Distribution of Clostridium botulinum.

The distribution of Clostridium botulinum in the natural environments of Denmark, The Faroe Islands, Iceland, Greenland, and Bangladesh was examined. A total of 684 samples were tested. Type E was found in 90% of samples from the aquatic environment of Denmark, including sediments from young artificial lakes, and in 86% of samples from the marine environment of Greenland. Type E was not found in Danish cultivated soil and woodlands, including cultivated soil from reclaimed sea beds, but type B was frequently demonstrated in these environments. C. botulinum types A, B, or E were found in 2.6% of samples from the environments of the Faroe Islands and Iceland, whereas types C or D were demonstrated in 42% of samples from Bangladesh. The incidence of type E in aquatic sediments was not related to general industrial pollution or a high content of rotting vegetation. Fish or a rich aquatic fauna, on the other hand, appeared to contribute to a high incidence of type E. Based on these findings, it is suggested that type E is a true aquatic organism, because this environment offers the best conditions for survival of the spore in nature. It is further suggested that its presence in aquatic bottom deposits is based on sedimentation after proliferation in the carrion of the aquatic fauna and dissemination by water currents and migrating fish.     

Plasmids in Clostridium botulinum and related Clostridium species.

Toxigenic Clostridium botulinum and nontoxigenic C. sporogenes, C. subterminale, and C. botulinum-like organisms from a variety of sources were screened for plasmids. Of the 68 toxigenic C. botulinum isolates, 56% carried one or more plasmids, ranging in mass from 2.1 to 81 megadaltons. Within individual groups (based on the type of neurotoxin produced), many strains showed identical plasmid banding patterns on agarose gels. Of the 15 nontoxigenic strains tested, 40% also carried one or more plasmids ranging from 1.7 to 25.0 megadaltons, with both unique and common banding patterns represented. A total of 67 plasmids from both toxigenic and nontoxigenic strains were detected. At this time, no phenotypic functions have been assessed for these plasmids, and they must therefore be considered cryptic. A variety of lysing and extraction techniques were necessary to detect plasmids in the different C. botulinum groups.     

Bile acid inhibition of Clostridium botulinum.

Bile acids and their glycine and taurine conjugates were tested in vitro for inhibition of Clostridium botulinum types A and B. Cholic acid inhibited most strains at 2 mg/ml, whereas chenodeoxycholic acid inhibited all strains at 0.4 mg/ml. Deoxycholic acid inhibited one strain at 0.08 mg/ml and other strains at 0.4 and 2 mg/ml. Lithocholic acid inhibited all strains at 0.016 mg/ml. Glycine conjugates also showed considerable inhibition of some strains, whereas taurine conjugates were inactive.     

Bile acid inhibition of Clostridium botulinum.

Bile acids and their glycine and taurine conjugates were tested in vitro for inhibition of Clostridium botulinum types A and B. Cholic acid inhibited most strains at 2 mg/ml, whereas chenodeoxycholic acid inhibited all strains at 0.4 mg/ml. Deoxycholic acid inhibited one strain at 0.08 mg/ml and other strains at 0.4 and 2 mg/ml. Lithocholic acid inhibited all strains at 0.016 mg/ml. Glycine conjugates also showed considerable inhibition of some strains, whereas taurine conjugates were inactive.     

Clostridium botulinum in the Gulf of Thailand.

A survey was carried out to determine the incidence of Clostridium botulinum in samples of mud, sand, and fish from the Gulf of Thailand. Enrichment cultures from 762 samples of mud and sand from seven different areas around the Gulf were tested. C. botulinum type D was present in 10 samples, and type E was present in 2 samples taken from the west coast at Hua Hin. Enrichment cultures from 16,773 fish grouped into 2,151 samples yielded 10 filtrates containing C. botulinum type D and 5 containing type E. All of the toxic filtrates were obtained from samples of fish taken from the west coast of the Gulf of Thailand.     

Clostridium botulinum in the Gulf of Thailand.

A survey was carried out to determine the incidence of Clostridium botulinum in samples of mud, sand, and fish from the Gulf of Thailand. Enrichment cultures from 762 samples of mud and sand from seven different areas around the Gulf were tested. C. botulinum type D was present in 10 samples, and type E was present in 2 samples taken from the west coast at Hua Hin. Enrichment cultures from 16,773 fish grouped into 2,151 samples yielded 10 filtrates containing C. botulinum type D and 5 containing type E. All of the toxic filtrates were obtained from samples of fish taken from the west coast of the Gulf of Thailand.     

Transposon Tn916 mutagenesis in Clostridium botulinum.

The study of toxinogenesis and other properties in Clostridium botulinum is limited by the absence of genetic methods that enable construction of defined mutants. In this study, tetracycline-resistant transposon Tn916 in Enterococcus faecalis was conjugatively transferred in filter matings to group I Clostridium botulinum strains Hall A and 113B. The Tn916 transfer frequencies to C. botulinum ranged from 10(-8) to 10(-5) Tcr transconjugant per recipient depending on the donor strain. Southern blot analyses of EcoRI or HindIII chromosomal digests extracted from randomly selected Tcr transconjugants showed that the transposon inserted at different sites in the recipient chromosome, and the copy number of Tn916 varied from one to three. Tn916 insertion gave several different auxotrophic mutants. This approach should be useful for the study of genes important in growth, survival, and toxinogenesis in C. botulinum.     

Survival of Clostridium botulinum Spores

Radiation survival curves of spores of Clostridium botulinum strain 33A exhibited an exponential reduction which accounted for most of the population, followed by a “tail” comprising a very small residual number [7 to 0.7 spore(s) per ml] which resisted death in the range between 3.0 and 9.0 Mrad dose levels. The “tail” was not caused by protective spore substances released into the suspensions during irradiation, by the presence of accumulated radiation “inactivated” spores, or by heat shock of pre-irradiated spores. The theoretical number of spore targets which must be inactivated by irradiation was estimated both by a graphical and by a computation method to be about 80, and the D value was calculated to be 0.295 and 0.396 Mrad, respectively, in buffer and in pork pea broth.     

Transposon Tn916 mutagenesis in Clostridium botulinum.

The study of toxinogenesis and other properties in Clostridium botulinum is limited by the absence of genetic methods that enable construction of defined mutants. In this study, tetracycline-resistant transposon Tn916 in Enterococcus faecalis was conjugatively transferred in filter matings to group I Clostridium botulinum strains Hall A and 113B. The Tn916 transfer frequencies to C. botulinum ranged from 10(-8) to 10(-5) Tcr transconjugant per recipient depending on the donor strain. Southern blot analyses of EcoRI or HindIII chromosomal digests extracted from randomly selected Tcr transconjugants showed that the transposon inserted at different sites in the recipient chromosome, and the copy number of Tn916 varied from one to three. Tn916 insertion gave several different auxotrophic mutants. This approach should be useful for the study of genes important in growth, survival, and toxinogenesis in C. botulinum.     

Toxin production by Clostridium botulinum in grass.

Investigations on farms where botulism has occurred in cows showed that proteolytic Clostridium botulinum type B was present in newly made grass silages. Experiments were undertaken to study growth and toxin production of C. botulinum in grass. Of the strains tested only proteolytic strains of C. botulinum types A and B were able to produce toxin with grass as a substrate. Proteolytic strains of type B produced both medium (12S) and large (16S) toxin forms. The minimal water activity (aw) for toxin production at pH 6.5 and 5.8 was 0.94. At pH 5.3, toxin was produced at an aw of 0.985. These results indicate that proteolytic strains of C. botulinum (if present) may multiply and produce toxin in wilted grass silages.     

Toxin production by Clostridium botulinum in grass.

Investigations on farms where botulism has occurred in cows showed that proteolytic Clostridium botulinum type B was present in newly made grass silages. Experiments were undertaken to study growth and toxin production of C. botulinum in grass. Of the strains tested only proteolytic strains of C. botulinum types A and B were able to produce toxin with grass as a substrate. Proteolytic strains of type B produced both medium (12S) and large (16S) toxin forms. The minimal water activity (aw) for toxin production at pH 6.5 and 5.8 was 0.94. At pH 5.3, toxin was produced at an aw of 0.985. These results indicate that proteolytic strains of C. botulinum (if present) may multiply and produce toxin in wilted grass silages.