraciones de nitrato y fueron sometidas al efecto del fuego. Todas las especies respondieron a la adición de nitratos incrementando su crecimiento. Phragmites respondió en altura y biomasa de raíces, Typha en biomasa aérea y de raíces y Schoenoplectus para todas las variables. Las interacciones entre especies fueron complejas y variaron entre años. Durante el primer año, sólo el efecto de Typha en si misma fue significativo. Para el segundo año, el efecto de Typha fue negativo en Phrangmites, el efecto de Schoenoplectus fue negativo en sí mismo y el efecto de Typha y Phragmites fue negativo en Typha. El fuego fue significativo para Phragmites y Schoenoplectus, las plantas no quemadas fueron más altas. Se detectaron efectos del fuego en las interacciones, la presencia de Schoenoplectus benefició el desempeño de Typha, y viceversa. En etapas tempranas, las interacciones más fuertes ocurrieron entre las especies no invasoras, permitiendo a la invasora responder a la concentración de nitratos, y el fuego tuvo su mayor efecto en la interacción entre nativas y no con la invasora.

Palabras clave: humedal, interacciones negativas, manejo, nutrimentos, restauración ecológica.

 

Introduction and methods

Wetland plant communities are complex systems in which abiotic factors can significantly alter its floristic composition (Zedler and Kercher, 2004). Among the most important of these factors are hydroperiod, salinity, and nutrient concentration, especially that of nitrogen and phosphorus (Cronk and Fennessy, 2001). It has been suggested that when wetlands are subjected to changes in the chemical composition of their water supply, particularly in the form of increases in nitrogen concentration, changes can occur in the richness and/or composition of species that can facilitate the domination of the system by invasive species (Cronk, 1995), whether native or exotic (Zedler and Kercher, 2004). Among the native species that present invasive behavior in wetlands many belong to the genus Typha which, in response to increases in nutrient concentration and other human disturbances, can form dense monospecific patches and thus displace other native species (Galatowitsch et al., 1999; Smith et al., 2001; Woo and Zedler, 2002; Levin et al., 2006). Others, such as certain lineages of Phragmites australis (Swearingen and Saltonall, 2010) are particularly aggressive invasives (Rickey and Anderson, 2004; Laegue et al., 2006; Saltonstall and Stevenson, 2007). Phragmites australis is a species considered to be native to Eurasia by some authors without recognizing subspecies (Lot et al., 2013), others (Saltonal et al., 2004) recognize one subspecies that they consider to be native to Canada and the United States of America, Phragmites australis subsp. americanus, and a lineage present from the Southern United States to Central America with uncertain origin, although this last lineage has been proposed as a new species, Phragmites karka (Ward, 2010). Despite the taxonomical discrepancies, an invasive form is recognized, characterized by morphological and population dynamics characteristics, in particular that forms dense clumps that exclude all other plant species (Sweringen and Saltonall, 2010).

To understand the dynamics of the displacement of native species by invasive species in wetlands, it is necessary to quantify the effects of factors, such as nutrient contents or fire, that can modify the interactions between species. The present study is based on observations of the vegetation structure and dynamics in a model system, the spring wetlands of the Mintzita (101°17'47" W, 19°38'43" N: 1930 masl) in the municipality of Morelia, in Michoacán, México (Escutia- Lara et al., 2009a). These wetlands are characterized by a natural zonation consisting of an area dominated by Schoenoplectus americanus close to the edge of the wetland, and a zone dominated by Typha domingensis that conforms to changes in the water level. Between both of these areas, there is a zone in which the two species coexist and where the distributions respond partially to the water level throughout the wetland; however, other factors, such as nutrient concentration and fire also seem to play an important role. Phragmites australis forms dense clumps consistent with those reported for the invasive lineage (Sweringer and Saltonal, 2010) in the wetlands irrespective of the dominant native species. In a previous study, it was found that individuals of T. domingensis in the wetland respond mainly to the addition of nitrogen; S. americanus also responds to increased nitrogen, but also to phosphorus in terms of the accumulation of aerial biomass (Escutia-Lara et al., 2010). The responses of P. australis have not been evaluated in this system but, in other wetlands, it has been reported that this species responds to increases in the concentrations of both nitrogen and phosphorus and also to the interaction of these two nutrients (Boar, 1996; Ennabili et al., 1998; Ehrenfeld, 2003). From field observations in the model wetland (Escutia-Lara et al., 2009a) and from controlled experiments (Escutia-Lara et al., 2009b; Escutia-Lara et al., 2010), it can be suggested that the competitive capacity of P. australis is greater or equal to that of T. domingensis and, in turn, greater than that of S. americanus; however, the magnitude and exact nature of the interactions between these species remains unknown. The objectives of the present study were to quantify the response of these species to different concentrations of nitrate, as this is the macronutrient to which all three species respond most markedly (Escutia-Lara et al., 2010) and to fire, in order to relate this recurring disturbance factor to patterns of species growth.

Rhizomes of the three species were collected at the study site; these were selected to be of similar size at the start of the experiment and were assigned at random to each of the replicates of the experiments described below. Experiments were conducted to quantify the effect of interactions between pairs of species: Typha domingensis, Phragmites australis and Schoenoplectus americanus. Each experimental unit consisted of two plants, either of the same species or of each possible pairing between them. Rhizomes were planted in five liter pots (25 cm high x 16 cm wide) filled with commercial peat. Thirty pots were planted with each one of the six possible species combinations (three with interspecific and three with intraspecific pairs) giving a total of 180 experimental units. In addition, for each species-interaction treatment, the effect of five treatments of fertilization with potassium nitrate (KNO₃) was tested: 0, 0.08, 0.16, 0.24 and 0.32 g/l of cultivation medium. In this way, six replicates were produced for each treatment of the combination of competition x fertilization. Addition of KNO₃ was carried out every 15 days for a period of six months (May to October). During the dry season (February of the following year), 15 pots were chosen at random from each interaction treatment (three for each fertilization X interaction combination of treatments) in order to burn the aerial biomass, while the other 15 were left as a control. In June, all remaining plants were harvested and aerial and root biomass recorded. In order to assess the importance of the interaction between the different species, three response variables were analyzed: plant height, and aerial and root biomass. In the case of same species interactions, the response variable considered was the average value from both plants in each pot. For different species interactions, the variable was measured in the individual of the species on which the effect of the interaction was to be determined. Analysis was conducted with general linear models, considering fertilization as a continuous variable, and the interaction and aerial biomass burning as categorical variables. Tests of hypothesis were carried out to generate ANOVA tables (Crawley, 2007) and to determine the effect of each of the variables and their interactions. All analyses were conducted with the statistical program R (R Development Core Team, 2011).

 

Results

Following burning of the aerial parts of the plants in the second growing season, all species responded to the addition of nitrate and, in some cases, to the interaction treatments and burning. For P. australis, there was a significant response in plant height to the added fertilizer (fig. 1a; F(1,78) = 71.2, P < 0.000001). The effect of the interactions (fig. 1b) was significant (F(2,78) = 6.6, P = 0.002): the intraspecific interaction produced the greatest average plant height (138 cm), followed by the interaction with S. americanus (120 cm) and with T. domingensis (115 cm). Burning of the aerial parts did not affect height in P. australis. In the case of aerial biomass (fig. 1b), significant differences were observed due to the addition of nitrate (F(1,78) = 118.3, P < 0.000001) and to the effect of the interaction (F(2,78) = 6.9, P = 0.002). These followed the same pattern observed in plant height (41 g for intraspecific interaction, 32 g for the interaction with S. americanus and 26 g for the interaction with T. domingensis). Significant differences (F(1,78) = 8.32, P = 0.005) were found with the burning treatment, since greater quantities of aerial biomass accumulated in those plants that had not been burned (36 g), relative to those that had (30 g). Root biomass (fig. 1c) only increased with increased nitrate addition (F(1,78) = 18.4, P < 0.0001).

Schoenoplectus americanus presented a more complex set of responses than P. australis. In terms of height (fig. 1d), this species responded to both nitrate addition (F(1,78) = 99.1, P < 0.000001) and to the interaction with other individuals (F(2,78) = 3.24, P = 0.045), since the plants reached the tallest average height (95 cm) in the presence of P. australis, followed by those grown with T. domingensis (92 cm) and finally by those grown in the intraspecific treatment (86 cm). They also responded to the burning treatment (F(1,78) = 9.1, P = 0.003), with plants that had been burned reaching an average height of 96 cm, while non-burned plants only reached 86 cm. There were also significant effects of the interaction between nitrate addition and burning treatment (F(1,78) = 4.15, P = 0.045), since non-burned plants presented lower rates of height increase than burned plants, with increasing concentrations of nitrates, as reflected in the slopes of the curves. The interaction between competition and burning treatment was also significant (F(2,78) = 5.73, P < 0.004) because the burned plants from the treatment of competition with T. domingensis reached a greater height (104 cm) than any other combination of levels of the two factors while non-burned plants of the same competition treatment were the shortest (80 cm).

Regarding aerial biomass (fig. 1e), S. americanus responded to the addition of nitrate (F(1,78) = 43.1, P < 0.000001) and to competition (F(2,78) = 56.2, P < 0.001), accumulating more biomass in the interspecific treatment with P. australis (4.0g) relative to the other two treatments (2.4 g with T. domingensis and 2.3 g in intraspecific competition). In the burning treatment, more aerial biomass was accumulated in the non-burned plants (3.35 g) than in burned plants (2.5 g). Regarding root biomass (fig. 1f), S. americanus presented the most complex pattern of responses to treatments: there were significant effects of nitrate addition (F(1,78) = 91.0, P < 0.000001), plant-plant interactions (F(2,78) = 8.0, P = 0.0006) and of the combination of factors (F(2,78) = 4.1, P = 0.02), since the intraspecific interaction treatment with fire produced a lower root biomass (4.6 g). Finally, the interaction between the three factors; addition of nitrate, plant-plant interactions and burning was also significant (F(2,78) = 5.5, P = 0.005), as reflected in the slopes of the curves of root biomass as a function of nitrate addition for each combination of the levels of experimental factors.

Typha domingensis responded to fewer factors than the other two species, since for no variable was there a response to the burning treatment. For plant height (fig. 1g), this species responded to the addition of nitrate (F(1,78) = 17.0, P < 0.0001) and to plant-plant interactions (F(2,78) = 18.3, P < 0.000001) since the plants reached greatest height on interaction with S. americanus (137 cm) and presented the shortest height with P. australis (118 cm). Accumulation of aerial biomass (fig. 1h) also responded to nitrate addition (F(1,78) = 12.0, P < 0.0008), and to plant-plant interactions (F(2,78) = 14.5, P < 0.0001), since the plants in intraspecific treatments accumulated the least biomass on average (3 g), followed by plants grown with P. australis (5.8 g) and finally those grown with S. americanus (9.0 g); the accumulation of root biomass only responded to plant-plant interactions (F(2,78) = 7.5, P = 0.001), and followed the same pattern observed in the aerial biomass; 11.8 g in intraspecific competition, 14.1 g with P. australis and 23.9 g with S. americanus).

 

Discussion

The results show, as expected, that all the study species responded positively to the addition of nitrate; however, in the presence of other individuals, performance variables differed depending on species. Interspecific interactions are not important for Phragmites australis and Schoenoplectus americanus since they present the same rates of growth as when they are growing alongside individuals of their own species. For Typha domingensis, the situation is different since intraspecific interactions were more detrimental than interspecific ones. Given that P. australis is invading the wetland, it was expected that P. australis would be a superior competitor to both T. domingensis and S. americanus and would suppress their performance, but this did not in fact occur. The addition of nutrients alone cannot explain the increase in abundance of P. australis in the Mintzita wetland, as nutrients do for other invasive species in other wetlands (Woo and Zedler, 2002). In the case of other species that present invasive behavior, it has been documented that they require anthropogenic disturbances in order to increase their numbers (Jesson et al., 2000; Fireswyck and Zedler, 2007).

In this experiment, the added disturbance is related to the burning of vegetation, a practice that currently takes place in Mintzita (Escutia-Lara et al., 2009a). With this disturbance, the plant response to nutrients remained surprisingly unchanged; the three species grew in line with the increases in nitrate concentration. However, the inter- relations associated with plant-plant inter- actions did change. For burned P. australis plants, interspecific interactions caused diminished growth, since taller and more robust plants were produced when grown in the presence of individuals of the same species. For T. domingensis, the contrary was true as the presence of S. americanus benefited its performance after burning and for S. americanus, the plants most favored were those grown with T. domingensis. The positive effects of ash from S. americanus in the growth of T. domingensis seedlings have been reported (Lopez-Arcos et al., 2012). It therefore appears that competition between these two species is less when growing together and there is a likelihood of fire. The modification of these competitive interrelations by anthropogenic disturbance, reported in previous studies for other wetland species (Woo and Zedler, 2002) as being of benefit to those species with invasive attributes, was not reflected in this experiment. It is worth noting that P. australis is always taller and of greater biomass than the other two species, making it likely in the long term that competition for light becomes a determining factor in its invasion of the site, and therefore this is a factor that must be fully taken into account in any future studies to predict the behavior of this invasive species.

 

Conclusions

The series of experiments indicate that nitrate availability altered the intensity of plant-plant interactions but that fire was more instrumental in altering these, in particular that presence of Schoenoplectus benefited Typha. Since several species of the later genus have shown invasive behavior, this study suggests an additional mechanism that deserves more attention under natural conditions, since the controlled conditions of the experiments undertaken limits its realism.

Finally, fire was a significant factor altering growth for Phragmites and Schoenoplectus, benefiting more the former than the later, therefore, strongest competition occurred between natives, leaving Phragmites, the invasive, free to respond to increased nitrate availability by growing more.

 

Acknowledgements

This work was funded by the Universidad Nacional Autónoma de México through the project PAPIIT IN203608 and CONACYT (SEP-CONACYT-2008-101335).

 

Literature cited

Boar, R.R., 1996. "Temporal variations in the nitrogen content of Phragmites australis (Cav) Trin ex Steud from a shallow fertile lake". Aq. Bot., 55: 171-181.         [ Links ]

Crawley, R., 2007. The R book. John Wiley and Sons, Ltd., USA.         [ Links ]

Cronk, J. K., y M.S. Fennessy, 2001. Wetland Plants: Biology and Ecology. Lewis Publishers. Washington D.C. EUA. 462 pp.         [ Links ]

Cronk, Q.C.B., 1995. Plant Invaders. Chapman and Hall. London, UK.         [ Links ]

Ehrenfeld, J.G., 2003. "Effects of exotic plant invasions on soil nutrient cycling processes". Ecosystems, 6: 503-523.         [ Links ]

Ennabili, A.; M. Ater, y M. Radoux, 1998. "Biomass production and NPK retention in macrophytes from wetlands of the Tingitan Peninsula". Aq. Bot., 62: 45-56.         [ Links ]

Escutia-Lara, Y.; E. de la Barrera, Y. Martínez de la Cruz, y R. Lindig-Cisneros, 2010. "Respuesta a la adición de nitrógeno y fósforo en el crecimiento de Typha domingensis y Schoenoplectus americanus". Boletín de la Sociedad Botánica de México, 87: 93-97.         [ Links ]

Escutia-Lara, Y.; M. Gómez-Romero, y R. Lindig-Cisneros, 2009b. "Nitrogen and phosphorus effect on Typha domingensis Presl. rhizome growth in a matrix of Schoenoplectus americanus (Pers.) Volkart ex Schinz and Keller". Aq. Bot., 90: 74-77        [ Links ]

Escutia-Lara, Y.; S. Lara-Cabrera, y R. Lindig-Cisneros, 2009a. "Fuego y dinámica de las hidrófitas emergentes del humedal de la Mintzita, Michoacán, México". Revista Mexicana de Biodiversidad, 80: 771-778.         [ Links ]

Frieswyk, C.B., y J.B. Zedler, 1997. Vegetation Change in Great Lakes Coastal Wetlands: Deviation from the Historical Cycle. J. Great Lakes Res., 33: 366-38.         [ Links ]

Galatowitsch, S.M.; N.O. Anderson, y P.D. Ascher. 1999. "Invasiveness in wetland plants in temperate North America". Wetlands, 19: 733-755.         [ Links ]

Jesson, L.; D. Kelly, y A. Sparrrow, 2000. The importance of dispersal, disturbance, and competition for exotic plant invasions in Arthur's Pass National Park, New Zealand. New Zealand J. Bot., 38: 451-468.         [ Links ]

League, M.T.; E.P. Colbert, y D.M. Seliskar, 2006. "Rhizome growth dynamics of native and exotic haplotypes of Phragmites australis (common reed)". Estuaries and Coasts, 29: 269-276.         [ Links ]

Levin, L.A.; C. Neira, y E.D. Grosholz, 2006. "Invasive cordgrass modifies wetland trophic function". Ecology, 87: 419-432.         [ Links ]

Lopez-Arcos, D.; M. Gomez-Romero, R. Lindig-Cisneros, y P.H. Zedler, 2012. "Fire-mobilized nutrients from hydrophyte leaves favor differentially Typha domingensis seedling growth". Env. Exp. Bot., 78: 33-38.         [ Links ]

Lot, A.; R. Medina Lemos, y F. Chiang, 2013. Plantas acuáticas mexicanas: Una contribución a la flora de México. vol. I, Monocotiledóneas. Instituto de Biología. Universidad Nacional Autónoma de México.         [ Links ]

R Development Core Team, 2011. "R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing". Vienna, Austria. ISBN 3-900051-07-0. URL: http://www.R-project.org.         [ Links ]

Rickey, M.A., y R.C. Anderson, 2004. "Effects of nitrogen addition on the invasive grass Phragmites australis and a native competitor Spartina pectinata". J. Appl. Ecol., 41: 888-896.         [ Links ]

Saltonall, K.; P.M. Peterson, y R.J. Soreng, 2004. "Recognition of Phragmites australis subsp. americanus (Poaceae:Arundinoideae) in North America: Evidence from morphological and genetic analyses". Sida, 21: 683-692.         [ Links ]

Saltonstall, K., y J.C. Stevenson, 2007. "The effect of nutrients on seedling growth of native and introduced Phragmites australis". Aq. Bot., 86: 331-336.         [ Links ]

Smith, S.M.; S. Newman, P.B. Garret, y J.A. Leeds, 2001. "Differential effects of surface and peat fires on soil constituents in a degraded wetland of the Northern Florida Everglades". J. Environ. Qual., 30: 1998-2005.         [ Links ]

Swearingen, J., y K. Saltonstall, 2010. "Phragmites Field Guide: Distinguishing Native and Exotic Forms of Common Reed (Phragmites australis) in the United States". Plant Conservation Alliance, Weeds Gone Wild.http://www.nps.gov/plants/alien/pubs/index.htm.         [ Links ]

Ward, D.B., 2010. "North America Has Two Species of Phragmites (Gramineae)". Castanea, 75: 394-401.         [ Links ]

Woo, I., y J.B. Zedler, 2002. "Can nutrients alone shift a sedge meadow towards dominance by the invasive Thypa X glauca?". Wetlands, 22: 509-521.         [ Links ]

Zedler, J.B., y S. Kercher, 2004. "Causes and Consequences of Invasive Plants in Wetlands: Opportunities, Opportunists, and Outcomes". Critical Revies in Plant Sciences, 23: 431-452.         [ Links ]