Erythrophoroma and Vertebral Dysplasia in Mystus gulio

Fishes found in polluted waters is susceptible to get affected by tumors which forms the base of the present study. The study is focused on Mytus gulio, a resident along the Veli lake stretch. This lake gets polluted from the nearby industrial stretches and also by human activities. On behalf of the study it was observe that the fishes were affected by tumour which was reddish in color with an unpigmented multilobular growth found at the caudal peduncle of the fish. Fusiform cells arranged in parallel arrays, multinucleate giant cells, pleomorphic cells and focal areas of hemorrhage with nests of tumor cells were interspersed throughout the tissue. Disposition of the vertebra, dysplastic vertebral bone, conical protrusion under the skin and at the base of the caudal fin etc. were noticed which is said to be the histopathological symptoms of erythrophorma, the tumor. The occurrence of these deformities was attributed to the intensity of industrial as well as sewage pollution in the environment. Through, the study it was found that infectious causes of deformities were of high percentage, so more studies and researches are to be done in the field and effective preventive measures must be put forward.

INTRODUCTION

Toxicants in aquatic systems causes adverse effects on fishes mainly tumours. Some types of tumors are effective monitors of ecosystem health. Even tumors caused by genomic interactions or by virus would not be good indicators. The present study is aiming to demonstrate tumors in fish from polluted areas and found to support a tumor-pollution linkage. Thus certain lesions in fish species or species groups may serve as a mechanism to assess one facet of ecosystem health. Mystus gulio (Hamilton-Buchanan, 1822) commonly known as Long Whiskers Cat fish, is widely distributed in the seas, estuaries and tidal waters of Sind, India and Burma (Day, 1878). Anthropogenic influx creates a wide array of disastrous effects on land as well as water which ultimately result in depletion of water quality. Pollutants in water include a wide spectrum of chemicals, pathogens, etc. These pollutants promote stress in the environment and there by negatively affects the natural system of living forms (Mukherjee, 2011). Several sites along Kerala are extremely under the threat of pollution from various sources especially Veli, Akkulam etc. (Anu and Latha, 2009).

Fish being a cheap source of rich protein for a balanced diet. Its culture and propagation have been given great priority in most of the developing countries. One of the serious problem faced in inland fisheries is the same problem (Moses et al., 2011; Sheela et al., 2011). Water pollution in India has become a major problem threatening the health of millions of people. Water pollution severely affects the aquatic life. India is today facing a serious problem of massive fish death and disease as an after effect of industrial pollution (Arvind, 2002). Some of the diseases which is seen to affect Mystus gulio and illustrated in the work are tumor, malformations in different tissues and deformity. The reasons for these malformations are attributed to the industrial effluents dumped to Veli Lake from Travancore Titanium Products, English clay factory and also from domestic sewage (Akiyama et al., 1986; Joseph et al., 2012; Baumann and Hamilton.,1984; Moses et al., 2011; Sheela et al., 2011). Tumors which are the non infectious diseases will affect the health of the fish (Paperna,1996). Contaminants or pollutants in water can be carcinogenic to aquatic wild life. Fish tumors have attracted the attention of several scientists (Smith, 2000; Matsusato, 1986; Paperna, 1996). Deformities have frequently been reported in fish and several factors have been attributed as causes for such conditions. Deformities may be due to lack of vitamins, infections by parasites, hereditary factors or mechanical injuries. Deformities caused by pollutants are reported by several scientists (Akiyama et al., 1986; Chonder, 1979; Koyama, 1996; Kraybill, 1976; Bengtsson, 1979; Srivastava, 1984; Das and Mukherjee, 2000; Murali and Anchrews, 1978; Shrestha, 1985). The main objective behind the present study is to cram the impact of pollutants on Mystus gulio and its after effects.

MATERIALS AND METHODS

Study site: The site selected for the present study was Veli Lake. It is a unique inland lake, separated by a narrow sand bar from the Arabian Sea. The lake is located in the outskirts of Thiruvananthapuram District. The Veli industrial area is situated at a distance of 10 km from the city. There are a number of large, medium and small industries along this area. The industrial area is affected by acute environmental problems causing adverse effects on health of the people. In addition to this, the water at Parvathi Puthanar gets polluted from the partly treated and untreated sewage discharged from the Sewage Treatment Plant.

Study period and sampling methods: The study was conducted for a period of one year from June 2010 to May 2011.

The samplings were made monthly using traditional fish capturing methods (http://www.ilmb.gov.bc.ca/risc/pubs/aquatic/fishcol/assets/fishml04.pdf). Mystus gulio was selected as the study material for the present study, as the fish showed abnormal tumorous growth. In the Laboratory the length (cm) and weight (g) of each sample was measured accurately to the nearest millimeter and milligram, respectively.

Histological procedure: The portion of the tumor along with caudal peduncle was fixed in 10% formalin after primary examinations during the study period. After fixation, the samples were rinsed in water, dehydrated in graded ethanol solutions, cleared in xylene and embedded in paraffin. Dewaxed sections (5-6 μm) were stained for histological and histochemical purposes with haematoxylin and eosin (H and E), Periodic-acid Schiff (PAS) and Alcian blue (pH 2.5). The sections were examined with a LEO 906 transmission electron microscope (Humason, 1979).

RESULTS

Tumor: The tumor noticed in M. gulio was reddish in color with an unpigmented multilobular growth found at the caudal peduncle of the fish (Fig. 1).

It was lightly collagenized, well vascularised, ulcerated and spindle shaped cell mass. Long delicate cytoplasmic extension provide a neural look. The biopsy from the outer edge of the lesion consisted of structurally intact epidermis (Fig. 2). The epidermis appeared normal and contained abundant mucous cells.The area beneath the basal lamina consisted of tumor cell pegs. Cells at the outer edge of the lesion were large and pleomorphic. Focal areas of hemorrhage were interspersed throughout the tissue (Fig. 3).

Fig. 1:	M. gulio with an unpigmented multilobular growth at the caudal peduncle (T-Tumor)

Fig. 2:	Biopsy showing structurally intact epidermis (ED: Epidermis, H: hemorrhage)

Fig. 3:	Area beneath the basal lamina with tumor (H: hemorrhage, BC: Blast cell)

Fig. 4:	Central part of the lesion with red pigmented granules (PG: Pigmented granules, MN: Multiple nucleoli)

Fig. 5:	Pleomorphic cells with large nuclei and multiple nucleoli (PG: Pigmented granules MN: Multiple nucleoli)

Nuclei also varied in size and shape and frequently contained multiple nucleoli. Multinucleate giant cells were also present. Deeper cells were fusiform, spindle shaped stellate and more uniform in size and shape. The fusiform cells were arranged in parallel arrays. Towards the central part of the lesion no uniform cellular morphology or tissue architecture was apparent.

Red pigmented granules were present (Fig. 4), large pleomorphic cells with large nuclei and multiple nucleoli were present (Fig. 5). Cells were fusiform and spindle shaped. The fusiform cells were arranged in parallel arrays, while the other type of cells in irregular pattern. Focal areas of haemorrhage and congested capillaries were also seen in the central part of the lesion. Focal nests of tumor cells (Fig. 6) were apparent in several areas.

Although pigment analysis were not made ,the morphologic characteristics of the tumor cells and the location of the lesion in a red pigmented area of the fish skin suggest diagnosis of erythrophoroma.

Fig. 6:	Focal nests of tumor cells (PG: Pigmented granulesm)

Fig. 7:	Caudal peduncle of M. guliowith (D: Deformity)

Fig. 8:	Conical protrusion under the skin deformity

Since the site of collection is subjected to industrial effluents as well as domestic sewage possibility of pollution can be one reason for the occurrence of tumor.

Deformity: The deformity was noticed at the caudal peduncle of M. gulio (Fig. 7). It was in the form of a conical protrusion under the skin and at the base of the caudal fin (Fig. 8).

Fig. 9:	Position of the vertebral column with associated muscle bands (VC: Vertebral column, MB: Muscle band)

Fig. 10:	Disposition of the vertebrae (VD: Vertebral disposition)

The caudal peduncle was bending approximately at 90°. Figure 9 represents the position of the vertebral column and the associated muscle bands.

Disposition of the vertebrae is shown in Fig. 10 and on the Fig. 11.The curvature of the vertebral column and the disposition of the vertebra had resulted in the formation of a tumor like outgrowth and the vertebral disposition was found continued to the tail (Fig. 12).

From these observations it could be inferred that the backbone makes a lateral curvature halfway between the dorsal fin and the caudal peduncle. The caudal tip of the backbone makes an abrupt 90° lateral bend and terminates in a spike to account for the protrusion grossly apparent on the caudal peduncle. Vertebral bone is slightly dysplastic proximal to the bend. There is no evidence of callus formation or inflammatory reaction associated with the bend to indicate a recent fracture. This combination of anomalies conclude that this deformity is due to the vertebral dysplasia and malformation following an old traumatic injury.

Fig. 11:	Disposition of the vertebrae (VD: Vertebral disposition)

Fig. 12:	Vertebral disposition was found continued to the tail (TG: tumorous growth, VD: Vertebral disposition)

DISCUSSION

Neoplasia occur commonly in some fishes from certain localities and the reports are on increase (Couch and Harshbarger, 1985; Paperna, 1996; Wellings, 1969). In the present study tumorous growth was observed on the caudal peduncle in M. gulio. Several neoplastic conditions have been reported due to parasites like digenetic trematodes. The occurrence of skin tumors in fish may have direct causal association with the presence in the marine environment of chemical carcinogens arising from industrial and other waste (Hard et al., 1979; Grace, 2007; Nigrelli et al., 1965; Stitch and Acton, 1976; Wellings, 1970). Furthermore, it is believed that fish species capable of expressing a high cancer prevalence may serve as a useful function as indicators of the quality and quantity of pollution (Hiraoka and Okuda, 1983; WHO, 1976). The present reports of diseased conditions in M. gulio was also made from the Veli Lake,a situation highly polluted with industrial effluents and sewage disposal. The accumulation of pollutants in soil can have a direct impact on the body as M. gulio being a bottom feeder. Occurrence of tumors is more frequent in bottom living fishes (Hard et al., 1979; Overstreet and Howse, 1976). They have observed pollutants as the major cause for the incidence of tumors in fish. However from the present study, although the environment was found to be highly polluted, a definite conclusion about the causative factor cannot be drawn.

The biopsy of the tumor shows the distribution of tumor cell pegs, focal areas of haemorrhage and a reddish hue to the presence of reddish pigment granules. The morphological characters of the tumor cell and the lesion in the red pigmented area of the skin suggest, the lesion as erythrophoroma. This report of erythrophoroma is similar to that reported in the ornamental carp Cyprinus carpio (Murchelano and Edwards, 1981).They have also reported the occurrence of red colored pigment and the presence of giant cells,fusiform spindle shaped and stellate cells which are arranged in parallel arrays.

Deformity: The mechanisms responsible for vertebral damage can be catagorized into two major factors, namely alterations of a structurally critical biological process or acute muscular contraction (Arvind, 2002). Causative agents acting by the first category include hereditary factors, defective embryonic development induced by high water temperature or low dissolved oxygen, radiation, dietary vitamin deficiencies (Vit.C and B₁₂) and toxic substances (Akiyama et al., 1986; Grace, 2007; Bernet et al., 1999; Ghittino, 1975; Kraybill, 1976; Koyama, 1996; Newsome and Piron, 1982; Nigrelli et al., 1965). Factors that could damage vertebrae by causing acute muscular contraction include parasitic infection, electrical current and toxic substances. A good many number of literature on the deformities of fish have been produced by several previous workers. Increased incidence of deformity to the lead content of the diet was also reported Mayer et al. (1977).There are also reports showing that lead caused spinal deformities by interfering with the metabolism of tryptophan. Some of the other important causative factors for the vertebral abnormalities are defects on the embryonic stage of development and mechanical injury to the fish (Baumann and Hamilton, 1984).

CONCLUSION

In the present study a disposition of the vertebrae was observed in the tail region. The reason attributed for the bend in the tail region was due to an old traumatic injury leading to the destruction of the vertebrae leading to a bend in the caudal region.