Periphytic algae biomass at different shading levels: an experimental approach

Biomassa de algas perifíticas sob diferentes níveis de sombreamento: uma abordagem experimental

Abstract:

Aim  Light is an essential component in the process of synthesis of organic compounds by photosynthetic organisms. Assuming that a higher level of luminosity would positively influence the production of biomass, we evaluated the influence of different levels of shading on the biomass of periphytic algae, through an experimental study.

Methods  Glass slides were used for this as an artificial substrate for the colonization and succession of algae in Garças Lake, on the upper Paraná River floodplain, and later transferred to nine aquaria. These were divided into three treatments: three without cover (AC), three with 50% shading screens (A50) and three with 80% shading screens (A80). Abiotic variables (pH, conductivity, turbidity, temperature and dissolved oxygen) and biomass were measured every five days for 15 days. The biomass was evaluated using the chlorophyll-a method. Concentrations of total phosphorus, phosphate, total nitrogen, nitrate and ammoniacal nitrogen were evaluated every five days.

Results  There was no significant variation of the biomass over time, however, there is a significant difference between the treatments. The highest biomass was found in the control treatment and the lowest was found in the treatment with 80% shading. The other limnological variables evaluated did not show significant changes over time.

Conclusions  The abiotic variables did not influence the biomass of the phycoperiphyton community, which was influenced only by luminosity. Thus, we conclude that light is a variable with direct influence on the production of periphytic biomass. At low intensity it is a variable that can limit the production of biomass. In high intensity however, it influences by increasing its production.

Keywords:  luminosity; periphyton; experiment; chlorophyll-a

Resumo:

Objetivo  A luz é um componente essencial no processo de síntese dos compostos orgânicos por organismos fotossintetizantes. Acreditando que um maior nível de luminosidade influencia de maneira positiva na produção de biomassa, buscamos avaliar a influência de diferentes níveis de sombreamento sobre a biomassa de algas perifíticas, através de estudo experimental em mesocosmo.

Métodos  Lâminas de vidro foram utilizadas como substratos artificiais para a colonização e sucessão das algas no Lago das Garças, planície de inundação do alto Rio Paraná, durante quinze dias, e posteriormente transferidos para nove aquários. Estes foram divididos em três tratamentos: três sem cobertura (AC), três com telas de sombreamento de 50% (A50) e três com telas de 80% de sombreamento (A80). Variáveis abióticas (pH, condutividade, turbidez, temperatura e oxigênio dissolvido) e biomassa foram mensuradas a cada três dias, durante 15 dias. A biomassa foi avaliada através do método de clorofila-a. A cada cinco dias foram avaliadas as concentrações de fósforo total, fosfato, nitrogênio total, nitrato e nitrogênio amoniacal.

Resultados  Não foi observada uma variação significativa da biomassa ao longo do tempo, entretanto, há uma diferença significativa entre os tratamentos. A maior biomassa média foi encontrada no tratamento controle e a menor foi encontrada no tratamento com 80% de sombreamento. As demais variáveis limnológicas avaliadas não apresentaram mudanças significativas ao longo do tempo.

Conclusões  As variáveis abióticas não influenciaram a biomassa da comunidade ficoperifítica, a qual foi influenciada apenas pela luminosidade. Assim, concluímos que a luz é uma variável com influência direta na produção de biomassa perifítica. Em baixa intensidade, é uma variável que pode limitar a produção de biomassa. Em alta intensidade, no entanto, influencia aumentando sua produção.

Palavras-chave:  luminosidade; perifíton; experimento; clorofila-a

1. Introduction

Light is an essential component in process of synthesis organic compounds by photosynthetic organisms. Its variation influences in different ways all the communities of a trophic web (Hill et al., 1995; Cadwell et al., 1998). Periphytic algae are photosynthetic organisms which contribute greatly to the primary productivity of aquatic ecosystems, and their biomass is present at several levels. (Vadeboncoeur & Steinman, 2002; Guariento et al., 2011).

Periphytic algae constitute a very diversified group of organisms, both morphologically and physiologically. Among the characteristics that distinguish them, we can highlight the different photosynthetic pigments that absorb specific light lengths in the photosynthetic process, forcing the groups to respond in different ways to different intensities (Boston & Hill, 1991). Thus, light can act in different ways on the development of the community of periphytic algae. For example, in low light it can limit the production of biomass of the community (Hill & Fanta, 2008), as it can also lead to a photo-adaptation of these organisms to this type of environment (Hill & Boston, 1991). A high level of brightness can cause increasing productivity (Guasch & Sabater, 1998; Dodds et al., 1996), just as it can also act as a limiting factor, because high levels of light radiation can resulty in photoinhibition, limiting productivity, and even provoke the death of these organisms (Boston & Hill, 1991; Antoine & Benson-Evans, 1983b).

However, in order for periphytic algae to have access to light, some barriers must be crossed. In addition to the fact that part of solar radiation is lost in its passage through the atmosphere through, among other factors (Fontana et al., 2012), the intensity of radiation reaching periphytic algal communities is still affected by the presence of suspended substances in the water, including the shading generated by the riparian forests, by macrophytes and even by the community´s self-shading generated by, for example, pedunculated algae (Hill, 1996; Cattaneo et al., 1998; Vis et al., 2006).

Numerous studies have already been carried out evaluating the influence of light on the communities of periphytic algae. However, many were realized in lotic environments, or in experiments simulating these environments (Wood et al., 2016; Winkworth et al., 2015; Krupek et al., 2014). Thus, there is a shortage of studies for lentic environments. In addition, a large part of the work in this type of environment has been carried out with the objective of evaluating the influence of multiple stressors, not only the light, but many are performed in situ, which makes it difficult to evaluate the factor that actually influence the community (Sanches et al., 2011; Antoine & Benson-Evans, 1983a).

Therefore, it is necessary to carry out more controlled experiments in order to exclude as many factors as possible and, as such, seek to determine more effectively the influence of the desired factor. The objective of this study was to evaluate the influence of different levels of shading on the biomass of periphytic algae through an experimental study carried out in mesocosm simulating a lentic environment. We hypothesize that a higher level of luminosity will promote an increase in the production of photosynthetic biomass (Dodds et al., 1996), because a greater luminous intensity affecting the community of periphytic algae, will promote greater photosynthesis and greater biomass.

2. Material and Methods

The experiment consisted of two stages, one in situ and one in mesocosm, simulating lakes of tropical environments. The two stages occurred in the spring, between October and November 2014. During this period, the weather is predominantly sunny, temperatures rise and rains are sporadic. The tourism in the region is less, reducing the flow of boats, jet skis and fishing activities close to the places where we carry out the experiments.

2.1. Study area

The study area (Figure 1), which was carried out in situ stage, Lake Garças, located in the State of Mato Grosso do Sul, at coordinates 22 ° 43'S and 53 ° 14'W, in the Upper Paraná River floodplain. The plain has an area of about 230 km and is located between the dam of Porto Primavera and the reservoir of Itaipú (Agostinho et al., 2008). Lake Garças is about 2,000 m in length, 150 m wide and has an average depth of 2.5 m. The lake is connected to the Paraná River through a channel about 100 m long.

Figure 1
Location of study area, Lake Garças (Source: Murakami et al., 2009)

2.2. Sampling and analyzed variables (in situ and experiment)

In the first stage of the experiment, glass slides on wood supports were used as artificial substrates for the colonization and establishment of the periphytic algae in the lake (Figure 2). These substrates were placed in a vertical position in relation to the water surface on wooden supports that remained submerged to a depth of approximately 15 cm. The duration of this stage was 15 days, time required for community establishment (Rodrigues & Bicudo, 2001; Murakami & Rodrigues, 2009). The support was placed in the limnetic region of the lake, close to a bank of the macrophyte Eichhornia azurea Kunth.

Figure 2
Artificial substrate used in the experiment (Adapted from Murakami, 2008).

In the second stage, and under the same period, slides were removed from the support, fixed in polystyrene supports, placed into a cooler with ice to be transferred posteriorly to nine aquariums arranged in an open area at the advanced field study base of the Universidade Estadual de Maringá. The aquariums were filled with water from the lake itself, to preserve the characteristics of the environment where the slides were colonized, and each received 24 slides. In the aquariums, the substrates were placed in a vertical position in relation to the water surface and remained submerged to a depth of approximately 10 cm. To maintain oxygenation, aquarium pumps were used. The aquariums were divided into three treatments (Figure 3) at random: three received a cover that generates a light attenuation of about 80% (A80), three received a cover that generates a light attenuation of about 50% (A50) and three were not covered (Control - AC). Sampling of the slides in the aquariums occurred on days 1, 3, 5, 7, 10, 13 and 15. For biomass analysis of each treatment, through the chlorophyll-a method, a slide was randomly sampled from each aquarium.

Figure 3
Random distribution of aquariums.

In the aquaria, on days 5, 10 and 15, water samples were taken to evaluate the following nutrients: total phosphorus, phosphate, total nitrogen, nitrate and ammoniacal nitrogen. Periphytic algae on the plain have a greater influence of these nutrients (Murakami & Rodrigues, 2009). These variables were also measured in the pond prior to transfer to the aquariums. Water samples collected in the aquariums were analyzed in the laboratory. In this analysis we quantified total nitrogen and nitrate (Giné et al., 1980); ammoniacal nitrogen and ammonium (Koroleff, 1976); phosphate and total phosphorus (Mackereth et al., 1978).

In addition to the nutrients, the following variables were measured: pH, conductivity, turbidity, temperature and dissolved oxygen, as well as luminous intensity. These abiotic variables were measured in loco, always in the morning, using portable devices (Digimed and YSI brands), and a light meter (Instrutherm brand) was used for the luminous intensity. Luminous radiation, measured above the water column.

The glass slides removed from the aquaria were scraped with a sheet of steel coated with aluminum foil, and the removed material was filtered on GF/C glass fiber filters, macerated in mortar with acetone (90%) as a solvent and the obtained extract was centrifuged. Then, the supernatant was used to determine the concentrations of chlorophyll-a ex situ by spectro-photometry (Golterman et al., 1978).

2.3. Statistical analysis

To evaluate if shading has a significant effect on periphytic algae productivity, a Factor Variance Analysis and a Post Hoc test, Tukey test at a significance level of 5% was used. The test for homoscedasticity was performed previously (Levene test). To perform this analysis, we used Statistica 7.1 software (StatSoft Inc., 2005).

3. Results

The control treatment was the one with the highest mean value of biomass throughout the experiment (0.233 μg/cm²), followed by treatment with 50% shading (0.149 μg/cm²). The treatment with 80% shading produced the lowest average biomass (0.129 μg/cm²). The highest values of biomass were observed on the 10^th day (0.327 μg/cm²) and on the 15^th day of succession (0.402 μg/cm²) in the control treatment. The lowest values of biomass were observed on the 3^rd day (0.064 μg/cm²), 10^th (0.084 μg/cm²), in the treatment with 80% shading, and on the 13^th day (0.079 μg/cm²) in the treatment with 50% shading.

The Factorial Variance Analysis, at a significance level of 5%, showed that there was no significant variation of the biomass over time (F: 1.38, G.L: 6, p: 0.24). However, there is a significant difference between the treatments (F: 4.05, GL: 2, p: 0.024 - Figure 4), and this difference occurred between the control treatments and with 80% shading according to the Post Hoc test, Tukey test at a significance level of 5% (p: 0.0278).

Figure 4
Variation of the biomass of the periphytic algae in the different treatments (AC: Control Treatment, A50: Treatment with 50% shading, A80: Treatment with 80% shading) over time.

Some variables showed variation between the beginning and the end of the experiment, like conductivity in all the treatments. In the treatment with 50% of shading, there was also a variation in relation to the turbidity. There was a greater variation of turbidity and ammoniacal nitrogen in the treatment with 80% shading (Table 1). Luminous radiation, measured above the water column, can have its results observed in detail in Table 2.

Table 1
Mean values of abiotic variables at the beginning and end of the experiment in the three treatments (Control, Treatment with 50% shading and Treatment with 80% shading).

Abiotic Variables	Day 0	Day 05			Day 15
	Lake	C	A50%	A80%	C	A50%
Temperature (°C)	29.5	27.1	26.1	25.9	25.5	24.7
Dissolved oxygen (mg.L-1)	5.95	7.29	7.33	7.48	7.51	7.42
pH	7.15	7.42	7.14	7.2	7.45	7.39
Conductivity (µS.cm -1)	72.2	67.96	65	64.8	99.8	84.7
Turbidity (UNT)	2.94	1.44	1.96	1.05	1.77	3.02
Total nitrogen (µg.l-1)	102.85	104.11	104.26	107.37	123.75	108.48
Ammoniacal nitrogen (µg/l-1)	24.94	4.72	11.66	17.69	4.64	9.42
Nitrate (µg.l-1)	0.02	0.02	0.02	0.03	0	0
Total phosphorus (µg.l-1)	32.29	22.77	15.30	13.58	24.92	19.38
Phosphate (µg.l-1)	24.12	5.53	5.16	4.67	7.35	6.36

Table 2
Mean values of luminous intensity in the treatments (Control, A50%: Aquarium with 50% coverage, A80%: Aquarium with 80% coverage) throughout the experiment.

Treatments	Light (µmol.m-2.s-1)
	Day 05	Day 10
Control	1484	1543
A50%	852	760
A80%	202	177

4. Discussion

Light is a limiting factor for the productivity of periphytic algae. In our work, we observed that the availability of more light was a determining factor for the increased production of biomass, and the average yield occurred in the treatment with the highest light availability, without cover, which was our control treatment. Higher light availability was also noted as a determinant for the increase of chlorophyll-a in a study conducted in a dark water lentic environment, due to a large amount of dissolved organic material, and so was the main factor regulating periphytic biomass (Sanches et al., 2011). The same was observed in the study conducted in a tropical reservoir, with mesotrophic characteristics, during the dry season. As a result of the higher light incidence, due to the reduction in the percentage of macrophytic bank coverage, there was a greater increase in biomass and periphytic growth (Pellegrini & Ferragut, 2012).

Some studies show that high intensity of light radiation can cause photoinhibition, reducing the production of biomass (Zhao et al., 2018; Wellnitz et al., 1996) but which did not occur in our experiment. This can be explained through our study by the fact that the community has already developed in an environment with high luminosity; the biofilm was already well developed when the substrates were transferred to the aquariums and, thus, the highest luminous intensity was attenuated by the self-shading of the community, protecting the lower layers of the photo-inhibition process, allowing them to produce biomass more efficiently (Hill & Boston, 1991). According to studies carried out by Boston & Hill (1991), photoinhibition in periphytic algae occurs significantly at a light intensity above 1100 μmol.m^-2.s^-1, however, high luminosity was not a factor that generated this process in the evaluated community, because the average value of the light intensity in the experiment did not exceed 1543 μmol.m^-2.s^-1.

There was no significant variation in community biomass over time. The variation on the fifth day of the aquarium experiment, which corresponds to the 20th day of colonization, can be explained by the variation in the community structure that occurs during the succession process, resulting in an increase in biomass, which was also reported in other studies completed in tropical environments (Vercellino & Bicudo, 2006; Pellegrini & Ferragut, 2012).

Light is a limiting resource for periphytic algae as well as nutrients, and can act interactively, where by increasing the supply of one of these limiting resources we find a corresponding increase in demand for another resource (Taulbee et al., 2005). Analyzing the variations between the abiotic components, we can observe that there were no great changes among the treatments during the experiment period, so that the increase or limitation of the light incidence did not affect the nutrient demand significantly.

The largest changes in the abiotic variables occurred at the end of the experiment, mainly with the variables of total nitrogen, conductivity and turbidity. The total nitrogen variable underwent a small change and the easily assimilated forms of nitrogen, such as ammoniacal nitrogen and nitrate (Esteves & Amado, 2011) did not present significant change. This increase did not influence the biomass of the community in this experiment. The increase in conductivity may be related to rain that fell the night before the last day of the experiment. The turbidity increase at the end of the experiment may be related to the mechanical degradation, chemical and/or biological transformations of material present in the environment, and can be considered a controlling factor of the colonization process (Felisberto & Rodrigues, 2012).

Thus, we conclude that light is a variable with direct influence on the periphytic biomass. At low intensity, which may be due to the presence of the macrophyte bank, riparian forests, turbidity of water bodies, for example, it is a variable that can limit the production of biomass. In high intensity however, it influences by increasing its production.

Acknowledgements

We thank the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) for the provision of PhD scholarship to Helivania Sardinha dos Santos and scientific productivity to Liliana Rodrigues.

• Cite as: Santos, H.S. and Rodrigues, L. Periphytic algae biomass at different shading levels: an experimental approach. Acta Limnologica Brasiliensia, 2021, 33, e9

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Edited by

• Associate Editor: Ronaldo Angelini.

Publication Dates

• Publication in this collection
  12 July 2021
• Date of issue
  2021

History

• Received
  23 July 2020
• Accepted
  20 Apr 2021