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Plankton crustaceans in bays with different trophic status in Llanquihue lake (41[degrees] S Chile)/ Crustaceos planctonicos crustaceo em baias com estado trofico diferente no lago Llanquihue (41[degrees] S Chile).

1. Introduction

The called Araucanian or Nord Patagonian lakes are located in Argentina and Chile between 38-41[degrees] S, these lakes are characterized by their oligo or oligomesotrophic status, and glacial origin (Thomasson, 1963). These lakes have low zooplankton species number with marked higher calanoid abundance compared to daphnids in oligotrophic status which can observed under oligomesotrophic status (Modenutti et al., 1998; De los Rios-Escalante, 2010).

These lakes located in Chile has marked human intervention due to changes in their surrounding basins, because the original native forest was replaced by towns, agricultural, and industrial activities, with consequent nutrient inputs (Soto, 2002). These increases were accentuated during the last three decades (Woelfl et al., 2003), and generate changes in zooplankton composition. In the last decades it was found an increase in species number, daphnids percentage and low calanoid percentage (De los Rios-Escalante, 2010).

In some lakes with small bays it was found different gradient of trophic status due nutrients inputs associated to presence/absence of human intervention, such as was observed for Llanquihue lake (Soto, 2002). The effects of these alterations in trophic status on zooplankton assemblages were previously described (De los Rios, 2003), and it was reported preliminary an increase of daphnids abundance in bays with towns or aquaculture activities. The aim of the present study is to analyze the zooplankton assemblages in different bays of Llanquihue lake in order to determine the potential role of nutrient and chlorophyll concentration on distinct zooplankton groups abundance.

2. Material and Methods

Th sampling sites were visited once, between December 2001 and March 2002. These sites correspond to different bays in Llanquihue lake with towns, aquaculture and with absence of marked human intervention (Figure 1; Table 1). Nutrient and chlorophyll samples were taken for each site and analyzed according to Wetzel and Likens (1991). Zooplankton samples were taken using 20 m vertical hauls with a plankton net of 20 cm diameter and 100 pm mesh size, and fixed with ethanol absolute. For analysis were considered the following groups daphnids (Daphnidae family), other cladocerans (Sididae and Bosminidae family), calanoids (Centropagidae and Diaptomidae) and cyclopoids. Specimens were identified with help of specialized literature (Araya and Zuniga, 1985; Reid, 1985; Bayly, 1992).

2.1. Data analysis

Data on nutrients and chlorophyll concentrations, daphnids, cladocerans, calanoid and cyclopoids percentages were analyzed using Statgraphics Centurion software, in order to determine the grouping variables, using a principal component analysis (PCA). In a second step, the Checkerboard score ("C-score") was calculated, which is a quantitative index of occurrence that measures the extent to which species co-occur less frequently than expected by chance (Gotelli, 2000, 2001). A community is structured by competition when the C-score is significantly larger than expected by chance (Gotelli, 2000, 2001). Finally, the co-occurrence patterns were compared with null expectations via simulation. Gotelli and Entsminger (2007) and Gotelli (2000) suggested the following robust statistical null models: (1) Fixed-Fixed: in this model the row and column sums of the matrix are preserved. Thus, each random community contains the same number of species as the original community (fixed column), and each species occurs with the same frequency as in the original community (fixed row). (2) Fixed-Equiprobable: in this algorithm only the row sums are fixed and the columns are treated as equiprobable. This null model considers all the samples (columns) as equally available for all species. (3) Fixed-Proportional: in this algorithm the species occurrence totals are maintained as in the original community, and the probability that a species will occur at a site (column) is proportional to the column total for that sample. The null model analyses were performed using Ecosim version 7.0 software (Gotelli and Entsminger, 2007; Tiho and Josens, 2007; Tondoh, 2006).

Finally, the available data was ordered for apply species richness estimation considering presence/absence data using the software SPADE with the aim of understanding the community properties (Chen and Chen, 2010), considering k = 3 as limit number for rare species because the crustacean zooplankton in southern Patagonia exhibits low species number (De los Rios-Escalante, 2010).

3. Results

The results shown in Table 1 denote the association of oligo-mesotrophic status with high daphnids percentage in sites near to towns and bays with aquaculture activities. Conversely, in zones without human intervention it was observed low nutrients and chlorophyll concentration and low daphnids abundances. The species reported revealed that Daphnia pulex occurred in many aquaculture and towns sites, whereas Ceriodaphnia dubia was present in practically all sites, similar to Boeckella gracilipes. Whereas Tumeodiaptomus diabolicus was present only in two aquaculture sites, Neobosmina chilensis occurred mainly in less polluted sites, and finally Mesocyclops araucanus was present mainly in mesotrophic sites (Table 1).

The Pearson index correlation matrix generated by PCA shows direct significant correlations between dissolved inorganic nitrogen and reactive soluble phosphorus, daphnids percentage with chlorophyll "a" concentration", daphnids percentage with cyclopoids percentage and nitrogen/phosphorus molar ratio with cyclopoids abundance, species number with N/P ratio, and daphnids with cyclopoids percentages. It was found significant inverse associations between calanoids percentage with daphnids and other cladocerans percentage (Table 2). The main variables correlated to the first axis were species number, daphnids and cyclopoids percentage and chlorophyll concentration. The main variables correlated to the second axis were total inorganic nitrogen, soluble reactive phosphorus and calanoid percentage (Table 3). The results of PCA revealed the presence of two main groups, one representing sites with low nutrient and chlorophyll concentrations and high calanoid percentage (Ensenada, Venado, Volcanes and Puerto Octay bays), and a second group with moderate to high nutrient and chlorophyll concentrations and moderate to high daphnids percentage and low calanoids percentage (Llanquihue, Puerto Phillippi and Puerto Chico Bays), and a third site corresponding to Puerto Rosales bay, an isolated eutrophic bay with high daphnids percentage (Figure 2).

The results of the co-occurrence null model analysis revealed the presence of regulator factors only for fixed-fixed model (Table 4), that would partially agree with the results of PCA analysis of strong driving force acting on crustacean communities. The species richness estimations, based on presence-absence data, revealed were weakly higher than the total species number reported, but the variation range was relatively wide (Table 5).

4. Discussion

The results revealed that nutrient and chlorophyll increases had a positive influence on daphnids and cyclopoids percentage, such as observed for North Patagonian lakes (Woelfl, 2007; De los Rios-Escalante, 2010). In Patagonia there are numerous oligotrophic lakes with low species number, low daphnids abundance and high calanoid dominance in their zooplankton assemblages (Soto and Zuniga, 1991; Kamjunke et al., 2009; De los Rios-Escalante, 2010). The trophic status of Llanquihue was based on first studies was carried out in Ensenada Bay and it was described as oligotrophic (Campos et al., 1988). Nevertheless the study of Soto (2002) described this lake based on the analyses of bays under towns and aquaculture influence and a control site in the center of the lake, and it observed that zones with human interference exhibited increases in total phosphorus and chlorophyll concentrations. In a first studies with zooplankton assemblages it was found increase in daphnids abundances in lakes between 39-41[degrees] S with higher chlorophyll concentrations (Soto and Zuniga, 1991; De los Rios-Escalante, 2010). In this context, Llanquihue lake has a gradient of chlorophyll concentration due human intervention in their surrounding basins. Despite that there is low dissolved organic matter concentrations, as other regionally similar lakes in Argentinean and Chilean Patagonia (Balseiro et al., 2007; De los Rios-Escalante, 2010). Therefore, the chlorophyll concentration, in spite of the kind of phytoplankton composition, can be an important as regulator factor for zooplankton abundances in Argentinean Patagonian lakes (Trochine et al., 2015).

Our results concerning Daphnids and other cladocerans (Bosminidae and Sididae families), are supported by Modenutti et al. (1998) who described opposite zooplankton abundances responses between Ceriodaphnia dubia and Neobosmina chilensis. The direct association between daphnids and cyclopoids percentage associated to chlorophyll increase was described for Chilean North Patagonian lakes (Woelfl, 2007; De los Rios-Escalante, 2010). Similar results were described for New Zealand lakes that have similar latitude and geographical characteristics of Nothofagus forests (Jeppesen et al., 1997, 2000).

Other important factor to be considered is the fish predation on zooplankton composition (Modenutti et al., 1998). In unpolluted conditions the calanoids copepods would have an important role as grazer on phytoplankton and in turn would be eaten by zooplanktivorous fishes in Argentinean and Chilean Patagonian lakes (Soto and Zuniga, 1991; De los Rios-Escalante, 2010; Reissig et al., 2015; Trochine et al., 2015). Additionally, the natural ultraviolet radiation exposure that increased in Patagonia affect zooplankton assemblages because the species have different tolerance to UV radiation under trophic gradient (Marinone et al., 2006; De los Rios-Escalante, 2010; Hylander et al., 2012). Then considering both view point, the zooplankton composition can be regulated by trophic variations, ultraviolet radiation exposure and fish predation.

The predicted results about species richness indicate that species number is independent of sampling replicates (Gongalsky et al., 2006). Thus, probably the species richness estimators would agree with null models, because first null models revealed the presence of many species repeated in many of sampled sites, and the species richness estimators would indicate that the species number would not vary. These results would agree with the descriptions about Chao 1 and Chao2 index that is a robust estimator (Cannon et al., 1998; Martinez-Aquino et al., 2011; Hoshi et al., 2014).

Our study revealed that zooplankton assemblages are associated to chlorophyll gradients in bays with different kind of human intervention. These results can be the base for future studies about spatial heterogeneity and trophic status in Patagonian lakes with difererent human interference, towards future environmental management and sustainable use.

http://dx.doi.org/10.1590/1519-6984.15515

Acknowledgements

The present study was founded by projects DID UACH d2011-11; CONICYT Chile (Doctoral Fellowship); IAI (Enhanced ultraviolet B radiation in natural ecosystems as an added perturbation due ozone depletion) and MECESUP UCT 0804, and M.I for her valuable comments and suggestions for improve the manuscript.

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P. De los Rios Escalante (a,b), *, D. Soto (c), R. Santander-Massa (d), P. Acevedo (e,f)

(a) Laboratorio de Ecologia Aplicada y Biodiversidad, Escuela de Ciencias Ambientales, Facultad de Recursos Naturales, Universidad Catolica de Temuco--UCTemuco, Casilla 15-D, Temuco, Chile

(b) Nucleo de Estudios Ambientales, Universidad Catolica de Temuco--UCTemuco, Casilla 15-D, Temuco, Chile

(c) Senior Fisheries Officer Inland Water Resources and Aquaculture Service--FIRI, Fisheries Department, FAO of UN, Via delle Terme di Caracalla, I-00100, Roma, Italia

(d) Programa de Ciencias Forestales, Universidad Austral de Chile, Valdivia, Chile

(e) Center for Optics and Photonics, Universidad de Concepcion--UdeC, Casilla 160-C, Concepcion, Chile

(f) Departamento de Fisica, Facultad de Ciencias e Ingenieria, Universidad de la Frontera--UFRO, Casilla 54-D, Temuco, Chile

* e-mail: prios@uct.cl

Received: October 1, 2015--Accepted: April 18, 2016--Distributed: August 31, 2017 (With 2 figures)

Caption: Figure 1. Map of localization of Llanquihue lake, and sites considered in the present study (1: Llanquihue town; 2: Puerto Chico bay; 3: Puerto Phillippi bay; 4: Puerto Rosales bay; 5: Ensenada bay; 6: Puerto Octay town; 7: Volcanes bay; 8: Venado beach).

Caption: Figure 2. Results of PCA analysis for variables and sites considered in the present study.
Table 1. Studied sites and results for dissolved inorganic nitrogen,
soluble reactive phosphorus, and chlorophyll concentrations (in
([micro]g/L), nitrogen / phosphorus molar ratio, daphnids, other
cladocerans, calanoids and cyclopoids.

Name of bays                   Llanquihue            Puerto Chico

Kind of bay                    Town                  Town
Geographical location          41[degrees]14'00"S;   41[degrees]19'00
                                                     "S;
                               72[degrees]02'00"W    72[degrees]58'00
                                                     'W
Soluble reactive phosphorus    1.80                  1.00
Dissolved inorganic nitrogen   10.50                 2.79
N/P                            3.07                  5.97
Chlorophyll "a"                15.95                 6.5
% Daphnidae                    56.34                 33.33
% Other Cladocerans            0.00                  66.67
% Calanoids                    43.19                 0.00
% Cyclopoids                   0.47                  0.00
Ceriodaphnia dubia Richard,    X
1894
Daphnia pulex Ley dig, 1860    X                     X
Neobosmina chilensis (Daday,                         X
1902)
Diaphanosoma chilense Daday,
1902
Boeckella gracilipes Daday,    X                     X
1902
Tumeodiaptomus diabolicus
(Brehm, 1935)
Mesocyclops arauconus          X
Loffler, 1962.

Name of bays                   Puerto Phillippi      Puerto Rosales

Kind of bay                    Aquaculture           Aquaculture
Geographical location          41[degrees]13'00"S;   41[degrees]17'02
                                                     "S;
                               72[degrees]02' 00"W   72[degrees]51'57
                                                     "W
Soluble reactive phosphorus    2.10                  30.20
Dissolved inorganic nitrogen   18.51                 181.10
N/P                            21.69                 12.85
Chlorophyll "a"                8.75                  12.7
% Daphnidae                    55.07                 33.34
% Other Cladocerans            0.00                  0.00
% Calanoids                    35.22                 66.67
% Cyclopoids                   1.21                  0.00
Ceriodaphnia dubia Richard,    X                     X
1894
Daphnia pulex Ley dig, 1860    X                     X
Neobosmina chilensis (Daday,
1902)
Diaphanosoma chilense Daday,   X
1902
Boeckella gracilipes Daday,    X                     X
1902
Tumeodiaptomus diabolicus      X                     X
(Brehm, 1935)
Mesocyclops arauconus          X
Loffler, 1962.

Name of bays                   Ensenada              Puerto Octay

Kind of bay                    Without use           Town
Geographical location          41[degrees]12'00"S;   40[degrees]58'00
                                                     "S;
                               72[degrees]35'00"W    72[degrees]54'00
                                                     "W
Soluble reactive phosphorus    1.00                  2.10
Dissolved inorganic nitrogen   4.00                  6.50
N/P                            8.86                  6.63
Chlorophyll "a"                1.95                  8.20
% Daphnidae                    13.60                 0.10
% Other Cladocerans            2.28                  0.30
% Calanoids                    72.73                 99.70
% Cyclopoids                   0.00                  0.00
Ceriodaphnia dubia Richard,
1894
Daphnia pulex Ley dig, 1860    X
Neobosmina chilensis (Daday,   X                     X
1902)
Diaphanosoma chilense Daday,
1902
Boeckella gracilipes Daday,    X                     X
1902
Tumeodiaptomus diabolicus
(Brehm, 1935)
Mesocyclops arauconus
Loffler, 1962.

Name of bays                   Volcanes bay          Venado beach

Kind of bay                    Aquaculture           Without use
Geographical location          41[degrees]08'56"S;   41[degrees]15'52
                                                     "S;
                               72[degrees]34'37'W    72[degrees]49'00
                                                     'W
Soluble reactive phosphorus    1.00                  1.00
Dissolved inorganic nitrogen   3.50                  3.10
N/P                            7.50                  6.86
Chlorophyll "a"                7.40                  3.9
% Daphnidae                    0.10                  0.01
% Other Cladocerans            0.30                  1.00
% Calanoids                    99.70                 99.00
% Cyclopoids                   0.00                  0.00
Ceriodaphnia dubia Richard,
1894
Daphnia pulex Ley dig, 1860
Neobosmina chilensis (Daday,   X                     X
1902)
Diaphanosoma chilense Daday,
1902
Boeckella gracilipes Daday,    X                     X
1902
Tumeodiaptomus diabolicus
(Brehm, 1935)
Mesocyclops arauconus
Loffler, 1962.

Table 2. Pearson correlation index matrix generated by PCA of
variables considered in the present study (values in bold denotes
significant correlations; p < 0.05).

Variables             Dissolved   N/P   Chlorophyll   % Daphnidae
                      inorganic         "a"
                      nitrogen

Soluble reactive      0.9         0.2   0.4           0.1
phosphorus
Dissolved inorganic               0.3   0.4           0.2
nitrogen
N/P                                     -0.1          0.3
Chlorophyll "a"                                       0.6
% Daphnidae
% Other Cladocerans
% Calanoids
% Cyclopoids

Variables             % Other       %           %            Species
                      Cladocerans   Calanoids   Cyclopoids   number

Soluble reactive      -0.1          0.0         -0.1         0.2
phosphorus
Dissolved inorganic   -0.1          -0.1        -0.1         0.3
nitrogen
N/P                   -0.2          -0.1        0.7          0.7
Chlorophyll "a"       -0.1          -0.2        0.3          0.4
% Daphnidae           0.1           -0.7        0.7          0.8
% Other Cladocerans                 -0.7        -0.2         0.0
% Calanoids                                     -0.3         0.6
% Cyclopoids                                                 0.8

Table 3. Scores of importance of PCA factors.

                               Component 1   Component 2

Soluble reactive phosphorus    -0.1          -0.5
Dissolved inorganic nitrogen   -0.2          -0.5
N/P                            -0.3          -0.1
Chlorophyll "a"                -0.3          -0.2
% Daphnidae                    -0.4          0.1
% Other Cladocerans            0.1           0.3
% Calanoids                    0.3           -0.3
% Cyclopoids                   -0.3          0.2
Species number                 -0.4          0.1

Table 4. Results of null model co-occurrence species for data included
in the present study ("p" values lower than 0.05 denotes the existence
of regulator factors in species associations).

Model                Observed   Mean    Standard      P
                     index      index   effect size

Fixe-fixed           2.4        1.7     5.7           < 0.01
Fixed-proportional   2.4        1.8     1.2           0.12
Fixed-equiprobable   2.4        2.0     0.8           0.24

Table 5. Results of estimated biodiversity parameters obtained from
SPADE software.

Estimator              Estimate   Estimate         95% confidence
                                  standard error   interval

Homogeneous model      7.6        1.0              (7.1-13.1)
Chao2                  7.2        0.7              (7.0-11.3)
Chao2-bc               7.0        0.1              (7.0-7.0)
Model 1(h)             7.3        0.8              (7.0-12.1)
Model 1(h)-1           7.3        0.8              (7.0-12.1)
Model (th)             7.2        0.8              (7.0-12.7)
Model (th)-1           7.2        1.0              (7.0-13.5)
1st Order jackkniffe   7.9        1.3              (7.0-14.1)
2nd Order jackkniffe   7.3        2.0              (7.0-20.5)
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Title Annotation:Original Article
Author:De los Rios Escalante, P.; Soto, D.; Santander-Massa, R.; Acevedo, P.
Publication:Brazilian Journal of Biology
Date:Jul 1, 2017
Words:3836
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