19
Growth and development of Calanus chilensis nauplii reared under laboratory conditions: testing the effects of temperature and food resources Cecilia G. Torres a , Ruben Escribano b, * a Departamento de Oceanografı ´a, Universidad de Concepcio ´n, P.O. Box 160 C, Concepcio ´n, Chile b Oceanographic Center for the Eastern South Pacific (COPAS), Departamento de Oceanografı ´a, Universidad de Concepcio ´n, P.O. Box 42, Dichato, Concepcio ´n, Chile Received 22 March 2002; received in revised form 28 April 2003; accepted 23 May 2003 Abstract We assessed growth and development of naupliar stages of Calanus chilensis Brodsky 1959, under a combination of three temperatures and two food levels in laboratory conditions. Both food supply and temperature significantly affected naupliar growth and development. High food, measured as chlorophyll a (Chl a) concentration, was 40 Agl 1 , on average, and yielded temperature-dependent growth rates in the range of 0.13 – 0.17 day 1 . Low food was about 1.2 Ag chlorophyll a l 1 and retarded or arrested development and drastically reduced the growth rate to the range of 0.05 – 0.09 day 1 . To test whether these experimental results were consistent with field data, we used published information on temperature and chlorophyll a variability in northern Chile and developed a combined temperature/food-dependent model to diagnose naupliar growth in the field through a 2-year seasonal cycle including the 1997 – 1998 El Nin ˜o conditions. We concluded that in the upwelling region off northern Chile, C. chilensis might seldom encounter conditions of food shortage, as those applied in the laboratory. Thus, naupliar growth of this species may be primarily controlled by environmental temperature and 0022-0981/03/$ - see front matter D 2003 Elsevier B.V. All rights reserved. doi:10.1016/S0022-0981(03)00261-2 * Corresponding author. Tel.: +56-41-683247; fax: +56-41-683902. E-mail addresses: [email protected] (C.G. Torres), [email protected] (R. Escribano). www.elsevier.com/locate/jembe Journal of Experimental Marine Biology and Ecology 294 (2003) 81 – 99

Growth and development of Calanus chilensis nauplii reared under laboratory conditions: testing the effects of temperature and food resources

Embed Size (px)

Citation preview

www.elsevier.com/locate/jembe

Journal of Experimental Marine Biology and Ecology

294 (2003) 81–99

Growth and development of Calanus chilensis

nauplii reared under laboratory conditions:

testing the effects of temperature and

food resources

Cecilia G. Torresa, Ruben Escribanob,*

aDepartamento de Oceanografıa, Universidad de Concepcion, P.O. Box 160 C, Concepcion, ChilebOceanographic Center for the Eastern South Pacific (COPAS), Departamento de Oceanografıa,

Universidad de Concepcion, P.O. Box 42, Dichato, Concepcion, Chile

Received 22 March 2002; received in revised form 28 April 2003; accepted 23 May 2003

Abstract

We assessed growth and development of naupliar stages of Calanus chilensis Brodsky 1959,

under a combination of three temperatures and two food levels in laboratory conditions. Both

food supply and temperature significantly affected naupliar growth and development. High food,

measured as chlorophyll a (Chl a) concentration, was 40 Ag l� 1, on average, and yielded

temperature-dependent growth rates in the range of 0.13–0.17 day� 1. Low food was about 1.2

Ag chlorophyll a l� 1 and retarded or arrested development and drastically reduced the growth

rate to the range of 0.05–0.09 day� 1. To test whether these experimental results were

consistent with field data, we used published information on temperature and chlorophyll a

variability in northern Chile and developed a combined temperature/food-dependent model to

diagnose naupliar growth in the field through a 2-year seasonal cycle including the 1997–1998

El Nino conditions. We concluded that in the upwelling region off northern Chile, C. chilensis

might seldom encounter conditions of food shortage, as those applied in the laboratory. Thus,

naupliar growth of this species may be primarily controlled by environmental temperature and

0022-0981/03/$ - see front matter D 2003 Elsevier B.V. All rights reserved.

doi:10.1016/S0022-0981(03)00261-2

* Corresponding author. Tel.: +56-41-683247; fax: +56-41-683902.

E-mail addresses: [email protected] (C.G. Torres), [email protected] (R. Escribano).

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9982

this might also be the case for the dynamics of the entire population inhabiting the coastal

upwelling zone.

D 2003 Elsevier B.V. All rights reserved.

Keywords: Copepods; Food supply; Nauplii; Northern Chile; Temperature; Upwelling

1. Introduction

Growth and development of marine copepods have been extensively studied in the field

and laboratory. Studies have concluded that both physiological rates are strongly dependent

on temperature (Huntley and Lopez, 1992) and food supply (Hirst and Lampitt, 1998).

Several works have described how copepods grow and develop under the effects of varying

temperature and food quantity and quality. However, the research has been mostly focused

on copepodite stages, with very few parallel studies for the naupliar phase (Mullin, 1988;

Hygum et al., 2000), despite the fact that nauplii are usually more abundant than

copepodites in the field and that their success in the plankton will ultimately determine

recruitment into the copepodite phase and, consequently, the population dynamics.

In the coastal upwelling region off northern Chile, the endemic and very abundant

copepod Calanus chilensis (Heinrich, 1973; Boyd et al., 1980) has received increasing

attention lately. Studies on its population dynamics, however, have only dealt with

copepodites and eggs and nauplii have seldom been considered (Escribano, 1998; Giraldo

et al., 2002). This has limited reliable estimates of population growth and a clear

understanding of the species life cycle (Escribano and McLaren, 1999).

C. chilensis reproduce and grow year round at northern Chile, under apparently lack of

food limitation (Escribano, 1998; Ulloa et al., 2001), such that copepodite growth might be

primarily determined by temperature (Escribano and McLaren, 1999). In the laboratory,

however, development and growth rates of copepodites C. chilensis become greatly

reduced under low food (Escribano et al., 1997), suggesting that food supply in the field

must remain sufficiently high to maintain maximal growth rates. This possibility has not

yet been assessed for nauplii in this species. In other Calanus species, naupliar growth has

been found to be less dependent on food supply compared to copepodite growth (Vidal,

1980; Hart, 1990; Hirst and Lampitt, 1998; Hygum et al., 2000). This could also be true

for nauplii of C. chilensis, whose development may depend on temperature as well. Such

possibility still needs to be examined. Nevertheless, because of their very small size ( < 0.5

mm) and usually fast moulting rates, in situ growth rates of nauplii are difficult to estimate.

To solve this, laboratory experiments can be considered as a useful tool because they may

provide insights on how individual growth responds to varying temperature/food regimes;

this can help understanding naupliar growth in nature.

Calbet et al. (2000) provided a method to study naupliar growth by estimating changes

in body volume with a digital image analyser system. Using this method, we studied the

growth and development of nauplii reared in the laboratory under controlled conditions of

temperature and food. We aimed at determining the relative importance of temperature and

food supply on regulating naupliar growth and development and further assess the

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 83

hypothesis that in the rich upwelling region off northern Chile, nauplii may indeed develop

into copepodites at temperature-dependent rates.

2. Methods

2.1. Experiments

Three experiments were performed during August–September 2001, corresponding to

the austral winter–spring conditions at the upwelling region off northern Chile. Zoo-

plankton were captured in the Bay of Mejillones (23jS), which is a highly productive

coastal embayment, under the influence of wind-driven coastal upwelling most of the year

(Marın et al., 2001; Escribano, 1998). Zooplankton were captured near the center of the

bay with a 0.5 opening diameter, 200-Am-mesh-size plankton net, which was vertically

towed in the upper 60 m on several occasions. Zooplankton samples were immediately

diluted with surface seawater, placed in coolers and transported to the laboratory within 2

h. Females C. chilensis were sorted under the microscope and maintained in filtered

seawater at about 15 jC, until the experiments.

We used a combination of three nominal temperatures, 10, 15 and 18 jC, and two levelsof food quantity, measured as concentration of chlorophyll a (Chl a). The temperature

range was that usually observed in the upper 50 m of Bay of Mejillones through seasons

(Escribano and McLaren, 1999). As food, a mixture (in variable proportion) of microalgal

cultures of Chaetoceros calcitrans (10–20 Am) and Isochrysis galbana (3.3–5.8 Am) was

added until a greenwish color was attained. This high Chl a was assumed as excess of

food. Low food level was obtained after 1/16 dilution of the high level. Algal cultures

were used during their exponential phase of growth for all the experiments. The micro-

algae I. galbana have proven to be an adequate food for C. chilensis copepodites. This

microalgae has been suscessfully used to grow nauplii and copepodites of this species in

the laboratory (Escribano et al., 1998) and to induce egg production (Escribano et al.,

1996). Chaetoceros spp. are common and abundant diatoms in the upwelling zone off

northern Chile (Rodriguez et al., 1996). Chl a was measured by the spectrophotometric

method (Parsons et al., 1992). For this, aliquots of the food media (100–300 ml) were

obtained, filtered in GF/C Whatman filter and pigments extracted in 90% acetone for 24 h.

Pigment absorbance was measured at 665 and 750 nm and Chl a concentration calculated

according to Greenberg et al. (1992). Table 1 summarises the experiments and associated

conditions of food and temperature.

The first experiment (Exp. 1) was carried out at a constant temperature of 10 jC, underexcess of food. For this, 10 females were placed in each of four 1-l glass jars, which

contained the food media at high level and a 450-Am sieve near the bottom to prevent

eventual cannibalism. Females were then left undisturbed and after 24 h of incubation at 10

jC in a semidark cold room, they were removed and the jars were gently poured onto 37-

Am sieves and the spawned eggs collected in petri dishes. Using pasteur pippetes, the eggs

were counted and transferred to 150 ml BOD glass-stopper bottles, which had previously

been filled with 1 Am filtered seawater, aerated overnight and kept at the same temperature.

BOD bottles were used because they allowed a rapid inspection of live nauplii, which could

Table 1

Summary of experiments to assess growth and development rates of C. chilensis nauplii reared in the laboratory at

three temperatures and under high and low food concentration

Food level Temperature Chl a(i) Chl a(f) Experiment

High 10 10.27 1

15–18 155.7F 88.08 6.0F 3.47 2

15–18 19.8F 5.19 7.0F 1.60 3

Low 15–18 1.2F 0.32 1.2F 0.20 3

Food level was measured as chlorophyll a (Ag l� 1). Chl a(i) is the mean (xF S.E.) of food concentration at every

replacement of the media, and Chl a(f) is the mean concentration of food at the end of each experiment.

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9984

be seen through the glass under the microscope without opening the bottles; food media

could be easily resuspended by turning the bottles; and also because of their small volume,

desired temperature could be rapidly achieved. Caution was taken to avoid presence of

bubbles, in which small nauplii can get caught. The initial number of eggs per BOD bottle

was about 100, depending on their availability; however, their concentration never

exceeded 900 egg l� 1. A total number of five BOD bottles were obtained in these

experiments. After 2–3 days, hatched nauplii could be observed through the glass.

Thereafter, subsamples (10–25 ml) were daily taken from the BOD bottles. The extracted

volume from the BOD bottles was replaced with fresh filtered seawater. These subsamples

were fixed with 5% formalin for later analysis. This experiment lasted about 2 weeks and

spawned eggs came from females captured in two opportunities in Bay of Mejillones.

Hatched nauplii were fed with 100% of I. galbana at the third day. The microalgae culture

was added into the BOD bottles with small pipettes. Nauplii were thereafter fed at each

daily observation. When larger nauplii (N4–N6) could be observed, small amounts

(f 25%) of the microalgae C. calcitrans were added along with I. galbana. Temperature

was recorded every 12 h, at the time when the BOD bottles were also carefully rotated to

allow algal become well mixed. A single measurement of Chl a was made during the

experiment using the remaining food media after nauplii had been fed.

A second experiment (Exp. 2) was performed 1 week later. In this case, two temper-

atures (15 and 18 jC) were used, under excess of food. Chl a was measured every 2 days,

when fresh food media was prepared. Additional measurements of Chl a were made at the

end of the experiment in the remaining media after all nauplii had been removed (Table 1).

In this experiment, the eggs were initially incubated in the BOD bottles, which had already

been filled with food media, containing only I. galbana. However, after 2 days, when

nauplii stage N3 were observed in the subsamples, the food media was replaced by a

mixture of 30% C. calcitrans and 70% I. galbana. For this experiment, a total number of

four BOD bottles were obtained for each temperature containing about 100 eggs per bottle.

Subsamples for nauplii were obtained every 12 h, removing 25 ml from one BOD bottle

per treatment. The volume of the subsample was increased up to 100 ml in some cases,

when too few nauplii were observed. At every removal of subsamples, the bottles were

refilled with fresh food media. After 10 days, all remaining nauplii had been removed and

the experiment was terminated.

A third experiment (Exp. 3) used the same procedure as Exp. 2; however, in this case,

the two food levels, high and low, were used. As in Exp. 2, Chl a was measured every 2

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 85

days (both high and low food), in the freshly prepared media, as well as in the remaining

media, at the end of each treatment. In this experiment, three BOD bottles, containing

between 50 and 100 eggs bottle, were obtained for each combination of temperature and

food. Subsamples for nauplii in this case were obtained every 24 h, removing 50 ml from

one BOD bottle per each treatment. This volume was increased (up to100 ml) in some

cases to obtain at least five nauplii per subsample. This experiment was finished when no

nauplii were obtained in the subsamples (after 10 days).

Preserved samples from the three experiments were analysed 1 month later. The

naupliar stages were identified and counted under the microscope to examine the stage

frequency through time, allowing estimations of naupliar development times. Naupliar

growth was studied by analysing daily changes in naupliar volume, regardless of

developmental stage. The naupliar volume was estimated using a microscope (40�magnification) equipped with a digital camera and connected to an image analyser system.

Digital images of nauplii were used to calculate naupliar volume, according to Calbet et al.

(2000), such that,

V ¼ 4

3A

w

2

� �ð1Þ

where V= volume (Am3), A= naupliar area (Am2) in a dorsal view, w = naupliar width (Am).

2.2. Data analysis

Naupliar growth was described by an exponential model, such that,

V ¼ Viegt ð2Þ

where Vi = initial volume (Am3), g= volume-specific instantaneous growth rate (day� 1),

and t= time (day). From this Eq. (2), g between observations was estimated as,

g ¼ ln ðViþ1=ViÞ=t ð3Þ

where Vi + 1 and Vi are naupliar volumes (Am3) between two subsequent observations and t

the time interval (day) between observations.

Development rates were evaluated for two time intervals during the naupliar phase: (1)

the duration between egg laying and first appearance of nauplii stage N3 (tegg– tN3), and

(2) the time at initial stage N3 and the time of first appearance of stage N6. The former was

assumed as purely temperature-dependent because nauplii are just starting to feed at this

stage N3, and the latter assumed as depending on both temperature and food conditions.

The time at egg laying (tegg) was assumed as the median time between two subsequent

observations during the incubation period of females (f 24 h) when they had laid eggs.

Time of initial stages N3 and N6 was assumed as the time when they first appeared in the

daily, or twice a day samples.

Temperature-dependent development times were described using the Belehradek

equation (McLaren, 1995) as,

D ¼ aðT þ aÞ�2:05 ð3Þ

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9986

where D = development time (day), T= temperature (jC), a and a are parameters that

define the size dependence and the temperature adaptation of development, respectively.

We used a fixed value of 2.05 as the exponent, which can be assumed as constant among

copepod species (McLaren, 1995). Belehradek equation for embryonic time of C. chilensis

was determined by Escribano et al. (1998) as,

D ¼ 947:7 ðT þ 11:0Þ�2:05 ð4Þ

Eq. (4) may be used to estimate temperature-dependent time of later stages assuming the

equiproportional rule of development (Corkett et al., 1986), which states that each stage

occupies a fixed proportion of the total development time. Estimated proportions at a

given temperature can thus be used to calculate stage durations at any other temperature.

We used this method to calculate the parameter a of Eq. (4) and hence obtain temperature-

dependent equations for durations of the phases egg–N3 and egg–N6.

Temperature–food effects on naupliar size were tested by ANOVA, whenever homo-

geneous variance among treatments could be demonstrated by Barlett’s test, or when this

became homogeneous after log transformation. Curve fittings were performed by

nonlinear estimates of parameters using the quasi-Newton algorithm (Wilkinson, 1990).

Parameters comparisons were made using the Student’s t-test.

3. Results

3.1. Temperature and food conditions

Controlled temperatures varied in narrow ranges in the cold room (meanF S.D.): 10.3

jCF 0.65, 14.95 jCF 0.30 and 17.95 jCF 0.10. Nauplii were fed with considerably

high amounts of food in terms of Chl a (Table 1). Concentration of Chl a also showed

sharp decreases after 2 days in treatments of high food levels, suggesting that nauplii were

actively feeding (Table 1). For all treatments under high food levels, the Chl a

concentration was, on average, more than 6 Ag l� 1 whereas low food level never exceeded

1.8 Ag l� 1. The low food level may represent an extreme condition of low phytoplankton

Table 2

Proportion of total C. chilensis nauplii obtained after incubation of eggs under five different combinations of

temperature� food treatments

Treatment Proportion (%)

Temperature (jC) Food level

10 High 15.5

15 High 21.7

Low 91.0

18 High 47.3

Low 76.0

This proportion represents the eggs that successfully hatched and survived until the end of each experiment from

the total of eggs initially incubated.

Table 3

Estimates of egg and naupliar volumes (meanF S.D.) of C. chilensis reared in laboratory conditions under two food levels (high and low) and at three temperatures

Temperature Food Volume (� 105 mm3)

resourceEgg N1 N2 N3 N4 N5 N6 n

10 High 1.85F 0.276

(20)

1.18F 0.103

(12)

1.73F 0.507

(24)

3.15F 0.555

(19)

6.44F 1.466

(5)

80

15 High 2.05F 0.220

(59)

1.22F 0.234

(13)

1.66F 0.313

(22)

2.84F 0.648

(55)

6.90F 1.441

(59)

9.05F 0.801

(12)

11.34F 0.597

(2)

222

15 Low 1.91F 0.207

(3)

1.11F 0.073

(15)

1.67F 0.376

(5)

2.80F 0.406

(87)

110

18 High 2.09F 0.313

(6)

1.31F 0.225

(9)

2.24F 0.572

(8)

2.89F 0.637

(81)

6.70F 1.667

(66)

9.88F 2.062

(38)

12.63F 2.582

(12)

220

18 Low 1.85

(1)

1.19F 0.098

(11)

2.94F 0.578

(51)

4.68F 0.730

(14)

77

Nauplii stages are N1 through N6. Numbers in parentheses are sample sizes, and n is total number of eggs and nauplii per treatment.

C.G.Torres,

R.Escrib

ano/J.

Exp.Mar.Biol.Ecol.294(2003)81–99

87

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9988

biomass in Bay of Mejillones in terms of Chl a (Escribano, 1998). The total number of

nauplii analysed for each experimental treatment depended on the initial number of

incubated eggs, on the proportion of egg that hatched and on naupliar mortality. From the

initial number of incubated eggs per treatment and the total number of sampled nauplii

thereafter, an estimate of the proportion of eggs that hatched, turned into nauplii and

Fig. 1. Growth in body volume of C. chilensis nauplii reared in the laboratory under three temperatures and two

food levels. The curves are nonlinear fittings of exponential model of growth. High food was assumed as excess

of food, measured as concentration of chlorophyll a, and low food was 1/16 of the high one.

Table 4

Parameter estimates after nonlinear regression of growth in body volume of C. chilensis nauplii reared in the

laboratory at three temperatures and two levels of food

T (jC) Food Vi SE g(d� 1) SE 95% Confidence limits

level (Am3� 105)Lower Upper

10 High 1.2 0.11 0.13 0.011 0.103 0.147

15 High 1.5 0.13 0.17 0.011 0.150 0.193

Low 1.9 0.10 0.05 0.007 0.039 0.068

18 High 2.8 0.24 0.14 0.012 0.111 0.160

Low 1.8 0.15 0.09 0.012 0.070 0.118

Vi = estimate of initial volume (Am3� 105), g= volume-specific growth rate (d� 1) and SE= asyntotic standard

errors.

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 89

survived until sampling is shown in Table 2. These proportions are significantly different

among treatments (G test, v2 = 144.1, p < 0.001), suggesting treatment-dependent mortali-

ties. It should be noted that lower survival was obtained at high food, and it is difficult to

establish which factor (temperature or food) caused more mortality.

3.2. Naupliar growth

Although naupliar volume was estimated independently from stages, they were actually

identified for subsequent analysis of temperature/food effects on development. However,

not all the treatments allowed complete development of naupliar stages. In fact, the final

nauplii stage N6 was only reached at 15 and 18 jC under high food. The low-temperature

(10 jC)/high food condition allowed development only up to stage N4 despite high food.

The number of eggs and nauplii available to obtain volume measurements was also

variable, depending on treatment. Table 3 summarises sample sizes and mean estimates of

naupliar volume per treatment.

Temperature effects on naupliar volume can be examined by comparing the treatments

under which nauplii developed up to stage N3, assuming that potential food effects are not

yet noticeable, as they are just starting to feed (Marshall and Orr, 1955). One-way analysis

of variance (ANOVA) showed that naupliar volume of stages N2 and N3 are significantly

affected by temperature (F2,56 = 4.88, p < 0.05 and F2,29 = 3.32, p < 0.05, respectively).

Table 3 shows that mean body volume of N3 cultured under low temperature (10 jC) isgreater than that obtained for N3 reared under 15 and 18 jC. Food effects on naupliar

Table 5

Values of Student’s t-test to compare growth rates ( g) of nauplii C. chilensis reared in the laboratory under three

temperatures and two food levels (high food =HF and low food = LF)

15j HF 15j LF 18j HF 18j LF

10j HF 2.09** 4.00** 0.48 1.35

15j HF 6.56** 1.52 3.35**

15j LF 4.37** 2.16**

18j HF 1.75

Values of Student’s t-test are at 5% level of significance (**) and infinite degrees of freedom.

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9990

volume could only be tested by comparing stages N4 reared under high and low food at 18

jC. In this case, body volume of N4 was significantly reduced (Table 3) under the low

food condition (F1,140 = 26.10, p < 0.001).

Fig. 2. Daily changes in the volume-specific growth rate ( g) of C. chilensis nauplii reared in the laboratory under

three temperatures and two food levels. g was estimated from the exponential model of growth between

subsequent daily observations. High food was assumed as excess of food, measured as concentration of

chlorophyll a, and low food was 1/16 of the high one.

Fig. 3. Daily changes in relative abundance of naupliar stages of C. chilensis reared in the laboratory under three

temperatures and two food levels. High food was assumed as excess of food, measured as concentration of

chlorophyll a, and low food was 1/16 of the high one.

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 91

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9992

When no nauplii could be observed in the samples, the experiments were terminated.

The experiments lasted between 10 and 11 days and this time was similar for all

treatments. Growth patterns, as shown by changes in body volume and fitted curves,

are illustrated in Fig. 1. Food effects on naupliar growth seem clear when comparing the

high and low food at 15 and 18 jC. The fitted exponential models, judging by the

determination coefficients (r2), are all significant ( p < 0.05). Estimated rates of growth ( g)

and their associated statistics are shown in Table 4. Confidence limits (95%) of g indicate

not only potential effects of food but also a temperature influence. There are significant

differences in g between temperatures and between food treatments although the most

remarkable difference is between high and low food at 15 jC (Table 5), suggesting that at

least at this temperature low food substantially reduced g.

Daily changes in g between consecutive observations for each treatment are shown in

Fig. 2. The growth rate, g, was more variable under high food condition, except for the low

temperature of 10 jC. Fig. 2 suggests a tendency of g to decrease during the first 3–4

days, becoming negative in some cases, but overall means of g were all positive and

greater than 0.08 day� 1 at all treatments.

3.3. Naupliar development

Attempts to estimate duration of single stages were made from changes in relative

abundance of stages through time. However, the lack of synchrony in moulting times, as

shown by Fig. 3, precluded the possibility of obtaining reliable estimates. In C. chilensis

under laboratory conditions, the lack of synchrony of development is even present in the

hatching time of eggs spawned in a single clutch within females (Escribano et al., 1998).

We thought that the partition of total naupliar time into two phases, egg–N3 and N3–N6,

may help reduce individual variation. The proportion of time occupied by each phase at a

given treatment was also estimated as well as the parameter a of the Belehradek equation

(Table 6). These estimates should be considered as temperature-dependent because they

were all obtained under conditions of high food. Using the mean value of the parameter a

Table 6

Duration (day) of the development phases egg to N3 (tegg– tN3), N3 to N6 (tN3– tN6) and egg to N6 (tegg– tN6) of

naupliar stages of C. chilensis, reared in the laboratory under three temperatures and excess of food

Developmental Temperature (jC) Mean time

phase10 15 18

proportion

tegg– tN3 4.24 2.58 2.56 0.38

tN3– tN6 6.91 6.00 3.00 0.62

tegg– tN6 11.15 8.58 5.56 1.00

Mean a

a (egg–N6) 5728 6826 5533 6029

a (egg–N3) 2179 2053 2548 2660

Durations are estimates of stage initial times. The value tN3– tN6 at 10 jC was not available from the experiments,

but was estimated using the mean proportion of time from the other temperatures, according to the

equiproportional rule (Corkett et al., 1986). The parameter a is that derived for the Belehradek equation.

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 93

from Table 6 and Eq. (4), development time (D) between egg and N6, as a function of

temperature (T), can be described as,

D ¼ 6029 ðT þ 11:0Þ�2:05; ð5Þ

Eq. (5) may thus be used to examine temperature-dependent development of nauplii and

combined with Eq. (2), the growth rate ( g) could be estimated for field conditions

provided some measurements of egg and N6 weights, carbon content or body volume as in

this study.

4. Discussion

Changes in body volume of copepod nauplii primarily occur at each moulting so that

growth should be considered as discrete. However, the incorporation of new somatic tissue

takes place continuously through development, giving rise to increases in size (biovo-

lume), even within stages, as reflected in changes in naupliar volume from initial stage to

end stage (Calbet et al., 2000). Therefore, although body volume may not necessarily

represent body weight, its relative changes, both within and between stages, allowed us to

examine the growth pattern and estimate a volume-specific growth rate, which can be

considered as an index of the mass-specific growth rate. Indeed, our estimates of naupliar

growth ( g), in the range of 0.05–0.17 day� 1, do not considerably differ from g estimated

for copepodids as 0.114 day� 1 at 15 jC, under excess of food (Escribano et al., 1998).

Furthermore, g did not show abrupt changes during the experiments (Fig. 2). These results

suggested that growth was rather uniform throughout naupliar development. Stability of g,

however, was accompanied by a large variation in moulting times, possibly originated

from between and within treatment variation in egg development. Females were incubated

for 24 h, but egg spawning did not occur before 12 h of incubation, possibly after

acclimation to conditions and feeding have taken place. Females in C. chilensis also

produce eggs in small groups, at variable times within a few hours (Escribano et al., 1996,

1998). Thus, high variability of egg development may even occur within clutches

(Escribano et al., 1996, 1998). This might give rise to lack of synchrony in naupliar

development, precluding the possibility of obtaining reliable estimates of mid-stage

moulting times as in other studies with different Calanus species (e.g. Peterson, 1986).

The estimate of average moulting times may not represent this individual variation either.

Thus, in order to make estimates for temperature-dependent development rates, we suggest

that initial stage times, assumed as the time for stage first appearance, may be a

recommended approach when dealing with continuously reproducing species.

As shown in a previous study (Escribano et al., 1997), both growth and development

rates of copepodids C. chilensis are highly sensitive to low food supply when reared in the

laboratory. Naupliar stages seem to respond similarly. Low food not only reduced the

growth rate but also retarded or even arrested naupliar development at stage N4; this was

independent of temperature. As at 10 jC, development stopped at N4 despite high food,

we think this temperature might be too low for C. chilensis development because in the

field, individuals tend to aggregate in the upper 20-m layer (Escribano et al., 2001), in

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9994

which they may not experience temperatures below 12 jC (Escribano and Hidalgo, 2000).

Furthermore, the parameter a of the Bılehradek equation has been estimated as 11.0 (Eq.

(3)), suggesting that the population at northern Chile is mostly adapted for developing at

temperatures higher than 11 jC. This might not be the case for populations of the species

distributed at coastal areas of Central/South of Chile (Marın et al., 1994). In this region,

temperatures are colder and it is likely that the temperature adaptation parameter may be

lower than 11 jC. This possibility, however, has not yet been assessed.

Phytoplankton seems to be the main food item for C. chilensis in northern Chile (Boyd

et al., 1980). The species was also successfully reared from egg to adult using mixtures of

phytoplankton in the laboratory (Escribano et al., 1997). The microalgae used in these

experiments, however, may not fully represent food resources available in the field, which

may comprise a rich variety of diatoms, flagellates and microheterotrophs in this area

(Gonzalez et al., 2000). Also, pigment concentration (measured as Chl a) should only be

considered as an index of food quantity. The actual organic carbon available as food may

greatly vary with Chl a. In fact, the carbon/Chl a ratio of diatoms is known to range widely

from 30 to 150, depending on culturing conditions (Omory and Ikeda, 1984). This means

that our low food condition could have been in the range of 0.03–0.18 mg C l� 1, whereas

the high food (about 40 Ag Chl a l� 1 on average) exceeded 1.2 mg C l� 1; that is, high

food was at least one order of magnitude higher than low food. We do not know if this

carbon content is sufficient (high food level) to allow maximal development rates of C.

chilensis nauplii; however, using Eq. (4), the estimated development time between egg and

N6 is about 7.58 days at 15 jC. This value does not differ from 7.4 days estimated by

Escribano et al. (1998), who used a mixture of natural phytoplankton as food. This

suggests that the applied food media, at least under high food, could have been adequate to

allow growth at temperature-dependent rates.

The drastic effects of low food on development and growth of C. chilensis nauplii

contrast with experimental results in nauplii of Calanus finmarchicus (Hygum et al.,

2000), in which nauplii were shown to obtain nearly maximal development rates at low

food (f 1 Ag Chl a l� 1, or 0.2 mg C l� 1). However, C. finmarchicus may not necessarily

respond like C. chilensis to low food. C. finmarchicus is a high-latitude species, subjected

to strong seasonaliy in food supply, such that at times, individuals must cope with

extremely low food, being forced to use alternate food resources such as microzooplankton

(Ohman and Runge, 1994). On the other hand, C. chilensis, exhibiting continuous

reproduction throughout the year, may not be adapted to withstand low food because

such condition is seldom found, at least in coastal waters off northern Chile (Escribano,

1998; Ulloa et al., 2001), with very high year-round primary production rates (Daneri et

al., 2000).

Nevertheless, food resources, in terms of phytoplankton biomass, and also water

temperature may show much spatial and temporal variability in the upwelling zone off

northern Chile (Thomas et al., 2001) in association with the spatial structure of cold

upwelled waters (Giraldo et al., 2002). In order to assess how this variability in food

resources and temperature may influence growth of C. chilensis nauplii in the field, we

made use of a time series of temperature and Chl a concentration obtained between June

1996 and January 1998 off Mejillones (23jS) at a fixed station (Hidalgo and Escribano,

2001). We chose data from 10 m because this depth seems to represent well the actual

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 95

habitat of this species (Escribano and McLaren, 1999). We assumed that under nonlimiting

conditions of food and combining Eqs. (2) and (4), maximal temperature-dependent

growth rate of naupliar stages may be expressed as,

gmax ¼ ½ln ðSN6=SeggÞ�=½6029ð11:0þ TÞ�2:05� ð6Þ

where gmax = temperature-dependent growth rate (day� 1); SN6 and Segg are sizes (weight,

carbon, or volume) of naupliar stage N6 and egg, respectively; and T is temperature (jC).An equivalent equation to describe g as a function of food concentration has not been yet

developed. However, we may approximate one using the half-saturation model, as the one

used by Mullin et al. (1975) to describe the ingestion rate as a function of food

concentration as follows,

g ¼ gmaxðC � C0Þ=½k þ ðC � C0Þ� ð7Þ

where g = size-specific growth rate (day� 1), C = food resource concentration, C0 = param-

eter to define a threshold of food concentration to initiate feeding (Parsons et al., 1967),

and k = the half-saturation food concentration, equivalent to a half of the concentration to

attain gmax.

If we substitute gmax of Eq. (6) into Eq. (7), the combined dependence of g on

temperature and food can be expressed as,

g ¼ ½ln ðSN6=SeggÞ�=ð½6029ð11:0þ TÞ�2:05�½ðC � C0Þ=ðk þ ðC � C0ÞÞ�Þ ð8Þ

Using Eq. (8), we can now examine how g responds to Chl a concentration and

temperature in the field. To do that, we first need to make estimates of k and C0.

Escribano et al. (1997) found that copepodids C. chilensis retarded their development at

Chl a concentration lower than 2.5 Ag l� 1. In our experiments with nauplii, the low food

never exceeded 1.8 Ag Chl a l� 1 although the mean value was about 1.2 Ag l� 1. It seems

that below 2.5 Ag Chl a l� 1, development is retarded so that we used this value as a critical

concentration needed to achieve gmax. The threshold parameter (C0) indicates the minimal

concentration required for initiating feeding and might not considerably affect g so that we

arbitrarily assume a value of 0.5 Ag Chl a l� 1. As size measurements of eggs and N6, we

used the overall means of volumes from the experiments, estimated as 2.0� 105 and

12.0� 105 Am3 for egg and N6, respectively. Potential body size variations of N6 and

perhaps of eggs in the field is certainly a shortcoming to fully account for temporal

changes in g and this may need further exploration.

The time series of temperature and Chl a obtained at time intervals of about 15 days

(Hidalgo and Escribano, 2001) included conditions before and during the 1997–1998 El

Nino, which caused abnormally warm waters in the coastal area (Ulloa et al., 2001). This

can be seen in the plot of temperature at 10-m depth (Fig. 4a). During the entire period,

Chl a exhibited much variability in the range of 1.0 Ag Chl a l� 1 in June 1996 to about 16

Ag l� 1 in May 1997 (Fig. 4b). The combined temperature/food-dependent growth rate ( g)

estimated with Eq. (8) and maximal temperature-dependent gmax with Eq. (6) are shown in

Fig. 4c. Although gmax always appears higher than g due to the dependence upon Chl a

concentration, it seems that both rates ( gmax and g) follow the pattern of temperature and

Fig. 4. Expected seasonal variation in the temperature-dependent ( gmax) and temperature/food-dependent ( g)

volume-specific growth rate of C. chilensis nauplii in Bay of Mejillones, northern Chile (upper panel); seasonal

changes in temperature at 10-m depth (mid panel); and concentration of chlorophyll a at 10-m depth (lower

panel). The shaded area represents the 1997–1998 El Nino conditions at northern Chile.

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9996

they even show a positive trend with increasing warming during El Nino period (Fig. 4c).

In fact, Ulloa et al. (2001) showed that C. chilensis increased in numbers during El Nino

period, suggesting an acceleration of development and growth rates upon elevated

temperatures, in the absence of food shortage. In any case, it became clear that temperature

explained much variability of g, accounting for a 44% of total variance, as compared to

Chl a concentration, which accounted for 26% (Fig. 5). Thus, growth of nauplii seems

primarily determined by temperature.

In coastal upwelling systems, copepods are multivoltine species, with 10 or more

generations a year, which can be sustained mostly because food may be high-throughout

seasons (Peterson, 1998). Upwelling zones are also advective habitats and circulation may

Fig. 5. The relationship between the expected volume-specific growth rate of C. chilensis nauplii in Bay of

Mejillones, northern Chile, and the temperature and chlorophyll a concentration at 10-m depth. The growth rate

was estimated as a function of temperature and chlorophyll a. Linear regressions and r2 illustrate the relative

importance of temperature and chlorophyll a quantity on the growth rate. Dotted lines are 95% confidence limits

of the regression lines.

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 97

impose physical forces with which copepods must deal to maintain their populations

nearshore. Peterson (1998) has suggested that such forces may be more important than

food supply and temperature for population dynamics of copepods in upwelling systems.

Off northern Chile, upwelling circulation may indeed affect abundance, distribution and

population growth of C. chilensis (Escribano et al., 2001; Giraldo et al., 2002). However,

our findings suggest that naupliar growth, which directly determine copepodid recruit-

ment, is mostly governed by temperature variability. Furthermore, the direct effect of

temperature on seasonal abundance (Escribano and Hidalgo, 2000), secondary production

(Escribano and McLaren, 1999), population size and body size (Ulloa et al., 2001) as well

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–9998

as on individual traits, such as reproductive state, lipid content, body weight and length

(Giraldo et al., 2002), altogether may be considered as sufficient evidence to support the

view that temperature is the driving force of population dynamics of C. chilensis at the

upwelling region off north Chile.

Acknowledgements

This work has been funded by FONDECYT-Chile, grant 199-0470. Partial support has

also been provided by the Oceanographic Center for the Eastern South Pacific (COPAS),

funded by FONDAP-CONICYT of Chile. We thank P. Hidalgo, J. Rodriguez and D.

Fernandez for helping during sampling and with the experiments. Valuable comments from

two anonymous reviewers have greatly helped clarify ideas and improve the work. [RW]

References

Boyd, C.M., Smith, S.L., Cowles, T.J., 1980. Grazing patterns of copepods in the upwelling system off Peru.

Limnol. Oceanogr. 25, 583–596.

Calbet, A., Trepant, I., Arin, L., 2000. Naupliar growth versus egg production in the calanoid copepod Centro-

pages typicus. Short Communication. J. Plankton Res. 22, 1393–1402.

Corkett, C.J., McLaren, I.A., Sevigny, J.-M., 1986. The rearing of the marine calanoid copepods Calanus

finmarchicus (Gunnerus), C. glacialis Jashnov and C. hyperboreus Kroyer with comment on the equipropor-

tional rule. Syllogeus - Can. Mus. Nat. 58, 539–546.

Daneri, G., Dellarossa, V., Quinonez, R., Jacob, B., Montero, P., Ulloa, O., 2000. Primary production and

community respiration in the Humboldt current system off Chile and associated oceanic areas. Mar. Ecol.

Prog. Ser. 197, 41–49.

Escribano, R., 1998. Population dynamics of Calanus chilensis in the Chilean eastern boundary Humboldt

current. Fish. Oceanogr. 7, 245–251.

Escribano, R., Hidalgo, P., 2000. Influence of El Nino and La Nina on the population dynamics of Calanus

chilensis in northern Chile. ICES J. Mar. Sci. 57, 1–8.

Escribano, R., McLaren, I.A., 1999. Production of Calanus chilensis in the upwelling area of Antofagasta,

northern Chile. Mar. Ecol. Prog. Ser. 177, 147–156.

Escribano, R., Irribarren, C., Rodriguez, L., 1996. Temperature and female size effects on egg production of

Calanus chilensis: laboratory observations. Rev. Chil. Hist. Nat. 69, 365–377.

Escribano, R., Irribarren, C., Rodriguez, L., 1997. The influence of food quantity and temperature on develop-

ment and growth of Calanus chilensis from northern Chile. Mar. Biol. 28, 281–288.

Escribano, R., Rodriguez, L., Irribarren, C., 1998. Temperature-dependent development and growth of Calanus

chilensis from northern Chile. J. Exp. Mar. Biol. Ecol. 229, 19–34.

Escribano, R., Marin, V., Hidalgo, P., 2001. The influence of coastal upwelling on the distribution of Calanus

chilensis in the Mejillones Peninsula (northern Chile): implications for its population dynamics. Hydrobio-

logia 453, 143–151.

Giraldo, A., Escribano, R., Marın, V., 2002. Spatial distribution of Calanus chilensis off Mejillones Peninsula

(northern Chile): ecological consequences upon upwelling. Mar. Ecol. Prog. Ser. 230, 225–234.

Gonzalez, H.E., Sobarzo, M., Figueroa, D., Nothig, E.-M., 2000. Composition, biomass and potential grazing

impact of the crustacean and pelagic tunicates in the northern Humboldt current area off Chile: differences

between El Nino and Non-El Nino years. Mar. Ecol. Prog. Ser. 195, 201–220.

Greenberg, A.E., Clesceri, L.S., Eaton, A.D. (Eds.), 1992. Standard Methods for the examination of Water and

Wastewater. American Public Health Association, Washington, DC, pp. 10–22.

Hart, R.C., 1990. Copepod post-embryonic durations. Pattern, conformity, and predictability. The realities of

C.G. Torres, R. Escribano / J. Exp. Mar. Biol. Ecol. 294 (2003) 81–99 99

isochronal and equiproportional development, and trends in the copepodid–naupliar durations ratio. Hydro-

biologia 206, 175–206.

Heinrich, A.K., 1973. Horizontal distribution of copepods in the Peru current region. Oceanology 13, 97–103.

Hidalgo, P., Escribano, R., 2001. Succession of pelagic-copepod species during the period 1996/1998 in northern

Chile: the influence of the 1997–98 El Nino. Hydrobiologia 453, 153–160.

Hirst, A.G., Lampitt, R.S., 1998. Towards a global model of in situ weight-specific growth in marine planktonic

copepods. Mar. Biol. 132, 247–257.

Huntley, M.E., Lopez, M.D.G., 1992. Temperature-dependent production of marine copepods: a global synthesis.

Am. Nat. 140, 201–242.

Hygum, B.H., Rey, C., Hansen, B.W., 2000. Growth and development of Calanus finmarchicus nauplii during a

diatom spring bloom. Mar. Biol. 136, 1075–1085.

Marın, V.H., Espinoza, S., Fleminger, A., 1994. Morphometric study of Calanus chilensis males along the

Chilean coast. Hydrobiologia 292/293, 75–80.

Marın, V.H., Escribano, R., Delgado, L.E., Olivares, G., Hidalgo, P., 2001. Nearshore circulation in a coastal

upwelling site off the northern Humboldt current system. Cont. Shelf Res. 21, 1317–1329.

Marshall, S.M., Orr, A.P., 1955. The Biology of a Marine Copepod Calanus finmarchicus (Gunnerus). Oliver &

Boyd, Edinburg.

McLaren, I.A., 1995. Temperature-dependent development in marine copepods: comments on choices of models.

J. Plankton Res. 17, 1385–1390.

Mullin, M.M., 1988. Production and distribution of nauplii and recruitment variability—putting the pieces

together. In: Rothschild, B.J. (Ed.), Toward a Theory on Biological–Physical Interactions in the World Ocean.

Kluwer Academic Publishing, Amsterdam, pp. 297–320.

Mullin, M.M., Stewart, E.F., Fuglister, F.J., 1975. Ingestion by planktonic grazers as a function of concentration

of food. Limnol. Oceanogr. 20, 259–262.

Ohman, M.D., Runge, J.F., 1994. Sustained fecundity when phytoplankton resources are in short supply: omni-

vory by Calanus finmarchicus in the Gulf of St. Lawrence. Limnol. Oceanogr. 39, 21–36.

Omory, M., Ikeda, T., 1984. Methods in Marine Zooplankton Ecology. Wiley, USA. 322 pp.

Parsons, T.R., LeBrasseur, R.J., Fulton, J.D., 1967. Some observations on the dependence of zooplankton grazing

on the cell size and concentrations of phytoplankton blooms. J. Oceanogr. Soc. Jpn. 23, 10–17.

Parsons, T.R., Maita, Y., Lalli, C.M., 1992. A Manual of Chemical and Biological Methods for Seawater

Analysis. Pergamon, Oxford.

Peterson, W.T., 1986. Development, growth, and survivorship of the copepod Calanus marshallae in the labo-

ratory. Mar. Ecol. Prog. Ser. 29, 61–72.

Peterson, W., 1998. Life cycle strategies of copepods in coastal upwelling zones. J. Mar. Syst. 15, 313–326.

Rodriguez, L., Escribano, R., Grone, G., Irribarren, C., Castro, H., 1996. Ecologıa del fitoplancton en la bahıa de

Antofagasta (23jS), Chile. Rev. Biol. Mar. (Valparaıso-Chile) 31, 1–16.

Thomas, A.C., Blanco, J.L., Carr, M.E., Strub, P.T., Osses, J., 2001. Satellite-measured chlorophyll and temper-

ature variability off northern Chile during the 1996–1998 La Nina and El Nino. J. Geophys. Res. 106,

899–915.

Vidal, J., 1980. Physioecology of zooplankton: I. Effects of phytoplankton concentration, temperature, and body

size on the growth rate of Calanus pacificus and Pseudocalanus sp. Mar. Biol. 56, 111–134.

Ulloa, O., Escribano, R., Hormazabal, S., Quinonez, R., Ramos, M., Gonzalez, R., 2001. Evolution and bio-

logical effects of the 1997–98 El Nino in northern Chile. Geophys. Res. Lett. 28, 1591–1594.

Wilkinson, L., 1990. SYSTAT: the System for Statistics. Systat, Evanston, IL.