Ammonium and phosphate removal using batch laboratory cultures by microalgae and cyanobacteria isolated from Costa Rica water bodies

This research analyzed three green microalgae (Scenedesmus sp., Chlamydomonas sp., and Chlorella sp.) and two cyanobacteria (Synechocystis sp. as unicellular strain and Nostoc sp. as filamentous strain) native from Costa Rica to remove high concentrations of ammonium and phosphate. Cultures were exposed for 120 h to initial concentrations of 70 mgL-1 ammonium and 9 mgL-1 phosphate, under constant light intensity of 60 μmol m-2s-1. Chlorella sp. showed the highest growth rate, followed by Chlamydomonas sp. and the cyanobacteria Nostoc sp. In contrast, Scenedesmus sp. and Synechocystis sp. cultures grew less than the other ones. The highest percentage of ammonium removal was achieved with Chlorella sp. followed by Chlamydomonas sp. and Synechocystis sp., then Scenedesmus sp. and Nostoc sp. Microalgae removed totally the initial phosphate concentration within 72 h, while cyanobacteria Synechocystis sp. and Nostoc sp. removed phosphate partially. These microorganisms are promising for wastewater reclamation. Rev. Biol. Trop. 66(Suppl. 1): S83-S91. Epub

Microalgae and cyanobacteria require nitrogen (N) and phosphorus (P) to synthesize nucleotides, amino acids, lipids, and carbohydrates (Dyhrman, 2016).These molecules are needed in energy transfer during metabolic reactions.N can be found in compounds like ammonium (NH 4 + ) or nitrate (NO 3 -) and P can be found in phosphates (PO 4 -3 ) (Glass, Wolfe-Simon, & Anbar, 2009).Microorganisms and plants regularly used NO 3 -, NH 4 + and PO 4 -3 in soils, fresh and oceanic water for many processes.However, high concentrations of N and P can promote water eutrophication which represents a serious ecological problem.Nutrient enrichment has generated blooms of some species of microorganisms like bacteria, cyanobacteria and microalgae, which release toxic compounds that impact ecosystems and biodiversity.High concentrations of NH 4 + and PO 4 -3 in water bodies can be generated by human activities, like domestic waste waters, the intensive use of fertilizers and agro industrial activities (Cai, Park, & Yebo, 2013).In Costa Rica, the main sources of water contamination are organic compounds, fertilizers and industrial sources which produce a high input of NH 4 + and PO 4 -3 in rivers and marine waters (Hidalgo, 2012).
In this work, we present data on the removal capacity of NH 4 -N and PO 4 -3 -P, the growth rates and productivity of three microalgae (Chlorella sp., Scenedesmus sp. and Chlamydomonas sp.) and two types of cyanobacteria, the unicellular type as Synechocystis sp. and the filamentous type as Nostoc sp.isolated from Costa Rican water bodies.

Organisms and culture conditions:
The organisms studied were native strains of microalgae (Scenedesmus sp., Chlorella sp. and Chlamydomonas sp.) and cyanobacteria (Nostoc sp. and Synechocystis sp.) isolated from different waters bodies of Costa Rica.Scenedesmus sp., Chlorella sp. and Synechocystis sp. were isolated from a small polluted creek in Río Azul, San José.Chlamydomonas sp. was found in a secondary treatment oxidation pond operated by the Instituto Costarricense de Acueductos y Alcantarillados in Liberia, Guanacaste.The cyanobacteria Nostoc sp. was isolated from a lagoon in Monteverde, Puntarenas.Cells were maintained in laboratory conditions in BG 11 medium (Rippka, 1988) in glass columns with a 400 ml nutritive medium, at 28 °C, bubbled with a mixture of air/CO 2 (97:3, v/v) and illuminated with cool white fluorescent light at 60 μmol photons m -2 s -1 measured on the surfaces of the cultures.
The culture medium was a synthetic medium (SM), enriched with NH 4 Cl and K 2 HPO 4 to adjust the concentration of NH 4 -N and PO 4 -3 -P to the same level found in Río Azul.The average initial concentrations of NH 4 -N and PO 4 -3 -P in the starting cultures were 70 mgL -1 and 9 mgL -1 , respectively.The pH of the medium was adjusted to 7.0 before sterilization.

Experimental design:
For the experimental set up, cells in the log phase were harvested by means of centrifugation (Beckman Coulter, model Avanti J-26 XP Centrifuge, Brea, CA, USA) and re-suspended in filtered sterile distillate water (three times) to eliminate any traces of BG 11 nutrients.
The experiments were carried out in duplicate 350 mL culture samples in 500 mL Erlenmeyer flasks.The initial dry weight was 200 mgL -1 .Cultures were incubated at a temperature ranging from 24-26 °C in an orbital incubator (New Brunswick Scientific, USA), under 60 μmol photons m -2 s -1 measured on the surface of the cultures with a flat quantum sensor Hansatech model SKP 200.All experiments were carried out under continuous illumination, with constant shaking of 75 RPM and supply of air/CO 2 ratio 97/3, v/v.The starting pH of the cultures was 7.0; it was controlled daily and adjusted to the initial value by adding a diluted solution of HCl.The constant supply of CO 2 and the daily adjustment of the pH to 7 avoid the PO 4 -3 precipitation and NH 4 -N degassing as ammonia (NH 3 ) at high pH.Controls (three replicates) without algal cells were maintained under the same conditions.
Collected data: From each treatment, 10 mL of culture were sampled at 24 h intervals to measure NH 4 -N and PO 4 -3 -P concentrations and culture dry weight.The controls where evaluated daily to detect any loss of NH 4 -N by outgassing or PO 4 -3 -P by precipitation.Cell dry weight determination was carried out on triplicate 5 mL samples.Each sample was filtered through a 0.45 μm pore size pre-weighted glass fiber filters (Whatman, Maidstone, UK) and then dried at 100 °C for two hours.PO 4 -3 -P and NH 4 -N concentrations (mgL -1 ) were determined by using a Photometer (Hanna Instruments: Multiparameter Bench Photometer for Laboratories model HI3200), in accordance with the Standard Methods for the Examination of Water and Wastewater (APHA, 1992).Samples were centrifuged at 6.000 xg for five minutes to separate the algal cells, and care was used to avoid any loss of gaseous ammonia during experiments.
The mean productivity of each batch run, Q x (mg L -1 day -1 ), was calculated as: (X 1 -X 0 ) / t 1 -t 0 where X 1 (mgL -1 ) is the dry weight measured at the time t 1 (day), and X 0 mgL -1 is the dry weight at time t 0 (day).
The total amount of NH 4 -N removal during the experiment, Q N (mgL -1 ), was calculated as: where N o (mgL -1 ) is the initial NH 4 -N concentration and N m (mgL -1 ) is the NH 4 -N concentration remaining in the medium at the end of the experiment.
The total amount of PO 4 3--P removal during the experiment (mgL -1 ) was calculated as: Q P = P o -P m , where P o (mgL -1 ) is the initial PO 4 -3 -P concentration and P m (mgL -1 ) is the PO 4 -3 -P concentration remaining in the medium at the end of the experiment.

Statistical analysis:
The variables were examined using an analysis of variance (ANOVA) with a significance level of p < 0.05.All the analyses were done in IBM SPSS statistics program v. 21.

Growth rate and culture productivity:
Calculation of growth rate over time indicated that no lag phase took place, with the first phase being exponential growth (µ) within 24 h, where all the studied strains showed a maximum growth rate (µ) (Fig. 1).Thereafter, growth rate remained constant followed by a decline at 72 h, except for Chlorella sp. which dropped drastically after 24 h.This strain showed higher growth rate compared to the other cultures (µ = 0.0296h -1 ), while the cyanobacterium Synechocystis sp. had the lowest growth rate (µ = 0.0039h -1 ).Significant differences in growth rates occurred between microalgae and cyanobacteria (p < 0.05) (Fig. 1).Among the microalgae, Chlorella sp.showed the highest average productivity (178.16mg L -1 d -1 ) and among cyanobacteria, Nostoc sp.productivity was higher (85.8mgL -1 d -1 ) compared to that attained with Synechocystis sp.(34.56 mg L -1 d -1 ) (Fig. 2).Nitrogen Removal: Nitrogen removal varied among the strains (p < 0.001) (Fig. 3a), except between the microalgae Scenedesmus sp. and the cyanobacteria Nostoc sp.where removal was similar (p > 0.05) (Table 1).After 24 h of culture, a decrease in its concentration was observed in all the strains (between 5 % and 25 % of the initial NH 4 -N concentration).Chlorella sp.strain reduced the initial NH 4 -N more than the half of the initial concentration within 48 h achieving almost a total removal of NH 4 -N at 120 h (92.25 %).Among the other microalgae, Chlamydomonas sp.performed better than Scenedesmus sp.(37.5 % and 27 %) respectively, while Synechocystis sp.showed a little higher removal of NH 4 -N compared to Nostoc sp.(Table 1).Phosphorus removal: Microalgae removed 100 % of the PO 4 -3 -P at the end of 120 h (p > 0.05), while cyanobacteria had the lowest percentages of removal (p < 0.001) (Table 1).The kinetics of PO 4 -3 -P removal was faster in all microalgae strains.There was a reduction of more than 50 % after 24 h in Chlorella sp. and after 36 h in Scenedesmus sp. and Chlamydomonas sp., with complete PO 4 -3 -P removal within 96 h (Fig. 3b).The cyanobacteria Synechocystis sp.showed a 50 % reduction within 96 h but did not completely remove PO 4 -3 -P (70 %) at the end of the experiment, Nostoc sp.showed the lowest PO 4 -3 -P removal (48.55 %) (Fig. 3b).

DISCUSSION
Ideal candidate algal species for wastewater treatment should present the main following characteristics: 1) able to growth with high concentrations of inorganic nutrients, 2) efficiency to remove the pollutants, 3) high metabolic activity in order to cope with harsh environmental conditions, and 4) high growth rate.Microalgae strains tested in this work, showed better growth than the cyanobacteria one.An initial phase of log growth after 24 h in all the strains followed by a decreased of the biomass accompanied by a pronounced fall in the PO 4 -3 -P concentration, indicated that the growth was strongly affected by the presence of PO 4 -3 -P and NH 4 -N in the medium, especially PO 4 -3 -P, suggesting that the consumption of this ion more than NH 4 -N by algae.
Culture growth depends on different factors such as light intensity, pH, nutrients, carbon dioxide, mixing, and temperature.In wastewater, growth depends in part by the active nutrient uptake of the photosynthetic cells and their transformation into biomass (Voltolina et al., 2005).An excessive cell density could limit the light penetration into the water column and thus reduce the growth, particularly in scarcely mixed cultures.
The mixing of the culture is one of the most important requirements to obtain high productivities of the microalgal biomass (Abalde, Cid, Fidalgo, Torres, & Herrero, 1995); it allows to maintain a homogeneous distribution of nutrients to the cells, prevents sedimentation and allows a more uniform light distribution in the water column.In our experiments, the constant mixing of the cultures favored the productivity of Chlorella sp. and Chlamydomonas sp.strains.Kong, Li, Martínez, & Ruan (2010) and Martínez et al., (2000) reported the agitation of the culture as one important factor in the growing of Chlamydomonas reinhardtii and Scenedesmus obliquus.
However, shaking in cyanobacteria cultures may have had a negative effect on the growth for example of Nostoc sp.This cyanobacterium has gas vacuoles for floating, favoring a better light incidence on the cell surface in absence of mixing.Shaking of the cultures, may represent an obstacle to buoyancy of Nostoc, reducing the possibility for it to capture the light and forsaking growth of cells.Similar findings have been reported by Silva-Benavides & Torzillo (2012) in cultures of monoalgal Planktothrix.Visser, Ibelings, Van Der Veer, Koedood, & Mur (1996), reported reduction in the growth of filamentous cyanobacteria as Aphanizomenon sp., in a lake in mixing conditions.Low pH in the water favored the growth of green algae and diatoms more than cyanobacteria (Shapiro, 1990;Visser et al., 1996).In our case, the pH of the cultures was close to 7.0, a condition that could have promoted the growth of algae more than cyanobacteria, which can to be more abundant in alkaline mediums.
Algal growth was accompanied by a decrease in NH 4 -N and PO 4 -3 -P concentrations in all the cultures, indicating that N and P removal could be mainly due to algal uptake and assimilation.The maintenance of pH 7 during the experiments prevents the conversion of ammonium to ammonia gas which it happens at high pH and phosphate precipitation which it occurs at low pH (Nurdogan & Oswald, 1995;Silva-Benavides & Torzillo, 2012).
The microalga Chlorella sp.showed a bioremoval capacity of almost 93 % of the ammonium, which was considerably higher than what is reported in the literature (Tam & Wong, 1996;Aslan & Karapinar, 2006;Silva-Benavides & Torzillo, 2012).The highest growth rate of this alga suggests that cells can recycle N in proteins into the cells to maintain their growth.Aslan & Karapinar (2006), pointed out that Chlorella vulgaris is able to remove around 50 % of NH 4 -N when the concentration is between 41.8-92.8mgL -1 and the removing efficiency decreased at concentrations over 129 mgL -1 .
Similar trends have been reported in Chlamydomonas in high concentrations of NH 4 -N, as the case of Chlamydomonas acidophila, which removed between 51.0 and 68.0 mgL -1 of NH 4 -N with an initial concentration of 95 and 650 mgL -1 in 240 h (Escudero et al., 2014).In our case, this alga showed a 37 % removal of NH 4 -N.
The microalgae Scenesdemus sp. can remove up to 100 % ammonium when the concentration of this ion is below 40mgL -1 (González, Cañizares, & Baena, 1997;Martínez et al., 2000;Voltolina et al., 2005), but concentrations higher than 100mgL -1 affect their removal capacity (Azov & Goldman, 1982;Godos et al., 2010;Park, Jin, LIm, Park, & Lee, 2010).In our study, the NH 4 -N concentration was 70mgL -1 , which it could have affected the removal of this ion by this alga.The microalga Scenedesmus sp. can use both sources of nitrogen (NO 3 and NH 4 + ) without any preference (Park et al., 2010).González-Garcinuño, Tabernero, Sánchez-Alvarez, del Valle, & Galán (2014) showed that the best growing medium in autotrophic conditions for Scenedesmus abundans was based on NH 4 NO 3 , where the ammonium bioremoval increased if the solution has nitrate.This fact could explain the reduced removal of ammonium by this alga in our study, which the only source of N was from NH 4 Cl.Aslan & Karapinar (2006), report that Chlorella sp.removes PO 4 -3 -P efficiently when its concentration is lower than 7.7mgL -1 , which was similar in our experiment.Given the microalgae cultures exhausted the content in the medium within 48-96 h, we argued that PO 4 -3 -P limited the growth of cultures, principally for Chlorella sp.The growth stops drastically at 24 h of the experiment; it is supposed that the decreasing of PO 4 -3 -P from 24 h could severely reduce the growth rate of this microalga, contrary to Scenedesmus sp. and Chlamydomonas sp. which showed a linear growth during the time of PO 4 -3 -P reduction in the medium.The fast removal pattern of PO 4 -3 -P against NH 4 -N for all the three microalgae has also been reported by Lynch et al. (2015), who found 3.3 times faster phosphate removal against ammonium in Chlorella sp. and Scenedesmus sp.Our study demonstrated that Chlorella sp. and Chlamydomonas sp., the uptake of NH 4 -N and PO 4 -3 -P have contributed to the higher growth and productivity of these microalgae.
The cyanobacteria show less tolerance to high concentrations of NH 4 + than microalgae (Glass et al., 2009;Collos & Harrison, 2014).In cyanobacteria, ammonium is incorporated into carbon skeletons mainly through the glutamine synthetase-glutamate synthase cycle (Herrero, Muro-Pastor, & Flores, 2001) and glutamate synthase (Muro-Pastor, Reyes, & Florencio, 2005).In our study, both cyanobacteria did not show a good performance in the removal either P or N. The majority of the enzymes used by cyanobacteria in N assimilation required several metals as cofactors (Glass et al., 2009).The synthetic medium used in this study was not supplemented with metals, so it could reduce the capacity to uptake ammonium.
Nostoc sp. is more sensitive to ammonium applications than others cyanobacterias in agricultural fields which induce a decrease of pH in the medium (Dai, Deblois, Liu, Jeneau & Qui., 2008).We avoided this negative effect by keeping a neutral pH.In reports with different sources of residual waste water, Nostoc muscurum showed a removal rate of 40 -60 % for PO 4 -3 -P and 20.9 -96 % for NH 4 -N (El-Sheekh, El-Shouny, Osman, & El-Gammal, 2014), similar to our findings.Concerning the assimilation of ammonium by phytoplankton species, cyanobacteria are better competitors than eukaryotic algae (Von Ruckert & Giani, 2004).We would expect a higher removal capacity by Synechocystis sp. and Nostoc sp.against microalgae; however, we did not find this trend, suggesting that conditions other than NH 4 -N concentration could be influenced its uptake.
Nostoc sp., removed the lowest NH 4 -N or PO 4 -3 -P compared with all the strains studied, behaving like a low nutrient removal filamentous strain.This fact has been already observed by Seale, Boraas, & Warren (1987) and Subramanian, Sumathi, & Sivasubramanian (2009).These authors found that the uptake of PO 4 -3 by Nostoc sp. was very low when sodium was not included in the medium solutions as in the present study.
The differences of removal of PO 4 -3 -P and NH 4 -N and the growth of the different microalga and cyanobacteria used in this experiment, suggest that the variations depend on the metabolic condition of the algae, the strain of algae and environmental conditions in the medium.The microalgae Chlorella sp. it is an excellent choice to pursue bioremediation of eutrophic waters with high input of N and P. In terms of removal of PO 4 -3 -P, all the algae, except Nostoc sp.showed an excellent performance compared to other studies (Aslan & Karapinar, 2006).There are some possible strategies to improve bioremediation and growing performance, the use of different sources of N in the medium (Gonzáles-Garcinuño et al., 2014;Lynch et al., 2015) or co-cultures microalgae and cianobacteria (Silva-Benavides & Torzillo, 2012).
The use of these native cyanobacteria strains as filamentous Nostoc sp. and the unicellular Synechocystis sp., together with the green microalgae Chlorella sp., Scenedesmus sp. and Chlamydomonas sp., which are better acclimated to the specific environmental conditions of the country are good candidates to removed N and P compounds derived from urban o agricultural wastewater.The resulting biomass obtained from the bioremediation process, it can be used for different biotechnological applications, like biofertilizers or biofuels production, and these uses of the biomass can also give an economical input decrease the cost of waste water treatment procedures.

Fig. 1 .
Fig. 1. Specific growth rate versus time (h) recorded in cultures of microalgae and cyanobacteria grown artificial medium.

Fig. 3 .
Fig. 3. NH4-N (a) and PO4-3-P (b) removal kinetics attained by the microalgae and cyanobacteria.Data were fitted with a one-phase exponential decay curve.Broken line indicates a 50 % reduction in the initial ammonium and phosphate concentration.