Here we provide evidence that both pharmacological and environmental manipulations similarly blunt the cortisol release in response to an acute stressor in adult zebrafish. Different groups of fish were maintained isolated or group-housed in barren or enriched tanks, and then exposed or not to diazepam or fluoxetine. Acute stress increased cortisol levels in group-housed zebrafish maintained in barren environment. Single-housed zebrafish displayed a blunted cortisol response to stress. Environmental enrichment also blunted the stress response and this was observed in both isolated and group-housed fish. The same blunting effect was observed in zebrafish exposed to diazepam or fluoxetine. We highlighted environmental enrichment as an alternative and/or complimentary therapeutic for reducing stress and as a promoter of animal welfare.
According to the regulatory agencies of research procedures and animal welfare1, experimental animals must be housed in environments with space and complexity to allow their normal behavioral expression. Thus, several studies have been conducted using environmental enrichment in behavioral experiments in rats2,3, mice4,5, humans6 and fish7,8.
One of the most used fish models is the teleost zebrafish (Danio rerio). Zebrafish have been used in several research areas due to genetic homology with humans9, as a model organism in neuroscience and behavioral studies, as well as to test candidate drugs10,11,12. The effects of many psychiatric drugs have been widely studied in relation to the zebrafish stress response13,14,15.
Zebrafish exhibit social behavior since early stages of life16, preferring swimming in shoals17. In fact, behavioral and endocrine responses may differ according to the housing conditions and thus may be particularly influenced by group and/or isolation18,19,20, as well as environment complexity.
However, to our knowledge, there are no studies regarding the effects of environmental enrichment, psychotropics and their association (environmental enrichment plus psychotropics) in different housing conditions on the zebrafish stress response. Hence the question: do environmental complexity and psychotropics modulate the stress neuroendocrine axis in different fish housing conditions? To answer this question, our strategy was to evaluate the acute stress response in single- or group-housed fish maintained in environmentally enriched or barren tanks, and exposed or not to diazepam or fluoxetine for a 15-day period.
Waterborne concentrations of FLU and DZP
Concentrations of FLU and DZP declined at 15 days after exposure compared to the nominal concentration. They remained above the range of ecologically relevant concentrations. Neither FLU nor DZP were detected in control water samples (Fig. 1A,B).
The basal cortisol levels were similar in all groups. Acute stress increased cortisol levels in group-housed zebrafish maintained in standard environment (barren tanks). Single-housed zebrafish displayed a blunted cortisol response to stress (Fig. 2C,D).
Environmental enrichment blunted the cortisol response to stress in both isolated and group-housed fish. The same effect was observed in zebrafish exposed to diazepam or fluoxetine (Fig. 2C,D).
Both diazepam and fluoxetine exposure blunted the cortisol response to stress in isolated and group-housed fish. The effects of diazepam in blunting the cortisol response were greater when combined with environmental enrichment (Fig. 2C,D). The 4-way ANOVA yielded significant main effects and interaction effects for housing, environment, stress and drug. Statistical data is shown in supplementary materials.
Here we provide evidence that both pharmacological and environmental manipulations similarly blunt the cortisol release in response to an acute stressor in adult zebrafish.
We achieve this conclusion since fish housed in environmental enriched tanks as well those exposed to fluoxetine or diazepam presented lower cortisol concentrations than fish housed in barren tanks. We also show that the environmental enrichment is capable to abolish the difference in cortisol concentrations between isolated and grouped zebrafish housed in barren tanks verified in our previous work19. Furthermore, cortisol levels after acute stress in fish housed in environmental enriched tanks are similar to unstressed fish.
We hypothesized that the stress-blunting effect of environmental enrichment occurs by providing fish a sense of safety or security in a natural environment with refuge alternatives. The difference between barren versus enriched is in the context in which the fish are housed, as the enriched environment is a natural environment that offers wellness with plants, sand and stones that can serve as protection from threats and interaction; while the barren aquarium does not meet these conditions making fish more vulnerable and therefore with a more responsive stress response – they remain on alert state.
In addition, after 15 days, the response to acute stress observed in fish housed in an enriched environment is similar to fish exposed to diazepam or fluoxetine. Although the inoculation of these drugs was made at the begin of the experimental period, the concentrations of fluoxetine measured at the end of the exposure period are sufficient to block the cortisol response to acute stress in zebrafish13. The lower concentrations measured reflect a combined effect of uptake by the fish21,22,23,24, adsorption to organic matter and photodegradation25,26. In the end of the exposure on day 15, drug concentrations remained above the range of ecological relevance27,28,29,30. Regarding DZP here show that the concentration at the end of exposure period blocked the response to acute stress. The decrease in the stress response by pharmacological agents (diazepam and fluoxetine) may represent the fish being susceptible to a possible lack of response when its needed, as the ability to promote ionic31, metabolic32 and behavioral15 necessary adjustments of the stress response.
Acute stress increases anxiety-like behavior, reduces social interaction and increases aggression in zebrafish that are modulated by fluoxetine and diazepam15. The similarity between the effect caused by environmental enrichment and exposure to drugs is thus reinforced by behavioral studies2,3,4,5,7.
The anxiolytic effect of environmental enrichment has been demonstrated in different species2,3,4,5,7. The preference by interaction with conspecific is abolished in fish isolated in enriched environment8, and in fish submitted to the acute exposure to fluoxetine and diazepam15.
Some studies show relationship between environmental enrichment and serotonin. In fact, environmental enrichment increases the expression of 5-HT receptors in mice5 and increase in threshold of pain33,34.
The environmental manipulation can be seen as a non-pharmacological approach to reduce the withdrawal symptoms2,35 and depressive-like behavior in rats2,5. In addition, environmental enrichment restores serum corticosterone and BDNF levels4,36 in the hippocampus of mice with Rett syndrome4 and rats submitted the prenatal morphine exposure36. In humans, environmental enrichment might be considered as a complementary treatment for autism6,37 and affective disorders and anxiety3,4,5,36.
Given the translational importance of zebrafish, we highlighted environmental enrichment as an alternative and/or complimentary therapeutic for reducing stress and as a promoter of animal welfare.
A stock population of 372 mixed-sex (50/50) adult wild-type zebrafish (Danio rerio), short-fin (SF) strain, was randomly distributed, isolated or in kept in groups of six fish in barren or enriched tanks and exposed for 15 days to diazepam or fluoxetine. A control group was submitted to the same experimental conditions but without pharmacological treatment (see the scheme in Fig. 2B).
This experimental setup was approved by the Ethics Commission for Animal Use of the Universidade de Passo Fundo, Brazil (Protocol #09/2014) and followed the guidelines of the Conselho Nacional de Controle de Experimentação Animal (CONCEA).
We used fluoxetine (Daforin®, EMS, Brazil) and diazepam (União Química, Brazil) at 50 μg/L and 16 μg/L, respectively based on previous results from13. We exposed fish to these drugs for 15 days. This period is considered a sufficient time to elicit different responses among isolated and grouped housed zebrafish19.
L tanks were equipped with biological filters, under constant aeration with air stone and under 14-10 h light-dark regime. We covered all the tanks to prevent water evaporation and to avoid fish jumping out of the tanks. Barren tanks consist of tanks containing only water while enriched tanks received sand and gravel as a bottom substrate, caps for refuge and natural plants (two branches of Cabombaceae and Pontederiaceae). See the Fig. 2A.
Water temperature was maintained at 27 ± 1 °C; pH 7.0 ± 0.2; dissolved oxygen at 6.3 ± 0.3 mg/L; total ammonia at <0.01 mg/L; total hardness at 6 mg/L; and alkalinity at 22 mg/L CaCO3. We fed fish twice a day with TetraMin (Tetra, Melle, Germany). During the experimental period, we did not change the water or remove wastes.
After the 15-day period, we applied an acute stress challenge in all fish by persecution with a pen net for 120 s. 15 minutes after the stress, fish were captured and immediately frozen in liquid nitrogen and stored at −20 °C until cortisol extraction. In order to prevent a possible stress response induced by manipulation, the time elapsed between capture and killing was less than 10 s. The 15-min time interval following stress is when cortisol level peaks38.
Whole-body cortisol determination
The extraction and measurement of cortisol from zebrafish have been described in detail by Barcellos et al.39. Briefly, each fish was weighed and minced, and a pool of three fish were minced and placed into a disposable stomacher bag with phosphate buffered saline. The contents were transferred to test tube and ethyl ether was added. The tube was vortexed and centrifuged and then frozen at liquid nitrogen and the unfrozen portion (ethyl ether containing cortisol) was decanted. The ethyl ether was transferred to a new tube and completely evaporated under a gentle stream of nitrogen, yielding a lipid extract containing the cortisol. The extract was stored at −20 °C until the ELISA was conducted on the samples suspended with 1 ml of PBS buffer.
Whole-body cortisol was measured in duplicate samples of tissue extract with a commercially available enzyme-linked immunosorbent assay kit (EIAgen™ CORTISOL test, BioChem ImmunoSystems). The specificity of the test was evaluated by comparing the parallelism between the standard curve and serial dilutions of the tissue extracts in PBS. The standard curve constructed with the human standards ran in parallel to that obtained using serial dilutions of zebrafish tissue extracts. In the linear regression test, a high positive correlation was found between the curves. The intra-assay coefficient of variation was 3.33–3.65%
Waterborne Concentrations of FLU and DZP
To determine the concentrations of FLU and DZP in the water, 0.2-L samples were collected from tanks and stored in amber glass bottles on days 0, 3, 6, 10, and 15. For each analysis, triplicate water samples were analyzed. All samples were filtered using 0.22-μm filters before the extraction.
Solid Phase Extraction (SPE)
For FLU extraction, the SPE Strata-X cartridges were conditioned with 10 mL methanol followed by 10 mL HPLC-grade water. Water samples (50 mL) containing FLU were slowly passed through the SPE cartridges at a flow rate of approximately 10 mL/min. After extraction, the cartridges were kept wet, and serial washes with 10 mL of HPLC-grade water were performed before they were vacuum-dried for approximately 10 min. Samples were eluted with 2 mL methanol acidified with acetic acid 0.1% and collected in disposable glass tubes. The DZP was injected after filtering.
Analyses were performed using a Shimadzu LCMS-8040 triple quadrupole mass spectrometer (Japan) with a binary pump. The analytical column was an XR-ODS III (150 × 2 mm, 2.2 μm particle size). The mobile phase consisted of: (A) water with 0.1% formic acid and (B) methanol. For the gradient elution, the percentage of (B) changed linearly as follows: 0 min, 5%; 2.0 min, 30%; 4.0 min, 95%; and 5.0 min, 5%; for re-equilibration after each analysis. The flow rate used was 0.3 mL/min and the injection volume was 10 μL. Column temperature was set at 40 °C. The MS/MS analysis was performed using electrospray ionization (ESI), with the source in the positive-ion mode, and selected reaction monitoring (SRM) acquisition. The transition with the highest intensity was selected for quantification and the transition with the second highest intensity was used as confirmation. Quantification was performed using an external standard method with a ten-point calibration curve. Linearity was confirmed using the Anderson-Darling normality test40,41 homogeneity of variances using the Cochran’s test42, and independence of residues using the Durbin-Watson test43,44. Regression parameters were estimated by ordinary least squares.
Cortisol data were analyzed by four-way ANOVA followed by Tukey’s multiple comparison test. FLU and DZP concentrations at 0 and 15 days after exposure were compared using a two-way ANOVA followed by the Tukey’s post hoc test. The homogeneity of variance was determined using Hartley’s test, and normality was assessed using the Kolmogorov–Smirnov test. Differences were considered significant at p < 0.05. Effect sizes were determined as partial Eta squared. The data are expressed as mean + standard error of mean (S.E.M).
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This study was funded by the Universidade de Passo Fundo and CNPq. L.J.G.B. hold CNPq research fellowships (301992/2014-2).
The authors declare no competing financial interests.
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Giacomini, A., Abreu, M., Zanandrea, R. et al. Environmental and Pharmacological Manipulations Blunt the Stress Response of Zebrafish in a Similar Manner. Sci Rep 6, 28986 (2016). https://doi.org/10.1038/srep28986
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