Effects of 60Co Gamma Radiation on Crotamine

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Effects of 60Co Gamma Radiation on Crotamine Brazilian Journal of Medical and Biological Research (2001) 34: 1531-1538 Gamma radiation effects on crotamine 1531 ISSN 0100-879X Effects of 60Co gamma radiation on crotamine M. Boni-Mitake1, 1Departamento de Radioproteção Ocupacional, H. Costa2, 2Departamento de Bioengenharia, and P.J. Spencer2, 3Diretoria de Materiais, Instituto de Pesquisas Energéticas e V.S. Vassilieff4 Nucleares (IPEN/CNEN/SP), São Paulo, SP, Brasil and J.R. Rogero3 4Ceatox - Centro de Assistência Toxicológica, Instituto de Biociências, Universidade Estadual Paulista, Botucatu, SP, Brasil Abstract Correspondence Ionizing radiation can change the molecular structure and affect the Key words M. Boni-Mitake biological properties of biomolecules. This has been employed to · Crotamine Departamento de Radioproteção attenuate animal toxins. Crotamine is a strongly basic polypeptide (pI · Gamma radiation Ocupacional, IPEN, CNEN 10.3) from Crotalus durissus terrificus venom composed of 42 amino · Chromatography Travessa R, 400 acid residues. It induces skeletal muscle spasms leading to a spastic · Toxicity 05508-900 São Paulo, SP · Circular dichroism Fax: +55-11-3816-9221 paralysis of hind limbs in mice. The objective of the present study was E-mail: [email protected] to carry out a biochemical study and a toxic activity assay on native and irradiated crotamine. Crotamine was purified from C.d. terrificus Research supported by CNPq. venom by Sephadex G-100 gel filtration followed by ion-exchange M. Boni-Mitake was the recipient chromatography, and irradiated at 2 mg/ml in 0.15 M NaCl with 2.0 of a doctoral fellowship from CNPq kGy gamma radiation emitted by a 60Co source. The native and (No. 142068/95-0). Publication irradiated toxins were evaluated in terms of structure and toxic activity supported by FAPESP. (LD50). Irradiation did not change the protein concentration, the electrophoretic profile or the primary structure of the protein although differences were shown by spectroscopic techniques. Gamma radia- Received January 26, 2001 tion reduced crotamine toxicity by 48.3%, but did not eliminate it. Accepted September 4, 2001 Introduction Crotamine is a strongly basic polypeptide (pI 10.3) from the venom of the South Ameri- The vast majority of radiation effects on can rattlesnake Crotalus durissus terrificus. proteins in solution is due to the indirect It is composed of 42 amino acid residues action of radiation. When interacting with tightly reticulated by three disulfide bonds aqueous solutions, gamma radiation produces (4). This toxin was first reported by Gonçalves - - · several reactive species like e aq, O2 , H and and Vieira (5). Crotamine produces skeletal OH· as a result of radiolysis of water (1), muscle spasms leading to spastic paralysis of which, in turn, can modify the biological hind limbs in mice (6,7). It appears to affect activity of proteins and peptides by reacting the functioning of voltage-sensitive sodium with certain sites or groups in the molecules. channels of the skeletal muscle sarcolemma, These properties have been successfully inducing a sodium influx resulting in depo- employed to attenuate animal toxins (2,3), larization and contraction of skeletal muscle yielding suitable immunogens for antiserum (7). In the present report, we investigated production. some of the effects of gamma radiation on Braz J Med Biol Res 34(12) 2001 1532 M. Boni-Mitake et al. the structure and biological activity of this tored as above. The fraction was then desalted toxin. by dialysis against water and lyophilized. Material and Methods High-performance size exclusion chromatography Venom, animals and chemicals The purified crotamine was submitted to Crude air-dried venom from the South high-performance size exclusion chromatog- American rattlesnake C.d. terrificus was sup- raphy (SE-HPLC) on a 7.5 mm x 60 cm Toso plied by the Butantan Institute (São Paulo, Haas TSK 2000 SW column equilibrated SP, Brazil). Mice used in the experiment with 50 mM ammonium bicarbonate, pH were obtained from the colony housed in the 7.0, at 1 ml/min and 25ºC. The eluent was Department of Bioengineering, IPEN/CNEN monitored at 280 nm. (São Paulo, SP, Brazil). They were main- tained on a 12-h light/12-h dark cycle (lights Reversed phase high-performance liquid on at 7:00 h) in a temperature-controlled chromatography environment (22 ± 2ºC). Food and water were freely available. Salts and other chemi- Reversed phase (RP)-HPLC was per- cals used in this study were of the best formed for analytical purposes using a 3.9 x quality available (ACS grade). 300 mm C18 µBondapak column with a 0 to 60% linear gradient of acetonitrile (v/v) in Crotamine purification 0.04% trifluoroacetic acid, at a flow rate of 1 ml/min and 25ºC. The eluent was monitored Crude venom was dissolved in 100 mM at 280 nm. formic acid/ammonium formate, pH 3.0, to improve solubility (Rogero JR, unpublished Crotamine irradiation results), centrifuged at 12,100 g for 10 min to remove insoluble material, and fraction- Purified crotamine was dissolved in 0.15 ated on a 2.5 x 85 cm Sephadex G-100 M NaCl to a concentration of 2 mg/ml and column (Pharmacia-LKB, Uppsala, Sweden) irradiated with 2.0 kGy using gamma rays and equilibrated in the same buffer at a flow emitted by a Gammacell 220 60Co source rate of 0.2 ml/min at 4ºC, and the absorbance (Atomic Energy Agency of Canada Ltd.) in of the eluate was monitored at 280 nm. The the presence of O2, at room temperature and fraction corresponding to crotamine, as veri- with a dose rate of 800 Gy/h. fied by electrophoresis, was pooled and re- fractionated on a 1-ml Resource S column Electrophoresis (SDS-PAGE) (Pharmacia) connected to a dual pump FPLC system (Pharmacia) and equilibrated in buf- Slab gel electrophoresis of native and fer A (25 mM phosphoric acid/NaOH, pH irradiated crotamine in the presence of SDS 7.8). Buffer B was identical to buffer A, was carried out following the method de- except that it contained 2 M NaCl. After an scribed by Schägger and von Jagow (8). The initial 5.0-ml wash with 5% buffer B, elution separation gel consisted of a 16.5% mono- was started with a linear gradient for 30 ml mer with a 6% cross-linker. The marker kit (slope = 1%/ml). The column was then re- for low molecular weight was obtained from generated with 10 ml 100% buffer B fol- Promega Corp., Madison, WI, USA. Protein lowed by a 10-ml buffer A wash. The flow bands were visualized by staining with Coo- rate was 3.0 ml/min and the eluent was moni- massie brilliant blue G-250. Braz J Med Biol Res 34(12) 2001 Gamma radiation effects on crotamine 1533 Protein concentration for five cycles (12). The peptide sequences were determined using an Applied Biosys- The protein content was estimated by the tems 476A analyzer equipped with the stan- method of Lowry et al. (9) modified by dard sequencer program (13), and the detec- Miller (10), using BSA as standard. tion of phenylthiohydantoin derivatives by HPLC. Ultraviolet absorption spectra Amino acid analysis The ultraviolet (UV) absorption spectra between 230 and 350 nm were obtained Samples were hydrolyzed in constant using an Ultrospec III (Pharmacia Biotech, boiling 6 N HCl and phenol at 110ºC for 24 Uppsala, Sweden) spectrophotometer with h (14). After hydrolysis, the samples were automated recording and a 10-mm light path. dissolved in buffer and submitted to amino Native and irradiated crotamine solutions acid analysis on a Beckman 7300 instrument were used at 1.0 mg/ml in 150 mM NaCl. using ninhydrin detection (15). The blank employed for baseline subtraction consisted of 150 mM NaCl. Circular dichroism Lethality assays The circular dichroism (CD) spectra were obtained using a Jasco J-720 spectropola- Lethality was evaluated after intraperito- rimeter. The native and irradiated crotamine neal (ip) injection, 0.25 ml/animal, of the solutions were used at 125 µg/ml in 20 mM solution into male Swiss mice (25 ± 2 g). sodium acetate buffer, pH 4.0. Far UV CD Lethal dose values (LD50) were calculated scans were measured from 260 to 190 nm at according to the method of Spermann-Kärber a scanning rate of 20 nm/min, with a 2-s (11). Seven groups of 5 mice each were response in a 2-mm path cuvette. Spectra injected with serial dilutions of the native or were corrected for background by subtract- irradiated crotamine dissolved in 150 mM ing a scan of buffer alone. Each spectrum is NaCl. The starting concentrations for the the result of two accumulations. native and irradiated toxin were 15.2 mg/kg (dilution factor 1.5) and 24.8 mg/kg (dilu- Fluorescence quenching tion factor 1.3), respectively. Fluorescence was measured with a Hita- Bioactivity tests chi F-4500 spectrofluorimeter at 25ºC. Exci- tation and emission slit widths were set at 5 Forty micrograms of crotamine was in- nm. The excitation wavelength was set at jected ip into Swiss mice (18-22 g) to deter- 295 nm and the emission was fixed at 355 mine if it produced the characteristic para- nm. Measurements were performed on se- lytic signs of hyperextension of hind limbs ries of samples with a fixed toxin concentra- associated with small basic myotoxins. tion and increasing amounts of KI (0-200 mM) with a 10-mm light path cuvette. To Amino acid sequencing preserve ionic strength, KCl was added to the samples to give a final molarity of 200 To confirm the amino acid sequence of mM. The crotamine concentration was 4 x native and irradiated crotamine, the com- 10-8 M in 100 mM phosphate buffer, pH 7.
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