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At least 19 recordsLinked to original sources
PubMed1977

Effects of reducing DDT usage on total DDT storage in humans.

Agricultural uses of the insecticide DDT were cancelled by the U.S. Environmental Protection Agency December 31, 1972. However, the domestic use of DDT had begun to decline before this action. Beginning July 1969, residues of DDT and its metabolites were measured in human adipose tissue collected through an annual national survey. Levels of total DDT equivalent residues in human adipose have decreased slightly, but the frequencies of finding DDT or its metabolites have remained high. The most marked decline in residue concentration has been found in the youngest age group (0-14 years). Approximately 80 percent of the total DDT equivalent found in this survey was DDE. These data show that the reduction of the agricultural uses of DDT has decreased human exposure to and storage of this chemical.

Adipose Tissue↗
PubMed1979

Residues of DDT in a Norwegian fruitgrowing district two and four years after the termination of DDT usage.

This study describes the extent of DDT contamination in a typical fruit growing district in Norway two and four years after the DDT ban. Residues of DDT in man, dairy cows and soil were about five to one hundred times higher than in the control groups, while residues found in samples from the marine biota were the same or moderately higher (Figure 3). The residues of DDT in cows, gulls and parts of the marine samples showed a significant decrease from 1972 to 1974, while the level in soil was almost constant. The amount of DDE had increased considerably in 1974 for all the species except for the gull, although not to the same degree. The distribution of DDE, DDD and DDT in soil were almost constant during the two years of sampling.

Adipose Tissue↗
PubMed1975

DDT and immunological responses. 3. Reduced anaphylaxis and mast cell population in rats fed DDT.

Previous work showed that anaphylaxis, mast cell population, and tissue histamine content are reduced in guinea pigs given DDT injections. This study was intended to determine whether dietary intake of DDT causes similar effects. Rats immunized with diphtheria toxoid and fed diets containing DDT at 20 and 200 ppm levels for 31 days did not show effects on their serum antitoxin titers, but the numbers of metachromatically stained, histamine-containing mast cells in mesenteries were reduced: in the 20 ppm group by 46% and in the 200 ppm group by 61%. The severity of anaphylactic shock was also reduced in proportion to the DDT dietary levels, and, thus, the magnitude of mast cells. Apparently, daily dietary DDT intake above 2.2 mg DDT/kg of body weight alters the physiology of mast cells in the rat, and thus affects histamine-mediated reactions.

Anaphylaxis↗
PubMed1978

DDT residues in rainwater in New Brunswick and estimate of aerial transport of DDT into the Gulf of St. Lawrence, 1967-68.

Residues of DDT were detected in 76 of 101 samples of rainwater collected during spring and summer at several sites in the Province of New Brunswick in 1967 and 1968, and at one site in the Magdalen Islands, Quebec, in 1968. The dominant residue was p,p'-DDT. Levels of DDT and metabolites combined ranged from less than 0.01 to 1.33 microgram/kg. Levels of DDT and metabolites in the pollen of four species of forest trees in New Brunswick ranged from 0.544 to 1.01 mg/kg; such contaminated pollen possibly contributed to residues in rainwater. Residue data for rainwater from two sites were used to estimate the amount of DDT aerially transported into the Gulf of St. Lawrence during July to October 1968.

Chromatography, Gas↗
PubMed1975

Dieldrin and DDT in the tissues of mice fed aldrin and DDT for seven generations.

Seven-Generation Study (P-F6): The concentration and total retention of dieldrin or p,p'-DDT and metabolites were determined in the total carcass of Swiss-Webster mice fed dietary supplements of aldrin 5 or 10 ppm, or DDT 100 ppm, to age 260 days. All groups showed a significant increase in total body retention (and concentration) of dieldrin or total DDT in the total carcass of the F1, F2, and F3 generations. Generally, these increases were related directly to increases in total body lipids, when compared with the P generations. The control (pesticide-free) diet was fed to all F4 generation experimental mice from weaning to age 260. The pesticides absorbed by these animals while in utero and via lactation were found, at the time of sacrifice, to have been excreted completely. When the experimental diets were resumed with the weanlings of the F2 generations, a repetition of the general findings in the P and F1 generations was noted-demonstrating that pesticide retention and total body lipids are closely interrelated, and that a high body lipid content favors a high retention rate of these fat-soluble pesticides. These results support our earlier studies in rats (Deichmann et al., 1972) and investigations with cirrhotic human livers with severe fatty infiltration (Oloffs et al., 1974). Conception became more delayed with each succeeding generation, requiring some degree of "selective" breeding of the F4, F5, and F6 generations.

Adipose Tissue↗
PubMed1976

DDT: the degradation of ring-labeled 14C-DDT to 14CO2 in the rat.

Ring fission of p, p'-DDT was studied in the rat following a single oral dose of 0.74 mg/kg (1.04 muCi) of uniformly ring-labeled 14C-DDT. Expired air was passed through a solution of ethanolamine-ethylene glycol monomethyl ether (1:2) to trap 14CO2. A total of 1.6% of the radioactivity administered was recovered in the expired air collected continually for 10 days, indicating that while degradation of the phenyl moiety is not a major route of p,p'-DDT metabolism in the rat, it is equal to the urinary excretion. Nevertheless, these results represent the most radical change accomplished in vivo of a residual insecticide yet reported in mammals.

Animals↗
PubMed1978

Residues of polychlorinated biphenyls, DDT, and DDT metabolites in Pennsylvania streams, community water supplies, and reservoirs, 1974--76.

Pennsylvania streams, community water supplies, and open water reservoirs were analyzed for PCB mixtures, DDT, and DDT metabolites. Streams were sampled in 1974 and again in 1975. Only 4 of 19 stream locations were contaminated. Maximum concentrations in community supplies of Aroclor 1242 (2 locations), Aroclor 1254 (3 locations), and sigmaDDT (2 locations) were 350, 260, and 620 ng/kg, respectively. Of the 110 community water supplies sampled in 1975 and 1976, only 7 contained residues. Maximum concentrations in community supplies of Aroclor 1242 (4 locations) and sigmaDDT (2 locations) were 460 ng/kg and 75 ng/kg, respectively. The seventh contained 0.7 ng/kg of dieldrin. None of the three open water reservoirs contained detectable residues of the compounds of interest. Essentially no correlation was found between PCB and DDT analogs in streams and those in fish from streams which had been samples at similar locations in a related study in 1976.

Chromatography, Gas↗
PubMed1976

[Comparative effects of intravitellin injections of p, p'-DDT and of commercial DDT on the germ cells of embryonic gonads of birds].

The p, p'-DDT present in the composition of commercial DDT, is responsible for the germ deficit in the gonads of bird embryos. Administered into the vitellus or on the shell, before incubation, the pesticide exerts the same reduction of the Quail germ population. While, for the Chick, the germ decrease is less significant after injection than after immersion.

Animals↗