# Acute Toxicity of Leaf Extracts ofEnydra fluctuans Lour in Zebrafish (Danio rerio Hamilton)

Authors: Jobi Xavier; Kshetrimayum Kripasana
Journal: Scientifica
 (2020)

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## Abstract

The present study was focused on the concentration-dependent changes in oral acute toxicity of leaf extracts ofE. fluctuans in zebrafish. The study was also aimed at the details of histopathological changes in the gill, liver, brain, and intestine of zebrafish exposed to the leaf extracts of the plant E. fluctuans. Enydra fluctuans Lour is an edible semiaquatic herbaceous plant used widely for the alleviation of the different diseases. Since there were no toxicity studies conducted on this plant, the present study was an attempt to look into the elements of toxicity of the plants. Two types of experiments are conducted in the present study. First, the acute oral toxicity study was conducted as per the OECD guidelines 203. Second, histopathological changes were observed in the fishes exposed to the lethal concentrations of plant extract. The oral acute toxicity studies conducted on Zebrafish have revealed that the leave extracts of E. fluctuans were toxic to the tested fish at the concentration of 200 mg/kg body weight. The histopathological studies conducted on the intestine of treated fishes showed that treatment has induced rupturing of the villi structure and fusion of villi the membrane and detachment of the villi structure from the basal membrane of the intestine. The histology of the liver also showed severe vacuolization in the cells while it is not affected in control. The studies on gills showed the detachment of the basal epithelial membrane in the gills compared to control which might have led to death of the fish. The histopathological observations of brain tissues treated with test samples also revealed the marked impingement in the brain parenchyma while the control is normal without impingement of the brain.


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## Body

## 1. Introduction

With the development of herbal industry, people started to use many plant extracts in the preparations of herbal products commercially. People are of the assumption that all plant products are safe to consume and there is no need to investigate on their safety aspects. Many studies have not been conducted on the toxicity of those herbal products. The present study was designed to investigate on toxicity level of leaf extracts of the plantEnydra fluctuans Lour in the zebrafish. The toxic agent is mostly released from sources like leaf, fruits, and barks of plants, animals, and microorganisms. As a toxic agent, it will transmit the toxic substance through the various modes of transmission mainly via direct contact. A toxicology test is necessary, not only for allopathic medicine but also for complementary and alternative medicine to discover any adverse effects which are not known until the signs and symptoms develop upon high consumption [1]. The assessment of toxicity using acute toxicity bioassay can prove the safety of traditional medicine using the plant E. fluctuans and promote its consumption.The importance of toxicity testing is to provide dose-dependent changes against the toxicity effect, study the safety of components in the sample, and authenticate methods of investigating toxicity [2]. In the toxicity studies, Zebrafsh (Danio rerio) is used as a good model to study the toxicity effect. It is used to inspect the bioactive compounds of the sample through toxicity assay. Commonly used mammalian models have some drawbacks with higher cost and prolonged time for results, being yet ethically questionable [1, 3, 4]. Studies have proved that humans show genetically great similarities of genomic sequences and brain patterning with Danio rerio. Thus, this makes zebrafish an advantageous assay in exploring many diversions of toxicology study yielding a prompt outcome [4–6].Enydra fluctuans Lour (Figure 1) is an edible semiaquatic herbaceous plant belonging to the family Asteraceae. The vernacular name of this plant is Helencha, Hinchashak, and Harhach and the English name Water Cress and Marsh Herb etc [7]. The leaves are slightly bitter, and the leaves are used to cure inflammation, skin diseases, bronchitis, nervous disorders, leukoderma, biliousness, and small pox and as a laxative. It possesses biological value, and its fuel extract has been reported to own analgesic, cytotoxic, antimicrobial, hepatoprotective, hypotensive, CNS depressant, and antidiarrheal activity [8].Figure 1
Enydra fluctuans.The objectives of the present study were to investigate on concentration-dependent changes in oral acute toxicity of leaf extracts ofE. fluctuans in zebrafish. The study was also focused on the details of histopathological changes in the gill, liver, brain, and intestine of zebrafish exposed to the leaf extracts of the plant E. fluctuans. Histopathological evaluation is one of the important parts of the assessment of the adverse effects of the plant extracts on the whole organism. Plants are not always safe to consume as they may contain poisonous chemical compounds in the different parts of the plant. Many studies have revealed that the many plant extracts become toxic to the different organs on a concentration-dependent manner and can lead to lethality. Many of the herbal products that are used as remedy to different diseases are not undertaken for their toxicity level [8]. The present study was an attempt to understand the toxic level of the widely used plant E. fluctuans. In the present study, the hsitopathological studies were performed in fishes which showed the mortality. It is hypothesized that higher concentrations of the leaf extracts could be detrimental to the fish exposed to the leaf extracts and affect the susceptible organs which can be examined histopathologically. Since there are no published data on the histopathological evaluations of the fish exposed to the different concentrations of the leaf extracts of E. fluctuans, the present study has been undertaken.


## 2. Materials and Methods

### 2.1. Preparation of Ethanolic Leaf Extract ofEnydra fluctuans

Enydra fluctuans (Authentication/PDDUIAS/2019/01) was collected from Yaiskul of Imphal West of Manipur, India. The leaves of the plants were dried and ground into fine powder. The extracts of the plants were prepared using 5 g of the dried powder in 50 mL of the ethanol. The extracts were filtered using a rotary evaporator, and various concentrations of the test solutions were prepared.


### 2.2. Oral Acute Toxicity of Ethanolic Leaf Extract ofEnydra fluctuans

Acute toxicity of ethanolic leaf extract of plant samples ofEnydra fluctuans was tested for acute toxicity in the zebrafish model (Danio rerio-IAEC/CU/ZF/2018/01) as per the OECD guidelines 203 [9]. The fish were exposed to the test substance preferably for a period of 96 hours. Mortalities were recorded at 24, 48, and 96 hours, and the concentrations which kill 50 percent of the fish were recorded.The fish were inspected after 24, 48, 72, and 96 hours. Concentrations of 12.5, 25, 50, 100, 200, and 400 mg/L were selected as effective concentrations for performing the main toxicity tests of the plant extracts of different concentrations. The fish were exposed to the sample based on a static exposure regime. For every experiment, 7 healthy fishes were directly transferred into each prepared concentration. Control groups (7 fishes) were also included for each treatment. The mortalities were recorded at 24, 48, 72, and 96 hours before exposure, and the LD50 values were calculated [8]. Fish were considered dead if there is no visible movement and upon touching of the caudal peduncle produces no reaction. Dead fishes were removed when mortalities are recorded. LD 50 was determined based on the concentration of the test substance in water which killed 50 percent of a test batch of fish within a particular period of exposure was observed.


### 2.3. Statistical Analysis

The median lethal concentration (LC50) of the acute toxicity experiment was calculated from the data using the PROBIT function as described by Finney in 1971 [10] and analyzed by IBM SPSS Statistics 21.0 software with 95% confidence limits. The safe level estimation after 96 hr exposure of zebrafish to the leaf extracts of E. fluctuans was carried out based on the work in [11] and [12], Committee on Water Quality Criteria (CWQC, 1972) [13], National Academy of Sciences/National Academy of Engineering (NAS/NAE, 1973) [14], and International Joint Commission (IJC, 1977) [16].


### 2.4. Histopathology of Zebrafish Based on Acute Toxicity

Fish were euthanized after cold temperature anesthesia below 15°C, and the Liver, Heart, Brain, and intestine tissues were removed and smear stained with Haematoxylin and Eosin using standard protocols. For behavioral and motor toxicity, the swim motion test and dive tank test were performed. The gills and skin of experimental fish were collected after the 96 hr exposure period and fixed in 10% neutral buffered formalin and paraffin, sectioned at 5μm, and stained with Haematoxylin and Eosin.


## 2.1. Preparation of Ethanolic Leaf Extract ofEnydra fluctuans

Enydra fluctuans (Authentication/PDDUIAS/2019/01) was collected from Yaiskul of Imphal West of Manipur, India. The leaves of the plants were dried and ground into fine powder. The extracts of the plants were prepared using 5 g of the dried powder in 50 mL of the ethanol. The extracts were filtered using a rotary evaporator, and various concentrations of the test solutions were prepared.


## 2.2. Oral Acute Toxicity of Ethanolic Leaf Extract ofEnydra fluctuans

Acute toxicity of ethanolic leaf extract of plant samples ofEnydra fluctuans was tested for acute toxicity in the zebrafish model (Danio rerio-IAEC/CU/ZF/2018/01) as per the OECD guidelines 203 [9]. The fish were exposed to the test substance preferably for a period of 96 hours. Mortalities were recorded at 24, 48, and 96 hours, and the concentrations which kill 50 percent of the fish were recorded.The fish were inspected after 24, 48, 72, and 96 hours. Concentrations of 12.5, 25, 50, 100, 200, and 400 mg/L were selected as effective concentrations for performing the main toxicity tests of the plant extracts of different concentrations. The fish were exposed to the sample based on a static exposure regime. For every experiment, 7 healthy fishes were directly transferred into each prepared concentration. Control groups (7 fishes) were also included for each treatment. The mortalities were recorded at 24, 48, 72, and 96 hours before exposure, and the LD50 values were calculated [8]. Fish were considered dead if there is no visible movement and upon touching of the caudal peduncle produces no reaction. Dead fishes were removed when mortalities are recorded. LD 50 was determined based on the concentration of the test substance in water which killed 50 percent of a test batch of fish within a particular period of exposure was observed.


## 2.3. Statistical Analysis

The median lethal concentration (LC50) of the acute toxicity experiment was calculated from the data using the PROBIT function as described by Finney in 1971 [10] and analyzed by IBM SPSS Statistics 21.0 software with 95% confidence limits. The safe level estimation after 96 hr exposure of zebrafish to the leaf extracts of E. fluctuans was carried out based on the work in [11] and [12], Committee on Water Quality Criteria (CWQC, 1972) [13], National Academy of Sciences/National Academy of Engineering (NAS/NAE, 1973) [14], and International Joint Commission (IJC, 1977) [16].


## 2.4. Histopathology of Zebrafish Based on Acute Toxicity

Fish were euthanized after cold temperature anesthesia below 15°C, and the Liver, Heart, Brain, and intestine tissues were removed and smear stained with Haematoxylin and Eosin using standard protocols. For behavioral and motor toxicity, the swim motion test and dive tank test were performed. The gills and skin of experimental fish were collected after the 96 hr exposure period and fixed in 10% neutral buffered formalin and paraffin, sectioned at 5μm, and stained with Haematoxylin and Eosin.


## 3. Results

### 3.1. Oral Toxicity Studies of Ethanolic Extracts of the Leaf ofEnydra fluctuans in Danio rerio

The study conducted on acute oral toxicity revealed that the leaf extracts ofEnydra fluctuans were more toxic to Danio rerio. Medial lethal concentration (LC50) is considered the most accepted basis to determine the acute toxicity test. In this toxicity study, 100% mortality was observed which clearly indicated the toxicity of the plant extract. The LC50 values with 95% confidence intervals of different concentrations of the leaf extracts of E. fluctuans were 204.132, 170.513, 139.478, and 92.956 mg/L for 24, 48, 72, and 96 hrs, respectively (Table 1). Concentration-dependent change in the mortality during 24, 48, 72, and 96 hrs exposure to leaf extract for the plant sample was observed in the fishes experimented. The plant extract was found to be lethal on the first day of the experiment within 24 hr at the highest concentrations of 400 mg/L since it killed all the seven fishes in the experiment. A dose-dependent increase and the time-dependent decrease were observed in mortality rate as the exposure time increased from 24 to 96 hrs, the median lethal concentration was reduced. A negative perfect correlation was observed between the exposure time and the LC50 (Table 2).Table 1
Lethal concentration (LC50) of leaf extracts of Enydra fluctuans with 95% confidence limit depending on exposure time (hr).
Exposure (hr)
LC50 (mg/L)
95% confidence limit (mg/L)
Calculated chi-square (X2)
Lower
Upper
24
204.132∗
140.995
328.660
2.389∗∗
48
170.513∗
116.640
258.155
0.445∗∗
72
139.478∗
90.168
234.294
1.568∗∗
96
92.956∗
57.734
159.960
2.970∗∗
∗
n = 7; ∗∗no significant difference observed.Table 2
Correlation analysis between exposure time and LC50.
LC50
Exposure time
LC50
Pearson correlation
1
−0.966∗
Sig. (2-tailed)
0.034
N
4
4
Exposure time
Pearson correlation
−0.966∗
1
Sig. (2-tailed)
0.034
N
4
4
∗Correlation is significant at 0.05 level (2-tailed).Fish were considered dead if there is no visible movement and if touching of the caudal peduncle produces no reaction. Dead fishes were removed when mortalities are recorded. LD50 was determined based on the concentration of the test substance in water which killed 50 percent of a test batch of fish within a particular period of exposure. Toxic effects of this plant sample ofEnydra fluctuans were observed. At a dose of 200 mg/L >70%, mortality was observed in zebrafish. Mortality was not observed at 50 mg/L of plant extract. Lethal dose to kill 50% of test fishes is recorded as 400 mg/L and 200 mg/L at 24 hr and 96 hr exposure period, respectively. The results indicated that the ethanolic extract did not induce toxicity when using the dose of ≤50 mg/L (Table 1). No mortality was observed in the control during the experimental period. Variations were observed in safe levels estimated by different methods at 96 hrs of exposure of zebrafish to the leaf extracts of the plant as shown in Table 3.Table 3
Estimation of safe levels of the plant extracts at 96 hr of exposure.
96 hr LC50 (mg/L)
Method
AF
Safe level (mg/L)
92.956
Hart et al. [11]∗
3.5692
Sprauge [12]
0.1
9.2956
CWQC [13]
0.01
0.92956
NAS/NAE [14]
0.1–0.00001
9.2956 to 0.0009256
CCREM [15]
0.05
4.6478
IJC [16]
5% of 96 h LC50
4.6478
∗
C = 48 hr LC50 × 0.03/S2 where C is the presumable harmless concentration and S = 24 hr LC50/48 hrs LC50.


### 3.2. Histopathology of Treated Zebrafish ofEnydra fluctuans Plant Extract with Control

Treatment of the zebrafish with plant extracts induced the rupturing of the villi structure and fusion of the villi membrane and detachment of the villi structure from the basal membrane in the intestine (Figures2 and 3). Tissues treated with samples have shown detachment of the basal epithelial membrane in the gills compared to control (Figures 4 and 5). Liver tissue in treated samples also showed severe vacuolization in the cells (Figures 6 and 7). Brain tissue treated with test samples was marked with impingement in the brain parenchyma (Figures 8 and 9).Figure 2
Control-intestine.Figure 3
Intestine treated with leaf extract.Figure 4
Control-gill.Figure 5
Gill treated with leaf extract.Figure 6
Control-liver.Figure 7
Liver treated with leaf extract.Figure 8
Control-brain.Figure 9
Brain treated with leaf extract.Figures2–9. Histopathology of the intestine, liver, gills, and brain from Zebrafish exposed to 400 mg/L.


### 3.3. Behavioural Responses

The test fishDanio rerio exposed to various lethal concentrations of leaf extracts of E. fluctuans exhibited altered behavioral responses. It was observed that in lethal concentrations of plant extracts, hyperactive behavior was increased initially and subsequently reduced expressing the sign of distress. The body showed depigmentation along with mucus secretion. Reduced swimming performance and lethargic movements were observed in the fish exposed to lethal concentrations of the plant extracts.


## 3.1. Oral Toxicity Studies of Ethanolic Extracts of the Leaf ofEnydra fluctuans in Danio rerio

The study conducted on acute oral toxicity revealed that the leaf extracts ofEnydra fluctuans were more toxic to Danio rerio. Medial lethal concentration (LC50) is considered the most accepted basis to determine the acute toxicity test. In this toxicity study, 100% mortality was observed which clearly indicated the toxicity of the plant extract. The LC50 values with 95% confidence intervals of different concentrations of the leaf extracts of E. fluctuans were 204.132, 170.513, 139.478, and 92.956 mg/L for 24, 48, 72, and 96 hrs, respectively (Table 1). Concentration-dependent change in the mortality during 24, 48, 72, and 96 hrs exposure to leaf extract for the plant sample was observed in the fishes experimented. The plant extract was found to be lethal on the first day of the experiment within 24 hr at the highest concentrations of 400 mg/L since it killed all the seven fishes in the experiment. A dose-dependent increase and the time-dependent decrease were observed in mortality rate as the exposure time increased from 24 to 96 hrs, the median lethal concentration was reduced. A negative perfect correlation was observed between the exposure time and the LC50 (Table 2).Table 1
Lethal concentration (LC50) of leaf extracts of Enydra fluctuans with 95% confidence limit depending on exposure time (hr).
Exposure (hr)
LC50 (mg/L)
95% confidence limit (mg/L)
Calculated chi-square (X2)
Lower
Upper
24
204.132∗
140.995
328.660
2.389∗∗
48
170.513∗
116.640
258.155
0.445∗∗
72
139.478∗
90.168
234.294
1.568∗∗
96
92.956∗
57.734
159.960
2.970∗∗
∗
n = 7; ∗∗no significant difference observed.Table 2
Correlation analysis between exposure time and LC50.
LC50
Exposure time
LC50
Pearson correlation
1
−0.966∗
Sig. (2-tailed)
0.034
N
4
4
Exposure time
Pearson correlation
−0.966∗
1
Sig. (2-tailed)
0.034
N
4
4
∗Correlation is significant at 0.05 level (2-tailed).Fish were considered dead if there is no visible movement and if touching of the caudal peduncle produces no reaction. Dead fishes were removed when mortalities are recorded. LD50 was determined based on the concentration of the test substance in water which killed 50 percent of a test batch of fish within a particular period of exposure. Toxic effects of this plant sample ofEnydra fluctuans were observed. At a dose of 200 mg/L >70%, mortality was observed in zebrafish. Mortality was not observed at 50 mg/L of plant extract. Lethal dose to kill 50% of test fishes is recorded as 400 mg/L and 200 mg/L at 24 hr and 96 hr exposure period, respectively. The results indicated that the ethanolic extract did not induce toxicity when using the dose of ≤50 mg/L (Table 1). No mortality was observed in the control during the experimental period. Variations were observed in safe levels estimated by different methods at 96 hrs of exposure of zebrafish to the leaf extracts of the plant as shown in Table 3.Table 3
Estimation of safe levels of the plant extracts at 96 hr of exposure.
96 hr LC50 (mg/L)
Method
AF
Safe level (mg/L)
92.956
Hart et al. [11]∗
3.5692
Sprauge [12]
0.1
9.2956
CWQC [13]
0.01
0.92956
NAS/NAE [14]
0.1–0.00001
9.2956 to 0.0009256
CCREM [15]
0.05
4.6478
IJC [16]
5% of 96 h LC50
4.6478
∗
C = 48 hr LC50 × 0.03/S2 where C is the presumable harmless concentration and S = 24 hr LC50/48 hrs LC50.


## 3.2. Histopathology of Treated Zebrafish ofEnydra fluctuans Plant Extract with Control

Treatment of the zebrafish with plant extracts induced the rupturing of the villi structure and fusion of the villi membrane and detachment of the villi structure from the basal membrane in the intestine (Figures2 and 3). Tissues treated with samples have shown detachment of the basal epithelial membrane in the gills compared to control (Figures 4 and 5). Liver tissue in treated samples also showed severe vacuolization in the cells (Figures 6 and 7). Brain tissue treated with test samples was marked with impingement in the brain parenchyma (Figures 8 and 9).Figure 2
Control-intestine.Figure 3
Intestine treated with leaf extract.Figure 4
Control-gill.Figure 5
Gill treated with leaf extract.Figure 6
Control-liver.Figure 7
Liver treated with leaf extract.Figure 8
Control-brain.Figure 9
Brain treated with leaf extract.Figures2–9. Histopathology of the intestine, liver, gills, and brain from Zebrafish exposed to 400 mg/L.


## 3.3. Behavioural Responses

The test fishDanio rerio exposed to various lethal concentrations of leaf extracts of E. fluctuans exhibited altered behavioral responses. It was observed that in lethal concentrations of plant extracts, hyperactive behavior was increased initially and subsequently reduced expressing the sign of distress. The body showed depigmentation along with mucus secretion. Reduced swimming performance and lethargic movements were observed in the fish exposed to lethal concentrations of the plant extracts.


## 4. Discussion

In this study, we analyzed the sensitivity of the leaf extracts ofE. fluctuans in the experimental fish and have shown that the lethal effect of the leaf extract was highest on zebrafish at the exposure time of 96 hrs. The LC50 at 96 hrs of exposure of zebra fish in the present study was 92.956, which was greater than the LC50 of tests conducted with cd2+ and Zn2+ in zebrafish, i.e., 6.5 and 44.48 mg/L and also greater than the 96 hr LC50 with Cu2+ and Hg2+, i.e., 0.17 and 0.14 mg/L [17]. Studies conducted by Nwani et al. [18] on the fish Channa punctatus have revealed the toxicity and expressed in terms of LC50 for glyphosate and atrazine as 32.540 and 42.380 mg/L and the 96 hr LC50 with carbosulfan, as 0.268 mg/L. Acute oral toxicity studies of Momordica charantia in zebrafish also reported the lethality of the fish at the concentrations of 50 mg/kg bw of the plant extracts [8].Histopathology of zebrafish treated with the plant extracts and control was studied in the present study. Histopathological studies conducted on the gills, intestines, liver, and brain isolated from the treated fish showed abnormal conditions when compared with the control. The histopathological studies conducted on the intestine of treated fishes showed that treatment has induced rupturing of the villi structure and fusion of the villi membrane and detachment of the villi structure from the basal membrane of the intestine, which lead to the death of the fish. Intestinal villi (singular: villus) are small, finger-like projections that extend into the lumen of the intestine. Villi increase the internal surface area of the intestinal walls making available a greater surface area for absorption. The studies on gills showed the detachment of the basal epithelial membrane in the gills compared to control which might have lead to death of the fish. Several studies have been made in the past on the histological organization and physiology of gills in a variety of fishes [19]. Gills are very important for the fishes since they are the main site of gaseous exchange and involved in osmoregulation [20]. The studies conducted by Rajini et al. [21] have revealed that the structural damages of gill like inflammatory cell infiltration, minimal congestion in primary lamellae, fusion of secondary lamellae, diffused epithelial hyperplasia, and multifoci mucus cell hyperplasia were observed in the zebrafish exposed to the sublethal concentrations of combination pesticides [21].The present study conducted on the liver also showed severe vacuolization in the cells while it is not affected in control. Several studies on histopathology of the liver revealed that the swelling with nonlipid cytoplasmic vacuolation of diffusely distributed hepatocytes were seen consistently after mild acute and subacute liver injury. Rajini et al. reported that moderate, diffused to severe cytoplasmic vacuolation, diffused minimal to mild sinusoidal congestion, steatosis, pyknotic, and karyorrhectic nuclei with complete dissolution of necrotic hepatocytes were observed in the liver of fishes exposed to pesticides [22]. Severe necrotic liver damage was observed in the fish treated with the extracts of M. charantia and was considered the cause of damage, which happens due to the lethal doses of momordin [8]. Momordin is found to be one of the major phytocompounds present in the Momordica charantia, which has a pivotal role in the induction of toxicity in animals and fishes [8, 23]. Several lines of evidence point to the possibility that this change may reflect a cellular adaptation beneficial to the host, rather than a degenerative change. But, in the present study, since fishes exposed to toxic level were found to be dead, those cellular degenerations were clear evidence of toxicity. The histopathological observations of brain tissues treated with test samples also revealed the marked impingement in the brain parenchyma while the control is normal without impingement of brain. Histological investigation of the brain of Channa punctatus in response to acute and subchronic exposure to the pesticide Chlorpyrifos revealed detachment in the superficial zone of the stratum opticum, stratum marginal due to degeneration of neuronal cells, spongiosis, congestion, necrosis, and appearance of clear areas around the nucleus of mononuclear cells in the lining of the stratum fibrosum griseum superficiale, stratum griseum centrale, and stratum album central [24].


## 5. Conclusion

In view of the data of the present study, it can be concluded that the leaf extracts ofEnydra fluctuans is toxic to the fishes in a concentration-dependent manner and thus can be toxic to human beings at the higher concentrations. So, that dosage-dependent use of the plant is very much required to avoid toxicity. Lower concentrations of the plant extract are found to be safe and can be consumed in lower concentrations. It is also reported that the histopathological changes in fishes exposed to 200 mg/L are more severe and to be very cautious of the use of the plant in daily life.



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*Source: 3965376-2020-04-25.xml*