SciELO - Scientific Electronic Library Online

 
vol.72 número2Ensambles de plantas vasculares asociadas a humedales temporales a lo largo del gradiente mediterráneo-templado en Chile índice de autoresíndice de materiabúsqueda de artículos
Home Pagelista alfabética de revistas  

Servicios Personalizados

Revista

Articulo

Indicadores

Links relacionados

  • En proceso de indezaciónCitado por Google
  • No hay articulos similaresSimilares en SciELO
  • En proceso de indezaciónSimilares en Google

Compartir


Gayana. Botánica

versión On-line ISSN 0717-6643

Gayana Bot. vol.72 no.2 Concepción dic. 2015

http://dx.doi.org/10.4067/S0717-66432015000200001 

STANDARD ARTICLES

 

Culture and growth of two benthic diatoms species isolated from the Salar del Huasco (North of Chile, 20° S) at different conditions of temperature, light and nutrient

Cultivo y crecimiento de dos especies de diatomeas bentónicas aisladas del Salar del Huasco (Norte de Chile, 20° S) a diferentes condiciones de temperatura, luz y nutrientes

 

EIMMY E. RAMÍREZ1*, MARIELA A. GONZÁLEZ2, ANA S. CIFUENTES2, INGRID INOSTROZA2 & ROBERTO E. URRUTIA1

1Aquatic Systems Unit/Environmental Science Center EULA-Chile, Universidad de Concepción, Concepción, Chile.
2Botany Department, Universidad de Concepción, Casilla 160-C, Concepción, Chile.

*E-mail: eimmy.ramirez@udec.cl


ABSTRACT

Benthic diatoms are cultured usually under laboratory conditions to be used as a food source for other organisms, of aquaculture interest or for biotechnological applications. Laboratory experiments demonstrate the incidence of the physical and chemical variables on abundance and growth rates of diatoms. While macronutrients are usually selected and dosed into common culture mediums to meet the general requirements of a wide range of diatoms, the availability and optimization of micronutrients are more susceptible to each organism’s particular physiological conditions. The aim of this study was to characterize the growth of two species of benthic diatoms isolated from the Salar de Huasco in batch cultures at different conditions of temperature (10, 15 and 20 °C), light intensity (40, 80 and 120 μmol m-2 s-1) and concentrations of silica (1.06 x 10-4 M Na2 SiO3 x 9H2O and 2.12 x 10-4 M Na2 SiO3x 9H2O) and selenium (10-8 M H2SeO3) in f/2 medium, on a light-dark cycle of 18:6 h. Both Nitzschia epithemioides Grunow in Cleve & Grunow (1880) as Nitzschia sp. showed higher maximum cell densities (692800 ± 107704 and 649600 ± 68942 cells ml-1, respectively) and exponential growth rates (1.80±0.56 and 0.97±0.32 div. d-1, respectively) at the highest temperature (20°C). The light intensity to which the cultures were exposed had no effect on cell density and exponential growth rate in both taxa. Regarding to nutrients, an increase in silicates concentrations on the culture medium could promote the growth of N. epithemioides and Nitzschia sp. since a tendency was observed to higher cell densities (1.08 x 106 ± 84,639 and 1.32 x 106 ± 109,038 cells ml-1, respectively) and exponential growth rates (1.98 ± 0.44 and 0.95 ± 0.18 div. d-1, respectively) with respect at the normal f/2 medium and f/2 medium plus selenium. Simultaneous addition of silicate and selenium to the culture medium increased the maximum cell density of the two strains under study, but this increase was significant (p = 0.05) only for N. epithemioides and among the normal f/2 medium (719200 ± 116895 cells ml-1) and the f/2 medium with double the amount of silicate and selenium (1498800 ± 209599 cells ml-1). However, the exponential growth rates were not significantly different when compared to those of the control (without the addition of silicate and selenium). In conclusion both N. epithemioides and Nitzschia sp. shown an increased cell density and exponential growth rate at 20 °C. The different light intensities not significantly influenced the growth of both taxa. An increase in the concentration of silicates or simultaneous increase in silicates and selenium in the culture medium can be considered as possible strategy to increase cell density of benthic diatom N. epithemioides in batch cultures.

KEYWORDS: Growth characteristics, culture, Nitzschia, selenium, silicate.


RESUMEN

Las diatomeas bentónicas usualmente son cultivadas bajo condiciones de laboratorio para ser utilizadas como fuente de alimento de otros organismos de interés acuícola o para aplicaciones biotecnológicas. Experimentos de laboratorio demuestran la incidencia de las variables físicas y químicas sobre la abundancia y tasas de crecimiento de las diatomeas. Mientras los macronutrientes están generalmente seleccionados y dosificados en los medios de cultivo más comunes para satisfacer los requerimientos generales de un amplio rango de diatomeas, la disponibilidad y optimización de micronutrientes son más susceptibles a las condiciones fisiológicas particulares de cada organismo. El objetivo de este estudio fue caracterizar el crecimiento de dos especies de diatomeas bentónicas aisladas del Salar de Huasco en cultivos tipo batch, a diferentes condiciones de temperatura (10, 15 y 20 °C), intensidad de la luz (40, 80 y 120 μmol m-2 s-1), y concentraciones de sílice (1.06 x 10-4 M Na2SiO3x 9H2O y 2.12 x 10-4 M Na2SiO3x 9H2O) y selenio (10-8 M H2SeO3) en medio f/2, a un ciclo 18:6 h luz-oscuridad. Tanto Nitzschia epithemioides Grunow in Cleve & Grunow (1880) como Nitzschia sp, exhibieron las mayores densidades celulares máximas (692800 ± 107704 y 649600 ± 68942 células mL-1, respectivamente) y tasas de crecimiento exponencial (1,80 ± 0,56 y 0,97 ± 0,32 div. d-1, respectivamente) a la temperatura más elevada (20 °C). La intensidad de luz a la cual los cultivos fueron expuestos no afectó la densidad celular y tasa de crecimiento exponencial en ambos taxa. En cuanto a los nutrientes, un incremento en la concentración de silicatos en el medio de cultivo, podría favorecer el crecimiento de N. epithemioides y Nitzschia sp. ya que se observó una tendencia al aumento en la densidad celular (1,08 x 106 ± 84.639 y 1,32 x 106 ± 109.038 células mL-1, respectivamente) y tasa de crecimiento exponencial (1,98 ± 0,44 y 0,95 ± 0,18 div. d-1, respectivamente) con respecto a los medios f/2 normal y f/2 más selenio. La adición simultanea de silicato y selenio al medio de cultivo aumentó las densidades celulares máximas de las dos cepas bajo estudio, pero este aumento fue significativo (p = 0,05) sólo para N. epithemioides y entre los medios de cultivo f/2 normal (719200 ± 116895 células mL-1) y medio f/2 con el doble de silicato y selenio (1498800 ± 209599 células mL-1). Sin embargo, las tasas de crecimiento exponencial no tuvieron diferencias significativas con el control (sin adición de silicato y selenio). En conclusión tanto N. epithemioides y Nitzschia sp. muestran un aumento en la densidad celular y la tasa de crecimiento exponencial a 20 °C. Las diferentes intensidades de luz evaluadas no influyeron significativamente en el crecimiento de ambos taxa. Un aumento en la concentración de silicatos o aumento simultáneo de silicatos y selenio en el medio de cultivo puede ser considerado como posible estrategia para incrementar la densidad celular de la diatomea bentónica N. epithemioides en cultivos discontinuos.

PALABRAS CLAVE: Características de crecimiento, cultivo, Nitzschia, selenio, silicato.


 

INTRODUCTION

Diatoms are the main microalgal component in biomass and in biodiversity of marine and freshwater aquatic ecosystems, making up a part of phytoplankton and phytobenthos. Their contribution to the global primary production in these ecosystems is highly significant (Round et al. 1990). The communities of benthic diatoms, predominantly pennate, are much more difficult to sample and quantify, because they are strongly adhered to different types of substrates and in varied types of environments; for this reason, biologists and ecologists have largely disregarded them and there is little data available in the literature (Raniello et al. 2007). Nonetheless, benthic diatoms are cultured usually under laboratory conditions to be used as a food source for other organisms, such as abalone and sea urchin (Dunstang et al. 1994) or for biotechnological applications (Stoermer & Smol 1991).
The physiological plasticity of diatoms to environmental factors such as temperature, salinity, light intensity and nutrient concentrations is the keys to their ability to survive and grow in different types of environments (Tomas 1996, Dempster & Sommerfeld 1998, Thessen et al. 2005, Affan et al. 2007). Numerous laboratory experiments demonstrate the incidence of these factors on abundance and growth rates (Méléder et al. 2003, Mercado et al. 2004, Van der Grinten et al. 2005, Affan et al. 2007, Raniello et al. 2007, D’Alelio et al. 2009). Particularly important are the concentrations of silicate (macronutrient) and selenium (micronutrient) in the culture medium for the diatoms (Harrison et al. 1988, Round et al. 1990, Nelson et al. 1995, Tréguer et al. 1995, Raniello et al. 2007). Silicates are essential as a components of the cell wall and as metabolic regulators. In his absence the proteins, DNA, chlorophyll and carotenoid synthesis are inhibited; photosynthesis and glycolysis are reduced; lipid synthesis also can be enhanced and altered by the availability of silicates (Werner 1978, Taguchi et al. 1987, Roessler 1988, Round et al. 1990). The role of selenium in cell function is still unclear. Some evidence suggests that it is important in cell division processes and maintaining internal membrane integrity (Doucette et al. 1987), while it is also an essential part of the enzyme glutathione peroxidase, which protects cells against the destructive effects of hydrogen peroxide (Overbaugh & Fall 1982, Price & Harrison 1988). While macronutrients are usually selected and dosed into common culture mediums to meet the general requirements of a wide range of diatoms, the availability and optimization of micronutrients are more susceptible to each organism’s particular physiological conditions (Keller & Selvin 1987).
Diatoms of the Salar de Huasco, in the northern Chilean Altiplano, are subject to severe changes in physical and chemical environmental variables. The limnic systems in this region are characterized by closed endorheic basins with more evaporation than precipitation (Vila & Mühlhauser 1987, Risacher et al. 2003). It has been hypothesized that due to the expansion and contraction of the lakes of the Altiplano, its aquatic organisms have been subjected to drastic changes in both water levels and composition of salts. This has resulted in aquatic systems with physicochemical characteristics that depend heavily on the availability of water (Chong 1988, Keller & Soto 1998, Risacher et al. 2003). It is likely that both the quality and the quantity of the water determine the biological diversity, its distribution and its ability to be present in this type of systems. The information on the systematics and ecology of benthic diatoms in limnic bodies of the Altiplano is scarce and mostly restricted to contributions with a strong physiographic orientation (Márquez-García et al. 2009).

The aim of this study was to characterize the growth of two species of benthic diatoms isolated from the Salar del Huasco in batch cultures at different conditions of temperature, light intensity and nutrient concentrations. Considering that the water of Salar de Huasco has high concentration of arsenic (ca. 12 mg L-1), the results of this study, among others, will pursue researches to evaluate the ability of these taxa to bioconcentrate and to biotransform inorganic arsenic in to organic compounds that are less toxic.

MATERIALS AND METHODS

SAMPLE SITE
Water and microalgae samples were collected in summer (November, 2012) from Lagoon Huasco, Salar de Huasco, located in the Altiplano (ca. 4000 m altitude), in the north of Chile (20°17’30"S; 68°52’20"W; Fig. 1). Its maximum depth is 40 cm and has unique physiographic and climatic characteristics (Risacher et al. 2003).

PHYSICOCHEMICAL ANALYSES
Water samples were collected in 1 liter polyethylene containers and then after being filtered (0.45 μm), the following parameters were measured: total dissolved solids (TDS), chloride (Cl), sulfate, (So3), hardness (CaCO4), nitrate (NO3), phosphate (PO4), sodium (Na) and potassium (K), according to standardized protocols (APHA, AWWA, WPCF 1992). In situ, measurements of temperature, electrical conductivity, pH, electrical potential and dissolved oxygen were taken using field equipment, WTW Multiline P3. These data were examined to obtain a reference of environmental conditions for growth of diatoms in terms of salinity, temperature, pH and nutrients.

COLLECTION, ISOLATION AND ESTABLISHMENT OF UNIALGAL CULTURE
Lagoon Huasco, with its high elevation, is subject to strong winds, and because the depth at the collection site was not more than 10 cm, it was possible to obtain, by filtering with 20 μm phytoplankton net, microalgae, mix with floating fine sediment. The retained material was deposited in polyethylene containers and transported, cold, to the laboratory. To establish unialgal cultures, the isolation method used was single-cell isolation by micropipette and successive washes, according to the protocol described by Andersen (2005, Chapter 6). Basically, the isolation was performed using well slides (with more than one depression) or directly on drops (of culture medium) placed on a slide (in rows) using an inverted microscope (Nikon TS 100). Using sterile Pasteur pipettes, the algal units were isolated and washed one by one, then deposited in test tubes or Petri dishes with f/2 culture medium (Guillard 1975, pH = 8.00, E.C = 52 mS cm-1, TDS = 33300 mg L-1). Finally non-axenic unialgal cultures of the taxa grew in 250 ml Erlenmeyer flasks (ca.
50 ml culture volume), incubated at 120 μmol photons m-2s-1 (LI-250 Light Meter, LI-COR. U.S.A.), at 20 ± 2 °C and with a L:D cycle of 18:6 h.

FIGURE 1. Map of the geographical location of the Salar de Huasco (modified from Chong, 1988).

FIGURA 1. Mapa de localización geográfica del Salar de Huasco (modificado de Chong, 1988).

 

DIATOM IDENTIFICATION
Taxonomic identification was performed based on the distinctive morphological characteristics of each taxon (Cleve-Euler 1953, Hustedt 1930, Krammer & Lange- Bertalot 1988, 1991, 2000, 2004). The morphology and data on cell dimensions of living diatoms were obtained using an Olympus light microscope (model CX 31. Camera, 518CU 5.0M CMOS). To remove the organic matter of the frustules, small volumes of the culture were washed with acid according to the method proposed by Hasle & Fryxell (1970). The frustules were prepared for a scanning electron microscope (SEM) as described by Amato et al. (2005) and examined under a scanning electron microscope SEM
JEOL JSM6380-LV. The morphology of the frustules were analyzed from photomicrographs taken with a camera (JSM-6830) attached to the SEM microscope.

Strains of benthic diatoms in study were deposited in the Culture Collection of Microalgae, University of Concepción (CCM-UdeC), Chile, under the numbers, CCM-UDEC 296 and CCM-UDEC 297.


EXPERIMENTAL CULTURE CONDITIONS
In order to evaluate growth rate and biomass production of the strains investigated, each taxon was cultured in f/2 + Si medium from Guillard (Guillard 1975). Three culture parameters were tested: temperature (10, 15 and 20 °C), photon flux density (40, 80 and 120 μmol m-2 s-1) and different concentrations of selenium and silicate (Table I). All treatments were maintained on a light-dark cycle of 18:6 h and manual shaking twice a day.
For each strain, 1 x 104 cells ml-1 was inoculated into Erlenmeyer flasks containing 100 ml of culture medium and incubated for 20 days. Four replicates were used. The growth was monitored daily by cell counting (2 ml iodine fixed), under a Zeiss inverted microscope, and using Utermöhl chambers of 1 ml capacity. For this purpose, the samples were sonicated during 20 s. The density of cells per ml was calculated with the following formula:

The specific growth rate (k) defined as the increase in cell density per unit time (Guillard 1973) was calculated according to the following equation:

k [div./day] = 3.322 log (N1–N0)/t1 – t0

Where N and N correspond to the cell density at the beginning (t ) and the end (t ) of the time interval selected between inoculation and maximum cell density, respectively. The average value of the replicates was used for the growth curves of each studied treatment.

STATISTICAL ANALYSES
To determine significant differences between exponential growth rates and cell densities in the different treatments (temperature, photon flux density, and different concentrations of silicate and selenium in f/2 medium), comparisons were carried out using one-way analysis variance (ANOVA), followed by multiple comparisons with a Tukey’s test. A value of p < 0.05 was considered significant. All of the statistical analysis was performed using the software SigmaPlot, version 11.0 (Systat Software Inc.).

 

TABLE I. Physiographic and climatic characteristics of the basin of the Salar de Huasco (Risacher et al. 2003).

TABLA I. Características fisiográficas y climáticas de la cuenca del Salar de Huasco (Risacher et al. 2003).

 

TABLE II. Physical and chemical parameters of water from Lagoon Huasco.

TABLA II. Parámetros físicos y químicos del agua de Laguna Huasco.

 

RESULTS

PHYSICOCHEMICAL ANALYSIS
The in situ measurements of temperature, electrical conductivity, pH, electrical potential, dissolved oxygen and the chemical analysis of the water (Table II), determined that the water was alkaline, saline and its major ions corresponded to sodium, chlorides and sulfates.

DIATOMS IDENTIFICATION
Light microscope (LM) observations for both taxa revealed single cells with an isopolar frustule and bilateral symmetry, with oval, elongated valves, rounded at the polar endings. Generally two chloroplasts per cell were observed (Fig. 2 A, B and F).

Under scanning electron microscope (SEM), it was possible to identify only one taxon at species level. This was Nitzschia epithemioides Grunow in Cleve & Grunow (1880). Its valves were depressed or constrained in the central region (Fig. 2 A-C); cell length 22.97 ± 3.41 μm and width 6.93 ± 1.08 μm; showed fibulae of two types (1) small isodiametrical structures, 9 to 12 in 10 μm (Fig. 2 E), and (2) transversely elongated ribs, some of which pass completely through the valve, 3 to 5 in 10 μm (Fig. 2 D, E). There is a central pair of fibulae farther apart than the others (Fig. 2 E); central raphe endings presented a thickening of the margin (Fig. 2 D).

The other taxon identified at genus level corresponded also to the genus Nitzschia (Fig. 2 F-J), cells were smaller than N. epithemioides: length 12.61 ± 2.54 μm and width 6.06 ± 0.97 μm; raphe system fibulate, usually along the border of the valve, with fibulae that are small and discrete, square or rectangular (Fig. 2 H-J).

GROWTH CURVES AT DIFFERENT TEMPERATURES
For Nitzschia epithemioides, the carrying capacity of the cultures was reached at 18 days of incubation at 10 and 15 °C, and at 16 days at 20 °C (Fig. 3 A). Significant differences (p ≤ 0.05) were found in cell density for the three temperatures tested. The higher maximum cell density was observed at 20 °C (692800 ± 107704 cells ml-1), followed by 15 °C (337200 ± 64351 cells ml-1) and 10 °C (85008 ± 11115 cells ml-1), respectively. All of the pairwise multiple comparison procedures based on the Tukey Test were significant (p = 0.05) for the cultures incubated at 20 and 10 °C and the cultures incubated at 20 and 15 °C. The exponential growth rate (k) was not significantly different among the three temperatures. However, the reported value at 20 °C was approximately double (1.80 ± 0.56 div. d-1), to that reported at 15 and 10 °C (1.09 ± 0.30 and 0.97 ± 0.36 div. d-1, respectively).
For Nitzschia sp. the carrying capacity of the cultures was reached at 18 days of incubation of the evaluated temperatures (Fig. 3 B). Significant differences (p ≤ 0.05) were found in cell density among the three temperatures. The higher maximum cell density was observed at 20 °C (649600 ± 68942 cells ml-1), followed by 15 °C (361900 ± 93734 cells ml-1) and 10 °C (247720 ± 46471 cells ml-1
). All of the pairwise multiple comparison procedures based on the Tukey Test were significant (p = 0.05) among the incubated cultures at 10 and 20 °C. The exponential growth rate (k) was not significantly different among the temperatures evaluated (0.97 ± 0.32, 0.59 ± 0.29 and 0.47 ± 0.07 div. d-1 at 20, 15 and 10 °C).

GROWTH CURVES AT DIFFERENT LIGHT INTENSITIES
Growth curves for Nitzschia epithemioides at 40, 80 and 120 μmol photons m-2 s-1 can be seen in Fig. 4 A. The carrying capacity of the cultures was reached at 16 days of incubation at all photon flux densities evaluated. Although, no significant differences (p≤0.05) were found at 40, 80 y
120 μmol photons m-2 s-1, both in maximum cell density (791200 ± 76114, 692800 ± 107704 and 719200 ± 116895 cells ml-1, respectively) and exponential growth rate (1.73 ± 0.38, 1.80 ± 0.56 and 1.38 ± 0.72 div. d-1, respectively), a tendency is observed at higher cell densities and growth rates of microalgae at lower irradiances.

For Nitzschia sp. the growth curves can be observed in Fig. 4 B. The carrying capacity of the cultures was reached at 18 days of incubation for all photon flux densities evaluated. No significant differences (p≤0.05) were found in maximum cell density among 40, 80 and 120 μmol photons m-2 s-1 (667200 ± 38467, 643800 ± 128640, 709440 ± 128200 cells ml-1, respectively). The exponential growth rate (k) neither showed significant differences (0.77 ± 0.60, 0.87 ± 0.38 y 0.96 ± 0.39 div. d-1, respectively). However, its value tended to increase in the higher irradiances.

FIGURE 2. Cell morphology of Nitzschia epithemioides (CCM-UDEC 196), live cells observed in light microscope (LM). A. Valve view; B. Conectival view; C. Oxidized frustule observed in LM; D. Frustule ultrastructure observed in scanning electron microscope (SEM), external view of valve, E. Internal view of valve. Cell morphology of Nitzschia sp. (CCM-UDEC 297), live cells observed in LM. F. Valve view; G. Conectival view; H. Oxidized frustule observed in LM; I. Frustule ultrastructure observed in SEM, External view of Valve; J. Internal view of Valve.

FIGURA 2. Morfología celular de Nitzschia epithemioides (CCM-UDEC 196), células vivas observadas en microscopía fotónica (LM). A. Vista valvar; B. Vista conectival; C. Frústulo oxidado observado en LM; D. Ultraestructura del frústulo observada en microscopia electrónica de barrido (SEM), vista valvar externa; E. Vista valvar interna; F. Morfología celular de Nitzschia sp. (CCM-UDEC 297), células vivas observadas en LM, vista valvar; G. Vista conectival; H. Frústulo oxidado observado en LM; I. Ultraestructura del frústulo observada en SEM, vista valvar externa; J. Vista valvar interna.

 


FIGURE 3. Growth curves for Nitzschia epithemioides (A) and Nitzschia sp. (B) derived at different temperatures and incubated in f/2 medium at 120 μmol photons m-2 s-1, with a 18:6 h light-dark cycle.

FIGURA 3. Curvas de crecimiento para Nitzschia epithemioides (A) y Nitzschia sp. (B) derivadas a diferentes temperaturas e incubadas en medio f/2 a 120 μmol de fotones m-2 s-1, con un ciclo 18:6 h luz-oscuridad.

 


FIGURE 4. Growth curves for Nitzschia epithemioides (A) and Nitzschia sp. (B) derived at different light intensities and incubated in f/2 medium at 20°C, with a 18:6 h light-dark cycle.

FIGURA 4. Curvas de crecimiento para Nitzschia epithemioides (A) y Nitzschia sp. (B) derivadas a diferentes intensidades de luz e incubadas en medio f/2 a 20°C, con un ciclo 18:6 h luz-oscuridad.

 

EFFECTS OF THE CHANGES IN THE CONCENTRATION OF SILICA AND SELENIUM
For the experiments at different concentrations of silicate and selenium, was selected the higher temperature (20 °C) and photon flux density (120 μmol m-2 s-1), since, in these conditions both taxa showed high cell densities.

For Nitzschia epithemioides the carrying capacity of the culture was reached within 16 days of incubation in normal f/2 medium and within 11 days in the f/2 medium with double silicate, f/2 medium with selenium, and f/2 medium with double silicate and selenium (Fig. 5 A). No significant differences were found in maximum cell density among normal f/2 medium (719200 ± 116895 cells ml-1), f/2 medium with double silicate (1085600 ± 84639 cells ml-1), f/2 medium with selenium (1133200 ± 142255 cells ml-1) and f/2 medium with double silicate and selenium (1498800 ± 209599 cells ml-1). Nevertheless, the multiple comparison procedures from the Tukey Test were significant (p = 0.05) among the f/2 medium with a double concentration of silicate and selenium and the normal f/2 medium. The exponential growth rate (k) was not significantly different among the four treatments (1.38 ± 0.31, 1.98 ± 0.44, 1.48 ± 0.54 and 1.77 ± 0.45 div d-1, respectively).

 


FIGURE 5. Growth curves for Nitzschia epithemioides (A) and Nitzschia sp. (B) cultures incubated in f/2 medium with diferent Na2SiO3 and H2SeO3 concentrations at 20°C and 120 μmol photons m-2 s-1, with a 18:6 h light-dark cycle.

FIGURA 5. Curvas de crecimiento para Nitzschia epithemioides (A) y Nitzschia sp. (B) cultivos incubados en medio f/2 con diferentes concentraciones de Na2SiO3 y H2SeO3 a 20°C y 120 μmol de fotones m-2 s-1, con un ciclo 18:6 h luz-oscuridad.

 

For Nitzschia sp., the carrying capacity of the culture was reached within 18 days of incubation for all concentrations of silicate and selenium evaluated (Fig. 5 B). No significant differences were found for maximum cell density among normal f/2 medium (7094400 ± 128640 cells ml-1), f/2 medium with double silicate (1320400 ± 109038 cells ml-1), f/2 medium with selenium (947520 ± 224525 cells ml-1) and f/2 medium with twice the concentration of silicate and selenium (1401120 ± 296267 cells ml-1), but it was observed that cells increased about twice in the medium with the highest nutrients concentration and normal f/2 medium. The exponential growth rate (k) showed no significant difference among the four treatments (0.91 ± 0.38, 0.95 ± 0.18, 0.72 ± 0.35 and 0.95 ± 0.31 div. d-1, respectively).

 

DISCUSSION

The existing literature on the ecology, taxonomy and cultivation of microalgae of high saline ecosystems in Chile and South America is very scarce. Studies conducted in aquatic systems of the Chilean Altiplano highlight diatoms as the most important algal group in terms of abundance, since they are more tolerant to the high salinities of these systems and, therefore, being the base of the food chain, especially as diet for waterfowl (i.e. flamingos) (Vargas et al. 2004, Márquez-García et al. 2009). Diatom studies conducted in Andean bodies of water in Chile are scarce (Mühlhauser et al. 1995, Cruces et al. 2006, Rivera & Cruces 2008, 2009), due to the difficulty of sampling, the variety of morphological and hydrological characteristics, complexity of the geological patterns of their water bodies, and the wide range of chemical and biological features for these environments. The diatom taxa investigated in these studies are generally epipelics, but some are really planktonic and periphytic. They are found in freshwater, brackish water and marine habitats. Nitzschia epithemioides, one of the species found in lagoon Huasco is a brackish water species, found in muddy habitats (saline lakes and coastal areas), and has a wide geographic distribution. It has been reported in Europe [Romania (Caraus 2002, 2012), Great Britain (Whitton et al. 2003), Germany (Scholz & Liebezeit 2012), Spain (Álvarez Cobelas & Estévez García 1982, Aboal et al. 2003)], Asia [China (Liu 2008), Taiwan (Shao 2003-2014)], North America [New Brunswick (Thaler & Kaczmarska 2009)] and South America [Salar de Uyuni (3650 m), Altiplano, Bolivia (Rumrich et al. 2000, Alvial et al. 2008), Jujuy, Argentina (Maidana et al. 2009)].

The temperature in Andean ecosystems, shows strong daily fluctuations and low average temperature of the water, particularly Lagoon Huasco which exhibited an average temperature of 5 °C (Risacher et al. 2003), in situ water temperature was 12.5 °C (November, summer 2012). Therefore, for laboratory cultures was evaluated as lower temperature, 10 °C, and to increased cell densities and growth rates 15 and 20 °C. Both taxa (N. epithemioides and Nitzschia sp.) exhibited growth rates and cell densities higher at the highest tested temperature (20 °C). These results are consistent with the trend found by other researchers in other benthic diatoms under culture conditions. Admiraal (1977) conducted unialgal cultures of estuarine benthic diatoms, Amphiprora cf. paludosa, Nitzschia cf. dissipata, Navicula arenaria and Nitzschia sigma at different temperatures, obtaining a higher growth rate from 16 to 20 °C for N. arenaria, the other three species obtained high growth rates at 25 °C or above this value. Grinten et al. (2005) studied the growth of the diatom Nitzschia perminuta at different temperatures (7, 15 and 20 °C), finding the highest maximum growth rate at 25 °C (0.65 ± 0.14 div. d-1), followed by 15 °C (0.30 ± 0.10 div. d-1) and 7 °C (0.26 ± 0.03 div. d-1). Scholz & Liebezeit (2012) evaluated the effect of different temperatures in the cultures of 25 species of marine benthic diatoms. Most species isolated reached maximum growth rates at higher temperatures (10 to 35 °C), with a low growth significant and decrease in cell density at temperatures ≥ 30 °C and ≤ 4 °C.

The results reported in this study suggest a good tolerance capacity of diatoms for a range of light among 40 and 120 μmol photons m-2 s-1, since, cell density and exponential growth rate were not affected by light intensity to which the cultures were exposed. Although there were no significant differences (p ≤ 0.05) in the exponential growth rate among irradiances evaluated, N. ephitemioides presented a trend to higher growth rates at the lower photon flux densities (1.73 ± 0.38 and 1.80 ± 0.56 div. d-1, at 40 and 80 μmol photons m-2 s-1, respectively). Instead, Nitzschia sp. exhibited the highest growth rate at 120 μmol photons m-2 s-1 (0.96 ± 0.39 div. d-1). Van der Grinten et al. (2005) reported results with a similar tendency to those found for N. ephitemioides in the diatom Nitzschia perminuta that presented a low increase in cell density at the higher light intensity (200 μmol m-2 s-1), compared to the lower light intensities (40 and 5 μmol m-2 s-1) and a highest maximum growth rate at 40 μmol m-2 s-1 (0.39 ± 0.04 d-1) than at 5 and 200 μmol m-2 s-1 (0.28 ± 0.03 and 0.29 ± 0.02 d-1, respectively). These differences in growth could be attributable to that benthic diatoms are efficient in the use of low irradiances for inorganic assimilation (Rivkin & Putt 1987). On the other hand, Correa-Reyes et al. (2001), isolated several strains of benthic diatoms of the Nitzschia gender in batch cultures under different light conditions and suggest that some strains of bentic diatoms could be cultured under high light irradiance without photoinhibition, which could explain the behavior that we reported in this study for Nitzschia sp. The available scientific information suggests that the saturation light intensity may vary among benthic diatoms species, several authors have speculated about an inherently greater resistance to irradiance stress of microphytobenthic algae. Diatoms intertidal microphytobenthos often are exposed to high radiation, disrupting the ability of the cells to balance the fluctuating supply of light energy with the demands of cellular metabolism and growth, thus exposing the photosynthetic machinery to the risks of over −excitation and oxidative damage. It is therefore likely that benthic microalgal species possess several mechanical and physiological adaptations that enable survival in a highly variable environment (Blanchard & Montagna 1992, Peletier et al. 1996, Kromkamp et al. 1998, Barranguet et al. 1998).

Silicon is an essential element for diatoms, both as structural material and as metabolic regulators, affecting a wide range of cellular processes. The results suggest that an increase in silicates concentrations on the culture medium could promote the growth of N. epithemioides and Nitzschia sp. since a tendency was observed to higher cell densities (1.08 x 106 ± 84.639 and 1.32 x 106 ± 109.038 cells ml-1, respectively) and exponential growth rates (1.98 ± 0.44 and 0.95 ± 0.18 div. d-1, respectively) with respect at the normal f/2 medium and f/2 medium plus selenium. Raniello et al. (2007) conducted experiments to evaluate the effect of different silicate and selenium concentrations on diatom Cocconeis neothumensis, reporting that one of the highest exponential growth rates was observed in f/2 medium with double the amount of silicate (0.85 ± 0.11 day-1). These experimental conditions also provided the highest cell density at saturation (ca. 2,700 cells mm-2).

The results on the effect of selenium in cultures of N. epitemioides and Nitzschia sp. were not significant, but these suggest an increase in the maximum cell density (1133200 ± 142255 and 947520 ± 224525 cells ml-1, respectively) compared to the maximum cell density observed in cultures using normal f/2 medium (ca. 720,000 cells ml-1 for both strains). However, exponential growth rates of both strains did not show a positive increase relative to other nutrient concentrations evaluated. This could be attributed to that despite the importance of selenium for normal development and growth of diatoms, intraspecific and interspecific differences exist for the requirement of selenium in microalgaes. Doblin et al. (1999) reported that there was no change in growth or biomass yields in Chaetoceros cf. tenuissimus cultures after approximately 60 generations, indicating that this diatom species has no selenium requirement, or that its selenium requirement was met by the background selenium levels in the culture medium. This adds to the findings of Harrison et al. (1988) who demonstrated the variable Se requirement within the Chaetoceros genus.

As for the simultaneous addition of silicate and selenium to the culture medium. We observed an increase in the maximum cell density for the two strains under study, although this was only significant (Tukey test) for N. epithemioides and among the normal f/2 medium (719200 ± 116895 cells ml-1) and the f/2 medium with double the amount of silicate and selenium (1498800 ± 209599 cells ml-1). The exponential growth rates were not significantly different in any treatment in both strains. Raniello et al. (2007) report different results for benthic diatom Cocconeis neothumensis indicating that a simultaneous increase of silicate concentration and the presence of selenium in the culture medium results in a loss of the positive effects detected with single nutrient. They argued that a higher SiO32- amount in the culture medium, lead to a decreased uptake of SeO32- by C. neothumensis cells and viceversa. Or occurring a negative interaction between selenium and silicates inside the cell, in the context of diatom physiology, although very limited data has been reported in the literature regarding the metabolic interference between selenium and silicates (Müller et al. 2005). These differences with our results could be attributed to that diatoms have different physiological and metabolic behavior, and to that culture conditions tested by Raniello were not the same of the present study.

In conclusion both N. epithemioides and Nitzschia sp. shown an increased cell density and exponential growth rate at 20 °C. The different light intensities not significantly influenced the growth of both taxa. An increase in the concentration of silicates or simultaneous increase in silicates and selenium in the culture medium can be considered as possible strategy to improve cell density of benthic diatom N. epithemioides in batch cultures.

ACKNOWLEDGMENTS

We thank Dr. Patricio Rivera (Facultad de Ciencias Naturales y Oceanográficas, Universidad de Concepción, Chile) for their help in the taxonomical identification of the diatom species. Thanks also to the group of microalgal research FICOLAB. This work was funded by Fondecyt N° 1120807 and project "CRHIAM /CONICYT/FONDAP/15130015"

REFERENCES

ABOAL, M., J.P. MARÍN & E. ZAFRA. 2003. Control de la calidad biológica de los ríos de Euskadi mediante el uso de microalgas. Campaña de verano 2002. Informe final. 126 pp.

ANBIOTEK S.L. In: M.D. Guiry & G.M. Guiry 2014. AlgaeBase. World-wide electronic publication, National University of Ireland, Galway. http://www.algaebase.org; searched on 16 December 2014.

ADMIRAAL, W. 1977. Influence of light and temperature on the growth rate of estuarine benthic diatoms in culture. Marine Biology 39: 1-9.

AFFAN, A., R. KARAWITA, Y.J. JEON & J.B. LEE. 2007. Growth characteristics and antioxidant properties of the benthic diatom Navicula incerta (Bacillariophyceae) from Jeju Island, Korea. Journal of Phycology 43: 823-832.

ÁLVAREZ-COBELAS, M. & A. ESTÉVEZ-GARCÍA. 1982. Catálogo de las algas continentales españolas. I. Diatomophyceae Rabenhorst 1864. Lazaroa 4: 269-285. In: M.D. Guiry & G.M. Guiry. 2014. AlgaeBase. World-wide electronic publication, National University of Ireland, Galway. http://www.algaebase.org; searched on 16 December 2014.

ALVIAL, I.E., F.J. CRUCES, A.E. ARANEDA, M. GROSJEAN & R.E. URRUTIA. 2008. Estructura comunitaria de diatomeas presentes en los sedimentos superficiales de ocho lagos andinos de Chile central. Revista Chilena de Historia Natural 81: 83-94.

AMATO, A., L. ORSINI, D. D’ALELIO & M. MONTRESOR. 2005. Life cycle, size reduction patterns, and ultrastructure of the pennate planktonic diatom Pseudo-nitzschia delicatissima (Bacillariophyceae). Journal of Phycology 41: 542-556.

ANDERSEN, R.A. 2005. Algal Culturing Techniques. Phycological Society of America, Elsevier Academic Press. Ed. Andersen R.A., Amsterdam. 578 pp.

APHA, AWWA, WPCF. 1992. Métodos normalizados para el análisis de aguas potables y residuales. Preparado y publicado conjuntamente por: American Public Health Association, American Water Works Association, Water Pollution Control Federation. Ed. Diaz de Santos S.A., Madrid, España. 1470 pp.

BARRANGUET, C., J. KROMKAMP & J. PEENE. 1998. Factors controlling primary production and photosynthetic characteristics of intertidal microphytobenthos. Marine Ecology Progress Series 173: 117-126.

BLANCHARD, G.F. & P.A. MONTAGNA. 1992. Photosynthetic response of natural assemblages of marine benthic microalgae to short- and long-term variations of incident irradiance in Baffin Bay, Texas. Journal of Phycology 28: 7-14.

CARAUS, I. 2002. The algae of Romania. Studii si Cercetari, Universitatea Bacau, Biologie 7: 1-694.

CARAUS, I. 2012. Algae of Romania. A distributional checklist of actual algae. Version 2.3 third revision. Bacau: Universitatea Bacau. In: M.D. Guiry & G.M. Guiry. 2014. AlgaeBase. World-wide electronic publication, National University of Ireland, Galway. http://www.algaebase.org; searched on 16 December 2014.

CHONG, G.D. 1988. The Cenozoic saline deposits of the Chilean Andes between 18°00’ and 27°00’ south latitude. In: H. Bahlburg, C. Breitkreuz & P. Geise (eds.), The Southern Andes, vol. 17, pp. 137-151. Lecture Notes in Earth System Sciences.

CLEVE-EULER, A. 1953. Die Diatomeen von Schweden und Finnland. Part II, Arraphideae, Brachyraphideae. Kongliga Svenska Vetenskaps-Akademiens Handligar ser. 4, 3/5: 1-255 pp.

CORREA-REYES, J.G., M. DEL PILAR SANCHEZ-SAAVEDRA, D.A. SIQUEIROS-BELTRONES & N. FLORES-ACEVEDO. 2001. Isolation and growth of eight strains of benthic diatoms, cultured under two light conditions. Journal of Shellfish Research 20: 603-610.

CRUCES, F., R. URRUTIA, O. PARRA, A. ARANEDA, H. TREUTLER, S. BERTRAND, N. FAGEL, L. TORRES, R. BARRA & L. CHIRINOS. 2006. Changes in diatom assemblages in an Andean lake in response to a recent volcanic event. Archiv für Hydrobiologie 165: 23-35.

D’ALELIO, D., A. AMATO, A. LUEDEKING & M. MONTRESOR. 2009. Sexual and vegetative phases in the planktonic diatom Pseudo-nitzschia multistriata. Harmful Algae 8: 225-232.

DEMPSTER, T.D. & M.R. SOMMERFELD. 1998. Effects of environmental conditions on growth and lipid accumulation in Nitzschia communis (Bacillariophyceae). Journal of Phycology 34: 712-21.

DOBLIN, M.A., S.I. BLACKBURN & G.M. HALLEGRAEFF. 1999. Comparative study of selenium requirements of three phytoplankton species: Gymnodinium catenatum, Alexandrium minutum (Dinophyta) and Chaetoceros cf. tenuissimus (Bacillariophyta). Journal of Plankton Research 21: 1153-1169.

DOUCETTE, G.J., N.M. PRICE & P.J. HARRISON. 1987. Effects of selenium deficiency on the morphology and ultrastructure of the coastal marine diatom Thalassiosira pseudonana (Bacillariophyceae). Journal of Phycology 23: 9-17.

DUNSTANG, G.A., J.K. VOLKMAN, S.M. BARRET, J.M. LEROY & S.W. JEFREY. 1994. Essential polyunsaturated fatty acid from 14 species of diatom (Bacillariophyceae). Photochemistry 35: 155-161.

GUILLARD, R.R.L. 1973. Division rates. In: J.R. Stein (eds.), Handbook of Phycological Methods: Culture Methods and Growth Measurements, pp. 289-312. Cambridge University Press, Cambridge.

GUILLARD, R.R.L. 1975. Culture of phytoplankton for feed marine invertebrates. In: W.L. Smith & M. H. Chanley (eds.), Culture of Marine Invertebrate Animals, pp. 29-60. Plenum Press, New York.

HARRISON, P.J., P.W. YU, P.A. THOMPSON, N.M. PRICE & D.J. PHILLIPS. 1988. Survey of selenium requirements in marine phytoplankton. Marine Ecology Progress Series 47: 89-96.

HASLE, G.R. & G.A. FRYXELL. 1970. Diatoms: cleaning and mounting for light and electron microscopy. Transactions of the American Microscopical Society 89: 469-74.

HUSTEDT, F. 1930. Bacillariophyta (Diatomae). In: A. Pascher (eds.), Die Süsswasser-flora Mitteleuropas, vol. 10, pp. 466. Gustav Fischer, Jena.

KELLER, M.D. & R.C. SELVIN. 1987. Media for the culture of oceanic ultraphytoplankton. Journal of Phycology 23: 633-638.

KELLER, B. & D. SOTO. 1998. Hydrogeologic influences on the preservation of Orestias ascotanenesis (Teleostei: Cyprinodontidae), in Salar de Ascotán, northern Chile. Revista Chilena Historia Natural 71: 147-156.

KRAMMER, K. & H. LANGE-BERTALOT. 1988. Bacillariophyceae 2. Teil: Bacillariaceae, Epithemiaceae, Surirellaceae. In: H. Ettl, J. Gerloff, H. Heynig & D. Mollenhauer (eds.), Süsswasserflora von Mitteleuropa. G. Fischer, Jena. 596 pp.

KRAMMER, K. & H. LANGE-BERTALOT. 1991. Bacillariophyceae 3. Teil: Centrales, Fragilariaceae, Eunotiaceae. In: H. Ettl, J. Gerloff, H. Heynig & D. Mollenhauer (eds.), Süsswasserflora von Mitteleuropa, 437 pp. Fischer Verlag, Stuttgart, Germany.

KRAMMER, K. & H. LANGE-BERTALOT. 2000. Bacillariophyceae 3. Teil: Centrales, Fragilariaceae, Eunotiaceae. In: H. Ettl, J. Gerloff, H. Heynig & D. Mollenhauer (eds.), Süsswasserflora von Mitteleuropa, 598 pp. Fischer Verlag, Stuttgart, Germany.

KRAMMER, K. & H. LANGE-BERTALOT. 2004. Bacillariophyceae 4. Teil: Achnanthaceae Kritische Ergänzungen zu Navicula (Lineolatae) und Gomphonema. In: H. Ettl, J. Gerloff, H. Heynig & D. Mollenhauer (eds.), Süsswasserflora von Mitteleuropa, 2(4): 468 pp. Spektrum Akademischer Verlag Heidelberg, Berlin.

KROMKAMP, J., C. BARRANGUET & J. PEENE. 1998. Determination of microphytobenthos PSII quantum efficiency and photosynthetic activity by means of variable chlorophyll fluorescence. Marine Ecology Progress Series 162: 45-55.

LIU, R. 2008. Checklist of biota of Chinese seas. Beijing: Science Press, Academia Sinica. 1267 pp.

MAIDANA, N.I., C. SEELIGMANN & M. MORALES. 2009. Bacillariophyceae del complejo lagunas Vilama (Jujuy, Argentina). Boletín de la Sociedad Argentina de Botánica 44(3-4): 257-271.

MÁRQUEZ-GARCÍA, M., I. VILA, L.F. HINOJOSA, M.A. MÉNDEZ, J.L. CARVAJAL & M.C. SABANDO. 2009. Distribution and seasonal fluctuations in the aquatic biodiversiy of the southern Altiplano. Limnologica 39: 314-318.

MELEDER, V., L. BARILLE, P. LAUNEAU, V. CARRERE & Y. RINCE. 2003. Spectrometric constraint in analysis of benthic diatom biomass using monospecific cultures. Remote Sensing of Environment 88: 386-400.

MERCADO, J.M., M.P. SÁNCHEZ-SAAVEDRA, G. CORREA-REYES, L. LUBIÁN, O. MONTERO & F.L. FIGUEROA. 2004. Blue light effect on growth, light absorption characteristics and photosynthesis of five benthic diatom strains. Aquatic Botany 78: 265-277.

MÜHLHAUSER, H., N. HREPIC, P. MLADINIC, V. MONTECINO & S. CABRERA. 1995. Water quality and limnological features of a high altitude Andean lake, Chungará in northern Chile. Revista Chilena de Historia Natural 68: 341-349.

MÜLLER, W.E.G., A. BOREJKO, D. BRANDT, R. OSINGA, H. USHIJIMA, B. HAMER, A. KRASKO, C. XUPENG, I.M. MÜLLER & H.C. SCHRÖDER. 2005. Selenium affects biosilica formation in the demosponge Suberites domuncula. Federation of European Biochemical Societies 272: 3838-3852.

NELSON, D.M., P. TRÉGUER, M.A. BRZEZINSKI & A. LEYNAERT. 1995. Production and dissolution of biogenic silica in the ocean: revised global estimates, comparison with regional data and relationship to biogenic sedimentation. Global Biogeochemical Cycles 9: 359-72.

OVERBAUGH, J.M. & R. FALL. 1982. Detection of glutathione peroxidases in some microalgae. FEMS Microbiology Letters 13: 371-375.

PELETIER, H., W.W.C. GIESKES & A.G.J. BUMA. 1996. Ultraviolet-B radiation resistance of benthic diatoms isolated from tidal flats in the Dutch Wadden Sea. Marine Ecology Progress Series 135: 163-168.

PRICE, N.M. & P.J. HARRISON. 1988. Specific selenium-containing macromolecules in the marine diatom Thalassiosira pseudonana. Plant Physiology 86: 192-199.

RANIELLO, R., M.M. IANNICELLI, M. NAPO, C. AVILA & V. ZUPO. 2007. Production of Cocconeis neothumensis (Bacillariophyceae) biomass in batch cultures and bioreactors for biotechnological applications: light and nutrient requirements. Journal of Applied Physiology 19: 383-391.

RISACHER, F., H. ALONSO & C. SALAZAR. 2003. The origin of brines and salts in salars: a hydrogeochemical review. Earth Science Reviews 63: 249-293.

RIVERA, P. & F. CRUCES. 2008. Fragilaria capuchina Desm. var. mesogongyla Frenguelli, una diatomea presente en la zona norte de la Cordillera de los Andes (Chile), con comentarios sobre la variabilidad del número de procesos labiados en algunos géneros arafidales. Gayana Botánica 65(2): 131-138.

RIVERA, P. & F. CRUCES. 2009. Diatomeas (Bacillariophyceae) de zonas andinas del Norte de Chile: nueva localidad geográfica para Haloroundia speciosa (Hustedt) Díaz et Maidana. Gayana Botanica 66(2): 280-282.

RIVKIN, R.B. & M. PUTT. 1987. Photosynthesis and cell division by the Antarctic microalgae: comparison of benthic, planktonic and ice algae. Journal of Phycology 23: 223-229.

ROESSLER, P.G. 1988. Effects of silicon deficiency on lipid composition and metabolism in the diatom Cyclotella cryptica. Journal of Phycology 24: 394-400.

ROUND, F.E., R.M. CRAWFORD & D.G. MANN. 1990. The diatoms. Biology and morphology of the genera. Cambridge University Press, New York, 747 pp.

RUMRICH, U., H. LANGE-BERTALOT & M. RUMRICH. 2000. Diatomeen der Anden von Venezuela bis Patagonien/Tierra del Fuego. Iconographia Diatomologica 9: 1-673.

SCHOLZ, B. & G. LIEBEZEIT. 2012. Growth responses of 25 benthic marine Wadden Sea diatoms isolated from the Solthörn tidal flat (southern North Sea) in relation to varying culture conditions. Diatom Research 27: 1, 65-73.

SHAO, K.T. 2003-2014. TaiBNET (Catalogue of Life in Taiwan) http://taibnet.sinica.edu.tw. Taiwan.

TAGUCHI, S., J.A. HIRATA & E.A. LAWS. 1987. Silicate deficiency and lipid synthesis of marine diatoms. Journal of Phycology 23: 260-267.

STOERMER, F. & J.P. SMOL. 1991. The Diatoms: Applications for the Environmental and Earth Sciences. Cambridge University Press, Cambridge. U.K. 484 pp.

THALER, M. & I. KACZMARSKA. 2009. Gyrosigma orbitum sp. nov. (Bacillariophyta) from a salt marsh in the Bay of Fundy, eastern Canada. Botanica Marina 52: 60-68.

THESSEN, A.E., Q. DORTCH, M.L. PARSONS & S. MOSSISON. 2005. Effect of salinity on Pseudo-nitzschia species (Bacillariophyceae) growth and distribution. Journal of Phycology 41: 21-9.

TOMAS, J. H. 1996. Effects of temperature and illuminance on cell division rates of three species of tropical oceanic phytoplankton. Journal of Applied Physiology 2: 17-22.

TRÉGUER, P., D.M. NELSON, A. J. VAN BENNEKOM, D.J. DEMASTER, A. LEYNAERT & B. QUEGUINER. 1995. The silica balance in the world ocean: a reestimate. Science 268: 375-379.

VAN DER GRITEN, E., A. JANSSEN, K. MUTSERT, C. BARRANGUET & W. ADMIRAAL. 2005. Temperature-and light-dependent performance of the cyanobacterium Leptolyngbya foveolarum and the diatom Nitzschia perminuta in mixed biofilms. Hydrobiologia 548: 267-278.

VARGAS, C., P. ACUÑA & I. VILA. 2004. Relación entre la calidad del agua y la biota en la cuenca Salar de Huasco. En: A. Fernández & V. Sánchez (eds.), El agua en Iberoamérica: Experiencias en gestión y valoración del agua, CYTED- XVII, pp. 145-152. Programa Iberoamericano de Ciencia y Tecnología para el Desarrollo, Buenos Aires.

VILA, I. & H. MUHLHAUSER. 1987. Dinámica de lagos de altura. Perspectivas de investigación. Arch. Experimental Biology and Medicine 20: 95-103.

WERNER, D. 1978. Regulation of metabolism by silicate in diatoms. In: G. Bendez & I. Lindqvist (eds.), Biochemistry of silicon and related problems, pp. 149-179. Plenum, New York.

WHITTON, B.A., D.M. JOHN, M.G. KELLY & E.Y. HAWORTH. 2003. A coded list of freshwater algae of the British Isles. Second Edition. In: M.D. Guiry & G.M. Guiry 2014. AlgaeBase. World-wide electronic publication, National University of Ireland, Galway. http://www.algaebase.org; searched on 16 December 2014.


Recibido: 06.01.15
Aceptado: 20.05.15

Creative Commons License Todo el contenido de esta revista, excepto dónde está identificado, está bajo una Licencia Creative Commons