The rapid worldwide decline in frog populations is now a well recognized phenomena which has attracted research efforts from scientists all over the planet in a concerted effort to understand the causes for this alarming occurrence. This problem has also attracted the attention of the World Conservation Union (IUCN) and the Species Survival Commission (SSC) which established the Declining Amphibian Populations Task Force (DAPTF) in 1991. The World Conservation Union is an umbrella organization linking many governmental and non-governmental organizations around the world. The SSC is the largest Commission within the IUCN. The DAPTF is a global network of biologists and conservationists concerned with the issue of declining amphibian populations.
There are good reasons for thinking that the disappearance of amphibians from human impacted and pristine environments is particularly alarming. Amphibians may be serving as a measure of the health of the environment; they perform important ecological functions, are a source of biomedicinal supplies (drugs manufactured from frog skins) and have an overall aesthetic appeal.
Several reasons have been proposed for the decline in amphibian populations including:
In 1996 we conducted a study designed to answer the question: Can adult frogs sense the pH of their environment and orient themselves towards a favorable pH? The results of this study, were published in the September 99 issue of the Journal of Herpetology (see JH_1999.pdf), and described in short below.
We exposed adult Rana pipiens to mild aci d conditions for a ten day period under controlled laboratory conditions. Frogs exposed to citrate buffered water at pH 5.5 for 10 days exhibited 72% mortality as compared with 3.5% mortality in the control group held at pH 7.0. Furthermore, within the pH 5.5 group there was a difference in the acid sensitivity based on the physiological state of the frogs. Frogs that had recently emerged from hibernation exhibited 100% mortality within the first four days of exposure to pH 5.5. This contrasts to frogs that were post breeding and suffered 58% mortality throughout the ten days of the experiment. Our results suggest that Rana pipiens are sensitive to mild acidic conditions, especially those emerging from hibernation.
We pondered whether Rana pipiens exposed to pH 5.5 elevate their metabolism as a response to this stress. Our data indicates that whole body metabolism of acid-exposed frogs for ten days, is not different from the metabolism of frogs exposed to pH 7.0 during the entire experimental period, in spite of the large differences in their survival (see abstract SICB 1998).
Based on data from several experiments we have developed a theoretical model (See JEB 2003) that provides a possible explanation for the effects of environmental acidification on the natural defense mechanisms of ranid frogs. This model also suggests that different parts of the natural defense systems of Rana pipiens exhibit differential sensitivities to acid exposure. We suggest that the gut epithelia may be compromised when frogs are exposed to an environmental pH of 6.0. In contrast, frogs exposed to pH 6.0 have the same total number of WBC/spleen as controls (frogs exposed to pH 7.0), the same percent WBC as controls and the same percent viable WBC (Journal of Herpetology 2002).
We are the first to demonstrate acid sensitivity of adult R. pipiens (Vatnick
et al, 1999). Our results fit well with hypotheses by other investigators
(Glorioso et al., 1974; Carey, 1993; Maniero and Carey, 1997). These authors
suggested that environmental stress is the initiating factor in a cascade
of physiological events. These events may start with immunosuppression
followed by systemic distribution of opportunistic and virulent bacteria,
and may ultimately lead to the death of adult frogs. We have recently published
(Environmental Toxicology and Chemistry 2006) further evidence to our model (See
JEB 2003) and
suggested that environment pollutants and toxicants serve as immunosupressors
(see also
SETAC GLOBE 2004
for our first coining of the term).
We also examined the interaction of cold and acid exposure on the immune
function of ranid frogs and found out that cold exposure by itself does
not cause a systemic bacterial infection in adult Rana pipiens, but acid
stress following cold exposure does (
Journal of Experimental
Zoology 2003).
Our most current experiments use peritoneal thyoglycollate injections
to induce an inflammatory response. This technique is widely used
to study immune responses in several species. We are working on characterization
of the acid effects on the amelioration of this response. We are interested
in the signals involved in the initation and supression of the immune
response in the presence and absence of an acidic environment. Specifically,
we are studying the role of Corticosterone and C Reactive Proteins (see our SICB 2003
poster)
Recently we have investigated the effects of atrazine on the natural defense
mechanisms of Rana pipiens. Atrazine exposure suppresses the innate
immune response of these frogs in very similar ways that acid does (see
SETAC GLOBE 2004).
Therefore we coined the term "immune disruptors" to describe environmental
pollutants that disrupt immune function to parallel the term endocrine
disruptors commonly used to describe the effect of certain environmental
pollutants on endocrine function.
References
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Blaustein, A.R. and Wake D. B. (1995). The puzzle of declining amphibian populations. Scientific American 272 : 52-57.
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