Mouse toxins

Reproductive Toxicity. No data are available that impHcate either hexavalent or trivalent chromium compounds as reproductive toxins, unless exposure is by way of injection. The observed teratogenic effects of sodium dichromate(VI), chromic acid, and chromium (HI) chloride, adininistered by injection, as measured by dose-response relationships are close to the amount that would be lethal to the embryo, a common trait of many compounds (111). Reported teratogenic studies on hamsters (117,118), the mouse (119—121), and rabbits (122) have shown increased incidence of cleft palate, no effect, and testicular degeneration, respectively. Although the exposures for these experiments were provided by injections, in the final study (122) oral, inhalation, and dermal routes were also tried, and no testicular degeneration was found by these paths. 

Sensitive to toxins, in this case means that the assay presents no false negative results. Primary hepatocytes can elucidate hepatotoxins, and mouse neuroblastoma cells can elucidate sodium channel-blocking neurotoxins therefore these assays can be used to screen for the appropriate toxins. 

It is obvious from the provisional risk assessment values for microcystins, and, being of the same order of magnitude of mammalian toxicity, similar values may be calculated for the cyanobacterial neurotoxins, that sensitive detection methods are required to detect these low concentrations of toxins. Of the biological methods of detection discussed earlier, the mouse and invertebrate bioassays are not sensitive enough without concentration of water samples, in that they are only able to detect mg of microcystins per litre. Only the immunoassays (ng-/rg 1 and the protein phosphatase inhibition assays (ng O... 

Not all cyanobacterial blooms and scums contain detectable levels of toxins. Indeed, the incidence of toxicity detection by mouse bioassay, and toxin detection by HPLC among environmental samples, ranges from about 40% to However, in view of this high occurrence, it is the policy of regulatory authorities and water supply operators in some countries to assume that blooms of cyanobacteria are toxic until tested and found to be otherwise. In the absence of available analytical facilities or expertise or for logistical reasons, this precautionary principle should be regarded as sensible and prudent. 

Diphtheria toxin, an exotoxin of Corynebacterium diphtheriae infected with a specific lysogenic phage, catalyzes the ADP-ribosylation of EF-2 on the unique amino acid diphthamide in mammalian cells. This modification inactivates EF-2 and thereby specifically inhibits mammalian protein synthesis. Many animals (eg, mice) are resistant to diphtheria toxin. This resistance is due to inability of diphtheria toxin to cross the cell membrane rather than to insensitivity of mouse EF-2 to diphtheria toxin-catalyzed ADP-ribosylation by NAD. 

Some Chemical Considerations Relevant to the Mouse Bioassay. Net toxicity, determined by mouse bioassay, has served as a traditional measure of toxin quantity and, despite the development of HPLC and other detection methods for the saxi-toxins, continues to be used. In this assay, as in most others, the molar specific potencies of the various saxitoxins differ, thus, net toxicity of a toxin sample with an undefined mixture of the saxitoxins can provide only a rough approximation of the net molar concentration. Still, to the extent that limits can be placed on variation in toxin composition, the mouse assay can in principle provide useful data on trends in net toxin concentration. However, the somewhat protean chemistry of the saxitoxins makes it difficult to define conditions under which the composition of a mixture of toxins will remain constant thus, attaining a reproducible level of mouse bioassay toxicity is difficult. It is therefore useful to review briefly some of the chemical factors that should be considered when employing the mouse bioassay for the saxitoxins or when interpreting results. Similar concepts will apply to other assays. 

Figure 9. Observed increases in mouse assay toxicity of test mixtures of shellfish meat and toxin Cl (4), hydrolyzed with varying concentrations of HCI acid. Two series of experiments are shown. The initial concentration of toxin Cl was uniform for all samples in a series. Toxicity is expressed on the vertical axis as percentage of the maximum toxicity attained for that series.

Figure 10. Calculated changes in the mouse bioassay toxicity of a sample initially containing 1 xmol of toxin C2. The horizontal axis represents the percentage of 11- -hydroxysulfate. The lower line indicates the toxicity of the sample with the 21-sulfo group intact, but with varying degrees of epimerization. The upper line indicates the toxicity of the corresponding carbamates, formed by hydrolysis of the 21-sulfo group.

The mouse bioassay for PSP, described in its original form by Sommer in 1937 (29), involves i.p. injection of a test solution, typically 1 mL, into a mouse weighing 17-23 g, and observing the time from injection to death. From the death time and mouse weight, the number of mouse units is obtained by reference to a standard table 1 mouse unit is defined as the amount of toxin that will kill a 20-g mouse in 15 min (77). The sensitivity of the mouse population used is calibrated using reference standard saxitoxin (70). In practice, the concentration of the test solution is adjusted to result in death times of approximately 6 min. Once the correct dilution has been established, 5 mice will generally provide a result differing by less than 20% from the true value at the 95% confidence level. The use of this method for the various saxitoxins and indeterminate mixtures of them would appear... 

Detection of the PSP toxins has proven to be one of the largest hurdles in the development of analytical methods. The traditional means, and still in wide use today, is determination of mouse death times for a 1 mL injection of the test solution. There are a variety of drawbacks to utilization of this technique in routine analytical methods, that have prompted the search for replacements. In 1975 Bates and Rapoport (3) reported the development of a fluorescence technique that has proven to be highly selective for the PSP toxins, and very sensitive for many of them. This detection technique has formed the basis for analytical methods involving TLC (77), electrophoresis (72), column chromatography (7J), autoanalyzers (7 ), and HPLC (5,6,7). 

Species, Strain, and Source Toxin Term Structure ip. Mouse... 

Assays of ciguatoxin. Determination of ciguatoxin levels in fish was carried out in many laboratories by mouse assays. Enzyme immunoassay to screen inedible fish has been proposed by Hokama (9). No specific chemical assay has been developed, as information on functional groups suitable for fluorescence labeling is not available. Analyses conducted in the authors laboratory on remnant fish retrieved from patients meals indicated that ciguatoxin content as low level as 1 ppb could cause intoxication in adults. An extremely high sensitivity and a sophisticated pretreatment method will be required for designing a fluorometric determination method for the toxin. 

MTX exceeds any other marine toxins known in the mouse lethality (0.13 ig/kg) and is 80 times more potent than commercial saponin (Merck) in hemolytic activity. According to Terao (72), MTX induced severe pathomorphological change in the stomach, heart and lymphoid tissues in mice and rats by i.p. injection of 200... 

Palytoxin isolated from zoanthids Palythoa spp. is known to be extremely lethal (0.5 fig/kgy mouse, i.p.) and to have the most complicated natural product structure (Figure 4) ever elucidated (13,14). The toxin was later revealed to be a potent tumor promoter (15). Yet, health risks due to the toxin have remained unclear, as the zoathids are the most unlikely organisms to be regarded as foodstuff. Recently, however, data are being compiled to indicate the wide distribution of this toxin among marine biota. 

Deteimination of palytoxin. A mouse bioassay method proposed by Teh and Gardiner (25) for determination of L. pictor toxin (=palytoxin) was useful in our studies on the palytoxin-containing animals. The toxin amount in mouse units (MU,... 

In addition to okadaic acid, dinophysistoxin-1 (i.e., 35-methylokadaic acid), 7-0-palmitoyl-okadaic acid, and pectenotoxin 2 are reported to be diarrhetic toxins from shellfish 34). Application of 1 xg of dinophysistoxin-1 to mouse ear caused as strong irritation as the same dose of okadaic acid. Interestingly, the potencies of these compounds in the irritant test on mouse ear correlated well with their potencies as diarrhetic shellfish poisons. Dinophysistoxin-1 induced ODC activity as strongly as okadaic acid. Recently, we found that dinophysistoxin-1 is also a new non-TPA type tumor promoter with as high activity as okadaic acid 35). 

Figure 2. Relative toxicity (LD50 and LD qq) estimates for actiniid sea anemone toxins upon crabs (Carcimis maenas) and mice. Values for Anemonia sulcata (As) and Anthopleura xanthogrammica (Ax) toxins are from ref. 24 data for Condylactis gigantea and Phyl-lactis flosculifera toxins are unpublished (Kem). The arrows indicate that the real mouse LD q values for Cg II and Pf II must exceed the values indicated in the Ogure. Although insufficient data are presently available to quantitatively define a relationship between mammalian and crustacean toxicity, it seems that there is usually an inverse relationship, which may be approximately defined by the stipple zone.

Homogenates of MetruUum senile, possibly the world s most common large sea anemone, yield extracts that are powerfully hemolytic for washed mammalian erythrocytes (22). The active substance, metridiolysin, is a protein of molecular weight approximately 80,000. In contrast to the sphingomyelin-inhibitable toxins, metridiolysin is an acidic protein having a pi of about 5. It is thermolabile and is inactivat by proteolytic enzymes. The optimal pH for hemolysis is between 5 and 6, and at pH 8 the lysin is inactive. It can be dissociated into two subunits of unequal size. Besides being cytolytic in vitro, metridiolysin is lethal when injected intravenously into mice. As shown in Table IV erythrocytes from the horse or dog are about a hundred times as sensitive to lysis as those from the mouse, and erythrocytes from other animals tested are intermediate in sensitivity. 

All sea snakes are poisonous and their venoms are extremely toxic. The LD q for crude sea snake venom can be as low as 0.10 fig/g mouse body weight (i). For purified toxin the LD q is even lower, suggesting the high toxicity of sea snake toxins and venoms. This toxicity is derived from the presence of potent neurotoxins. Compared to snake venoms of terrestrial origin, sea snake venoms have been studied less. Different enzymes reported to be present or absent are summarized in Table I. 

Safety tests. Beeause many vaccines are derived from basic materials of intense pathogenieity— the lethal dose of a tetanus toxin for a mouse is estimated to be 3 x 10 (ig—safety testing is of paramount importance. Effective testing provides a... 

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