Abstract:Exposure to the mutagen triethylenemelamine on rat bone marrow, blood, and testis was studied using flow cytometry of DAPI-stained nuclei. Increased coefficients of variation (CVs) of the GI peaks were observed in bone marrow and blood after both 1 d and 5 d exposures. After 5 d exposure and 7 d recovery both tissues had recovered, in some cases to significantly lower CVs. Increased CVs of the 1C peak of testis were observed only after 5 d exposure to the high dose with no subsequently observed recovery. Bone … Show more
“…This distress may be indicative of toxicological antagonism at an end point other than chromosomal damage. Two recent studies have observed a similar phenomenon in whole animal studies and reached similar conclusions (18,22). This hypothesis is further supported by the observation that when all three herbicides are combined at the lower concentrations, the CVs are higher than the CVs of cells exposed to the same trio of chemicals at a higher concentration (see Tables 1 and 2).…”
Pesticide contamination of drinking water supplies has increased over the past decade. A major concern is how exposure to combinations of low levels of pesticides, especially herbicides, could affect public health. Flow cytometric analysis was performed to determine the dastogenic potential of herbicide interaction on Chinese hamster ovary (CHO) cells. The cells were exposed to atrazine, simazine, cyanazine, and all possible combinations of these chemicals for 48 hr. Two concentrations were used for each sample: the U.S. EPA maximum contmination level (MCL) and the highest contamination level found in Illinois water supplies. Nuclei were isolated from the cells and analyzed by flow cytometry. The efects of dastogenicity were measured by the coefficient of variation (CV) of the Gi peak of whole cells and the change in CV of the largest chromosome in the flow karyotype. At both levels tested, atrazine caused chromosomal damage to the CHO cells. Simazine was observed to induce whole-ell clastogenicity but not flow karyotype damage. Cyanazine did not induce any measurable chromosomal damage in either analysis. Each of the herbicides, although all three were triazines, had di&Terent efcts with respect to chromosome damage as measured by flow cytometry. CHO ceLls treated with a combination of atrazine and simazile, or atrazine and cyanazine, were observed to have whole-cell and flow karyotype damage. This damage was, however, equal to or less severe than the damage caused by either atrazine or simazine alone. No synergy was observed. When all three herbicides were combined, three of the four possible combinations gave no observable dastogenic response.
“…This distress may be indicative of toxicological antagonism at an end point other than chromosomal damage. Two recent studies have observed a similar phenomenon in whole animal studies and reached similar conclusions (18,22). This hypothesis is further supported by the observation that when all three herbicides are combined at the lower concentrations, the CVs are higher than the CVs of cells exposed to the same trio of chemicals at a higher concentration (see Tables 1 and 2).…”
Pesticide contamination of drinking water supplies has increased over the past decade. A major concern is how exposure to combinations of low levels of pesticides, especially herbicides, could affect public health. Flow cytometric analysis was performed to determine the dastogenic potential of herbicide interaction on Chinese hamster ovary (CHO) cells. The cells were exposed to atrazine, simazine, cyanazine, and all possible combinations of these chemicals for 48 hr. Two concentrations were used for each sample: the U.S. EPA maximum contmination level (MCL) and the highest contamination level found in Illinois water supplies. Nuclei were isolated from the cells and analyzed by flow cytometry. The efects of dastogenicity were measured by the coefficient of variation (CV) of the Gi peak of whole cells and the change in CV of the largest chromosome in the flow karyotype. At both levels tested, atrazine caused chromosomal damage to the CHO cells. Simazine was observed to induce whole-ell clastogenicity but not flow karyotype damage. Cyanazine did not induce any measurable chromosomal damage in either analysis. Each of the herbicides, although all three were triazines, had di&Terent efcts with respect to chromosome damage as measured by flow cytometry. CHO ceLls treated with a combination of atrazine and simazile, or atrazine and cyanazine, were observed to have whole-cell and flow karyotype damage. This damage was, however, equal to or less severe than the damage caused by either atrazine or simazine alone. No synergy was observed. When all three herbicides were combined, three of the four possible combinations gave no observable dastogenic response.
“…Nuclei of disrupted kidney, liver and spleen cells were stained with propiduim iodide and analysed with a Coulter Profile II flow cytometer (Coulter Electronics Inc., Krefeld, Germany) equipped with a 488‐nm Argon laser. The cytometer was adjusted to fit the G1/G0 peak of chicken red blood cells on channel 250 (Bickham et al ., 1994). DNA content was estimated as the ratio of X divided by the mean channel number of the G1/G0 peak for the animal tested, multiplied by 2.54 (pg DNA) over channel 250 for the chicken red‐blood cell standard (Fisher et al ., 1994).…”
We assessed genome size variation by flow cytometry within and among 31 species of nine families of African and South American hystricognath rodents. Interspecific variation was extensive and genome size was relatively high among the South American radiation whereas only moderate variation and smaller estimates of genome size were observed in the African counterparts. The largest genome size, indicating tetraploidy was recorded in the South American octodontid, Tympanoctomys barrerae (16.8 pg DNA). This quantum shift in DNA content represents a novel mechanism of genome evolution in mammals. As expected in polyploid organisms, varying nucleotypic effects were observed in the dimensions of the sperm cells and lymphocytes of T. barrerae. The role of control mechanisms that influence cell dimensions in polyploid organisms is discussed.
“…FCM was used to estimate DNA content variation within red blood cells (RBC) of both European pond turtles (Emys orbicularis) and Caspian turtles (Mauremys caspica). This method has been shown to be an effective biomarker of chromosomal damage, caused by a variety of contaminants including PAHs, radionuclides, and some pesticides, in many wildlife studies McBee and Bickham, 1988;Dallas and Evans, 1990;George et al, 1991;Lamb et al, 1991Lamb et al, , 1995Bickham et al, 1992Bickham et al, , 1994Custer et al, 1994;Lingenfelser et al, 1997aLingenfelser et al, , 1997bLowcock et al, 1997;Theodorakis et al, 2001;Matson et al, in press). Of more importance to this study is the fact that flow cytometry data tend to correlate well with petroleum products and PAHs in particular (Bickham et al, 1998a;Custer et al, 2000).…”
The Caspian region and specifically the Apsheron peninsula of Azerbaijan are known to be polluted with a variety of environmental contaminants. These complex mixtures of contaminants make risk assessment difficult. We used the flow cytometry method (FCM) and the micronucleus assay (MN) to assess chromosomal damage in aquatic turtles (Emys orbicularis, the European pond turtle; and Mauremys caspica, the Caspian turtle) inhabiting contaminated wetlands in Azerbaijan. Evidence of genetic damage was found for two sites, Neftchala and Sumgayit, relative to a reference site, Ali Bairamly. Sediment samples from each site were analyzed for PAHs and mercury to evaluate potential contaminant associations with genetic damage. A significant positive correlation was documented between three-ring PAH sediment concentrations and FCM estimates of chromosomal damage in E. orbicularis. These data combine to show that the contaminated wetlands in Sumgayit and Neftchala are genotoxic and that three-ring PAHs are likely a significant influence on observed genotoxicity.
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